FRACTURED BEDROCK CHARACTERISATION AND EFFECTIVE REMEDY SELECTION IN REGION 4 BEN BENTKOWSKI, P.G. EPA REGION 4
11/2/2010 EPA Region 4 Perspective 1
FRACTURED BEDROCK CHARACTERISATION AND EFFECTIVE REMEDY SELECTION IN - - PowerPoint PPT Presentation
FRACTURED BEDROCK CHARACTERISATION AND EFFECTIVE REMEDY SELECTION IN REGION 4 BEN BENTKOWSKI, P.G. EPA REGION 4 11/2/2010 EPA Region 4 Perspective 1 Presentation Outline Region 4s area with Fractured Bedrock Aquifers Examples of three
FRACTURED BEDROCK CHARACTERISATION AND EFFECTIVE REMEDY SELECTION IN REGION 4 BEN BENTKOWSKI, P.G. EPA REGION 4
11/2/2010 EPA Region 4 Perspective 1
Region 4’s area with Fractured Bedrock Aquifers Examples of three kinds of aquifers
Fractured Metamorphic Fractured Igneous Fractured Sedimentary
Characterization and Remediation
Five Federal Facilities Four Non-Federal Facilities
Summary and Conclusions
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Fractured Metamorphic Rock
Lawrenceville, GA
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Fractured Igneous Rock
Fractured Sedimentary Rock
West Trenton, NJ Manchester, TN
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Air Force Plant No. 6 - Marietta, GA Fractured Metamorphic Rock - Piedmont
Site Map
Air Force Plant No. 6 - Marietta, GA Fractured Metamorphic Rock - Piedmont
Airplane Assembly since WWII Multiple Solvent Releases Detailed Characterization Groundwater contamination in saprolite, partially
weathered rock (PWR) (together considered the
Dissolved Phase and DNAPL
Most recent report – (third) Annual Corrective Action
Effectiveness Report - RCRA
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Air Force Plant No. 6 - Marietta, GA Fractured Metamorphic Rock - Piedmont
Bedrock cores and thin section analysis (gneiss v. schist) Borehole geophysics PWR aquifer test - one connected anisotropic aquifer
but with differing properties
Site-wide water level gauging and gradient analysis
suggesting less flow in BR
Extensive soil and groundwater sampling Conceptual Site Model development
10 11/2/2010 EPA Region 4 Perspective
Air Force Plant No. 6 - Marietta, GA Fractured Metamorphic Rock - Piedmont
Hydrogeology Conceptual Site Model DNAPL Conceptual Site Model
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Air Force Plant No. 6 - Marietta, GA Fractured Metamorphic Rock - Piedmont
Conceptual Site Model
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Air Force Plant No. 6 - Marietta, GA Fractured Metamorphic Rock - Piedmont
TCE in the Overburden Aquifer
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Air Force Plant No. 6 - Marietta, GA Fractured Metamorphic Rock - Piedmont
TCE in the Bedrock Aquifer
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Air Force Plant No. 6 - Marietta, GA Fractured Metamorphic Rock - Piedmont
Air Sparge/Soil Vapor Extraction in Overburden Aquifer and Vadose Zone In-Situ Chemical Oxidation in Overburden Aquifer Microbiological Enhancement with Microbes Permeable Reactive Barrier Monitored Natural Attenuation Land Use Controls
11/2/2010 EPA Region 4 Perspective 15
Air Force Plant No. 6 - Marietta, GA Fractured Metamorphic Rock - Piedmont
GOALS: Reduce Mass Flux and Offsite Migration & Facilitate MNA
This is happening but offsite investigation handled by different contractor
TIMEFRAME: Estimated for Overburden, not for Bedrock aquifer NOTE: No treatment of DNAPL in the fractured bedrock
“It is important to emphasize that the presence of residual DNAPL does not impact the conclusions of the RA (risk assessment) and the recommendations for site risk management.”
