Draft National 304(a) Aluminum Aquatic Life Criteria
Diana EignorEcological Risk Assessment Branch
Health and Ecological Criteria DivisionOffice of Science and Technology
Office of Water US Environmental Protection Agency
bull Attendees who are members of the media can submit any questions to the press office Trisha Lynn (202) 564-2615
2
Overview
Background 2017 Recommended Criteria Status
3
Sources of Aluminumbull Aluminum is found in most rocks and
minerals and can enter the environment through natural weathering
bull Aluminumrsquos solubility increase under acidic (pH lt6) or basic (pH gt8) water conditions
bull Aluminum is actively mined from bauxite used in industrial processes and alum (potassium aluminum sulfate) is used in the clarification process at drinking water facilities 4
Current 1988 Aluminum Criteriabull The current 1988 criteria account for the
ndash Influence of pH on toxicity (solely by limiting criteria application range)
ndash Similarity of acute toxicity of fish and invertebrates
ndash The greater sensitivity of invertebrates in chronic toxicity tests
5
Current 1988 Aluminum Criteriabull The final 1988 criteria document recommended
ndash An acute criterion of 750 microgL total aluminum when the pH is between 65 and 90
ndash Chronic criterion of 87 microgL total aluminum when the pH is between 65 and 90
ndash The 1988 freshwater chronic criterion of 87 microgL was lowered based on two tests (brook trout and striped bass)
ndash The studies were not pH adjusted and all the data were not normalized for hardness The 1988 existing criteria did not take hardness and DOC into account
6
Aluminum Standardsbull Aluminum Standards
ndash About 20 states have numeric criteria for aluminum for aquatic life
bull Most are based on EPArsquos 1988 values and two are hardness-based equations (CO and NM)
bull There are numerous site-specific criteria that involve the Biotic Ligand Model (BLM) or a Water Effects Ratio (WER) -adjusted 1988 aluminum criteria
ndash Aluminum is not a priority pollutant
7
Criteria Development Processbull All EPA Aquatic Life Criteria for Toxics undergo rigorous
scientific development and review processbull Develop criteria document draftbull Intra-agency peer review process bull Independent external peer reviewbull Revisions based on external peer review
Intra-agency review of draft criteria documentbull Release to the public in draft form to obtain scientific views
Revisions considering public comments Intra-agency review of final criteria document
bull Publication of final criteria document bull States may then consider recommended criteria in
development and adoption of state water quality standards8
Framework for Updated Draft Aluminum Criteria
I Screen toxicological studies for high
quality data
II Consider water conditions effects on
aluminum bioavailability
III Normalize toxicity data in species
sensitivity distribution to a set of water quality conditions
IV Construct sensitivity distribution to determine criteria
at set conditions
9
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
bull Attendees who are members of the media can submit any questions to the press office Trisha Lynn (202) 564-2615
2
Overview
Background 2017 Recommended Criteria Status
3
Sources of Aluminumbull Aluminum is found in most rocks and
minerals and can enter the environment through natural weathering
bull Aluminumrsquos solubility increase under acidic (pH lt6) or basic (pH gt8) water conditions
bull Aluminum is actively mined from bauxite used in industrial processes and alum (potassium aluminum sulfate) is used in the clarification process at drinking water facilities 4
Current 1988 Aluminum Criteriabull The current 1988 criteria account for the
ndash Influence of pH on toxicity (solely by limiting criteria application range)
ndash Similarity of acute toxicity of fish and invertebrates
ndash The greater sensitivity of invertebrates in chronic toxicity tests
5
Current 1988 Aluminum Criteriabull The final 1988 criteria document recommended
ndash An acute criterion of 750 microgL total aluminum when the pH is between 65 and 90
ndash Chronic criterion of 87 microgL total aluminum when the pH is between 65 and 90
ndash The 1988 freshwater chronic criterion of 87 microgL was lowered based on two tests (brook trout and striped bass)
ndash The studies were not pH adjusted and all the data were not normalized for hardness The 1988 existing criteria did not take hardness and DOC into account
6
Aluminum Standardsbull Aluminum Standards
ndash About 20 states have numeric criteria for aluminum for aquatic life
bull Most are based on EPArsquos 1988 values and two are hardness-based equations (CO and NM)
bull There are numerous site-specific criteria that involve the Biotic Ligand Model (BLM) or a Water Effects Ratio (WER) -adjusted 1988 aluminum criteria
ndash Aluminum is not a priority pollutant
7
Criteria Development Processbull All EPA Aquatic Life Criteria for Toxics undergo rigorous
scientific development and review processbull Develop criteria document draftbull Intra-agency peer review process bull Independent external peer reviewbull Revisions based on external peer review
Intra-agency review of draft criteria documentbull Release to the public in draft form to obtain scientific views
Revisions considering public comments Intra-agency review of final criteria document
bull Publication of final criteria document bull States may then consider recommended criteria in
development and adoption of state water quality standards8
Framework for Updated Draft Aluminum Criteria
I Screen toxicological studies for high
quality data
II Consider water conditions effects on
aluminum bioavailability
III Normalize toxicity data in species
sensitivity distribution to a set of water quality conditions
IV Construct sensitivity distribution to determine criteria
at set conditions
9
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Overview
Background 2017 Recommended Criteria Status
3
Sources of Aluminumbull Aluminum is found in most rocks and
minerals and can enter the environment through natural weathering
bull Aluminumrsquos solubility increase under acidic (pH lt6) or basic (pH gt8) water conditions
bull Aluminum is actively mined from bauxite used in industrial processes and alum (potassium aluminum sulfate) is used in the clarification process at drinking water facilities 4
Current 1988 Aluminum Criteriabull The current 1988 criteria account for the
ndash Influence of pH on toxicity (solely by limiting criteria application range)
ndash Similarity of acute toxicity of fish and invertebrates
ndash The greater sensitivity of invertebrates in chronic toxicity tests
5
Current 1988 Aluminum Criteriabull The final 1988 criteria document recommended
ndash An acute criterion of 750 microgL total aluminum when the pH is between 65 and 90
ndash Chronic criterion of 87 microgL total aluminum when the pH is between 65 and 90
ndash The 1988 freshwater chronic criterion of 87 microgL was lowered based on two tests (brook trout and striped bass)
ndash The studies were not pH adjusted and all the data were not normalized for hardness The 1988 existing criteria did not take hardness and DOC into account
6
Aluminum Standardsbull Aluminum Standards
ndash About 20 states have numeric criteria for aluminum for aquatic life
bull Most are based on EPArsquos 1988 values and two are hardness-based equations (CO and NM)
bull There are numerous site-specific criteria that involve the Biotic Ligand Model (BLM) or a Water Effects Ratio (WER) -adjusted 1988 aluminum criteria
ndash Aluminum is not a priority pollutant
7
Criteria Development Processbull All EPA Aquatic Life Criteria for Toxics undergo rigorous
scientific development and review processbull Develop criteria document draftbull Intra-agency peer review process bull Independent external peer reviewbull Revisions based on external peer review
Intra-agency review of draft criteria documentbull Release to the public in draft form to obtain scientific views
Revisions considering public comments Intra-agency review of final criteria document
bull Publication of final criteria document bull States may then consider recommended criteria in
development and adoption of state water quality standards8
Framework for Updated Draft Aluminum Criteria
