Cyanobacterial Harmful Algal Blooms An Increasing Risk to ...Cyanobacterial Harmful Algal Blooms An...

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Ken Hudnell, PhD US EPA, Office of Research and Development, National Health and Environmental Effects Research Laboratory, Neurotoxicology Division California and Oregon Workshops on Cyanobacterial Blooms in the Klamath River, November 8&9, 2005 Cyanobacterial Harmful Algal Blooms An Increasing Risk to Human Health & Ecosystem Sustainability

Transcript of Cyanobacterial Harmful Algal Blooms An Increasing Risk to ...Cyanobacterial Harmful Algal Blooms An...

Page 1: Cyanobacterial Harmful Algal Blooms An Increasing Risk to ...Cyanobacterial Harmful Algal Blooms An Increasing Risk to Human Health & Ecosystem Sustainability ORD Research Center,

Ken Hudnell, PhD

US EPA, Office of Research and Development, National Health and Environmental Effects Research Laboratory, Neurotoxicology Division

California and Oregon Workshops on Cyanobacterial Blooms in the Klamath River, November 8&9, 2005

Cyanobacterial Harmful Algal Blooms

An Increasing Risk to Human Health& Ecosystem Sustainability

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ORD Research Center, RTP, NC

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0

200

400

600

800

1000

1200

1960

-196

419

65-1

969

1970

-197

419

74-1

979

1980

-198

419

85-1

989

1989

-199

419

95-1

999

2000

-200

4

Number of Articles Cited in CHAB Search 1960Number of Articles Cited in CHAB Search 1960--20042004

Wayne Carmichael

Cyanobacterial Harmful Algal Blooms(CHABS): Recent Area of Science

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The Discipline of CyanoHABsThe Discipline of CyanoHABsThe Discipline of CyanoHABs• 1980. First International Conference On Toxic

Cyanobacteria. Proceedings entitled: “The Water Environment Algal Toxins and Health”. Plenum Press, 1981 (ed. by WW Carmichael).

• 1993. Bath, UK; 1995. Bornholm, DK.

• 1998. 4th ICTC. Beaufort, NC, USA.

• 2001. 5th ICTC. Noosa, Queensland, AUS.

• 2004. 6th ICTC. Bergen, Norway.

• 2005. ISOC-HAB. 1st Government Symposium

• 1980. First International Conference On Toxic Cyanobacteria. Proceedings entitled: “The Water Environment Algal Toxins and Health”. Plenum Press, 1981 (ed. by WW Carmichael).

• 1993. Bath, UK; 1995. Bornholm, DK.

• 1998. 4th ICTC. Beaufort, NC, USA.

• 2001. 5th ICTC. Noosa, Queensland, AUS.

• 2004. 6th ICTC. Bergen, Norway.

• 2005. ISOC-HAB. 1st Government Symposium

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OverviewISOC-HAB: The Interagency, InternationalSymposium on Cyanobacterial HarmfulAlgal Blooms, September 6-10, 2005Legislative Drivers, Participants & ProductsTheoretical FrameworkCyanobacteria & their Toxins* Microcystin EffectsOccurrenceRisk AssessmentCauses, Prevention & MitigationFuture

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ISOC-HAB Legislative Drivers, Participants, Topics & Products

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Clean Water Act* EPA authority to regulate recreational waters

Safe Drinking Water Act* EPA authority to regulate drinking waters- Cyanobacteria & their toxins are on the CCL2

Harmful Algal Bloom and Hypoxia Research & Control (HABHRCA) Act Reauthorized & Expanded- Now Includes Freshwater Harmful Algal Blooms- Mandates Interagency Products on Cyanobacteria

ISOC-HAB Legislative Drivers

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ISOC-HAB Participants & TopicsEPA NOAA US Army Corps

Of Engineers

32 Member Organizing Committee - K. Hudnell, Lead

200+ Attendees, 94 Invited Participants, 25 Speakers* Speaker Charges - State of the Science

Six Main Session Topics & Workgroups* Workgroup Charges - Identify & Prioritize Research

• Causes, Prevention,Mitigation & Treatment

• Toxins• Effects

• Occurrence ofBlooms & Toxins

• Exposure Assessment• Risk Assessment

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ISOC-HAB Products

Monograph Published by Springer Press in the Series, Advances in Experimental Medicine & Biology, Spring, 2006. Presented to HABHRCA Task Force to Help Meet Mandates

