Treatment of Heavy Metals in Soil and Groundwater Using Iron … · • Chemistry: Solubility and...
Transcript of Treatment of Heavy Metals in Soil and Groundwater Using Iron … · • Chemistry: Solubility and...
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Treatment of Heavy Metals in Soil and Groundwater Using Iron and Reactive
Minerals 15 September – 2016
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Today’s Webinar: Aims
Will examine the reduction, adsorption, and precipitation of heavy metals in groundwater by reagents based on elemental iron, iron sulphides and related reactive minerals.
Key topics include:
– Review of metals treatment terminology;
– Review of relevant chemistry;
– Performance data from independent testing & full scale results.
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Today’s Webinar: Speakers
Alan Seech – a scientist with 25 years experience in soil chemistry, microbiology, and environmental remediation. His focus has been on development of technologies for treatment of soil, sediment, and groundwater containing hard to degrade organics, such as PAHs, pesticides, and organic explosive compounds.
Mike Mueller – PeroxyChem’s Business Development Manager in EMEA - responsible for their Soil & Groundwater Remediation technologies portfolio. Based in Austria, he has been working in this region for over 6 years, initially with Adventus (which was acquired by FMC Corporation), now known as PeroxyChem.
Chair – Ian Grant – Brownfield Briefing Managing Editor
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Questions
Please submit questions during the webinar using your chat box.
If you have any unanswered questions please submit them to the Brownfield Briefing LinkedIn group, following the webinar.
http://brownfieldbriefing.com/li
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Treatment of Heavy Metals in Soil & Groundwater
using Elemental Iron and Reactive Minerals
1. PeroxyChem Environmental Solutions 2. Alan Seech Ph.D., California USA
3. Mike Mueller MBA, Innsbruck Austria
Brownfield Briefing Webinar Series 15 S t b 2016
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Presentation Outline
• Background: History, definitions, MetaFix® reagent composition, features, dosage, and application methods
• Chemistry: Solubility and stability of heavy metal hydroxides vs. heavy metal sulfides vs. heavy metal iron oxyhydroxides
• Removal mechanisms for major heavy metals
• A detailed look at Chromium
• Bench-scale Tests: some results from comparisons of MetaFix® and other reagents, mixed metals, and metals with cVOCs
• Case Studies: Soil and Groundwater Treatment
• Questions & Answers
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ZVI Reduction of Inorganics: Some History Elemental Metals in Chemical Reduction Processes
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More Recently for Organics
Use of Elemental Metals for Environmental Remediation
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And then for Heavy Metals
• Treatment of heavy metals and other inorganic contaminants by reductive precipitation and adsorption
• Various materials including ZVI, pyrite, organic carbon, gypsum
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MetaFix® Reagents
MetaFix® is a family of injectable reagents designed to treat heavy metals in soil and groundwater using chemical reduction, precipitation, and adsorption. Reagents do not rely on in situ biological sulfate reduction or carbon
metabolism -- so their performance is not inhibited by high toxicity (e.g., alkalinity, acidity, salts, high COI concentrations)
Composed of iron-bearing reducing agents
Treatment results in conversion of aqueous heavy metals to low solubility mineral precipitates with broad pH stability
Adsorption on iron corrosion products is also important
Custom formulations for unusual site conditions
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Low Dosage Rates: 0.5% - 4.0% (w/w) for soil 0.1% - 1.0% (w/w) for groundwater
Application by soil mixing, trenching, or injection
(40% – 50% solids) aqueous suspension Low cost treatability testing (£1,800) to
determine dosage and enable bespoke formulation
MetaFix® Reagents
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Metal
Precipitation as Metal
Hydroxides or Iron Metal
Oxyhydroxides
Precipitation as Metal
Sulfides/Iron Metal
Sulfides
Adsorption and Co-
precipitation with Iron Corrosion Products
Precipitation as Metal
Carbonates
Adsorption of organo-
metal species
As (III, V) ● ● ●
Cr(VI) ● ●
Pb, Cd, Ni ● ● ● ● ●
Cu, Zn ● ● ●
Se ● ● ●
Hg ● ● ●
MetaFix® Mechanisms
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Fe0.75Cr0.25(OH)3
EPA 625/8-80-003, 1980; Banerjee et al., 2013. Veolia Water Inc. Environ. Sci. Technol. 1988, 22, 972-977
Aqueous Solubility & Stability of Heavy Metals as Hydroxides, Iron Oxyhdroxides, and Sulfides
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14 EPA 625/8-80-003, 1980
Heavy Metal Precipitates: Sulfides, Carbonates, and Hydroxides
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Chromium Reduction by FeS
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Adsorption on Iron Corrosion Products
From Dick Brown, ERM Ewing NJ
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Cr(VI) Reduction Sulfide vs. Sulfide + Iron Oxyhydroxide
Kim et al., 2007. Geochemical Journal. 41: 397-405.