I Screen toxicological studies for high
quality data
II Consider water conditions effects on
aluminum bioavailability
III Normalize toxicity data in species
sensitivity distribution to a set of water quality conditions
IV Construct sensitivity distribution to determine criteria
at set conditions
9
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Sources of Aluminumbull Aluminum is found in most rocks and
minerals and can enter the environment through natural weathering
bull Aluminumrsquos solubility increase under acidic (pH lt6) or basic (pH gt8) water conditions
bull Aluminum is actively mined from bauxite used in industrial processes and alum (potassium aluminum sulfate) is used in the clarification process at drinking water facilities 4
Current 1988 Aluminum Criteriabull The current 1988 criteria account for the
ndash Influence of pH on toxicity (solely by limiting criteria application range)
ndash Similarity of acute toxicity of fish and invertebrates
ndash The greater sensitivity of invertebrates in chronic toxicity tests
5
Current 1988 Aluminum Criteriabull The final 1988 criteria document recommended
ndash An acute criterion of 750 microgL total aluminum when the pH is between 65 and 90
ndash Chronic criterion of 87 microgL total aluminum when the pH is between 65 and 90
ndash The 1988 freshwater chronic criterion of 87 microgL was lowered based on two tests (brook trout and striped bass)
ndash The studies were not pH adjusted and all the data were not normalized for hardness The 1988 existing criteria did not take hardness and DOC into account
6
Aluminum Standardsbull Aluminum Standards
ndash About 20 states have numeric criteria for aluminum for aquatic life
bull Most are based on EPArsquos 1988 values and two are hardness-based equations (CO and NM)
bull There are numerous site-specific criteria that involve the Biotic Ligand Model (BLM) or a Water Effects Ratio (WER) -adjusted 1988 aluminum criteria
ndash Aluminum is not a priority pollutant
7
Criteria Development Processbull All EPA Aquatic Life Criteria for Toxics undergo rigorous
scientific development and review processbull Develop criteria document draftbull Intra-agency peer review process bull Independent external peer reviewbull Revisions based on external peer review
Intra-agency review of draft criteria documentbull Release to the public in draft form to obtain scientific views
Revisions considering public comments Intra-agency review of final criteria document
bull Publication of final criteria document bull States may then consider recommended criteria in
development and adoption of state water quality standards8
Framework for Updated Draft Aluminum Criteria
I Screen toxicological studies for high
quality data
II Consider water conditions effects on
aluminum bioavailability
III Normalize toxicity data in species
sensitivity distribution to a set of water quality conditions
IV Construct sensitivity distribution to determine criteria
at set conditions
9
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Current 1988 Aluminum Criteriabull The current 1988 criteria account for the
ndash Influence of pH on toxicity (solely by limiting criteria application range)
ndash Similarity of acute toxicity of fish and invertebrates
ndash The greater sensitivity of invertebrates in chronic toxicity tests
5
Current 1988 Aluminum Criteriabull The final 1988 criteria document recommended
ndash An acute criterion of 750 microgL total aluminum when the pH is between 65 and 90
ndash Chronic criterion of 87 microgL total aluminum when the pH is between 65 and 90
ndash The 1988 freshwater chronic criterion of 87 microgL was lowered based on two tests (brook trout and striped bass)
ndash The studies were not pH adjusted and all the data were not normalized for hardness The 1988 existing criteria did not take hardness and DOC into account
6
Aluminum Standardsbull Aluminum Standards
ndash About 20 states have numeric criteria for aluminum for aquatic life
bull Most are based on EPArsquos 1988 values and two are hardness-based equations (CO and NM)
bull There are numerous site-specific criteria that involve the Biotic Ligand Model (BLM) or a Water Effects Ratio (WER) -adjusted 1988 aluminum criteria
ndash Aluminum is not a priority pollutant
7
Criteria Development Processbull All EPA Aquatic Life Criteria for Toxics undergo rigorous
scientific development and review processbull Develop criteria document draftbull Intra-agency peer review process bull Independent external peer reviewbull Revisions based on external peer review
Intra-agency review of draft criteria documentbull Release to the public in draft form to obtain scientific views
Revisions considering public comments Intra-agency review of final criteria document
bull Publication of final criteria document bull States may then consider recommended criteria in
development and adoption of state water quality standards8
Framework for Updated Draft Aluminum Criteria
I Screen toxicological studies for high
quality data
II Consider water conditions effects on
aluminum bioavailability
III Normalize toxicity data in species
sensitivity distribution to a set of water quality conditions
IV Construct sensitivity distribution to determine criteria
at set conditions
9
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Current 1988 Aluminum Criteriabull The final 1988 criteria document recommended
ndash An acute criterion of 750 microgL total aluminum when the pH is between 65 and 90
ndash Chronic criterion of 87 microgL total aluminum when the pH is between 65 and 90
ndash The 1988 freshwater chronic criterion of 87 microgL was lowered based on two tests (brook trout and striped bass)
ndash The studies were not pH adjusted and all the data were not normalized for hardness The 1988 existing criteria did not take hardness and DOC into account
6
Aluminum Standardsbull Aluminum Standards
ndash About 20 states have numeric criteria for aluminum for aquatic life
bull Most are based on EPArsquos 1988 values and two are hardness-based equations (CO and NM)
bull There are numerous site-specific criteria that involve the Biotic Ligand Model (BLM) or a Water Effects Ratio (WER) -adjusted 1988 aluminum criteria
ndash Aluminum is not a priority pollutant
7
Criteria Development Processbull All EPA Aquatic Life Criteria for Toxics undergo rigorous
scientific development and review processbull Develop criteria document draftbull Intra-agency peer review process bull Independent external peer reviewbull Revisions based on external peer review
Intra-agency review of draft criteria documentbull Release to the public in draft form to obtain scientific views
Revisions considering public comments Intra-agency review of final criteria document
bull Publication of final criteria document bull States may then consider recommended criteria in
development and adoption of state water quality standards8
Framework for Updated Draft Aluminum Criteria
I Screen toxicological studies for high
quality data
II Consider water conditions effects on
aluminum bioavailability
III Normalize toxicity data in species
sensitivity distribution to a set of water quality conditions
IV Construct sensitivity distribution to determine criteria
at set conditions
9
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Aluminum Standardsbull Aluminum Standards
ndash About 20 states have numeric criteria for aluminum for aquatic life
bull Most are based on EPArsquos 1988 values and two are hardness-based equations (CO and NM)
bull There are numerous site-specific criteria that involve the Biotic Ligand Model (BLM) or a Water Effects Ratio (WER) -adjusted 1988 aluminum criteria
ndash Aluminum is not a priority pollutant
7
Criteria Development Processbull All EPA Aquatic Life Criteria for Toxics undergo rigorous
scientific development and review processbull Develop criteria document draftbull Intra-agency peer review process bull Independent external peer reviewbull Revisions based on external peer review
Intra-agency review of draft criteria documentbull Release to the public in draft form to obtain scientific views
Revisions considering public comments Intra-agency review of final criteria document
bull Publication of final criteria document bull States may then consider recommended criteria in