• Synopsis - National Research Plan on CHABS

• 6 Workgroup Reports - Research Needs

• 25 Speaker Papers - State of the Science

• Multiple Poster Abstracts - Latest Research

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Theoretical Framework

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NATURALFORCES

HUMANACTIVITIES

Habitat Alteration &Environmental Pollutants

ECOSYSTEMSOcean Estuary Fresh Water Land

TOXIGENIC CYANOBACTERIA

Ecosystem Sustainability

Human Health

Theoretical Framework

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Cyanobacteria & their Toxins

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MicrocystisUnicellular, no heterocyst

Lyngbya, OscillatoriaFilamentous, no heterocyst

CylindrospermopsisAnabaena, Planktothrix, AphanizomenonFilamentous, heterocyst

Toxic Cyanobacteria GeneraToxic Cyanobacteria Genera~3.5 Billion Years OldProkaryotic, Asexual

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Anabaena, Aphanocapsa,Microcystis, Nostoc, Oscillatoria, Radiocystis, Hapalosiphon

Anabaena, Aphanizomenon,Oscillatoria

Anabaena, Oscillatoria

Aphanizomenon,Cylindrospermopsis, Umezakia

Anabaena, Aphanizomenon, Cylindrospermopsis, Lyngbya

Cyclic PeptidesMicrocystins

Alkaloids

Anatoxin-a

Anatoxin-a(s)

Cylindrospermopsin

SaxitoxinNeosaxitoxin

Many Genera Make the Same ToxinMany Genera Make Multiple Toxins

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Class MW SourceProteins 10,000- Culture/Extract/

100,000 PurifyCyanotoxins 50-500 Culture/Extract/

PurifyAlkaloid Toxins 150-300 SynthesizeChemical Weapons <50-300 Synthesize

Cyanotoxins are Highly PotentCompounds & LD50 (ug/kg)

Saxitoxin 9 Ricin 0.02Anatoxin-a(s) 20 Cobra toxin 20Microcystin LR 50 Curare 500Anatoxin-a 50 Strychnine 2000

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Many Cyanotoxins Unidentified

Crude Cell Extracts Always MoreToxic than Pure Toxin

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MS/MS analysis of Copco Sample 222-1MS/MS analysis of Copco Sample 222-1E:\Jeanette\...\Copco222-1MSMS 11/03/05 04:05:17 PM

RT: 5.00 - 20.00

6 8 10 12 14 16 18 20Time (min)

0

10

20

30

40

50

60

70

80

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Rel

ativ

e Ab

unda

nce

12.54995.48

12.87995.43

NL: 9.77E9Base Peak m/z= 995.0-996.0 F: + c ESI SIM ms [ 995.00-996.00] MS Copco222-1MSMSMCYST-LR

M+H=995

Wayne CarmichaelNovember, 3, 2005

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N N N

N[X]

NC

O O C

O

O

C

C

R1

C

C

C

R2

O

O

O N[Y]O

N

CH3

H3

H3

H3

H

OOH

H2

H3

OOH

H H

H

Microcystin

H H

1

2345

67

89

1011

1213

1415

16

17

1819

20D-Ala

(1)

(2)

D-Masp

(3)

(4)

(5)

ADDA

(6)

D-Glu

(7)

Mdha

Microcystis aeruginosa Microcystins

~80 analoguesLD50 (ip, mouse, 24hr): 50 μg/kgRequire active uptake by “bile acid transporter” –concentrates the toxinInhibit protein phosphatases 1 and 2ALoss of regulation of cytoskeleton, cell cycle, generalmetabolism, apoptosis

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Microcystins and Hepatotoxicity

Wayne Carmichael, Scientific American, January, 1994

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1931: USA, Illness in 5000-8000 people drinking water from Ohio & Potomac rivers during Microcystis Bloom(Veldee 1931, Tisdale 1931)

1959: Canada, Microcystis & Anabaena bloomrecreational water, animals and humans with multiple-system illness. Organisms isolated from physician’sstool sample (Dillenberg 1960)

1981: Australia, Microcystis in drinking water & elevatedliver enzymes (liver damage) in population (Falconer 1983)

1988: Brazil, Microcystis bloom in reservoir. 2000 GIillnesses over 42 Days, 88 Deaths (Teixeira 1993)

1989: England, 10 soldiers with severe illness afterswimming/canoeing in Microcystis Bloom (Turner 1990)

1994: Sweden, GI illness in 121/304, MC in drinking H20

Human Microcystin Poisonings

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•Epidemiology in China: •Contaminated drinking water ↔primary liver and colon cancer.

