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LONG TERM MONITORING DATA
EVALUATION OF BIOAUGMENTATION
DURING ISCR-ENHANCED
BIOREMEDIATION OF TCE DNAPL
James G.D. Peale, RG
Erik I. Bakkom, PE
(Maul Foster & Alongi Inc.)
Jeff Roberts, Sandra Dworatzek
(SiREM Laboratories)
Josephine Molin
(FMC Environmental Solutions)
June 2013
 Site Overview
 Technology Summary
 Problem Statement
 Analysis
 Results
 Summary
 Implications
TOPICS
 Former MGP waste site redeveloped for
manufacturing in 1970s
 80+ acres adjacent to Portland Harbor NPL site
 TCE released from a recycling system (1980-1985)
 Impacts from release discovered in 2002
 TCE DNAPL Source Zone
 Impacts from about 5-34 m bgs
 TCE up to 592,000 ug/L (DNAPL levels)
 No TCE DNAPL observed
 Cis-1,2-DCE up to 90,800 ug/L
 Very little VC (< 100 ug/L)
Site Overview
Site Overview
Technology Summary
 EHC
 Powdered blend of zero-valent iron (ZVI) and hydrophilic
organic carbon
 Creates strongly reducing conditions in groundwater for in situ
chemical reduction (ISCR)
 ISCR results in abiotic dechlorination and supports anaerobic
bacteria
 KB-1
 Anaerobic consortium of dechlorinating bacteria
 Includes dehalococcoides sp.
 Requires ORP < -75 mV
 Both technologies demonstrated success for
dissolved CVOC plumes
Technology Summary
 EHC+KB-1 Full-Scale Implementation
 46 m x 21 m x 3 m PRB – Source area only
 Injected from ~12 – 34 m bgs
 Supplemental upgradient areas
 200+ injection points
 ~269,400 kg EHC
 1,831 L KB-1
 Direct-push drilling
 23 Performance Monitoring Wells
Injection Layout
Injection Layout
Source Area Geometry
Problem Statement
 Remedial action objective is 11,000 ug/L
 Threshold indicator for TCE DNAPL
 Achieved in less than 12 months
 Achieved mean TCE 3 ug/L
 Declining cDCE and VC, but still elevated in
some wells
 Dhc counts 107 – 108
 Question: how long can this continue?
 Will we see rebound?
Problem Statement
 How long will Dhc sp. flourish?
 Organic carbon needs
 (other)
 Continued reducing conditions?
 Field data
 Other functional requirements?
 Continued cVOCs?
Long-Term Data Sets
 Pilot Study Data
 2006-2008
 Shallow and deep wells, within and
downgradient of injection zone
 Full-scale Data
 2009-present
 19 wells + pilot study wells
 Monitoring program includes:
 VOCs, TOC, Dhcv, vCRA
 Field parameters
CVOC Data – kg estimated in
source area (EVS)
0
200
400
600
800
1,000
1,200
1,400
1,600
1,800
11/1/2008 5/20/2009 12/6/2009 6/24/2010 1/10/2011 7/29/2011 2/14/2012 9/1/2012 3/20/2013
TCE (kg) cDCE VC Ethene
CVOC Data – normalized (C/C0) to show
ethene generation (also VC…uh oh)
0.001
0.01
0.1
1
10
100
Nov-08 May-09 Dec-09 Jun-10 Jan-11 Jul-11 Feb-12 Sep-12 Mar-13
TCE cDCE VC Ethene CVOC
Not to worry - VC Data regression
y = -0.1601x + 6676.3
R² = 0.7136
-20
0
20
40
60
80
100
120
140
160
Dec-11 Apr-12 Jul-12 Oct-12 Jan-13 May-13 Aug-13 Nov-13 Mar-14 Jun-14
Estimated VC Mass (kg)
Estimated VC Mass (kg) Linear (Estimated VC Mass (kg))
TOC Data – Mean of Full Scale
Data Set (n=23)
194
0
500
1000
1500
2000
2500
3000
3500
Total Organic Carbon (Total and Dissolved)
Primary Well Group (mg/L)
TOC (Total) - Mean TOC (Total) - Geometric Mean TOC (Dissolved) - Mean TOC (Dissolved) - Geometric Mean
Background TOC ~ 10 mg/L
Dhc Data – Full Scale Data Set
(n=23)
1.E+04
1.E+05
1.E+06
1.E+07
1.E+08
1.E+09
1.E+10
7/1/2009 1/17/2010 8/5/2010 2/21/2011 9/9/2011 3/27/2012 10/13/2012 5/1/2013
DHC
Full Scale Well Group (Count)
1/2 of non-detect values used
vCRA Data – full scale data set
1.00E+04
1.00E+05
1.00E+06
1.00E+07
1.00E+08
1.00E+09
1.00E+10
6/1/2008 12/18/2008 7/6/2009 1/22/2010 8/10/2010 2/26/2011 9/14/2011 4/1/2012 10/18/2012 5/6/2013 11/22/2013
vcrA
Primary Well Group
(Count)
1/2 of non-detect values used
TOC and DHC Data – Long Term
(n=4)
1.E+03
1.E+04
1.E+05
1.E+06
1.E+07
1.E+08
1.E+09
0
500
1000
1500
2000
2500
3000
3500
4000
5/1/2006 9/13/2007 1/25/2009 6/9/2010 10/22/2011 3/5/2013
Dhc(count)
TOC(mg/L)
WS-19 WS-18-101 WS-18-71 DHC
ORP data
-200
-150
-100
-50
0
50
100
150
200
37922 38288 38653 39018 39383 39749 40114 40479 40844 41210
Redox potential
Mean of Primary Well Group (n varies) eH - Mean
Analysis
 All indicators look good!