Final Corrective Action Plan, p. 2-5
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Alabama Army Ammunition Plant - Childersburg, AL Fractured Sedimentary Rock
Located 40 miles southeast of Birmingham, AL Operated 1941 -1945 manufacturing TNT, DNT Approximately 5,000 acres Standby 1946 – 1973 and declared excess Property no longer owned by Army CERCLA investigations started in the 1980s Source Control - 120,000 cubic yard soil incineration
1994-97
2010 - Final Soils ROD Groundwater RI completed 2010
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Alabama Army Ammunition Plant - Childersburg, AL Fractured Sedimentary Rock
Formation, carbonates
tectonic activity resulting in significant fractures
whose course is fracture controlled
Alabama Army Ammunition Plant - Childersburg, AL Fractured Sedimentary Rock
MAIN MANUFACTURING AND STORAGE AREA I nvest i gat ed wi t h t r adi t i
ased/ hotspotm et hods butdi d notpr
de accept abl e gr
erchar act er i zat i
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Alabama Army Ammunition Plant - Childersburg, AL Fractured Sedimentary Rock 2003 - 2009 GW Investigation
the fractured nature bedrock
relatively minor problem
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Redstone Arsenal - Huntsville, AL Fractured Sedimentary Rock
38,300 acres just west of Huntsville, AL 1,841 acre Marshall Space Flight Center within
Redstone Arsenal property
158 active IRP sites, 20 surface media OUs, 13 GW
investigation areas
Finalized on NPL in 1994 COCs – solvents, metals, pesticides, perchlorate &
chemical weapons material
Karst hydrogeology with fractured bedrock influence
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Redstone Arsenal - Huntsville, AL Fractured Sedimentary Rock
Structural setting –horst
and graben
Dipping limestones Thermal imaging of springs Coring, hydro-physics,
flute wells
Complicated groundwater
chemistry with salt water and natural oil at depth
Redstone Arsenal - Huntsville, AL Fractured Sedimentary Rock
Local Conceptual Hydrogeologic Model Ar ea- wi de Concept ualHydr
calM odel
Figures from MSFC reports 11/2/2010 EPA Region 4 Perspective 22
Redstone Arsenal - Huntsville, AL Fractured Sedimentary Rock
C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! ! C ! ! ! C ! ! ! ! ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! ! ! ! C ! C ! C C C C ! ! C ! C ! C ! C ! C ! C C C C ! C C ! ! C ! C ! C ! C ! C ! C !! C! C ! C ! C ! C C C C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! ! C ! C ! C ! C ! C C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C ! C
schkaem per ,O ctM ap showi ng TCE Pl um e and W el l s wi t h G r
er > 1% Ef f ect i ve Sol ubi l i t y
l ayed wi t h t he I nt er pr et ed Faul t s based on Sei sm i c Li nes RSA
11/2/2010 EPA Region 4 Perspective
M ap by Kay W iExpl anat i
! C
W el l s wi t h Ef f ect i ve Sol ubi l i t y > 1% Sei sm i c Faul tLi nes2009 TCE G r
erPl um e
Concent r at i
( ug/ L)
1 -10 10 -100 100 -1, 000 1, 000 -10, 000 10, 000 -100, 000 >100, 00023
11/2/2010 EPA Region 4 Perspective 24
Oak Ridge Reservation, Oak Ridge, TN Anniston Army Depot, Anniston, AL Fractured Sedimentary Rock
Very large, very complex sites in Valley and Ridge Hydrogeology is a blend of fractured due to tectonic
activity and karst due to carbonates
Both facilities have performed source
control/removals and interim actions for receptor protection
Neither have final groundwater remedies for their
largest releases
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Fractured Metamorphic Rock – Piedmont with Igneous Intrusions Source Area (Tank Farm)
Overall, much smaller scale of release & remedial action BUT uses broad range of characterization techniques COCs – Benzene, Chlorobenzene Cis-1,2-DCE, Vinyl Chloride
Fractured Metamorphic Rock – Piedmont with Igneous Intrusions
Regional recon and outcrop mapping – site at edge of thrust
sheet
Lineament studies and rose diagrams Trenching perpendicular to creek and structural dip – detailed
logging
Found series of intrusive dikes in soil/saprolite Used structural information to predict anisotropy and
design aquifer characterization
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Fractured Metamorphic Rock – Piedmont with Igneous Intrusions
Membrane Interface Probe used in Source Areas Cored bedrock with packer and analytical tests on
fracture features
Bedrock aquifer test – 60 GPM with minimal drawdown
(14 GPM Steady State P&T)
Capture zone analysis using simplified three layer model Ozone sparging source control/treatment Groundwater recovery system – plume migration
control
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Fractured Metamorphic Rock – Piedmont with Igneous Intrusions
GW Flow direction Baseline conditions After 90 and 200 days
Ozone Air Sparge Progress
Fractured Metamorphic Rock – Piedmont with Igneous Intrusions
Why was Ozone Sparging Successful at J.P. Stevens?
