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Middlefield-Ellis-Whisman (MEW)
        Superfund Study Area
        S     f     S


             EPA Update:
Site-Wide Groundwater Feasibility Study
                                y     y


NAS M ff tt Fi ld R t
    Moffett Field Restoration Advisory
                         ti   Ad i
                Board


              May 12, 2011
2
Purpose of Site-wide Groundwater
Feasibility Study

Evaluate alternative technologies to
 accelerate groundwater cleanup

 Current groundwater extraction &
  treatment system decreasing in
  efficiency

 Minimize the need for vapor mitigation
  by d i
  b reducing groundwater concentrations
                  d t          t ti
Key Feasibility Study Inputs

 Pilot tests

 Community Criteria and Suggested
  Strategy Paper
Community Criteria and Suggested
Strategy Paper
1) FS and Remedy Selection should focus on:

 Areas with high mass
 Areas that continue to act as sources
 A
  Areas of th plume that encroach on residential
         f the l     th t         h     id ti l
    neighborhoods, schools and other sensitive uses
   Reduce the need to long-term vapor intrusion mitigation
                          g         p                g
   Enable reasonable future reuse of property

2) Incorporate results from optimization evaluations

3) Consider specific technologies
Scope of Groundwater
Cleanup

• Large disperse
 commingled plume with
 multiple source areas

• FS strategy treatment of
 source & high conc. Areas

• Range of concentrations
 within plume

• Cleanup timeframes key
 component of FS
EPA Screening of Technologies
In Situ Treatment Technologies:
  In Situ Bioremediation, In Situ Chemical Oxidation (ISCO),
  and Abiotic Dechlorination using Zero Valent Iron (ZVI)

Extraction, Removal, Treatment and Disposal Technologies –
           ,        ,                   p              g
 – Physical Treatment with Air Sparging
 – Groundwater Extraction and Treatment
 –M li h
    Multiphase Extraction
               E      i
 – In Situ Thermal
 – Removal by Excavation
Barriers – Permeable reactive barriers, phytoremediation
Monitored Natural Attenuation
In Situ Treatment Technologies
• Evaluating In Situ Bioremediation, In Situ Chemical Oxidation
 (ISCO), and Abiotic Dechlorination using Zero valent iron

• Technologies rely on direct contact or create conditions to
 degrade contaminants.

• Typically used for hot spot treatment/limited area.

• Challenging to distribute material into heterogeneous
 subsurface. Multiple injections typically needed.

• Technologies piloted at the site with varying success.
Extraction, Removal, Treatment and
Disposal Technologies

  Air Sparging
  Air injected into sat rated
                    saturated
  zone at high pressure; strips
  solvents, which are extracted.

  In Situ Thermal
  Uses electrodes or heaters
  attached to power supplies to
  heat subsurface and
  volatilize VOCs; vapor
  collection.

  Multiphase Extraction
  Uses a high vacuum system
  to extract soil vapor and
  groundwater simultaneously.
Barriers
                                   Continuous
Permeable Reactive Barriers        Wall

• Intercepts and treats
  contaminants as groundwater
  flows through reactive barrier

• Common reactive media ZVI;

• C
  Construction – Depths
 generally less than 100 feet
                                                Funnel and
• Lifespan (15 to 25 years)                     Gate System
                                                (need to add
                                                photo)

• Issues – fouling/movement
                 g
 around wall
Monitored Natural Attenuation

 – Relies on natural processes to cleanup pollution in
  soil and groundwater.
           groundwater

 – Conditions monitored to ensure that contaminants are
  degrading and not migrating.

 – Criteria to demonstrate MNA:
   • Plume stability
   • Review of temporal trends in well
   • Geochemical and biological parameters indicate conditions
     supporting degradation


 – Component of alternative
Technologies Retained

1. Groundwater Extraction and Treatment
2. In Sit R d T h l i (i l di I Sit
2 I Situ Redox Technologies (including In Situ
   Bioremediation, In Situ Chemical Oxidation and Zero
   Valent Iron Injections) to treat high conc. areas
                 j       )            g
3. Permeable Reactive Barriers (PRB)
4. Monitored Natural Attenuation (as component of an
   alternative)
    lt    ti )
Projected VOC Plume – A Aquifer (0 to
45 feet bgs)


     1992           2009          2019
EPA Working Alternatives – Shallow A Aquifer
Alt. 1    No Action
Alt.      Extraction & Treatment (Existing & Optimized)
2A/2B
Alt. 3    Extraction & Treatment (Optimized), Monitored Natural Attenuation [MNA]*


Alt. 4    In Situ Redox (High Conc. Areas > 1,000 ppb)
          Optimized Extraction and Treatment (Remaining Areas), MNA*

Alt. 5A   In Situ Redox (High Conc. Areas > 1,000 ppb)
                        ( g                  ,    pp )
          Permeable Reactive Barriers (PRB)(Treatment downgradient of high
          concentrations areas)
          Optimized Extraction and Treatment (Remaining Areas), MNA*
Alt. 5B   Same as Alt. 5A except PRB would be replaced by barrier wells.