 VOC mass decreasing
 Sustained elevated TOC levels
 Sustained negative ORP levels
 Continued ethene generation
 Regression predicts VC decrease by 2014
 Some indicators look iffy?
 Would like to see higher Dhc numbers?
 Others?
Results
 Success!
 Other considerations
 DNAPL/CVOC reduction
 Other
 Useful?
Summary (tbd)
 Literature range sets boundaries
 20 – 750 yrs (latter less useful)
 Developing data set
 Regression provides simple tool for prediction
 Dual rates observed and should be considered
 Early consumption followed by equilibrium
 Modeling is promising approach
 Estimates match lower range of regression
 Can provide conservative (short) predictions to
improve site planning/closure
Implications (tbd)
 Micro-scale ZVI is extremely durable
 Data fit well with other observations
 Similarity to presumed P&T timeframes (30 yrs)
 How do we manage long-term?
 Is monitoring required to demonstrate complete
exhaustion?
 How can we extend confidence of this long-term
remedy to support site closure?
Acknowledgements/Questions
 Thank you.
 SiREM Laboratories
 FMC Environmental Solutions
 Questions?

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Long Term Monitoring Data 2013

  • 1. LONG TERM MONITORING DATA EVALUATION OF BIOAUGMENTATION DURING ISCR-ENHANCED BIOREMEDIATION OF TCE DNAPL James G.D. Peale, RG Erik I. Bakkom, PE (Maul Foster & Alongi Inc.) Jeff Roberts, Sandra Dworatzek (SiREM Laboratories) Josephine Molin (FMC Environmental Solutions) June 2013
  • 2.  Site Overview  Technology Summary  Problem Statement  Analysis  Results  Summary  Implications TOPICS
  • 3.  Former MGP waste site redeveloped for manufacturing in 1970s  80+ acres adjacent to Portland Harbor NPL site  TCE released from a recycling system (1980-1985)  Impacts from release discovered in 2002  TCE DNAPL Source Zone  Impacts from about 5-34 m bgs  TCE up to 592,000 ug/L (DNAPL levels)  No TCE DNAPL observed  Cis-1,2-DCE up to 90,800 ug/L  Very little VC (< 100 ug/L) Site Overview
  • 5. Technology Summary  EHC  Powdered blend of zero-valent iron (ZVI) and hydrophilic organic carbon  Creates strongly reducing conditions in groundwater for in situ chemical reduction (ISCR)  ISCR results in abiotic dechlorination and supports anaerobic bacteria  KB-1  Anaerobic consortium of dechlorinating bacteria  Includes dehalococcoides sp.  Requires ORP < -75 mV  Both technologies demonstrated success for dissolved CVOC plumes
  • 6. Technology Summary  EHC+KB-1 Full-Scale Implementation  46 m x 21 m x 3 m PRB – Source area only  Injected from ~12 – 34 m bgs  Supplemental upgradient areas  200+ injection points  ~269,400 kg EHC  1,831 L KB-1  Direct-push drilling  23 Performance Monitoring Wells
  • 10. Problem Statement  Remedial action objective is 11,000 ug/L  Threshold indicator for TCE DNAPL  Achieved in less than 12 months  Achieved mean TCE 3 ug/L  Declining cDCE and VC, but still elevated in some wells  Dhc counts 107 – 108  Question: how long can this continue?  Will we see rebound?