Sparge and multi-level injection points enhance shape
Monitoring of indicator parameters (ORP, DO)
substantiated ozone was impacting groundwater
Good interconnection between saprolite and bedrock Multiple depths of injection and monitoring Well-designed pilot study
Length of monitoring before, during, and after Spacing of monitoring points
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Hitachai - Greenville, SC Fractured Metamorphic Rock
Release of 12,000+ lbs of TCE This remedial action employed
In-Situ Thermal Desorption in soils and shallow bedrock
14 Heater wells (~90’ bls) 10 Heater vacuum points (~95’
bls)
2 Recovery wells (~45-76’ bls)
recovered 72,000 gallons of
water during operation before water became steam
Ther m alTr eat m entAr ea 33’ x76’ x90’deep PW R at55’
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Hitachai Greenville, SC Fractured Metamorphic Rock
BEFORE AFTER Note: treatment zone only 2,500 ft2
Hitachai Greenville, SC Fractured Metamorphic Rock
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Hitachai Greenville, SC Fractured Metamorphic Rock
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Hitachai Greenville, SC Fractured Metamorphic Rock
Removed about 12,000 lbs TCE (~5 months operation) Met treatment goals for vadose zone soil
Goal was 60 ug/kg TCE Attained 13.41 ug/kg TCE (UCL) Overall soil (vadose and subaqueous) 17.05 ug/kg TCE
Initial reductions of 75% to 99% of TCE in groundwater Rebound noted (DNAPL; Fractures, Relic Fractures, Back-
Diffusion)
Longer treatment period required for more bedrock
improvement
Progress towards but not the Final Remedy
Fractured Metamorphic Bedrock
Historical solvent release managed with shallow SVE
and ozone treatment in nearby springs – interim remedy
Ongoing investigation focused on facility and
generally shallower portions of bedrock aquifer
Private deep bedrock drinking water supply wells
contaminated up to 1 mile away
Detailed geological mapping by State Geologic Survey Detailed hydrogeological characterization by USGS
11/2/2010 EPA Region 4 Perspective 35
Robi nso n Cr eek Conco r d R d . Chap e l H i l l Chur c h R d . M i l l s G a p R d .
4 5 1 3 5 2 2 5 3 1 5 4 5 1 3 5 2 2 5 3 1 5 4 5 1 3 5 2 2 5 3 1 5 4 5 1 3 5 2 2 5 3 1 5 4 5 1 3 5 2 2 5 3 1 5 4 5 1 3 5 2 2 5 3 1 5 45 135 225 315 4 5 1 3 5 2 2 5 3 1 5 4 5 1 3 5 2 2 5 3 1 5 45 135 225 315 225 315 225 315Expl anat i
!
