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May 10, 2012




                    Bioremediation -
             How microbes are used to clean up
                    DOD Installations




Traditional                                                                                                       Innovative
Environmental Services                                                                              Solutions & Technologies
                         Chemical • Petroleum • Pharmaceutical • Manufacturing • Utilities • Land Development
Overview

►   Who is Solutions-IES?
►   Brief History of Remediation Technology
►   Bioremediation basics
►   Enhanced Reductive Dechlorination
►   Project Examples
►   New Technologies & Emerging Contaminants
Who is Solutions-IES, Inc.?

Full service environmental company
  ►   Formed in Raleigh in 1999
  ►   Licensed Engineering and Geology firm
  ►   Woman Owned Small Business (WOSB)
        Certified 8(a) DB firm
        North Carolina HUB
  ►   DCAA approved accounting system
  ►   Serving DoD and private industry
  ►   Providing both traditional and innovative solutions
Historical Perspective
(1980s to 2000)
►   Pump & Treat
►   Dig & Haul
     Energy & Capital intensive
     Transfer contamination
      between medium
     Difficult to reach closure
Historical Perspective
(mid-1990s to mid-2000s)
►   In Situ Treatment Technologies
     Physical:
        •   Air Sparge;
        •   Soil Vacuum Extraction (SVE);
        •   In Situ Chemical Oxidation (ISCO);
        •   Fe0 walls
     Biological:
        •   Biosparge;
        •   Biovent;
        •   Oxygen and Nutrient Addition;
        •   Substrate Addition;
        •   Biobarriers
Current Perspective
(mid-2000s to now)
►   Optimization
►   Sustainability
►   Emerging Contaminants
       Chlordane
       1,4-Dioxane
       PFOS/PFOA
       Low Permeability Zones
Typical Remediation Costs
         ►   Surfactant Co-solvent Flushing*    $385/yd3
         ►   Chemical Oxidation*                $125/yd3
         ►   Thermal Treatment*                  $88/yd3
         ►   Stabilization                     $15-80/yd3
         ►   Dig and Haul                       $4-10/yd3 + T&D
         ►   Pump & Treat                          ∞
         ►   Enhanced Bioremediation*            $29/yd3

*From: McDade, Travis and Newell, 2005
In Situ Bioremediation
  In Situ                                  Bio                                Remediation



  In Place                              Microbial                              Method to Fix




 Biological agents (bacteria, fungi, plants, or their enzymes) used to
               clean up pollution in the environment.

         Reference: Lisa Alvarez-Cohen, Civil and Environmental Engineering
         University of California, Berkeley, Earth Science Division, LBNL
How Does It Work?

Growth-Promoting Biological Reduction




                    +                                                  +

 Electron Donor        Electron Acceptor           Waste Products                 Energy
     (Food)         (something to breathe)       [CO2, N2, FeS2, Cl-]
                  [O2, NO3-, SO42-, TCE, etc.]
                                                      (Drawing Modified from AFCEE and Wiedemeier)
Applying In Situ Bioremediation

   Natural
               Biostimulation   Bioaugmentation
 Attenuation

   Have           Have              Need
  Microbes       Microbes          Microbes

 Have food                        Have food
               Need food
   and                              and
               or nutrients
 nutrients                        nutrients
Anaerobic Bioremediation
             Target Contaminants
►   Chlorinated Organics
      Ethenes (PCE, TCE)
      Ethanes (TCA)
      Methanes (CT)
►   Petroleum Hydrocarbons
        Aromatic Hydrocarbons
        Total Petroleum Hydrocarbons (TPH)
        Benzene, Toluene, Ethylbenzene, and Xylenes (BTEX)
        Methyl tert-butyl ether (MTBE)
        tert-Butyl Alcohol (TBA)
►   Nitrate, Perchlorate, Chromate
►   Explosives (TNT, RDX, HMX)
►   Acid Mine Drainage
How Does It Work?
Enhanced Reductive Dechlorination

►   In Situ anaerobic bioremediation
►   Injected into contaminated aquifer
►   Source zone and/or PRB treatment
►   The organic substrate:
      Develops an anaerobic and reducing treatment zone
      Generates hydrogen through fermentation reactions
      Stimulates microbial growth and metabolism of contaminants of
       concern
Dehalococcoides ethenogenes
►   Multiple strains (BAV1, 195, VS, MB, FL2)
►   Obligate anaerobe
►   Disc-shaped; spontaneous motility
►   Prefers neutral pH environment
►   Complete dechlorination to VC & ethene
►   Grows slowly; prefers life in consortium
►   Uses acetate for C source;
     H2 as electron donor
►   Can use chloroethenes,
     chlorophenols and PCBs as
     terminal electron acceptors.
AEC
Tarheel Army Missile Plant
Burlington, NC
In Situ Bioremediation of TCE
Tarheel Army Missile Plant