Mechanism: Free sulfide ion reduced to elemental sulfur on goethite surface promotes formation of ferrous iron which reduces hexavalent chromium to precipitated trivalent form as shown in TEM image.
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Iron-based Chromium Treatment
• Reduction of Cr+6 to Cr+3 by ZVI is followed by its precipitation as mixed Fe-Cr oxyhydroxides with a mineral structure similar to that of goethite (α-FeOOH), with some Cr+3 also deposited into a hematite-like structure (Fe2O3).1,2
• Solubility of Fe-Cr oxyhydroxides is <0.05 µg/L over a broad pH range (5.0 - 12.0)3
• The Fe-Cr oxide which has the form of hematite (Fe2O3) is primarily deposited on the surface of precipitates2
1. Blowes et al., 2000. J. Contam. Hydrol. 45: 123-137 2. Tratnyek et al., 2003. In: Tarr, M. Chemical Degradation Methods for Wastes and Pollutants 3. Eary and Rai. 1988. Env. Sci. Technol. 22:972-977.
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19 Rai et al., 1989. Sci. Tot. Env. 86:15-23.
Solubility of Mixed Fe-Cr Oxyhydroxides
Reduction of Cr(VI) to Cr(III) by Fe+2 is rapid (minutes) and the main product is a mixed Fe-Cr oxyhydroxide. Precipitates with more Fe/less Cr have lower solubility but all are much less soluble than Cr(OH)3 and have solubility well below most remedial standards for groundwater. The free energy of formation for Fe-Cr oxyhydroxide is lower than that for Cr(OH)3, so it will be preferentially formed when free Fe+2 is available.
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20 Independent Test Results from Professor D. Cassidy, WMU. , D. Gray AECOM. 2014
Performance of MetaFix® and calcium polysulfide in treatment of Cr and Ni in soil/groundwater slurry
79.3
31.9
13.4 12.1 11.4 6.4 4.1
8.4 3.3 2.1
0
10
20
30
40
50
60
70
80
90
Cr Ni
SPLP
Con
cent
ratio
ns, m
g/L
Reagent Dosing, wt/wt% and pH after 20 Days of Treatment
Control (20 day pH 6.4) CaPS 1.5% (20 day pH 8.2)MetaFix 1.0% (20 day pH 6.6) CaPS 7.3% (20 day pH 9.4)MetaFix 5.0% (20 day pH 6.5)
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21 Batch study, 10.0 g soil + 200 mL groundwater, 7 days incubation,
Influence of EHC® Metals and MetaFix® on TCLP lead and arsenic (US Site)
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22 Confidential Client, Independent Laboratory
Mixed Metal/cVOC Plumes
Table 1. Influence of control and treatment on heavy metal concentrations.
Biotic Control
MetaFix® I-6
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23 Confidential Client, Independent Laboratory
Mixed Metal/cVOC Plumes
Table 1. Influence of control and treatment on VOC concentrations in microcosms.
Biotic Control
MetaFix® I-6
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Case Study 1 Ex-situ treatment of Lead-impacted industrial process waste.
TCLP lead reduced from 11.7 mg/L to 0.22 mg/L.