development and adoption of state water quality standards8
Framework for Updated Draft Aluminum Criteria
I Screen toxicological studies for high
quality data
II Consider water conditions effects on
aluminum bioavailability
III Normalize toxicity data in species
sensitivity distribution to a set of water quality conditions
IV Construct sensitivity distribution to determine criteria
at set conditions
9
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Criteria Development Processbull All EPA Aquatic Life Criteria for Toxics undergo rigorous
scientific development and review processbull Develop criteria document draftbull Intra-agency peer review process bull Independent external peer reviewbull Revisions based on external peer review
Intra-agency review of draft criteria documentbull Release to the public in draft form to obtain scientific views
Revisions considering public comments Intra-agency review of final criteria document
bull Publication of final criteria document bull States may then consider recommended criteria in
development and adoption of state water quality standards8
Framework for Updated Draft Aluminum Criteria
I Screen toxicological studies for high
quality data
II Consider water conditions effects on
aluminum bioavailability
III Normalize toxicity data in species
sensitivity distribution to a set of water quality conditions
IV Construct sensitivity distribution to determine criteria
at set conditions
9
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Framework for Updated Draft Aluminum Criteria
I Screen toxicological studies for high
quality data
II Consider water conditions effects on
aluminum bioavailability
III Normalize toxicity data in species
sensitivity distribution to a set of water quality conditions
IV Construct sensitivity distribution to determine criteria
at set conditions
9
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
I Screen toxicological studies for high quality data
bull First step in all criteria developmentndash Data are evaluated based on the data quality objectives
outlined in the 1985 Guidelines methodology and other toxicity testing recommendations (ie EPA ASTM)
ndash High quality data are used quantitatively to develop criteria magnitudes
ndash Lower quality data are used qualitatively if appropriatendash Lowest quality data are considered unacceptable and not
usedbull Data are grouped into acute and chronic exposures
10
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Aluminum Toxicity Databull The updated freshwater aluminum criteria meets the
acute and chronic minimum data requirements outlined in EPArsquos 1985 Guidelines
InvertebrateSpecies
Fish Species
AmphibianSpecies
Total Genera
Acute1988 AWQC 8 7 - 142017 Draft AWQC 11 8 1 18
Chronic1988 AWQC 2 1 - 32017 Draft AWQC 7 4 - 11
11 1988 AWQC Chronic CCC based on two studies for the striped
bass and brook trout
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Aluminum Toxicity Data Freshwater mussels have been
suggested to be potentially sensitive to aluminum
EPA worked collaboratively with USGSrsquos Columbia Environmental Research Center (CERC) to have acute and chronic aluminum toxicity tests conducted with a unionid mussel (fatmucket Lampsilis siliquoidea) in water-only exposures to obtain additional data on invertebrates New data on amphipod (Hyalella azteca)
were collected to confirm laboratory conditions
12
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Aluminum Toxicity Data
13
bull New data and models examinedndash Data submitted to EU REACH program
bull New freshwater aluminum toxicity data generated by Oregon State University
bull 2016 BLM model provided by the European Aluminum Association
ndash Saltwater data provided by Australia bull Insufficient data to develop estuarinemarine acute or chronic
criteria at this timendash Multiple Linear Regression (MLR) model developed by
DeForest et al 2017bull DeForest DK KV Brix LM Tear and WJ Adams 2017 Multiple Linear Regression (MLR) models for predicting chronic aluminum
toxicity to freshwater aquatic organisms and developing water quality guidelines Environ Toxicol Chem (DOI101002etc3922)
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
14
Minimum Dataset For Freshwater Criteria Derivation
SALMONID SECONDFISHFAMILY
CHORDATA
PLANKTONICCRUSTACEAN
BENTHIC CRUSTACEAN
INSECT ROTIFERA ANNELIDA MOLLUSCA
OTHERINSECT ORMOLLUSCA
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
EstuarineMarine Minimum Data Requirements
15
Family Minimum Data Requirement EstuarineMarine
Acute(Phylum Family Genus)
Chronic(Phylum Family Genus)
Family in the phylum Chordata - -
Family in the phylum Chordata - -
Either the Mysidae or Penaeidae family - -
Family in a phylum other than Arthropoda or Chordata Mollusca Ostreidae Crassostrea -
Family in a phylum other than Chordata Annelida Nereididae Neanthes -
Family in a phylum other than Chordata Annelida Capitellidae Capitella -
Family in a phylum other than Chordata Annelida Ctenodrilidae Ctenodrilus -
Any other family Arthropoda Ameiridae Nitokra -
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
II Evaluate water quality conditions to determine applicability
bull Criteria are often based on one or more water quality conditions (eg hardness) that affect toxicity of the material to test organisms
bull Aluminum toxicity is highly dependent on the pH of the test waterndash The pH of test waters affects the amount and form
of aluminum that is bioavailable to test speciesndash Hardness and DOC (Dissolved Organic Carbon)
also influence the amount of aluminum that is bioavailable
16
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Multiple Bioavailability Modeling Approaches Underwent External Peer Review
17
bull Biotic Ligand Modelsbull Full aluminum BLM (2016 model version) ndash Temperature pH
Dissolved organic carbon (DOC) Major cations (calcium [Ca] magnesium [Mg] sodium [Na] and potassium [K]) Major anions (sulfate [SO4] and chloride [Cl]) Alkalinity and Sulfide
bull Simplified aluminum BLM - pH hardness DOC temperature
bull Multilinear Regression Equationsbull pH and Hardness
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Accounting for Effects of Water Chemistry on Bioavailability and Toxicity
bull Water quality criteria can be modified quantitatively when enough data are available to demonstrate that those conditions similarly affect the results with a variety of speciesndash High quality data in the draft aluminum document demonstrated
that pH DOC and hardness affected a variety of species in a similar way when exposed to aluminum concentrations
bull Recent publications by Cardwell et al (2017) and Gensemer et al (2017) summarized short-term aluminum chronic toxicity data across a range of DOC pH and hardness values for three species
18
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Multiple Linear Regression (MLR) Models to Account for Effects of Water Chemistry
bull MLR models were developed for each species (DeForest et al 2017)ndash 119862119862 119889119889119906119906119887119887119894119894119886119886 11986411986411986211986220=119890119890[minus41026+[0525timesln(119863119863119874119874119862119862)]+[2201timesln(ℎ119886119886119903119903119889119889)]+(11282times119901119901119867119867)minus(0633times1199011199011198671198672)minus[0264times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
ndash 119875119875 119901119901119903119903119900119900119898119898119890119890119897119897119886119886119904119904 11986411986411986211986220=119890119890[minus14029+[0503timesln(119863119863119874119874119862119862)]+[3443timesln(ℎ119886119886119903119903119889119889)]+(3131times119901119901119867119867)minus[0494times119901119901119867119867ln(ℎ119886119886119903119903119889119889)]]
bull These models were applied to both the acute and chronic aluminum toxicity datandash The C dubia model was applied to invertebrate datandash The P promelas model was applied to vertebrate data
19
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
III Normalize toxicity data in species sensitivity distribution to a set of water
quality conditionsbull Just like single parameter hardness models the MLR
models were used to normalize the aluminum toxicity data to a single set of water quality conditionsndash As an illustration for one set of calculations the draft
