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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
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
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?