•Injection of toxin ± initiator: •Increased size/number of livercancer precursors.

•Oral M. aeruginosa. extract:•Skin papillomas larger/heavier. •No effect on duodenal tumoursor lymphoma.

Evidence for Tumor Promotion by Microcystins

Colon cancer precursors larger.

Andrew Humpage

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Jussi Meriluoto

Microcystin in Aquatic Environment

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Microcystin LR Inhibits Plant Growth

Jussi Meriluoto

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Occurrence

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Occurrence Worldwide

ISOC-HAB Occurrence Workgroup, Wayne Carmichael

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137

5590

107

Europe

South America

Australia

North America

Number of CHABS Reported by Continent

ISOC-HAB Occurrence Workgroup, Wayne Carmichael

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Occurrence North America

ISOC-HAB Occurrence Workgroup, Wayne Carmichael

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Occurrence Northwest US

ISOC-HAB Occurrence Workgroup, Wayne Carmichael

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NEBRASKA EXPERIENCECyanobacterial Harmful Algal Blooms

Steve Walker402-471-4227

Water Quality Assessment SectionNebraska Department of

Environmental Quality (NDEQ)(www.deq.state.ne.us)

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Buccaneer BayMay 4, 2004

• 2 dogs died after drinking water from buccaneer bay lake

• Lake had dense algae bloom• Investigated by NDEQ and water samples

collected • Microcystin toxin level in water measured at

69.4 ppb • Autopsy on dog revealed microcystin toxins in

lethal concentrationsSteve Walker

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Interagency Meetings• Nebraska Department of Environmental

Quality• Nebraska Game and Parks Commission• Nebraska Health and Human Services

System• University of Nebraska – Lincoln• County health departments • Natural resources districts

Steve Walker

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Cyanobacteria ProblemsQuickly Addressed

• Excellent cooperation and quick action among government entities in Nebraska

• Monitoring and public notification strategies developed within two weeks

• ELISA lab equipment ordered and set up within two weeks

Steve Walker

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ELISA Method forMicrocystin Analysis

Steve Walker

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Microcystin Analysis

Steve Walker

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Advantages of ELISA Method for Microcystin Analysis

• Semi-Quantitative Measure of Microcystin• Quick Turnaround Times• Relatively Easy Procedure• Relatively Inexpensive

Approximately $20/test• Accurate & Precise

MDL = 0.15 ppbGood Duplicate Results

Steve Walker

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Cost Savings Using ELISA Tests

• NDEQ700 Samples @ $20/Sample X 2 Dilutions = $28,000

• Contract LabCost per Microcystin HPLC or LC/MS Analysis = $150/Sample X 700 Samples = $105,000

• Savings$77,000

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Cyanobacteria Summary

• 700+ samples analyzed in 2004111 different lakes

• Health alerts (microcystins > 15 ppb)26 different lakes

• Health advisories (microcystins > 2 ppb)69 different lakes

• Longest health alert duration: Carter Lake - 15 weeks Swan Creek Lake (5A) - 14 weeks Pawnee Lake - 12 weeksIron Horse Trail Lake – 12 weeks

Steve Walker

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Health Alerts Issuedon 26 Lakes During 2004

Steve Walker

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Pawnee Lake near Emerald

Steve Walker

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PAWNEE LAKE

• Observed significant bloom at east swimming beach while collecting bacteria data 7/12/04

• Microcystin analysis > 15 ppb• Meeting with HHS and G&P• Signs mistakenly posted at only east beach.