Notes:    In Situ Redox = in situ bioremediation, in situ chemical oxidation, or zero
          valent i
             l t iron i j ti
                      injections
          *MNA = MNA where demonstrated
Conceptual Layout
Optimized Pump and Treat


  Nort                 Sout
  h of                 h of
  101                  101
Conceptual Layout
In Situ Redox in A Aquifer

• In Situ Redox in high
 concentrations areas
        t ti
 >1,000 ppb

• Optimized pump &
 treat for remaining
 areas of plume until
 MNA demonstrated
Conceptual Layout
with PRBs in A Aquifer

• PRBs downgradient of
 high
 hi h concentration
              t ti
 areas to treat residual
 contamination

• Modeling to determine
 number of PRBs

• Type of PRBs to be
 determined
Projected VOC Plume – B1/A2 Aquifer
(50 to 75 feet bgs)


       1992       2009        2019
VOC Plume (B2 Aquifer 75 to 110 feet bgs)
EPA Work Alternatives – Deeper Aquifer
Alt. 1    No Action

Alt.      Extraction & Treatment (Existing & Optimized)
2A/2B
Alt. 3    Extraction & Treatment (Optimized), Monitored Natural Attenuation [MNA]*
Alt. 4    Facility-Specific Source Areas
          In Situ Redox (Source Areas)
          Optimized Extraction and Treatment (Remaining Areas), MNA*

          Regional Plume Areas
          Optimized Extraction & Treatment, MNA*
Alt. 5A   Same as Alt. 4 except PRBs would be included to treat residual
          contamination from facility-specific source and Regional Plume Areas
                                    y p                     g

Alt. 5B   Same as Alt. 5A except PRBs would be replaced by barrier wells.

Notes:    In Situ Redox = in situ bioremediation, in situ chemical oxidation, or zero
          valent iron injections
          *MNA = MNA where demonstrated
Conceptual Layout with
PRBs in A2/B1 Aquifer

• PRBs more difficult to   DRAFT FOR
                           DISCUSSION ONLY

 install t deeper depths
 i t ll at d      d th     ALTERNATIVE 5A
                           CONCEPTUAL LAYOUT
                           B1/A2 Zone


                           PRBs Downgradient of
                           High Concentration Areas


• PRBs extended from       Optimized Extraction and
                           Treatment in Remaining
                           Areas


 A Aquifer in areas of           Regional Plume PRB

                           NOTES:

 elevated concentrations
  l   t d         t ti     1) PRB reactive media
                              may consist of
                              zero-valent iron,
                              chelators, sorbents,
                              or microbes
Groundwater Feasibility Study Challenges

• Scale of cleanup.

• Difficult to implement in situ technologies in developed
 areas.

• Geology & matrix diffusion effects limit ability to
 accelerate cleanup
            cleanup.

• Potential recontamination of areas treated within different
 portions of the plume.
     i     f h l

• Focusing on what we can do.
         g
EPA Site-wide Groundwater Feasibility
Study - Tentative Schedule

• Summer 2011 – Draft Feasibility Study Report for review
• F ll 2011 R
  Fall 2011 – Remedy Review Board
                   d R i B d
• Winter 2012 – Final Feasibility Study Report, Proposed Plan for 
  public review
  public review
• Spring 2012  – Public Meeting and Public Comment Period
• Fall 2012 – Groundwater ROD Amendment

**Community involvement activities throughout the process 
Community Advisory Board Meetings – February 9, March 31     
RAB Meetings – Regular Updates on Vapor Intrusion and Groundwater
Property Owner Meetings – February 15 
Upcoming Meetings – Property Owners Meeting – May 24
Discussion/Questions
Contact Information

