effective bioremediation of chlorinated solvent sites

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Page 1: Effective Bioremediation of Chlorinated Solvent Sites

Products & Services for In Situ Remediation • tersusenv.com© 2021 Tersus Environmental, LLC. All Rights Reserved.

Advances in EVO Deployment Using In Situ Alcoholysis

Part 1, Wednesday, April 28, 2021

Effective Bioremediation of Chlorinated Solvent Sites – Avoiding Pitfalls and

Maximizing Performance

Page 2: Effective Bioremediation of Chlorinated Solvent Sites

Products & Services for In Situ Remediation • tersusenv.com© 2021 Tersus Environmental, LLC. All Rights Reserved.

Agenda

01 02

03

05

04

06

Biological Reductive Dechlorination

Bioremediation

History and Advancements

Emulsified Vegetable Oils

Why do Wells Bio-Foul?

Bio-Fouling

Overview and Options

Electron Donors

Impact of pH on Dechlorination

pH

Method for Improved ROI and Fatty Acid Distribution

Subsurface Distribution

Page 3: Effective Bioremediation of Chlorinated Solvent Sites

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How Does Bioremediation

Work?Energy

Electron

Donor

(Food)

Electron

Acceptor

(something to

breathe)

[O2, NO3, SO4,

TCE, etc.]

Waste Products

[CO2, N2, FeS2, Cl-]

+ +

(Drawing Modified from AFCEE and Wiedemeier)

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Page 4: Effective Bioremediation of Chlorinated Solvent Sites

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What is needed?

•Organic substrates that ferment to:oAcetateoHydrogen (H2)

•Strong reducing conditions•Right organohalide respiring bacteria•Nutrients

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Page 5: Effective Bioremediation of Chlorinated Solvent Sites

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O2

Ethene and other

degradation

products

DhbDhb

DhcDhc

Dhc

Dhb

Electron

Donor Fermented

Dhc

Dhc

Dhb

H2 (Energy)

TCE or Others

(Electron acceptor)

Cell GrowthDhc

Dhb

Dhb

Dhb

DhbDhc

Dhc

Dhc

Dhb

Slide Courtesy of SiREM

Biological Reductive Dechlorination

Page 6: Effective Bioremediation of Chlorinated Solvent Sites

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Reductive Dechlorination by Dhc

PCE-reductase

TCE-reductase

cDCE-reductase

VC-reductase

PCE

TCE

cDCE

VC

TCE

cDCE

VC

Ethene

Cl

ClCl

Cl+ H2

Cl

ClH

Cl+ Cl

-

+ H+

Cl

ClH

Cl+ H2

Cl

HH

Cl+ Cl

-

+ H+

Cl

HH

Cl+ H2

H

HH

Cl+ Cl

-

+ H+

H

HH

Cl+ H2

H

HH

H+ Cl

-

+ H+

Page 7: Effective Bioremediation of Chlorinated Solvent Sites

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Anaerobic Fermentation

Soybean oil ferments to acetic acid and hydrogen

Page 8: Effective Bioremediation of Chlorinated Solvent Sites

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Electron Donors

Average Composition and Electrons Released During Anaerobic Fermentation

Electron

Donor

Atoms per Mole Substrate

Average

Molecular

Weight

H2 Released

per mole

Substrate

Moles H2

Released

per

gram

Substrate

Carbon Hydrogen Oxygen

Acetate 2 4 2 60.1 4 0.0666

Lactate 3 6 3 90.1 6 0.0666

Glucose 6 12 6 180.2 12 0.0666

Soybean Oil 56.3 99.5 6 873.1 156.5 0.1792

Ref: ESTCP, May 2006, Table 2.3

Page 9: Effective Bioremediation of Chlorinated Solvent Sites

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A Historic Look at Soybean Oil Prices

COVID & TightGlobal Supplies

Dawn of Biodiesel

Supply Concerns

Recession

Page 10: Effective Bioremediation of Chlorinated Solvent Sites

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Trade War Phase One Announcement Reopening Jitters/Election

COVID Lockdowns

Tight Supply

Concerns

Nearby Continuous Soybean Oil Chart (02.03.2021)

Page 11: Effective Bioremediation of Chlorinated Solvent Sites

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Soybean Fatty Acid Distribution

Fatty Acid PercentC-16:0 Palmitic 11.0 %

C-18:0 Stearic 4.0 %

C-18:1 Oleic 24.0 %

C-18:2 Linoleic 54.0 %

C-18:3 Linolenic 7.0 %

𝐻2𝐶 − 𝑂 − 𝐶 − 𝑅𝑖

𝑂=

𝐻2𝐶 − 𝑂 − 𝐶 − 𝑅𝑖

𝑂=

𝐻2𝐶 − 𝑂 − 𝐶 − 𝑅𝑖

𝑂=

Alpha-Linolenic Acid

Page 12: Effective Bioremediation of Chlorinated Solvent Sites

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Fatty Acid Oxidation

Linoleic Acid Multiple step metabolic process

• Removes two carbons from the chain

• Releases:• Four hydrogen atoms (H)