1944 – 1992 GOCO Facility
  ►   1993 Soil and groundwater contamination discovered
      (BTEX and TCE)
  ►   1995 AS/SVE placed in operation
  ►   1999 P&T initiated NW corner
  ►   2003 Guaranteed fixed price bids from multiple
      vendors
  ►   2004 Army selects Solutions-IES to perform work
  ►   2004 AS/SVE system turned off and
      Solutions-IES begins EOS® injection
Costs (in $1,000)

                                           Pilot     Full
Vendor              Process - Reagent                       Total
                                          (GFP)    (Est.)
NA                  MNA                       0     250      250
Solutions-IES       ERD - EOS               256     728      984
Magnus pHA          Cometabolic- C3H8       321     894 1,215
Cl-Solutions        Cometabolic- Cl-Out     373    1,141 1,515
Arcadis             ERD - molasses          339    1,456 1,795
Electro-Petroleum   AS with CO2             291    1,763 2,054
Regenesis           ERD - HRC               475    1,645 2,120
Geo-Cleanse         ISCO - Fenton           281    2,411 2,692
TAMP Site Conditions

Source area 100’ x 100’
Existing AS/SVE System
  ►   Oxidative conditions
Chlorinated Solvents
  ►   2 – 4 mg/L
Regulatory Challenges

Groundwater Reinjection
  ►   Recovered groundwater is a “waste”
  ►   Innovative below-ground reinjection system


Bioaugmentation
  ►   First approved use of DHC
      bioaugmentation in NC
TAMP - Summary

►   EOS® effectively distributed throughout treatment area
►   Quickly established favorable geochemistry for reductive
    dechlorination
►   TCE reduced to below detection (<1.0 µg/L) in monitor wells
    in treatment area
►   Remedial goals met within
    6 months of injection
►   US Army has sold property!
►   Site has been redeveloped as
    commercial / office complex
NAVFAC Southeast
NAS Pensacola
SWMU 1 – WWTP
In Situ Bioremediation of TCE in a Sulfate-Rich Acidic Aquifer
Site History

• Former WWTP (SWMU 1),

• TCE plume with DNAPL source

• Sulfuric acid spill 1983

• Concentrations in the source area:
    pH – 3.5
    TCE – 18,000 µg/L

• Remedial activities:
    P&T 1986-1997
    ISCO w/Fenton’s 1998-1999
    MNA for downgradient plume

• Further treatment required
Remediation Plan

• AquaBupH™ to promote in situ
  bioremediation
  Emulsified oil substrate
  Alkaline solids to adjust pH
  Nutrients

• Pilot Study – 2008
  2 injections in source area

• Full-Scale – 2010
  2 rounds of injections




  AquaBupH™ is a licensed product of EOS Remediation, LLC.; Raleigh, NC
pH affects on Dehalococcoides sp.


                                                                                pH=7.0


                                                                                          pH=6.5




                                                                                         pH=6.0


                                                                                         pH=5.5 & 8.0




                  .
Ashley Eaddy, 2008 Scale-Up and Characterization of an Enrichment Culture for
Bioaugmentation of the P-Area Chlorinated Ethene Plume at the Savannah River
Site. M.S. Thesis, Clemson University.
Total Organic Carbon & pH Results
                           5,000                                   8
TOC Concentration (mg/L)




                           4,000                                   7


                           3,000                                   6




                                                                        pH
                           2,000                                   5
                                                         TOC
                           1,000                                   4
                                                         pH

                              0                                     3
                              Jun-08   Jun-09   Jun-10         Jun-11
Emerging Contaminants &
             New Technologies

Soil Remediation
  ►   VOS™
  ►   Range Sustainability
  ►   Chlordane
GW Remediation
  ►   EAS™
  ►   MNA for perchlorate remediation
Summary

►   Bioremediation
        Wide range of applicability
        One of many remediation options
        Sustainable
        Cost-effective
►   On-going Research
      Micro-Biological Tools (MBTs)
      Emerging Contaminants
      Optimization
Contact

       Tony Lieberman
       Solutions-IES, Inc.
          Raleigh, NC
    919-873-1060 (ext. 117)
tlieberman@solutions-ies.com



  www.Solutions-IES.com

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1 lieberman-ecec2012 - bioremediation 05-10-2012