For More Information

www.epa.gov/region9/mew
www.epa.gov/region9/moffettfield

Penny Reddy
Groundwater Project Manager
EPA Region 9 Superfund Division
415.972.3108
Reddy.Penny@epa.gov
Reddy Penny@epa gov
26
EPA Working Alternatives – Shallow A
Aquifer
Alt. 1 (No Action)          Description of Alternative
Alt. 2A (P&T/Slurry Wall)
        (         y     )   Existing Remedy
                                   g      y
Alt. 2B (P&T/Slurry Wall)   Existing Remedy Optimized for mass removal
Alt. 3 (P&T/Slurry Wall)    Existing Remedy Optimized for mass removal,
                            Monitored Natural Attenuation (MNA)*
                                                          (MNA)
Alt. 4                      Facility Specific Source Areas
                            In Situ Redox (High Conc. Areas > 1,000 ppb)
                            In Situ Redox or Optimized P&T (Med. & Low Conc
                                                           (Med          Conc.
                            Area), MNA*

                            Regional Plume
                            In Situ Redox – High Conc. Areas (>1,000 ppb)
                            Optimized P&T (Remaining Areas), MNA*
Notes:                      In Situ Redox = in situ bioremediation, in situ chemical
                            oxidation, or zero valent iron injections
                            *MNA = MNA where demonstrated
Regional Groundwater Progress Update
• Semi-annual water level measurements of nearly 1000
    wells (Black Thursday)
•   Annual sampling of approximately 500 wells
•   Approximately 100 extraction wells pump over 450 gpm
•   Over 4.5 billion gallons groundwater treated through
    2009
•   Over 95,000 pounds of VOCs removed through 2009
MEW / NAS Moffett Field Site Background

• ROD Signed in 1989 to address soil and groundwater
• Enforcement – Admin Order Consent Decree Federal
                       Order,          Decree,
    Facility Agreement
•   Soil remedy (excavation and/or soil vapor extraction)
•   Groundwater remedy - slurry walls, seal conduits, and
    G      d            d    l      ll     l    d i      d
    pump and treat
•   Hydrogeology – interbedded sands, silts, clays (Bay mud)
     y     g    gy                      ,    ,  y ( y       )
•   Shallow groundwater – 5 to 20 feet bgs
•   Current TCE in shallow groundwater
    up to 40,000 ppb inside slurry walls
          40 000
•   Groundwater not used for potable use, but being cleaned
    up to its beneficial use
VOC Plume (B2 Aquifer 75 to 110 feet bgs)
B1/A2 Aquifer   B2 Aquifer
Conceptual Layout
with PRBs in A Aquifer

• PRBs downgradient of
 high concentration areas
 to treat residual
 contamination

• Modeling to determine
 number of PRBs

• Type of PRBs to be
 determined
Draft Conceptual Layout
In Situ Redox in A2/B1Aquifer

• Focusing treatment on Facility-
 Specific Source Areas and
 High Concentration

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Moffett/Ellis/Whisman Presentation to the Moffett RAB