  • 11. Problem Statement  How long will Dhc sp. flourish?  Organic carbon needs  (other)  Continued reducing conditions?  Field data  Other functional requirements?  Continued cVOCs?
  • 12. Long-Term Data Sets  Pilot Study Data  2006-2008  Shallow and deep wells, within and downgradient of injection zone  Full-scale Data  2009-present  19 wells + pilot study wells  Monitoring program includes:  VOCs, TOC, Dhcv, vCRA  Field parameters
  • 13. CVOC Data – kg estimated in source area (EVS) 0 200 400 600 800 1,000 1,200 1,400 1,600 1,800 11/1/2008 5/20/2009 12/6/2009 6/24/2010 1/10/2011 7/29/2011 2/14/2012 9/1/2012 3/20/2013 TCE (kg) cDCE VC Ethene
  • 14. CVOC Data – normalized (C/C0) to show ethene generation (also VC…uh oh) 0.001 0.01 0.1 1 10 100 Nov-08 May-09 Dec-09 Jun-10 Jan-11 Jul-11 Feb-12 Sep-12 Mar-13 TCE cDCE VC Ethene CVOC
  • 15. Not to worry - VC Data regression y = -0.1601x + 6676.3 R² = 0.7136 -20 0 20 40 60 80 100 120 140 160 Dec-11 Apr-12 Jul-12 Oct-12 Jan-13 May-13 Aug-13 Nov-13 Mar-14 Jun-14 Estimated VC Mass (kg) Estimated VC Mass (kg) Linear (Estimated VC Mass (kg))
  • 16. TOC Data – Mean of Full Scale Data Set (n=23) 194 0 500 1000 1500 2000 2500 3000 3500 Total Organic Carbon (Total and Dissolved) Primary Well Group (mg/L) TOC (Total) - Mean TOC (Total) - Geometric Mean TOC (Dissolved) - Mean TOC (Dissolved) - Geometric Mean Background TOC ~ 10 mg/L
  • 17. Dhc Data – Full Scale Data Set (n=23) 1.E+04 1.E+05 1.E+06 1.E+07 1.E+08 1.E+09 1.E+10 7/1/2009 1/17/2010 8/5/2010 2/21/2011 9/9/2011 3/27/2012 10/13/2012 5/1/2013 DHC Full Scale Well Group (Count) 1/2 of non-detect values used
  • 18. vCRA Data – full scale data set 1.00E+04 1.00E+05 1.00E+06 1.00E+07 1.00E+08 1.00E+09 1.00E+10 6/1/2008 12/18/2008 7/6/2009 1/22/2010 8/10/2010 2/26/2011 9/14/2011 4/1/2012 10/18/2012 5/6/2013 11/22/2013 vcrA Primary Well Group (Count) 1/2 of non-detect values used
  • 19. TOC and DHC Data – Long Term (n=4) 1.E+03 1.E+04 1.E+05 1.E+06 1.E+07 1.E+08 1.E+09 0 500 1000 1500 2000 2500 3000 3500 4000 5/1/2006 9/13/2007 1/25/2009 6/9/2010 10/22/2011 3/5/2013 Dhc(count) TOC(mg/L) WS-19 WS-18-101 WS-18-71 DHC
  • 20. ORP data -200 -150 -100 -50 0 50 100 150 200 37922 38288 38653 39018 39383 39749 40114 40479 40844 41210 Redox potential Mean of Primary Well Group (n varies) eH - Mean
  • 21. Analysis  All indicators look good!  VOC mass decreasing  Sustained elevated TOC levels  Sustained negative ORP levels  Continued ethene generation  Regression predicts VC decrease by 2014  Some indicators look iffy?  Would like to see higher Dhc numbers?  Others?
  • 22. Results  Success!  Other considerations  DNAPL/CVOC reduction  Other  Useful?
  • 23. Summary (tbd)  Literature range sets boundaries  20 – 750 yrs (latter less useful)  Developing data set  Regression provides simple tool for prediction  Dual rates observed and should be considered  Early consumption followed by equilibrium  Modeling is promising approach  Estimates match lower range of regression  Can provide conservative (short) predictions to improve site planning/closure
  • 24. Implications (tbd)  Micro-scale ZVI is extremely durable  Data fit well with other observations  Similarity to presumed P&T timeframes (30 yrs)  How do we manage long-term?  Is monitoring required to demonstrate complete exhaustion?  How can we extend confidence of this long-term remedy to support site closure?
  • 25. Acknowledgements/Questions  Thank you.  SiREM Laboratories  FMC Environmental Solutions  Questions?