  • 1. May 10, 2012 Bioremediation - How microbes are used to clean up DOD Installations Traditional Innovative Environmental Services Solutions & Technologies Chemical • Petroleum • Pharmaceutical • Manufacturing • Utilities • Land Development
  • 2. Overview ► Who is Solutions-IES? ► Brief History of Remediation Technology ► Bioremediation basics ► Enhanced Reductive Dechlorination ► Project Examples ► New Technologies & Emerging Contaminants
  • 3. Who is Solutions-IES, Inc.? Full service environmental company ► Formed in Raleigh in 1999 ► Licensed Engineering and Geology firm ► Woman Owned Small Business (WOSB)  Certified 8(a) DB firm  North Carolina HUB ► DCAA approved accounting system ► Serving DoD and private industry ► Providing both traditional and innovative solutions
  • 4. Historical Perspective (1980s to 2000) ► Pump & Treat ► Dig & Haul  Energy & Capital intensive  Transfer contamination between medium  Difficult to reach closure
  • 5. Historical Perspective (mid-1990s to mid-2000s) ► In Situ Treatment Technologies  Physical: • Air Sparge; • Soil Vacuum Extraction (SVE); • In Situ Chemical Oxidation (ISCO); • Fe0 walls  Biological: • Biosparge; • Biovent; • Oxygen and Nutrient Addition; • Substrate Addition; • Biobarriers
  • 6. Current Perspective (mid-2000s to now) ► Optimization ► Sustainability ► Emerging Contaminants  Chlordane  1,4-Dioxane  PFOS/PFOA  Low Permeability Zones
  • 7. Typical Remediation Costs ► Surfactant Co-solvent Flushing* $385/yd3 ► Chemical Oxidation* $125/yd3 ► Thermal Treatment* $88/yd3 ► Stabilization $15-80/yd3 ► Dig and Haul $4-10/yd3 + T&D ► Pump & Treat ∞ ► Enhanced Bioremediation* $29/yd3 *From: McDade, Travis and Newell, 2005
  • 8. In Situ Bioremediation In Situ Bio Remediation In Place Microbial Method to Fix Biological agents (bacteria, fungi, plants, or their enzymes) used to clean up pollution in the environment. Reference: Lisa Alvarez-Cohen, Civil and Environmental Engineering University of California, Berkeley, Earth Science Division, LBNL
  • 9. How Does It Work? Growth-Promoting Biological Reduction + + Electron Donor Electron Acceptor Waste Products Energy (Food) (something to breathe) [CO2, N2, FeS2, Cl-] [O2, NO3-, SO42-, TCE, etc.] (Drawing Modified from AFCEE and Wiedemeier)
  • 10. Applying In Situ Bioremediation Natural Biostimulation Bioaugmentation Attenuation Have Have Need Microbes Microbes Microbes Have food Have food Need food and and or nutrients nutrients nutrients
  • 11. Anaerobic Bioremediation Target Contaminants ► Chlorinated Organics  Ethenes (PCE, TCE)  Ethanes (TCA)  Methanes (CT) ► Petroleum Hydrocarbons  Aromatic Hydrocarbons  Total Petroleum Hydrocarbons (TPH)  Benzene, Toluene, Ethylbenzene, and Xylenes (BTEX)  Methyl tert-butyl ether (MTBE)  tert-Butyl Alcohol (TBA) ► Nitrate, Perchlorate, Chromate ► Explosives (TNT, RDX, HMX) ► Acid Mine Drainage
  • 12. How Does It Work?
  • 13. Enhanced Reductive Dechlorination ► In Situ anaerobic bioremediation ► Injected into contaminated aquifer ► Source zone and/or PRB treatment ► The organic substrate:  Develops an anaerobic and reducing treatment zone  Generates hydrogen through fermentation reactions  Stimulates microbial growth and metabolism of contaminants of concern
  • 14. Dehalococcoides ethenogenes ► Multiple strains (BAV1, 195, VS, MB, FL2) ► Obligate anaerobe ► Disc-shaped; spontaneous motility ► Prefers neutral pH environment ► Complete dechlorination to VC & ethene ► Grows slowly; prefers life in consortium ► Uses acetate for C source; H2 as electron donor ► Can use chloroethenes, chlorophenols and PCBs as terminal electron acceptors.
  • 15. AEC Tarheel Army Missile Plant Burlington, NC In Situ Bioremediation of TCE
  • 16. Tarheel Army Missile Plant 1944 – 1992 GOCO Facility ► 1993 Soil and groundwater contamination discovered (BTEX and TCE) ► 1995 AS/SVE placed in operation ► 1999 P&T initiated NW corner ► 2003 Guaranteed fixed price bids from multiple vendors ► 2004 Army selects Solutions-IES to perform work ► 2004 AS/SVE system turned off and Solutions-IES begins EOS® injection
  • 17. Costs (in $1,000) Pilot Full Vendor Process - Reagent Total (GFP) (Est.) NA MNA 0 250 250 Solutions-IES ERD - EOS 256 728 984 Magnus pHA Cometabolic- C3H8 321 894 1,215 Cl-Solutions Cometabolic- Cl-Out 373 1,141 1,515 Arcadis ERD - molasses 339 1,456 1,795 Electro-Petroleum AS with CO2 291 1,763 2,054 Regenesis ERD - HRC 475 1,645 2,120 Geo-Cleanse ISCO - Fenton 281 2,411 2,692
  • 18. TAMP Site Conditions Source area 100’ x 100’ Existing AS/SVE System ► Oxidative conditions Chlorinated Solvents ► 2 – 4 mg/L
  • 19. Regulatory Challenges Groundwater Reinjection ► Recovered groundwater is a “waste” ► Innovative below-ground reinjection system Bioaugmentation ► First approved use of DHC bioaugmentation in NC
  • 20. TAMP - Summary ► EOS® effectively distributed throughout treatment area ► Quickly established favorable geochemistry for reductive dechlorination ► TCE reduced to below detection (<1.0 µg/L) in monitor wells in treatment area ► Remedial goals met within 6 months of injection ► US Army has sold property! ► Site has been redeveloped as commercial / office complex
  • 21. NAVFAC Southeast NAS Pensacola SWMU 1 – WWTP In Situ Bioremediation of TCE in a Sulfate-Rich Acidic Aquifer
  • 22. Site History • Former WWTP (SWMU 1), • TCE plume with DNAPL source • Sulfuric acid spill 1983 • Concentrations in the source area: pH – 3.5 TCE – 18,000 µg/L • Remedial activities: P&T 1986-1997 ISCO w/Fenton’s 1998-1999 MNA for downgradient plume • Further treatment required
  • 23. Remediation Plan • AquaBupH™ to promote in situ bioremediation Emulsified oil substrate Alkaline solids to adjust pH Nutrients • Pilot Study – 2008 2 injections in source area • Full-Scale – 2010 2 rounds of injections AquaBupH™ is a licensed product of EOS Remediation, LLC.; Raleigh, NC
  • 24. pH affects on Dehalococcoides sp. pH=7.0 pH=6.5 pH=6.0 pH=5.5 & 8.0 . Ashley Eaddy, 2008 Scale-Up and Characterization of an Enrichment Culture for Bioaugmentation of the P-Area Chlorinated Ethene Plume at the Savannah River Site. M.S. Thesis, Clemson University.
  • 25. Total Organic Carbon & pH Results 5,000 8 TOC Concentration (mg/L) 4,000 7 3,000 6 pH 2,000 5 TOC 1,000 4 pH 0 3 Jun-08 Jun-09 Jun-10 Jun-11
  • 26. Emerging Contaminants & New Technologies Soil Remediation ► VOS™ ► Range Sustainability ► Chlordane GW Remediation ► EAS™ ► MNA for perchlorate remediation
  • 27. Summary ► Bioremediation  Wide range of applicability  One of many remediation options  Sustainable  Cost-effective ► On-going Research  Micro-Biological Tools (MBTs)  Emerging Contaminants  Optimization
  • 28. Contact Tony Lieberman Solutions-IES, Inc. Raleigh, NC 919-873-1060 (ext. 117) tlieberman@solutions-ies.com www.Solutions-IES.com