  • 1. Middlefield-Ellis-Whisman (MEW) Superfund Study Area S f S EPA Update: Site-Wide Groundwater Feasibility Study y y NAS M ff tt Fi ld R t Moffett Field Restoration Advisory ti Ad i Board May 12, 2011
  • 2. 2
  • 3. Purpose of Site-wide Groundwater Feasibility Study Evaluate alternative technologies to accelerate groundwater cleanup Current groundwater extraction & treatment system decreasing in efficiency Minimize the need for vapor mitigation by d i b reducing groundwater concentrations d t t ti
  • 4. Key Feasibility Study Inputs Pilot tests Community Criteria and Suggested Strategy Paper
  • 5. Community Criteria and Suggested Strategy Paper 1) FS and Remedy Selection should focus on:  Areas with high mass  Areas that continue to act as sources  A Areas of th plume that encroach on residential f the l th t h id ti l neighborhoods, schools and other sensitive uses  Reduce the need to long-term vapor intrusion mitigation g p g  Enable reasonable future reuse of property 2) Incorporate results from optimization evaluations 3) Consider specific technologies
  • 6. Scope of Groundwater Cleanup • Large disperse commingled plume with multiple source areas • FS strategy treatment of source & high conc. Areas • Range of concentrations within plume • Cleanup timeframes key component of FS
  • 7. EPA Screening of Technologies In Situ Treatment Technologies: In Situ Bioremediation, In Situ Chemical Oxidation (ISCO), and Abiotic Dechlorination using Zero Valent Iron (ZVI) Extraction, Removal, Treatment and Disposal Technologies – , , p g – Physical Treatment with Air Sparging – Groundwater Extraction and Treatment –M li h Multiphase Extraction E i – In Situ Thermal – Removal by Excavation Barriers – Permeable reactive barriers, phytoremediation Monitored Natural Attenuation
  • 8. In Situ Treatment Technologies • Evaluating In Situ Bioremediation, In Situ Chemical Oxidation (ISCO), and Abiotic Dechlorination using Zero valent iron • Technologies rely on direct contact or create conditions to degrade contaminants. • Typically used for hot spot treatment/limited area. • Challenging to distribute material into heterogeneous subsurface. Multiple injections typically needed. • Technologies piloted at the site with varying success.
  • 9. Extraction, Removal, Treatment and Disposal Technologies Air Sparging Air injected into sat rated saturated zone at high pressure; strips solvents, which are extracted. In Situ Thermal Uses electrodes or heaters attached to power supplies to heat subsurface and volatilize VOCs; vapor collection. Multiphase Extraction Uses a high vacuum system to extract soil vapor and groundwater simultaneously.
  • 10. Barriers Continuous Permeable Reactive Barriers Wall • Intercepts and treats contaminants as groundwater flows through reactive barrier • Common reactive media ZVI; • C Construction – Depths generally less than 100 feet Funnel and • Lifespan (15 to 25 years) Gate System (need to add photo) • Issues – fouling/movement g around wall
  • 11. Monitored Natural Attenuation – Relies on natural processes to cleanup pollution in soil and groundwater. groundwater – Conditions monitored to ensure that contaminants are degrading and not migrating. – Criteria to demonstrate MNA: • Plume stability • Review of temporal trends in well • Geochemical and biological parameters indicate conditions supporting degradation – Component of alternative
  • 12. Technologies Retained 1. Groundwater Extraction and Treatment 2. In Sit R d T h l i (i l di I Sit 2 I Situ Redox Technologies (including In Situ Bioremediation, In Situ Chemical Oxidation and Zero Valent Iron Injections) to treat high conc. areas j ) g 3. Permeable Reactive Barriers (PRB) 4. Monitored Natural Attenuation (as component of an alternative) lt ti )
  • 13. Projected VOC Plume – A Aquifer (0 to 45 feet bgs) 1992 2009 2019
  • 14. EPA Working Alternatives – Shallow A Aquifer Alt. 1 No Action Alt. Extraction & Treatment (Existing & Optimized) 2A/2B Alt. 3 Extraction & Treatment (Optimized), Monitored Natural Attenuation [MNA]* Alt. 4 In Situ Redox (High Conc. Areas > 1,000 ppb) Optimized Extraction and Treatment (Remaining Areas), MNA* Alt. 5A In Situ Redox (High Conc. Areas > 1,000 ppb) ( g , pp ) Permeable Reactive Barriers (PRB)(Treatment downgradient of high concentrations areas) Optimized Extraction and Treatment (Remaining Areas), MNA* Alt. 5B Same as Alt. 5A except PRB would be replaced by barrier wells. Notes: In Situ Redox = in situ bioremediation, in situ chemical oxidation, or zero valent i l t iron i j ti injections *MNA = MNA where demonstrated
  • 15. Conceptual Layout Optimized Pump and Treat Nort Sout h of h of 101 101
  • 16. Conceptual Layout In Situ Redox in A Aquifer • In Situ Redox in high concentrations areas t ti >1,000 ppb • Optimized pump & treat for remaining areas of plume until MNA demonstrated