• Direct soil mixing with excavator
• Reagent dosage at 6.0 % w/w
• Soil water content set to 80% of WHC (wet, not saturated)
• 7 day treatment time
• Earlier attempts at treatment with FeSO4 and fly ash at 40% w/w were ineffective
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• Site: Manufacturing facility, Oregon USA
• Consultant: Maul, Foster and Alongi
• COCs: Mixed heavy metals including Al, As, Cd, Cr, Cu, Pb, Hg and Ni; High pH
• Treatment: Excavation of source area soil combined with 80 ft (25 m) long MetaFix PRB to prevent migration of any residual impacts into adjacent river
• Application: Reagent mixed into backfill to cover down-gradient wall of excavation
and form PRB
Case Study 2 PRB for Treatment of Mixed Heavy Metals
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Influence of pH on Aluminium Solubility
Soluble species of Aluminium • Solubility sharply influenced by
aqueous pH
• At low pH a trivalent cationic form exists, but as pH moves toward neutral protons are lost, and charge falls from +3 to +2 to +1 and on to neutral
• As pH moves alkaline solubility of the neutral form Al(OH)3 increases
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Phase I: Screening of three different MetaFix formulations at two dose rates of 4 and 8% by soil mass
Bench Scale Treatability Study: Phase I, Reagent Screening
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• Phase II: MetaFix I-3F selected for further evaluation and tested at three lower dosages of 1, 2 and 3 % by soil mass to refine dosing requirements
• Results from the two studies indicate that a 4.0% (w/w) dosage was as effective as
the higher 8.0% dosage. In addition, based on the results of the 2nd study, concluded that dosage of 4.0% would be somewhat more effective than a 3.0% dose, and substantially more effective than either the 1.0% or 2.0% dosages.
Bench Scale Treatability Study: Phase II – Dosage Evaluation
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• Impacted soil was excavated down to 18 ft (5.5 m) bgs and removed
• MetaFix PRB was installed along sheet piling at the downgradient wall of excavation, in conjunction with backfilling the excavation with clean soil
• PRB Dimensions: 80 ft long x 3 ft wide x 15 ft thick (from 5 to 20 ft bgs) • MetaFix Target Dosage in Soil: 6% by soil mass
• MetaFix Mass: 24,000 lbs (12 x 1 tonne supersacks)
PRB Design and Implementation
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Site Map
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MetaFix Blended into Soil using Backhoe
MetaFix applied in 1.25 ft (0.4 m) lifts with one supersack per lift, and then blended into soil using backhoe
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Early Results
1
10
100
1000
10000
Tota
l met
als (
ug/L
)
MW-02
Al As Cu
• Post installation monitoring data available from ~3 and 4 months after PRB installation
• Small post installation increase presumably attributable to physical mobilisation of metals
pH Eh (mV)
DO (mg/L)
Cond. (µS/cm)
Baseline 10.24 -62 0.88 1,800 3 months 9.83 -47 0.09 6,360 4 months 9.8 9.6 0.91 7,061
PRB installation
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Case Study 3 Mercury Treatment to Non-Detect Levels at
Former Industrial Site
• Mercuric chloride was used as a catalyst in chemical synthesis at this former chemical plant
• Soil Hg concentrations in the contaminated area ranged from 300 to 420 mg/kg.
• Remedial goal: stabilise the soil and then dispose treated material at an offsite landfill; the land will be developed for residential use.
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• Results from the treatability study indicated the optimum MetaFix formation
could be applied at a dosage rate as low as 0.5% (w/w) to achieve the RG (<1.0
µg/L ) of SPLP Hg.
Mercury Treatment to 0.1 µg/L SPLP at a Former Industrial Site
Control MetaFix 0.5%
(wt/wt) MetaFix 1.0%
(wt/wt)
Moisture (%) 18.3 18.5 20.0
pH 8.6 8.0 7.9
Total Hg (mg/kg)
315 293 314
SPLP Hg (µg/L)
35.1 <1.0 <1.0
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A pilot study was conducted in four treatment cells:
• MetaFix applied at 0.5,% 1.0,% and 2.0% (w/w)
~ 50 - 100 m3 batches
• Reagent spread on soil and mixed with an excavator
• Further mixing with a screening bucket
• Water added to adjust the moisture content close to the saturation level while the soil was mixed with an excavator bucket
• Final mixing was completed with the screening bucket to assure homogeneity
• Soil was covered to react anaerobically for 7 days
0.117 0.1308 0.0911 0.0732
0.0001
0.001
0.01
0.1
1
0.5% 0.5% 1% 2%Hg S
PLP
Conc
entr
atio
ns (µ
g/L)
MetaFix Dosage (w/w)
Baseline MetaFix
ND
ND
ND
ND
• Hg was treated to non-detect levels of <1.0 µg/L
Mercury Treatment to Non-Detect Levels at a Former Industrial Site
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• The MetaFix dosage of 0.5% w/w selected for
the full scale treatment.