• Acetic Acid (C2H4O2)

Beta (β)

Alpha (α)

Carboxyl group

CnH2nO2 + 2 H2O ⇒ Cn-2H2n-4O2 + 2 H2 + C2H4O2

Page 13: Effective Bioremediation of Chlorinated Solvent Sites

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Distribution of the Correct Type of Fatty Acids is EssentialAcetate

• Slow consumption

•Will migrate downgradient

• Stimulates PCE -> TCE -> cDCE

•Will not stimulate cDCE -> VC -> ethene

Hydrogen (H2)Produced from linolenic acid, propionate, butyrate, etc.

• Rapid consumption

• Does not migrate beyond injection zone

• Required for cDCE -> VC -> ethene

Page 14: Effective Bioremediation of Chlorinated Solvent Sites

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pH Plays a Key Role in VFA Production

Systems under alkaline conditions

• Enhances the activity of fatty acid-producing bacteria

• Inhibits methanogens

• Increases production of VFAs

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Page 15: Effective Bioremediation of Chlorinated Solvent Sites

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Impact of pH on

Dechlorination

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6.0 8.55.0

No

Dechlorination

10

Complete

Dechlorination

7.5

• pH of 6.0-8.5 is generally required for dechlorination to ethene*

• pH 6.8-7.5 is considered optimal range, 7.5 is best*

• Sites with low pH more likely to accumulate cDCE/VC

Optimal

Dechlorination

6.8

No

Dechlorination

Incomplete/Slow

Dechlorination

Incomplete/Slow

Dechlorination

*Rowlands, 2004 (Slide Courtesy of SiREM)

Page 16: Effective Bioremediation of Chlorinated Solvent Sites

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Why is low pH so Common?

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• Some sites have intrinsic groundwater pH in the 5.0-6.0 range

• Reductive dechlorination produces hydrochloric acid

PCE

Cl

ClCl

Cl

TCE

Cl

ClH

Cl

cDCE VC Ethene

Cl

HH

Cl H

HH

Cl H

HH

H

2H HCl 2H HCl 2H HCl 2H HCl

Page 17: Effective Bioremediation of Chlorinated Solvent Sites

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Fermentation of electron donors generates acidic byproducts

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Lactic Acid

• 2H2 + Acetate + CO2

• CO2 dissolves in water forming carbonic acid

Page 18: Effective Bioremediation of Chlorinated Solvent Sites

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BiofoulingNutrients in the vicinity of aerobic wells promote excessive biomass growth that reduce permeability

Bacterial growth within delivery wells

Hard Soap and Soap Scum

Page 19: Effective Bioremediation of Chlorinated Solvent Sites

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SaponificationThe Process of Making Soap

+ =Acid(Oil)

Base(Lye)

Salt(Soap)

Page 20: Effective Bioremediation of Chlorinated Solvent Sites

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Hard Water

• Water that contains salts of calcium and magnesium principally as:

oBicarbonates

oChlorides

o Sulfates

• Ferrous iron may also be present

Page 21: Effective Bioremediation of Chlorinated Solvent Sites

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Hard Water

Calcium and Magnesium Ions

• React with the fatty acids to form an insoluble gelatinous curd

Page 22: Effective Bioremediation of Chlorinated Solvent Sites

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Treated Samples

Co-solvent liquifies soap scum

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Page 23: Effective Bioremediation of Chlorinated Solvent Sites

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Alkaline Groundwater

Page 24: Effective Bioremediation of Chlorinated Solvent Sites

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Bench test to liquify viscous material

• Samples mixed with co-solvent liquifies insoluble gelatinous curd

• Addition of water, forms an EVO

Page 25: Effective Bioremediation of Chlorinated Solvent Sites

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Field Mixing• TASK™ EVO Self-

Emulsifier

• RBD Soybean Oil

EVO Deployment Using In Situ Alcoholysis

Emulsified Vegetable Oil(EVO)

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Page 26: Effective Bioremediation of Chlorinated Solvent Sites

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Anaerobic Bioremediation Deploying Electron Donor Via In Situ Alcoholysis