People used the west beach and rest of lake• Following week > 50 reports of people sick

with cyanobacteria symptoms

Steve Walker

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Pawnee Lake near Emerald

Steve Walker

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Florida SurveyFlorida Survey19991999--20032003

John BurnsJohn Burns

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Microcystis DistributionMicrocystis Distribution

John Burns

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Microcystin YRMicrocystin YR--20002000

0

10

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30

40

50

Freq

uenc

y/Pr

eval

ence

(%)

0 0-0.1 0.1-1 1-10 10-100 >100

ug/L

n = 99max. = 107 ug/L

John Burns

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Microcystins in Drinking Microcystins in Drinking Water ResourcesWater Resources

0.1

1

10

ug/L

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15

Paired Samples

Raw Water SourceFinish Water

* Max. environmental value = 106 ug/L

Microcystins in DrinkingWater Resources - Florida

John Burns

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Exposure at the Tap?

Post Chloraminated Water @ WTPPost Chloraminated Water @ WTP

Home FiltersHome Filters

John Burns

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m-RR m-YR m-LR m-LA0

20

40

60

80

100

initial concentration, 5 μgL-1

30 minute contact time%

rem

oved

Analogue

wood coal

From: Gayle Newcombe, BrentonNicholson

Particulate Activated Carbon

Microcystins

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0

5

10

15

20

25

30

Dec-98 Jan-99 Feb-99 Mar-99 Apr-99 May-99 Jun-99 Jul-99 Aug-99 Sep-99 Oct-99 Nov-99 Dec-99

Num

ber

of M

orta

litie

s

0

50000

100000

150000

200000

Cel

ls/m

l.

Alligator mortalitiesCylindrospermopsis raciborsk ii

# A

lliga

tor M

orta

litie

sC

ylindrospermopsis C

ells/ml

Wildlife Death – St. John’sChain of Lakes in Florida

John Burns

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Risk Assessment

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What are Guidelines & MCLs?World Health Organization“….. A guideline value represents the

concentration of a constituent that does not result in any significant risk to the health of the consumer over a lifetime of consumption."

US Environmental Protection Agency“….. The recommended maximum contaminant

level must be set to prevent the occurrence of any known or anticipated health event."

Mike Burch

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Drinking Water GuidelinesMicrocystins

• WHO 1998 1 µg / L (LR)• Brazil 2000 1 µg / L (All, Reg)• France 2001 1 µg / L (LR)• Australia 2001 1.3 µg / L (LR Tox Eq)• Canada 2002 1.5 µg / L (LR Tox Eq)• New Zealand 2005 1 µg / L (LR Tox Eq)

Mike Burch

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Deriving the WHO Guideline for Microcystin LR

• Microcystin has been treated as a threshold toxicant – i.e. non-genotoxic, non-carcinogenic

• Tolerable Daily Intake (TDI) [i.e. Reference Dose (RfD] was calculated from NOAEL (40 µg/kg/day) in 13-week sub-chronic oral mouse dosing study with MC-LR

• Uncertainty Factors: x 10 intraspecies, x 10 interspecies, x 10 for limitations of data – lack of data on chronic toxicity and carcinogenicity = Total UF x 1000

• GV (MCL) = TDI x BW x Pintake = 0.04 x 60kg x 0.8 = 0.96Daily Consumption 2L ~ 1µg/L

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Recreational Water Guidelines

• WHO Level 1 20,000 Cells/L ~

Mike Burch

4 µg/L ~ 1/5 TDI/100mlLevel 2 100,000 Cells/L ~ 20 µg/L ~ TDI/100mlLevel 3 Surface Scum ~ >>>>>>>>> TDI/100ml

‘Immediate action to control scum contact’ (Chorus & Bartram, 1999)

• France Same as WHO• Australia Level 1 50,000 Cells/L ~ 10 µg/L, >4 mm3/L

Level 2 Biovolume > 10 mm3/L or Scum• Netherlands 1 Level 20 µg MCY-LR/L• Germany Level 1 <10 µg/L, Level 2 >10-<100 µg/L

Level 3 > 100 µg/L

Cells Microcystins or Tox Eq

Biovolume

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Causes, Prevention & Mitigation

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CHAB Control: CHAB Control: Physical, Chemical & Biotic Physical, Chemical & Biotic FactorsFactors

Microbial interactionsMicrobial interactions

Hans Paerl

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Nutrient IssuesNutrient Issues

N & P enrichments are stimulatoryN & P enrichments are stimulatory

N:P Input ratios are importantN:P Input ratios are important(N:P < 15 favors N(N:P < 15 favors N22 Fixers)Fixers)