aluminum AWQC set these conditions to pH 7 hardness of 100 mgL and DOC of 1 mgL
bull This allows for comparisons to be made between species based on their sensitivity to aluminumndash Apples to apples
20
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
IV Construct sensitivity distribution to determine criteria at set conditions
21
Figure 8 Ranked Summary of Total Aluminum Genus Mean Acute Values (GMAVs) - Freshwater at pH 7 Hardness of 100 mgL and DOC of 1 mgL
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
IV Construct sensitivity distribution to determine criteria at set conditions
22
Figure 10 Ranked Summary of Total Aluminum Genus Mean Chronic Values (GMCVs) ndash Freshwater Supplemented with Other Data to Fulfill Missing MDRs at pH 7 Hardness of 100 mgL and DOC of 1 mgL
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Aluminum Criteria Calculatorbull The relative ranking of genera in the sensitivity
distribution to which the toxicity data are normalized will change based on the set of water chemistry conditions (ie pH hardness and DOC)
bull To make calculating aluminum criteria easier EPA developed an Aluminum Criteria Calculatorndash Automated so that user only needs to enter water chemistry
conditions of interestndash Allows quick calculations for a variety of conditionsndash Limits calculations to the recommended conditions for which
the MLR models were developed were specified for hardness and DOC
bull No extrapolation beyond hardness and DOC empirical data bounds
23
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Aluminum Criteria Calculator SD Example
24
pH=7 Hardness=100 DOC=1 pH=6 Hardness=25 DOC=1
Chronic Ranked GMCVRank GMCV Genus
12 17098 Aeolosoma Invert11 gt 9746 Rana Amphib - Other Data10 5908 Chironomus Invert
9 4877 Lymnaea Mollusk8 2555 Brachionus Invert7 2488 Pimephales Fish6 1713 Hyalella Invert5 1182 Ceriodaphnia Invert4 1102 Danio Fish3 1042 Lampsilis Mollusk2 591 Salvelinus Fish1 509 Salmo Fish
FCV = 3940 microgL total aluminum
Chronic Ranked GMCVRank GMCV Genus
12 gt 2131 Rana Amphib - Other Data11 1710 Aeolosoma Invert10 591 Chironomus Invert
9 544 Pimephales Fish8 488 Lymnaea Mollusk7 255 Brachionus Invert6 241 Danio Fish5 171 Hyalella Invert4 129 Salvelinus Fish3 118 Ceriodaphnia Invert2 111 Salmo Fish1 104 Lampsilis Mollusk
FCV = 987 microgL total aluminum
Run Scenarios
Run Scenarios
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 1710 | 1710 | 1710 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 255 | 255 | 255 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 488 | 488 | 488 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 104 | 104 | 104 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 190 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 272 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 110 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 80 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 89 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 56 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 106 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 101 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 136 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 116 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 176 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 110 | 118 | 118 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 101 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 289 | 171 | 171 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 119 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 2258 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 766 | 591 | 591 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 1112 | 1112 | 1112 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 59 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 283 | 1293 | 1293 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 781 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 379 | 544 | 544 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 241 | 241 | 241 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 2131 | gt | 2131 | 2131 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 4843 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 2699 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 2404 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 5034 | 3546 | 3546 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 2983 | gt | 2983 | 2983 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 173 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 129 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 243 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 111 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 250 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 289 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 500 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 761 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 336 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 169 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 709 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 1007 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 162 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 367 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 473 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 429 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 419 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 796 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 2076 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 1163 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 1516 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 861 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 315 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 316 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 85 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 482 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 4357 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 2379 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 634 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 1039 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 908 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 1246 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 633 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 792 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 4880 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 713 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 590 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 1212 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 810 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 1014 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 555 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 619 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 270 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 188 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 604 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 624 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 253 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 693 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 24 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 380 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 737 | 509 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 201 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 5531 | 1054 | 733 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 338 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 2030 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 287 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 227 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 92 | 333 | 333 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 1022 | 1022 | 1022 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 1217 | 1217 | 1217 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 2800 | gt | 2800 | 2800 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 2050 | gt | 2050 | 2050 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 2536 | 2536 | 2536 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 6232 | gt | 6232 | 6232 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 1256 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 1140 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 1489 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 1676 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 260 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 333 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 701 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 777 | 801 | 801 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 4602 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 531 | 1564 | 1564 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 6947 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 6209 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 2988 | 5051 | 5051 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 5255 | gt | 5255 | 5255 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | gt | 8620 | 8620 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 4707 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 2837 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 104 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 1191 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 2398 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 7839 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 8620 | 2224 | 2224 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 859 | 859 | 859 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 4377 | gt | 4377 | 4377 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 6 | FAV | 360 | ||||||||||||||||||||||||||||||||
Hardness | 25 | CMC | 180 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 99 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 8620 | Hybognathus | Fish | 12 | gt | 2131 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
17 | gt | 6232 | Paratanytarsus | Invert | 11 | 1710 | Aeolosoma | Invert | |||||||||||||||||||||||||||
16 | gt | 5255 | Lepomis | Fish | 10 | 591 | Chironomus | Invert | |||||||||||||||||||||||||||
15 | 5051 | Salvelinus | Fish | 9 | 544 | Pimephales | Fish | ||||||||||||||||||||||||||||
14 | gt | 4377 | Hyla | Amphibian | 8 | 488 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
13 | 3546 | Physa | Mollusk | 7 | 255 | Brachionus | Invert | ||||||||||||||||||||||||||||
12 | gt | 2983 | Lampsilis | Mollusk | 6 | 241 | Danio | Fish | |||||||||||||||||||||||||||
11 | gt | 2800 | Hyalella | Invert | 5 | 171 | Hyalella | Invert | |||||||||||||||||||||||||||
10 | 2536 | Chironomus | Invert | 4 | 129 | Salvelinus | Fish | ||||||||||||||||||||||||||||
9 | 2224 | Pimephales | Fish | 3 | 118 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
8 | gt | 2050 | Acroneuria | Invert | 2 | 111 | Salmo | Fish | |||||||||||||||||||||||||||
7 | 1564 | Salmo | Fish | 1 | 104 | Lampsilis | Mollusk | ||||||||||||||||||||||||||||
6 | 1217 | Crangonyx | Invert | ||||||||||||||||||||||||||||||||
5 | 1022 | Stenocypris | Invert | ||||||||||||||||||||||||||||||||
4 | 859 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
3 | 801 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
2 | 733 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
1 | 333 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Micropterus | 859 | 676 | 4564 | 0211 | 0459 | 12 | 4 | Salvelinus | 129 | 486 | 2364 | 0308 | 0555 | ||||||||||||||||||||
3 | Oncorhynchus | 801 | 669 | 4469 | 0158 | 0397 | 3 | Ceriodaphnia | 118 | 477 | 2277 | 0231 | 0480 | ||||||||||||||||||||||
2 | Ceriodaphnia | 733 | 660 | 4352 | 0105 | 0324 | 2 | Salmo | 111 | 471 | 2220 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 333 | 581 | 3374 | 0053 | 0229 | 1 | Lampsilis | 104 | 465 | 2159 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 2585 | 1676 | 0526 | 141 | Sum | 1899 | 902 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1987 | S2 = | 059 | ||||||||||||||||||||||||||||||||
L = | 4890 | L = | 4420 | ||||||||||||||||||||||||||||||||
A = | 5887 | A = | 4592 | ||||||||||||||||||||||||||||||||
FAV = | 360 | FCV = | 987 | ||||||||||||||||||||||||||||||||
CMC = | 180 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Appendix C Acceptable Chronic Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||
MLR equation | ||||||||||||||||||||||||||||||||||
Species | Hardness (mgL as CaCO3) | pH | DOC(mgL) | EC20 Endpoint | EC20(microgL) | Normalized Conc- EC20(microgL) | SMCV-EC20(microgL) | GMCV-EC20(microgL) | Genus | DOC Notes | Dilution water | |||||||||||||||||||||||
Oligochaete Aeolosoma sp | 48 | 6 | 025 | Reproduction (population size) | 1235 | 17098 | 17098 | 17098 | Aeolosoma | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Rotifer Brachionus calyciflorus | 100 | 62 | 025 | Reproduction (population size) | 431 | 2555 | 2555 | 2555 | Brachionus | Invert | Author reported half the detection limit | |||||||||||||||||||||||
Great pond snail Lymnaea stagnalis | 117 | 61 | 025 | Biomass | 746 | 4877 | 4877 | 4877 | Lymnaea | Mollusk | Author reported half the detection limit | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | 1055 | 604 | 040 | Biomass | 169 | 1042 | 1042 | 1042 | Lampsilis | Mollusk | Author reported | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 50 | 715 | 11 | Reproduction - youngstarting adult | 1780 | 1898 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 26 | 73 | 05 | Reproduction - youngfemale | 1557 | 2718 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 46 | 75 | 05 | Reproduction - youngfemale | 8087 | 1102 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 96 | 79 | 05 | Reproduction - youngfemale | 6519 | 796 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 194 | 81 | 05 | Reproduction - youngfemale | 6836 | 888 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 703 | 05 | Reproduction (youngfemale) | 250 | 563 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 713 | 05 | Reproduction (youngfemale) | 860 | 1061 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 25 | 798 | 05 | Reproduction (youngfemale) | 700 | 1006 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 61 | 803 | 05 | Reproduction (youngfemale) | 1010 | 1363 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 122 | 810 | 05 | Reproduction (youngfemale) | 870 | 1164 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 255 | 633 | 05 | Reproduction (youngfemale) | 260 | 1758 | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | 121 | 636 | 05 | Reproduction (youngfemale) | 390 | 1101 | 1182 | 1182 | Ceriodaphnia | Invert | Author reported | |||||||||||||||||||||||
Amphipod Hyalella azteca | 95 | 61 | 051 | Biomass (28 d) | 1993 | 1014 | Hyalella | Author reported | ||||||||||||||||||||||||||
Amphipod Hyalella azteca | 106 | 604 | 033 | Biomass (28 d) | 425 | 2895 | 1713 | 1713 | Hyalella | Invert | Author reported | |||||||||||||||||||||||
Midge Chironomus riparius | 118 | 558 | 18 | Adult midge emergence | 2955 | 1192 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 119 | 505 | 18 | Adult midge emergence | 8442 | 22578 | Chironomus | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | |||||||||||||||||||||||||
Midge Chironomus riparius | 91 | 66 | 051 | Reproduction ( of eggscase) | 3387 | 7664 | 5908 | 5908 | Chironomus | Invert | Author reported | |||||||||||||||||||||||
Atlantic salmon Salmo salar | 127 | 57 | 18 | Biomass | 6156 | 5085 | 5085 | 5085 | Salmo | Fish | Based on Cleveland et al 1989 reported values at a similar pH | wellRO mix | ||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 123 | 655 | 19 | Biomass | 1644 | 270 | Salvelinus | Author reported | wellRO mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | 128 | 565 | 18 | Biomass | 1435 | 1295 | 5914 | 5914 | Salvelinus | Fish | Author reported | wellRO mix | ||||||||||||||||||||||
Fathead minnow Pimephales promelas | 220 | 770 | 16 | Biomass | 6194 | 3569 | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | well water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | 96 | 620 | 025 | Fry survival | 4286 | 1734 | 2488 | 2488 | Pimephales | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Zebrafish Danio rerio | 83 | 61 | 025 | Biomass | 2344 | 1102 | 1102 | 1102 | Danio | Fish | Author reported half the detection limit | |||||||||||||||||||||||