EDS-Activator™

𝐻2𝐶 − 𝑂𝐻

𝐻2𝐶 − 𝑂𝐻

𝐻2𝐶 − 𝑂𝐻

+

Mixture ofFatty Acid Esters

EDS-QR™Salts of the

Carboxylic Acids+ +

In Situ Generation of Slowly Fermenting and Soluble Electron Donors

+

EDS-Advanced™

TASK™ MicroEVO™Self-Emulsifier &Substrate Shuttle

Vegetable Oil

𝐻2𝐶 − 𝑂 − 𝐶 − 𝑅𝑖

𝑂=

𝐻2𝐶 − 𝑂 − 𝐶 − 𝑅𝑖

𝑂=

𝐻2𝐶 − 𝑂 − 𝐶 − 𝑅𝑖

𝑂=

+ 𝑅𝑖 − 𝐶 − 𝑂−

𝑂=

𝑅𝑖𝑖 − 𝑂 − 𝐶 − 𝑅𝑖

𝑂=

+ 𝑅𝑖 − 𝐶 − 𝑂−

𝑂=𝑅𝑖𝑖 − 𝑂 − 𝐶 − 𝑅𝑖

𝑂=

+ 𝑅𝑖 − 𝐶 − 𝑂−

𝑂=

𝑅𝑖𝑖 − 𝑂 − 𝐶 − 𝑅𝑖

𝑂=

Page 27: Effective Bioremediation of Chlorinated Solvent Sites

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Activator Options

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• Homogeneous Alkaline Catalysto Alkyl oxides (RO−)

• Heato Steam hydrolysiso Electrical resistance heatingo Thermal conduction heatingo Gas thermal heatingo Residual heat from an in-situ thermal remediation project

• Biocatalysto Enzyme (triglyceride lipases)

Page 28: Effective Bioremediation of Chlorinated Solvent Sites

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EDS-Advanced™Unrestricted Electron Donor Subsurface Distribution for Anaerobic Bioremediation

• Improved subsurface distribution of a vegetable oil-based electron donor

• Improved ROI, fatty acid distribution and TOC when compared to EVO

• Eliminates dependence on EVO droplet size

• Aids in reducing cVOC inhibitory concentrations by sequestering DNAPL

• High alcohol content and high solubility reduces injection well biofouling risk

Page 29: Effective Bioremediation of Chlorinated Solvent Sites

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Typical Application Rates

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EDS-ER™ (Soybean Oil and TASK™MicroEVO™ Self-Emulsifier

2 to 8 g/L

EDS-Activator™ 16 to 20% of EDS-ER Dose

EDS Substrate Shuttle (Co-Solvent) 0 to 0.4 g/L

mZVI Suspension 4 to 6 g/L

Page 30: Effective Bioremediation of Chlorinated Solvent Sites

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Case Study

ZVI with Biostimulationand Bioaugmentation

Page 31: Effective Bioremediation of Chlorinated Solvent Sites

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Former Dry Cleaner Site

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Page 32: Effective Bioremediation of Chlorinated Solvent Sites

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Former Dry Cleaner Site

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Page 33: Effective Bioremediation of Chlorinated Solvent Sites

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PCE Isoconcentration

Contours

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Page 34: Effective Bioremediation of Chlorinated Solvent Sites

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140 Injection Points

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• MW5A total CVOCs dropped from 1016 to 4 ppb in 5 months

• MW14 PCE dropped from 451 to 97 ppb in 5 months

Former Dry Cleaner

Page 35: Effective Bioremediation of Chlorinated Solvent Sites

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Field Mixing

TASK™ EVO Self-Emulsifier totes Bulk tanker delivery of soybean oil

Page 36: Effective Bioremediation of Chlorinated Solvent Sites

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Quality Control Testing

Field prepared EDS-ER™ Field prepared EVO

Add Water

Page 37: Effective Bioremediation of Chlorinated Solvent Sites

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Distribution Centers

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Page 38: Effective Bioremediation of Chlorinated Solvent Sites

PRODUCTSANDSERVICES

ISCO

Modulated TersOx™ LiquidActivated and Controlled Exothermic (ACE)

AEROBIC BIOREMEDIATION

TersOx™ Family of Products

ELECTRON ACCEPTORS FORANEROBIC BIOREMEDIATIONSulfate Enhanced In Situ Remediation ofPetroleum Hydrocarbons using Nuristulfate®and NutriBind®

ELECTRON DONORS

Enhanced Anerobic Bioremediation of Chlorinated Solvents

PERFORMANCE MONITORING

Compound Specific Isotope Analysis (CSIA) and Molecular Diagnostic Tools (MDT)

NAPL REMEDIATION

Tersus Advanced Surface Kinetics (TASK™) liberates NAPL and captures them with enhanced recovery techniques

EQUIPMENT

Subsurface Delivery SystemsAdditive injection and groundwater recirculation trailers available for short- or long-term leases

TECHNICAL SUPPORT

Professional technical services

ZVI AND ISCR

ZVI Powders, mZVI, & ISR-Cl

Page 39: Effective Bioremediation of Chlorinated Solvent Sites

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Gary M. Birk, P.E. (NC, VA, & FL) T. 919.453.5577 x2001 | M. 919.638.7892 [email protected] www.tersusenv.com | www.surbec.com

Course Code ISNC