Hinweis der Redaktion

  1. Natural Attenuation – biotransformation occurs naturally: indigenous microbes present, substrates &amp; nutrients present (can be MNA)Biostimulation - indigenous microbes present, substrates &amp;/or nutrients must be addedBioaugmentation – indigenous microbes not present, organisms are added
  2. The WWTP received domestic and industrial wastes from the 40’s through the 70’s. Releases resulted in xxxx. NAVFAC has tried several remedial actions to address the contamination including pump and treat and isco using Fenton’s reagent. The combination of DNAPL and very low pH levels resulting from the sulfuric acid spill would imply that biological reductive dechlorination may be limited or impossible. Our objective was to evaluate the potential for a substrate with added buffering agents to raise the pH levels and promote biological reductive dechlorination.
  3. Remedial objectives: raise pH and distribute oil to promote biodegradation. This project has progressed in a series of stages. We began work in 2008 with a small pilot study in the presumed source area where injected an emulsified oil substrate (EOS) with alkaline solids – AquaBupH. We saw a very good response in the well with the highest concentrations (AE-01), pH levels were adjusted and concentrations diminished. Based on those results, NAVFAC contracted us to conduct a full-scale injection. We collected some additional information on the aquifer materials and geochemistry which I will discuss in more detail later. In May/June 2010, we injected AquaBupH across the site.
  4. TOC distributed well across the site. pH levels raised in many of the wells, some lag in other wells presumably as buffer overcomes the high acidity of the aquifer. pH levels in the wells exposed to pilot study have responded well and pH is within the optimal range for bioreductivedechlorination. In addition, we had strongly reducing ORP values, we were generating methane and the aquifer conditions appeared to be appropriate for the microbes to do their work.