O aks W el l s t hatwer e E- Logged Col l uvi um adj acentt
aul t
A
AWCol l uvi um Uni t
CTS W el l s and Spr i ngs
16 14 12 10 8 AWAl l uvi um
Sam pl eType
r u ct ur es 6 4 ERT- 7 Al lSt r uct ur es 10 2 AW 270# * Spr
i ng
8 6 14 12 2Col l uvi alDeposi t s f r
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4 10 12 O aks- 2 Al lSt r uct ur es 6 4 8 10 8 18 8 6 10 2 16 6! >
12 14W el l
G eol
c Uni t s
14 270 10 8 6 4 2 2 4 6 8 4 10 4 90 ERT- 6 Al lBor ehol e St r uct ur es 12 2 2 10 16 2 270 14 12 10 8 6 4 2 2 4 6 8 10 12 14 90 8 270 12 10 8 6 18 4 2 2 4 6 8 10 12 90 12 180 6 2 4 2 10 8 2 4 6 6 6St r eam s
Uni tNam e
4 4 270 18 16 14 12 10 8 6 4 2 8 6 10 8 2 4 8 4 10 6 2 270 12 10 8 6 4 2 2 12 14 10Am phi bol i t e
8 180M i l l s G ap Faul tZone m ai n cor r i dor
12 180 2 10 4 12 6 14 16 8 180M et agr aywacke
18 10 12 180CTS Si t e
180Schi st
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Rose Di agr am s depi ct i ng
CHR Al l Stt he O r i ent at i
Al lSt r uct ur es i n t he O aks
7 6 5W el l s,t hatwer e l
Acoust i c Tel evi ewerFr act ur es atCTS
1 1 1 2 2 3 3 4 4 5 5 6 6 7 7 8 8 90 270 1Buncom be Count y ,NC
2 3 4 5 6 7 8 180 C TS- 9B ATV Fr act ur es 14 12 10 CTS- 4B ATV Fr act ur es 8 6M W
M W - 6 M W - 7A
2 10 4 5 6M W - 6A
8 270 25 20 15 10 5 5 10 15 20 25 90 10 12 W el l1 Al lSt r uct ur es 5 14 10 18 CTS- 11B ATV Fr act ur es 16 180 15M W
SPR- 01
8 25M W - 3A
10 6 4SPR- 03
8 C TS- 1B ATV Fr act u r es 180 6 14 2 4 12 270 10 8 6 4 2 2 4 6 8 10 90 10 2 8 6 270 18 16 14 12 10 8 6 4 2 2 4 6 8 10 12 14 16 18 90 4M W - 10BM W - 10
2 2 4 2 6 4235 470 940 1, 410 1, 880
Feet
Fi gur e by Kay W i schkaem per ,O ct
,201,M i l l s G ap Rd.
11/2/2010 EPA Region 4 Perspective 36
Fractured Metamorphic Bedrock
Historical site understanding focused investigation
topographically downgradient and shallower
Employed sophisticated characterization techniques to
understand possible connections between solvent releases and contaminated private drinking wells
Deepest contaminated well discovered to date - 700’
deep
Recent characterization work will guide future work
with a much improved conceptual site model. However, it does not represent an easy path forward.
11/2/2010 EPA Region 4 Perspective 37
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Actual Example of Poor Characterization Fractured Rock – North Carolina Piedmont
One well with 50’ open hole completion in bedrock with DNAPL
solvents
Two analytical data points -1 set of three diffusion bag samplers and 1
sample collected 6 months later by low flow purge
Proposed one well pilot study - Enhanced Reductive Dechlorination
11/2/2010 EPA Region 4 Perspective 39
Actual Example of Poor Characterization Fractured Rock – North Carolina Piedmont
Just a Few of the Problems with This Approach
Contamination not delineated No surveys to identify fractured zones No other proposed monitoring wells Pilot Study would invalidate the use of this one well as a
monitoring location
No demonstration of how this well relates to the rest of
the site or how this test would benefit the rest of the site
11/2/2010 EPA Region 4 Perspective 40
SUMMARY EPA Region 4 Perspective
Large facilities, Large number of releases, Large volume of
releases
Applying a wide range of increasingly sophisticated
characterization technologies
Performing source removal, source control and receptor
protection
Final groundwater remedies - uncommon Deep fractured bedrock remediation - no final answer YET
11/2/2010 EPA Region 4 Perspective 41
SUMMARY EPA Region 4 Perspective
Smaller facilities and smaller releases Also applying a wide range of increasingly sophisticated
characterization technologies
Appear to have made more progress
Smaller problems, smaller solutions different motivation - Industry v. Federal
Deep fractured bedrock remediation – no final answer YET
11/2/2010 EPA Region 4 Perspective 42
CONCLUSIONS This Hydrogeologist’s Perspective
Last 20 years have made great advances in types and sophistication of characterization.
Focus on flow zones and geophysics/sensors
Biggest number of unresolved sites have dissolved or DNAPL solvents in fractured bedrock. At a basic level, it still a question of really understanding the nature and extent of the contamination and how that affects the selection of an effective remedy.
CONCLUSIONS This Hydrogeologist’s Perspective
Good progress on remediating saprolite and partially
weathered bedrock
Fractured Bedrock and Solvents
No cure for this problem yet Difficult and expensive to characterize flow pathways at depth Back diffusion and time (cost) to remediate – biggest
impediments
Ultimate Goal The MCL CONCENTRATION
11/2/2010 EPA Region 4 Perspective 43