Wood frog Rana sylvatica | 115 | 469 | 16 | MATC-survival | gt | 2000 | gt | 9746 | gt | 9746 | 9746 | gt | Rana | Amphib - Other Data | Value is from 2007 FW Cu AWQC Appendix C recommendation | aged tap water | ||||||||||||||||||
Appendix A Acceptable Acute Toxicity Data of Aluminum to Freshwater Aquatic Animals | ||||||||||||||||||||||||||||||||||||
Species | Methoda | Hardness (mgL as CaCO3) | pH | DOC(mgL) | LC50 or EC50 Conc (microgL) | Reference | Normalized Conc - LC50(microgL) | Species Mean Acute Value(microgL) | Genus Mean Acute Value(microgL) | Genus | DOC Note | Dilution water | ||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 659 | 11 | gt | 23400 | Call 1984 Call et al 1984 | gt | 48425 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 755 | 11 | 30600 | Call 1984 Call et al 1984 | 26986 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 817 | 11 | gt | 24700 | Call 1984 Call et al 1984 | gt | 24040 | - | Physa | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Snail Physa sp | S M T | 474 | 746 | 11 | 55500 | Call 1984 Call et al 1984 | 50338 | 35462 | 35462 | Physa | Mollusk | Value is from 2007 FW Cu AWQC Appendix C recommendation | Raw Lake Superior water | |||||||||||||||||||||||
Fatmucket Lampsilis siliquoidea | F M T | 1060 | 612 | 048 | gt | 6302 | Wang et al 2016 Wang et al 2017 | gt | 29834 | gt | 29834 | 29834 | gt | Lampsilis | Mollusk | Author reported | ||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 742 | 11 | 1900 | McCauley et al 1986 | 1728 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 505 | 786 | 11 | 1500 | McCauley et al 1986 | 1294 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | UW-S Lake Superior lab water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M A | 500 | 813 | 11 | 2560 | McCauley et al 1986 | 2431 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 26 | 75 | 05 | 720 | ENSR 1992d | 1113 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 46 | 76 | 05 | 1880 | ENSR 1992d | 2495 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | R M T | 96 | 78 | 05 | 2450 | ENSR 1992d | 2894 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 3727 | Fort and Stover 1995 | 5002 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 90 | 715 | 05 | 5673 | Fort and Stover 1995 | 7613 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U NR | 89 | 76 | 05 | 2880 | Soucek et al 2001 | 3362 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Mod Hard Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 7112 | European Al Association 2009 | 1691 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 605 | 2 | 6865 | European Al Association 2009 | 7088 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 609 | 4 | 15581 | European Al Association 2009 | 10072 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 601 | 05 | 681 | European Al Association 2009 | 1620 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 603 | 05 | 1630 | European Al Association 2009 | 3674 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 597 | 05 | 1785 | European Al Association 2009 | 4732 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 592 | 05 | 1410 | European Al Association 2009 | 4295 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 699 | 05 | gt | 1300 | European Al Association 2009 | gt | 4189 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 785 | 05 | gt | 5000 | European Al Association 2009 | gt | 7960 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 68 | 2 | gt | 10000 | European Al Association 2009 | gt | 20755 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 782 | 2 | gt | 15000 | European Al Association 2009 | gt | 11626 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 677 | 4 | gt | 10000 | European Al Association 2009 | gt | 15161 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 766 | 4 | gt | 15000 | European Al Association 2009 | gt | 8608 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 79 | 05 | gt | 2000 | European Al Association 2009 | gt | 3150 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 106 | 789 | 05 | gt | 2000 | European Al Association 2009 | gt | 3156 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 604 | 05 | 1108 | European Al Association 2009 | 850 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 598 | 2 | 11371 | European Al Association 2009 | 4817 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 573 | 4 | 80467 | European Al Association 2009 | 43570 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 671 | 05 | gt | 10000 | European Al Association 2009 | gt | 23786 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 783 | 05 | gt | 5000 | European Al Association 2009 | gt | 6344 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 679 | 2 | gt | 10000 | European Al Association 2009 | gt | 10394 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 767 | 2 | gt | 15000 | European Al Association 2009 | gt | 9082 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 668 | 4 | gt | 15000 | European Al Association 2009 | gt | 12461 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 60 | 762 | 4 | gt | 15000 | European Al Association 2009 | gt | 6332 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 606 | 2 | 33868 | European Al Association 2009 | 7920 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 56 | 4 | 104842 | European Al Association 2009 | 48800 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 693 | 05 | gt | 5000 | European Al Association 2009 | gt | 7126 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 788 | 05 | gt | 5000 | European Al Association 2009 | gt | 5898 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 676 | 2 | gt | 15000 | European Al Association 2009 | gt | 12117 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 771 | 2 | gt | 15000 | European Al Association 2009 | gt | 8096 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 66 | 4 | gt | 15000 | European Al Association 2009 | gt | 10139 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S U T | 120 | 76 | 4 | gt | 15000 | European Al Association 2009 | gt | 5545 | - | Ceriodaphnia | Author reported | ||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11971 | European Al Association 2010 | 2699 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 27478 | European Al Association 2010 | 6194 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 603 | 05 | 11998 | European Al Association 2010 | 2705 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 607 | 05 | 92495 | European Al Association 2010 | 1876 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 609 | 05 | 31337 | European Al Association 2010 | 6035 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 61 | 05 | 33235 | European Al Association 2010 | 6238 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 708 | 05 | gt | 8864 | European Al Association 2010 | gt | 2534 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 779 | 05 | gt | 42783 | European Al Association 2010 | gt | 6930 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 106 | 753 | 05 | 13204 | European Al Association 2010 | 244 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 601 | 05 | 46326 | European Al Association 2010 | 3798 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia dubia | S M T | 600 | 599 | 05 | gt | 8590 | European Al Association 2010 | gt | 7366 | 5094 | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 451 | 60 | 11 | 304 | Shephard 1983 | 2009 | - | Ceriodaphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Ceriodaphnia reticulata | F M T | 40 | 55 | 11 | 362 | Shephard 1983 | 55307 | 10542 | 7328 | Ceriodaphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake SuperiorDI Mix | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U NR | 453 | 774 | 11 | 3900 | Biesinger and Christensen 1972 | 3382 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S M T | 220 | 76 | 16 | 38200 | Kimball 1978 | 20303 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Well water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 451 | 725 | 11 | 2800 | Shephard 1983 | 2868 | - | Daphnia | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 599 | 05 | 5000 | European Al Association 2009 | gt | 2265 | - | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Cladoceran Daphnia magna | S U T | 168 | 792 | 05 | 7950 | European Al Association 2009 | 920 | 3332 | 3332 | Daphnia | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon | |||||||||||||||||||||||