  • 17. Conceptual Layout with PRBs in A Aquifer • PRBs downgradient of high hi h concentration t ti areas to treat residual contamination • Modeling to determine number of PRBs • Type of PRBs to be determined
  • 18. Projected VOC Plume – B1/A2 Aquifer (50 to 75 feet bgs) 1992 2009 2019
  • 19. VOC Plume (B2 Aquifer 75 to 110 feet bgs)
  • 20. EPA Work Alternatives – Deeper Aquifer Alt. 1 No Action Alt. Extraction & Treatment (Existing & Optimized) 2A/2B Alt. 3 Extraction & Treatment (Optimized), Monitored Natural Attenuation [MNA]* Alt. 4 Facility-Specific Source Areas In Situ Redox (Source Areas) Optimized Extraction and Treatment (Remaining Areas), MNA* Regional Plume Areas Optimized Extraction & Treatment, MNA* Alt. 5A Same as Alt. 4 except PRBs would be included to treat residual contamination from facility-specific source and Regional Plume Areas y p g Alt. 5B Same as Alt. 5A except PRBs would be replaced by barrier wells. Notes: In Situ Redox = in situ bioremediation, in situ chemical oxidation, or zero valent iron injections *MNA = MNA where demonstrated
  • 21. Conceptual Layout with PRBs in A2/B1 Aquifer • PRBs more difficult to DRAFT FOR DISCUSSION ONLY install t deeper depths i t ll at d d th ALTERNATIVE 5A CONCEPTUAL LAYOUT B1/A2 Zone PRBs Downgradient of High Concentration Areas • PRBs extended from Optimized Extraction and Treatment in Remaining Areas A Aquifer in areas of Regional Plume PRB NOTES: elevated concentrations l t d t ti 1) PRB reactive media may consist of zero-valent iron, chelators, sorbents, or microbes
  • 22. Groundwater Feasibility Study Challenges • Scale of cleanup. • Difficult to implement in situ technologies in developed areas. • Geology & matrix diffusion effects limit ability to accelerate cleanup cleanup. • Potential recontamination of areas treated within different portions of the plume. i f h l • Focusing on what we can do. g
  • 23. EPA Site-wide Groundwater Feasibility Study - Tentative Schedule • Summer 2011 – Draft Feasibility Study Report for review • F ll 2011 R Fall 2011 – Remedy Review Board d R i B d • Winter 2012 – Final Feasibility Study Report, Proposed Plan for  public review public review • Spring 2012  – Public Meeting and Public Comment Period • Fall 2012 – Groundwater ROD Amendment **Community involvement activities throughout the process  Community Advisory Board Meetings – February 9, March 31      RAB Meetings – Regular Updates on Vapor Intrusion and Groundwater Property Owner Meetings – February 15  Upcoming Meetings – Property Owners Meeting – May 24
  • 25. Contact Information For More Information www.epa.gov/region9/mew www.epa.gov/region9/moffettfield Penny Reddy Groundwater Project Manager EPA Region 9 Superfund Division 415.972.3108 Reddy.Penny@epa.gov Reddy Penny@epa gov
  • 26. 26
  • 27. EPA Working Alternatives – Shallow A Aquifer Alt. 1 (No Action) Description of Alternative Alt. 2A (P&T/Slurry Wall) ( y ) Existing Remedy g y Alt. 2B (P&T/Slurry Wall) Existing Remedy Optimized for mass removal Alt. 3 (P&T/Slurry Wall) Existing Remedy Optimized for mass removal, Monitored Natural Attenuation (MNA)* (MNA) Alt. 4 Facility Specific Source Areas In Situ Redox (High Conc. Areas > 1,000 ppb) In Situ Redox or Optimized P&T (Med. & Low Conc (Med Conc. Area), MNA* Regional Plume In Situ Redox – High Conc. Areas (>1,000 ppb) Optimized P&T (Remaining Areas), MNA* Notes: In Situ Redox = in situ bioremediation, in situ chemical oxidation, or zero valent iron injections *MNA = MNA where demonstrated
  • 28. Regional Groundwater Progress Update • Semi-annual water level measurements of nearly 1000 wells (Black Thursday) • Annual sampling of approximately 500 wells • Approximately 100 extraction wells pump over 450 gpm • Over 4.5 billion gallons groundwater treated through 2009 • Over 95,000 pounds of VOCs removed through 2009
  • 29. MEW / NAS Moffett Field Site Background • ROD Signed in 1989 to address soil and groundwater • Enforcement – Admin Order Consent Decree Federal Order, Decree, Facility Agreement • Soil remedy (excavation and/or soil vapor extraction) • Groundwater remedy - slurry walls, seal conduits, and G d d l ll l d i d pump and treat • Hydrogeology – interbedded sands, silts, clays (Bay mud) y g gy , , y ( y ) • Shallow groundwater – 5 to 20 feet bgs • Current TCE in shallow groundwater up to 40,000 ppb inside slurry walls 40 000 • Groundwater not used for potable use, but being cleaned up to its beneficial use
  • 30. VOC Plume (B2 Aquifer 75 to 110 feet bgs)
  • 31. B1/A2 Aquifer B2 Aquifer
  • 32. Conceptual Layout with PRBs in A Aquifer • PRBs downgradient of high concentration areas to treat residual contamination • Modeling to determine number of PRBs • Type of PRBs to be determined
  • 33. Draft Conceptual Layout In Situ Redox in A2/B1Aquifer • Focusing treatment on Facility- Specific Source Areas and High Concentration