• Full scale implementation utilises an
integrated soil mixing system where soil
crushing/screening and reagent dosing/mixing
are completed in a single process.
• Treatment time is 7 days.
• Thousands of tonnes successfully treated
Mercury Treatment to Non-Detect Levels at a Former Industrial Site
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Stability of MetaFix® Mineral Precipitates
Independent Laboratory Multiple Extraction Testing; Values (mg/L are 9.02, 0.02, 0.80, 0.06
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Key Benefits Summary
1. Lower solubility of heavy metal precipitates based on iron and iron-sulfide chemistry provides high assurance of attaining remedial goals.
2. Not dependent on alkalinity for removal of metals. Broad pH range stability of metal precipitates based on iron and iron-sulfide chemistry reduces the danger of rebound.
3. Proven ability to address multiple heavy metals including: Al, As, Cd, Cr, Cu, Hg, Ni, Pb, Se, V, and Zn. Superior Cr(VI) treatment with the formation of more stable mixed (Cr, Fe) hydroxides.
4. Ability to treat heavy metals successfully at sites where the soil/groundwater has high acute toxicity.
5. Capable of treating comingled plumes. Simultaneous removal of soluble heavy metals, and dehalogenation of chlorinated solvents.
6. Longevity of treatment (micro-scale ZVI and FeS estimated > 10 years).
7. Low overall treatment costs based on lower reagent dosing rates, as low as 0.1% - 4% (wt/wt), versus other metals treatment technologies.
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Technology that really Works
Treatment of Heavy Metals in Soil and Groundwater using Elemental Iron and Reactive Minerals
Alan Seech, Ph.D.
PeroxyChem Environmental Solutions Senior Manager – Technology Applications
3334 E. Coast Highway, Suite 114, Corona Del Mar, CA 92625 P: +1 949-388-7065 | M: +1 949-514-1068
Mike Mueller, B.Sc., MBA PeroxyChem Environmental Solutions
Business Development Manager, EMEA | Soil & Groundwater Remediation Franz-Plattner-Straβe 28F, 6170 Zirl, Tirol, Austria P: +43 (0)5238.53262 | M: +43 (0)664.180.3060
www.PeroxyChem.com/Remediation
Questions?
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Q&A Session
If you have any unanswered questions please submit them to the Brownfield Briefing LinkedIn group, following the webinar.
http://brownfieldbriefing.com/li
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Upcoming events…
Free webinar: The National Quality Mark Scheme for Land Contamination Management: 13:00 BST, Tuesday 20 September
Brownfield Remediation 2016: London, Thursday 13 October
Brownfield Briefing Awards: London, Thursday 13 October
http://brownfieldbriefing.com/events
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Today’s Webinar: Speakers
Alan Seech – a scientist with 25 years experience in soil chemistry, microbiology, and environmental remediation. His focus has been on development of technologies for treatment of soil, sediment, and groundwater containing hard to degrade organics, such as PAHs, pesticides, and organic explosive compounds.
Mike Mueller – PeroxyChem’s Business Development Manager in EMEA - responsible for their Soil & Groundwater Remediation technologies portfolio. Based in Austria, he has been working in this region for over 6 years, initially with Adventus (which was acquired by FMC Corporation), now known as PeroxyChem.
Chair – Ian Grant – Brownfield Briefing Managing Editor
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Thank you for attending
A downloadable recording of this presentation (with slides) will be available shortly. If you have any questions, please contact Glen ([email protected])