Ostracod Stenocypris major | R M T | 1563 | 651 | 16 | 310196 | Shuhaimi-Othman et al 2011a | 10216 | 10216 | 10216 | Stenocypris | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Malaysia) | |||||||||||||||||||||||
Amphipod Crangonyx pseudogracilis | R U T | 50 | 675 | 16 | 9190 | Martin and Holdich 1986 | 12174 | 12174 | 12174 | Crangonyx | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (UK) | |||||||||||||||||||||||
Amphipod Hyalella azteca | F M T | 105 | 613 | 048 | gt | 5997 | Wang et al 2016 Wang et al 2017 | gt | 28002 | gt | 28002 | 28002 | gt | Hyalella | Invert | Author reported | ||||||||||||||||||||
Stonefly Acroneuria sp | S M T | 474 | 746 | 11 | gt | 22600 | Call et al 1984 | gt | 20498 | gt | 20498 | 20498 | gt | Acroneuria | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Midge Chironomus plumosus | S U T | 80 | 70 | 16 | 30000 | Fargasova 2001 | 25361 | 25361 | 25361 | Chironomus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | tap water (Slovakia) | |||||||||||||||||||||||
Midge Paratanytarsus dissimilis | S M T | 1743 | 728 | 28 | gt | 77700 | Lamb and Bailey 1981 1983 | gt | 62318 | gt | 62318 | 62318 | gt | Paratanytarsus | Invert | Value is from 2007 FW Cu AWQC Appendix C recommendation | Liberty Lake Washington | |||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 274 | 758 | 05 | gt | 9840 | Gundersen et al 1994 | gt | 5745 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 452 | 762 | 05 | gt | 8070 | Gundersen et al 1994 | gt | 5212 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 895 | 758 | 05 | gt | 8160 | Gundersen et al 1994 | gt | 6807 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1304 | 758 | 05 | gt | 8200 | Gundersen et al 1994 | gt | 7662 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 232 | 825 | 05 | 6170 | Gundersen et al 1994 | 1190 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 350 | 826 | 05 | 6170 | Gundersen et al 1994 | 1523 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 836 | 829 | 05 | 7670 | Gundersen et al 1994 | 3205 | - | Oncorhynchus | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||||
Rainbow trout Oncorhynchus mykiss | F M T | 1158 | 830 | 05 | 6930 | Gundersen et al 1994 | 3554 | 3661 | 3661 | Oncorhynchus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | RO treated well water then added salts | |||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 55 | 05 | 584 | Hamilton and Haines 1995 | 21042 | - | Salmo | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||||
Atlantic salmon Salmo salar | S U T | 68 | 65 | 05 | 599 | Hamilton and Haines 1995 | 2430 | 7151 | 7151 | Salmo | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Soft recon | |||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 40 | 56 | 16 | 6530 | Tandjung 1982 | 31767 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 18 | 56 | 16 | 3400 | Tandjung 1982 | 28391 | - | Salvelinus | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||||
Brook trout Salvelinus fontinalis | S U T | 2 | 56 | 16 | 370 | Tandjung 1982 | 13663 | 23097 | 23097 | Salvelinus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green sunfish Lepomis cyanellus | S M T | 474 | 755 | 11 | gt | 50000 | Call et al 1984 | gt | 24028 | gt | 24028 | 24028 | gt | Lepomis | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||
Rio Grande silvery minnow Hybognathus amarus | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | gt | 39414 | 39414 | gt | Hybognathus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 761 | 11 | gt | 48200 | Call et al 1984 | gt | 21522 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | S M T | 474 | 805 | 11 | gt | 49800 | Call et al 1984 | gt | 12972 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lake Superior water | |||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 26 | 78 | 05 | 1160 | ENSR 1992c | 477 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 46 | 76 | 05 | 8180 | ENSR 1992c | 5446 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 96 | 81 | 05 | 20300 | ENSR 1992c | 10966 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 194 | 81 | 05 | 44800 | ENSR 1992c | 35847 | - | Pimephales | Value is from 2007 FW Cu AWQC Appendix C recommendation | Lab Recon water | |||||||||||||||||||||||||
Fathead minnow Pimephales promelas | R M T | 140 | 81 | 05 | gt | 59100 | Buhl 2002 | gt | 39414 | 10168 | 10168 | Pimephales | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | Recon water | |||||||||||||||||||||
Smallmouth bass Micropterus dolomieui | S M T | 1245 | 505 | 16 | 130 | Kane and Rabeni 1987 | 3929 | 3929 | 3929 | Micropterus | Fish | Value is from 2007 FW Cu AWQC Appendix C recommendation | well waterDI mix | |||||||||||||||||||||||
Green tree frog Hyla cinerea | R M T | 455 | 549 | 05 | gt | 4052 | Jung and Jagoe 1995 | gt | 20016 | gt | 20016 | 20016 | gt | Hyla | Amphibian | Value is from 2007 FW Cu AWQC Appendix C recommendation | artificial soft recon | |||||||||||||||||||
Normalization Chemistry | |||||||||||||||||||||||||||||||||||
pH | 7 | FAV | 2741 | ||||||||||||||||||||||||||||||||
Hardness | 100 | CMC | 1400 | ||||||||||||||||||||||||||||||||
DOC | 1 | CCC | 390 | ||||||||||||||||||||||||||||||||
Acute Ranked GMAV | Chronic Ranked GMCV | ||||||||||||||||||||||||||||||||||
Rank | GMAV | Genus | Rank | GMCV | Genus | ||||||||||||||||||||||||||||||
18 | gt | 62318 | Paratanytarsus | Invert | 12 | 17098 | Aeolosoma | Invert | |||||||||||||||||||||||||||
17 | gt | 39414 | Hybognathus | Fish | 11 | gt | 9746 | Rana | Amphib - Other Data | ||||||||||||||||||||||||||
16 | 35462 | Physa | Mollusk | 10 | 5908 | Chironomus | Invert | ||||||||||||||||||||||||||||
15 | gt | 29834 | Lampsilis | Mollusk | 9 | 4877 | Lymnaea | Mollusk | |||||||||||||||||||||||||||
14 | gt | 28002 | Hyalella | Invert | 8 | 2555 | Brachionus | Invert | |||||||||||||||||||||||||||
13 | 25361 | Chironomus | Invert | 7 | 2488 | Pimephales | Fish | ||||||||||||||||||||||||||||
12 | gt | 24028 | Lepomis | Fish | 6 | 1713 | Hyalella | Invert | |||||||||||||||||||||||||||
11 | 23097 | Salvelinus | Fish | 5 | 1182 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||
10 | gt | 20498 | Acroneuria | Invert | 4 | 1102 | Danio | Fish | |||||||||||||||||||||||||||
9 | gt | 20016 | Hyla | Amphibian | 3 | 1042 | Lampsilis | Mollusk | |||||||||||||||||||||||||||
8 | 12174 | Crangonyx | Invert | 2 | 591 | Salvelinus | Fish | ||||||||||||||||||||||||||||
7 | 10216 | Stenocypris | Invert | 1 | 509 | Salmo | Fish | ||||||||||||||||||||||||||||
6 | 10168 | Pimephales | Fish | ||||||||||||||||||||||||||||||||
5 | 7328 | Ceriodaphnia | Invert | ||||||||||||||||||||||||||||||||
4 | 7151 | Salmo | Fish | ||||||||||||||||||||||||||||||||
3 | 3929 | Micropterus | Fish | ||||||||||||||||||||||||||||||||
2 | 3661 | Oncorhynchus | Fish | ||||||||||||||||||||||||||||||||
1 | 3332 | Daphnia | Invert | ||||||||||||||||||||||||||||||||
N | Rank | Genus | GMAV | ln(GMAV) | ln(GMAV)2 | P=R(N+1) | sqrt(P) | N | Rank | Genus | GMCV | ln(GMCV) | ln(GMCV)2 | P=R(N+1) | sqrt(P) | ||||||||||||||||||||
18 | 4 | Salmo | 7151 | 887 | 7876 | 0211 | 0459 | 12 | 4 | Danio | 1102 | 700 | 4907 | 0308 | 0555 | ||||||||||||||||||||
3 | Micropterus | 3929 | 828 | 6849 | 0158 | 0397 | 3 | Lampsilis | 1042 | 695 | 4829 | 0231 | 0480 | ||||||||||||||||||||||
2 | Oncorhynchus | 3661 | 821 | 6733 | 0105 | 0324 | 2 | Salvelinus | 591 | 638 | 4074 | 0154 | 0392 | ||||||||||||||||||||||
1 | Daphnia | 3332 | 811 | 6579 | 0053 | 0229 | 1 | Salmo | 509 | 623 | 3883 | 0077 | 0277 | ||||||||||||||||||||||
Sum | 3347 | 2804 | 0526 | 141 | Sum | 2657 | 1769 | 0769 | 170 | ||||||||||||||||||||||||||
S2 = | 1223 | S2 = | 1080 | ||||||||||||||||||||||||||||||||
L = | 7134 | L = | 5242 | ||||||||||||||||||||||||||||||||
A = | 7916 | A = | 5976 | ||||||||||||||||||||||||||||||||
FAV = | 2741 | FCV = | 3940 | ||||||||||||||||||||||||||||||||
CMC = | 1371 |
All concentrations reported are microgL total Aluminum | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