Specific chemical forms of N Specific chemical forms of N (i.e. nitrate, ammonium, organic N) may (i.e. nitrate, ammonium, organic N) may

regulate algal community composition & toxicityregulate algal community composition & toxicity

Other nutrients (Fe, trace elements)?Other nutrients (Fe, trace elements)?Hans Paerl

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HydrodynamicsHydrodynamics

•• Turbulence/Vertical Mixing Turbulence/Vertical Mixing (Low turbulence conditions favor cyanobacteria, (Low turbulence conditions favor cyanobacteria,

especially Nespecially N2 2 fixers)fixers)

•• Water residence time/flushing Water residence time/flushing (long residence time favors cyanobacterial (long residence time favors cyanobacterial

dominance)dominance)

Hans PaerlHans Paerl

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spring ‘95 spring ‘96

Chesapeake Bay: Remotely sensed chl-a from SeaWiFS Aircraft Simulator (SAS II) during low flow

(’95) and high flow (’96) years

Chesapeake Bay: Remotely sensed chlChesapeake Bay: Remotely sensed chl--a from a from SeaWiFS Aircraft Simulator (SAS II) during low flow SeaWiFS Aircraft Simulator (SAS II) during low flow

((’’95) and high flow (95) and high flow (’’96) years96) years

Hans PaerlHans Paerl

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Climatic FactorsClimatic Factors•• TemperatureTemperature

(high temperature favors cyanobacteria) (high temperature favors cyanobacteria)

•• IrradianceIrradiance(high irradiance favors (high irradiance favors mostmost cyanobacteria)cyanobacteria)

Salinity•• Selects for specific taxa

Hans PaerlHans Paerl

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Average global surface temperatures from 1860-2000, showing deviation from the baseline 1961-1990

average temperature

Valeria Paul

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CHABS: Multi-Barrier ApproachTo Prevention & Mitigation

Clean, safe, reliable drinking water

Drinking water

Treatment

SourceWater

Protection

Drinking WaterDistribution

System

Public Involvementand Awareness

Legislativeand policy

frameworks

Research, science and technology

Guidelines, standards,

and objectives

Judy Westrick

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Mike Piehler

A.Partnerships -- Those people most affected by management decisions are involved throughout and shape key decisions.

B.Geographic Focus -- Activities are directed within specific geographic areas, typically the areas that drain to surface water bodies or that recharge or overlay ground waters or a combination of both.

C.Sound Management Techniques based on Strong Science and Data --

i.assessment and characterization of the natural resources and thecommunities that depend upon them; ii.goal setting and identification of environmental objectives based on the condition or vulnerability of resources and the needs of the aquatic ecosystem and the people within the community; iii.identification of priority problems; iv.development of specific management options and action plans; v.implementation; and vi.evaluation of effectiveness and revision of plans, as needed.

Watershed Approach

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UltimateDriver

ProximalDriver

StatusIndicator = f

CHABS e.g. nutrient concentrations

and/or flow regime

e.g. landuse

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C-HAB prevention

Watershed conservation, restorationand rehabilitation

•Terrestrial•Land-water margin•Aquatic•Atmospheric

Mike Piehler

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Recreational Water Treatment

• Watershed Management• Aeration• Alum addition• Electrocoagulation• Algicides• Harvesting

Judy Westrick

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Drinking Water Treatment• Treatment to remove extracellular algal toxins

OxidationBiologically active filtersPhysical removal

• Treatment to remove intracellular algal toxinsMembrane technologies• Micro and ultra

Conventional treatment• Coagulation/sedimentation/filtration• Dissolved air floatation

New technologies Judy Westrick

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Future

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ISOC-HAB ProductState of the Science* EPA - Sufficient for Regulatory Determination?

- Occurrence Data- Health Data- Management Options Available

* Yes - Risk Assessments- Produce Guidelines or Regulate

* No Research Priorities

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Research Priorities* Occurrence - If Methods Available, Implement Unregulated Contaminate Monitoring Rule

* Health - Dose-Response Data* Prevention & Mitigation - Watershed Management- Drinking Water Treatment- Education

National Research Plan* To CENR Task Force, to Congress* Interagency Implementation

ISOC-HAB Product

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Thank You