lt-----Click Button after entering data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
ENTER DATA HERE | ERRORNUM | ACUTE | CHRONIC | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
Rank 1 | Rank 2 | Rank 3 | Rank 4 | Rank 1 | Rank 2 | Rank 3 | Rank 4 | |||||||||||||||||||||||||||||||||||||||||||||||||||
SiteName | DOC(mgL) | Hardness(mgL as CaCO3) | pH | FAV | CMC | CCC | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMAV | Genus | GMCV | Genus | GMCV | Genus | GMCV | Genus | GMCV | ||||||||||||||||||||||||||||||||||||
Site 1 | 50 | 25 | 9 | 75428737034162 | 35229324666008 | 1800 | 770 | Daphnia | 33452 | Ceriodaphnia | 73576 | Stenocypris | 102576 | Crangonyx | 122230 | Lampsilis | 10463 | Ceriodaphnia | 11865 | Hyalella | 17200 | Brachionus | 25648 | |||||||||||||||||||||||||||||||||||
Site 2 | 50 | 50 | 9 | 75428737034162 | 31204991509063 | 1600 | 680 | Daphnia | 29631 | Ceriodaphnia | 65171 | Stenocypris | 90859 | Crangonyx | 108267 | Lampsilis | 9268 | Ceriodaphnia | 10510 | Hyalella | 15236 | Brachionus | 22718 | |||||||||||||||||||||||||||||||||||
Site 3 | 50 | 75 | 9 | 75428737034162 | 29067527928199 | 1500 | 640 | Daphnia | 27601 | Ceriodaphnia | 60707 | Stenocypris | 84635 | Crangonyx | 100851 | Lampsilis | 8633 | Ceriodaphnia | 9790 | Hyalella | 14192 | Brachionus | 21162 | |||||||||||||||||||||||||||||||||||
Site 4 | 50 | 100 | 9 | 75428737034162 | 27640367912592 | 1400 | 600 | Daphnia | 26246 | Ceriodaphnia | 57726 | Stenocypris | 80480 | Crangonyx | 95899 | Lampsilis | 8209 | Ceriodaphnia | 9309 | Hyalella | 13495 | Brachionus | 20123 | |||||||||||||||||||||||||||||||||||
Site 5 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 6 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 7 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 8 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 9 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 10 | 50 | 150 | 9 | 75428737034162 | 25747072099401 | 1300 | 560 | Daphnia | 24448 | Ceriodaphnia | 53772 | Stenocypris | 74967 | Crangonyx | 89330 | Lampsilis | 7647 | Ceriodaphnia | 8672 | Hyalella | 12571 | Brachionus | 18745 | |||||||||||||||||||||||||||||||||||
Site 11 | 50 | 25 | 85 | 75428737034162 | 63245275664384 | 3200 | 1400 | Daphnia | 60055 | Ceriodaphnia | 132086 | Stenocypris | 184149 | Crangonyx | 219432 | Lampsilis | 18783 | Ceriodaphnia | 21301 | Hyalella | 30879 | Brachionus | 46045 | |||||||||||||||||||||||||||||||||||
Site 12 | 50 | 50 | 85 | 75428737034162 | 61388044609926 | 3100 | 1300 | Daphnia | 58291 | Ceriodaphnia | 128208 | Stenocypris | 178742 | Crangonyx | 212988 | Lampsilis | 18232 | Ceriodaphnia | 20676 | Hyalella | 29972 | Brachionus | 44693 | |||||||||||||||||||||||||||||||||||
Site 13 | 50 | 75 | 85 | 75428737034162 | 60327020429132 | 3000 | 1300 | Daphnia | 57284 | Ceriodaphnia | 125992 | Stenocypris | 175652 | Crangonyx | 209307 | Lampsilis | 17917 | Ceriodaphnia | 20318 | Hyalella | 29454 | Brachionus | 43920 | |||||||||||||||||||||||||||||||||||
Site 14 | 50 | 100 | 85 | 75428737034162 | 59585352130146 | 3000 | 1300 | Daphnia | 56580 | Ceriodaphnia | 124443 | Stenocypris | 173493 | Crangonyx | 206734 | Lampsilis | 17696 | Ceriodaphnia | 20068 | Hyalella | 29092 | Salmo | 41264 | |||||||||||||||||||||||||||||||||||
Site 15 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 16 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 17 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 18 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 19 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 | |||||||||||||||||||||||||||||||||||
Site 20 | 50 | 150 | 85 | 75428737034162 | 58555485487011 | 2900 | 1500 | Daphnia | 55602 | Ceriodaphnia | 122292 | Stenocypris | 170494 | Crangonyx | 203161 | Lampsilis | 17391 | Ceriodaphnia | 19722 | Hyalella | 28589 | Salmo | 30370 |
Boundaries of the Criteria Outputsbull MLR models were developed using data that
encompassndash DOC range of 008-5 mgLndash Hardness range of 98-127 mgL (as CaCO3)ndash pH range of 6-81
bull MLR criteria outputs are bounded atndash Maximum of 150 mgL total hardness (as CaCO3)
ndash DOC of 50 mgLndash pH range of the model is 50 to 90
25
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Aluminum Criteria Look-Up Tables
26
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=05 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 23 a 14 b 69 c 160 f 350 f 620 i 540 b 410 a 230 a
50 43 a 24 b 100 d 170 f 310 f 630 f 670 j 400 a 200 a
75 61 a 33 b 130 e 180 f 290 f 530 f 730 i 390 a 190 a
100 78 a 41 b 150 e 190 f 280 g 460 f 770 c 390 a 180 a
150 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
200 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
250 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
300 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
350 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
400 11 a 55 b 180 f 200 g 270 h 390 g 650 f 430 b 170 a
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Aluminum Criteria Look-Up Tables
27
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=10 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 33 a 21 b 99 c 220 f 490 f 900 i 780 b 590 a 330 a
50 61 a 35 b 150 e 250 f 440 f 890 f 960 j 580 a 290 a
75 88 a 47 b 180 e 260 f 410 f 740 f 1100 i 570 a 270 a
100 11 a 59 b 210 e 270 f 390 g 650 f 1100 c 560 b 260 a
150 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
200 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
250 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
300 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
350 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
400 16 a 80 b 250 f 280 g 380 h 540 g 910 f 620 b 240 a
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Aluminum Criteria Look-Up Tables
28
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=25 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 54 a 34 b 160 c 350 f 770 f 1500 i 1300 b 960 a 540 a
50 99 a 57 b 230 e 390 f 690 f 1400 f 1600 j 930 a 470 a
75 14 a 77 b 290 e 410 f 640 f 1200 f 1700 i 920 a 440 a
100 18 a 96 b 330 e 420 f 620 g 1000 f 1800 d 920 b 420 a
150 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
200 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
250 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
300 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
350 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
400 26 a 130 b 390 f 450 g 590 h 860 g 1400 f 1000 b 390 a
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Aluminum Criteria Look-Up Tables
29
bull EPA also provided criteria look-up tables in Appendix K
Har
dnes
s
CCC(microgL total aluminum)
(DOC=50 mgL)
pH 50 pH 55 pH 60 pH 65 pH 70 pH 75 pH 80 pH 85 pH 90
25 77 a 49 b 230 c 500 f 1100 f 2100 c 1900 b 1400 a 770 a
50 14 a 82 b 330 e 540 f 970 f 2000 f 2200 j 1300 a 680 a
75 20 a 110 b 410 e 570 f 900 f 1600 f 2500 i 1300 a 640 a
100 26 a 140 b 460 f 590 f 880 g 1400 f 2500 d 1300 b 600 a
150 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
200 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
250 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
300 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
350 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
400 38 a 190 b 550 f 630 g 840 h 1200 g 2000 f 1500 b 560 a
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Status
30
bull Draft Document Released to the Federal Register on 72817ndash Public comment period of 60 days ndash Due Date for Comments is 92617
bull Revisions will be made considering public commentsbull Subsequent EPA intra-agency review of final criteria
document will then be conducted bull Publication of final criteria document planned for Late Fall
2017
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Federal Register Webpagehttpswwwfederalregistergovdocuments201
707282017-15968request-for-scientific-views-draft-updated-aquatic-life-ambient-water-quality-criteria-for-aluminum
Aluminum Criteria Webpagehttpswwwepagovwqc2017-draft-aquatic-life-
criteria-aluminum-freshwater-documents
31
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
Contact Information
Aluminum Criteria Lead Diana EignorEignorDianaepagov
202-566-1143
Kathryn Gallagher Branch Chiefgallagherkathrynepagov
202-564-1398 32
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