in situ thermal treatment– lessons...
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22nd Annual NARPM Training Program 1 22nd Annual NARPM Training Program 22nd Annual NARPM Training Program
In Situ Thermal
Treatment– Lessons
Learned
Jim Cummings
Technology Innovation and Field Services Division OSRTI/OSWER/USEPA
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Organization of Presentation
National Perspective on In Situ Thermal Treatment
Lessons Learned
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In Situ Thermal Treatment
Electrical Resistance Heating (ERH)
Thermal Conductive Heating (TCH)
Steam Enhanced Extraction (SEE)
• * * * *
• Radio Frequency Heating (RF)
• * * * *
• Self Sustaining Technology for Active Remediation (STAR)
• Gas Thermal Remediation (GTR)
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National Perspective
+/- 100 Completed In Situ Thermal projects - domestic and international (# growing)
All vendors report being very busy
May result in few(er) bids in response to RFPs
(Grants, NM dry cleaner project had one bidder)
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National Perspective (cont.)
Variety of contaminants Low boiling point solvents Petroleum hydrocarbons High boiling point coal tars and PCB’s
Variety of unconsolidated and consolidated lithologies (Fractured rock, the Last Frontier…)
Variety of conditions/situations Beneath (inhabited) buildings Considerable depth (c. 130’) Below the water table
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Attributes
Effective across a wide range of permeabilities
Thermal conductivity varies +/-2 over 106
permeability contrast
Significant shortening of remedial timeframes
In Situ Process Control
Possible beneficial impacts on downgradient contamination
No evidence of (dreaded) ‘rebound’
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‘Sampler’ of Completed In Situ Thermal
Projects at NPL and NPL-caliber sites
Visalia, Ca NPL wood treater - SEE
Delisted from NPL
Pemaco, Ca Solvent NPL Site - ERH+
Camelot Cleaners, Fargo ND - ERH
Tight clays
Groveland Wells, Ma - ERH+SEE
Silresim, Ma - ERH
Grants, NM Drycleaner - ERH+
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‘Sampler’ – On-
Going/Planned/Prospective NPL caliber
In Situ Thermal Projects
Frontier Fertilizer, Ca (pesticides) - ERH
SRSNE, Conn - TCH
S Muni Water Supply Well site,
Peterborough, NH - ERH+
Carter Carburetor, Mo. – PCB - TCH(?)
Wyckoff, Wa., wood treater - SEE/TCH
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ERH Innovations
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Angled Electrode Boring – AF Plant
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Photo Courtesy
URS
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Sheet Pile Electrodes
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Horizontal Electrodes
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Lessons Learned
Actual performance often exceeds cleanup goals
For ERH, need to add water adjacent to electrodes to prevent soil drying and ensure current flow
Media conductivity (e.g., fill) may affect ERH applicability/performance
For SEE, ensure proper closure of existing monitoring wells, etc. in treatment volume prior to heating (NOT hypothetical)
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Lessons Learned
Possible to heat discrete zones – horizontally and vertically – reduce treatment volume
Systems can be installed entirely below grade
No conflict w/ facility operations or pedestrian/vehicular traffic
Subsidence rarely a problem But see Fargo, ND dry cleaner as main/only(?) exception
Buried utilities, etc., usually not a problem (but see SRSNE)
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Naphthalene Pipe Clogging
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Lessons Learned
‘Step 1…’ – Check with local utility regarding power and equipment availability (and KEEP checking)
Especially in areas undergoing development
If there is a lot of contamination in the ground, you will recover it Have the (big) catcher’s mitt ready
Cummings’ rule of remediation – mass = 2-5X estimated
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Lessons Learned
Specifying generic ISTT in RFP for CVOC sites will allow both ERH and TCH vendors to bid
‘Hot sampling’ allows discontinuing heating of zones which have met cleanup goals
• Don’t have to wait 12-18 months for site to cool before demobilizing treatment equipment
Concentrate power in zones not cleaning up as quickly
A point about sustainability: Carbon footprint for electrically heating 1 yd3 of contaminated soil
digging and hauling it 65 miles (source: Terratherm)
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Resources
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EPA-542-R-04-010 –
Mar 04
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Resources/Contact Information
Jim Cummings [email protected] 703-603-7197
Eva Davis
[email protected] 580-436-8548
Web-based resources www.cluin.org www. Frtr.gov
In Situ Thermal Treatment of Chlorinated Solvents: Fundamentals and Field Applications – EPA 540-R-04-010 Mar 2004
In Situ Thermal Treatment – Lessons Learned – In preparation
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Selective Heating – Memphis Depot
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Dunn Field,
Memphis Depot,
TN
8 DNAPL
source areas,
CVOCs
49,800 cubic
yards
(Semi-) Surgical
remediation
(Heron et al. 2009)
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Aerial View of Memphis Site (During Demob)
367 heaters
68 extraction wells
367 heaters
68 extraction wells
Central Treatment
Equipment
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New Kids on the Block
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STAR – Self-Sustaining Technology for
Active Remediation
In Situ Combustion Exothermic reaction converting
carbon compounds CO2 + H2O
-Take advantage of BTU content of wastes
Smoldering Flameless
Occurs in porous materials
Temperatures typically 400 – 800 oC
Propagation typically 5 ft/day
Oxygen-limited, thus controllable
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HEATER OFF
Heating
Element
AIR
SUPPLY
NAPL
SOIL GRAINS
GROUNDWATER
NAPL Smoldering
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STAR Application
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Post-pilot Soil Sampling
Pilot Results – Pitt Consol DuPont
Facility in NJ
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Before
After
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Post-pilot Soil Sampling
Average
Concentration
Reduction = 99.72%
Approximately
10,000 # of coal tar
destroyed in situ
Proceeding to full-
scale
STAR Pilot Results
Before STAR TreatmentCombustion Zone
T > 600 oC
2,4-Dimethylphenol 635 1
2-Methylnaphthalene 7,900 10
2-Methylphenol 475 3
4-Methylphenol 595 5
Acenaphthene 3,950 6
Acenaphthylene 295 1
Anthracene 16,700 10
Benzene 36 0
Benzo(a)anthracene 775 2
Benzo(a)pyrene 505 1
Benzo(b)fluoranthene 640 2
Benzo(g,h,i)perylene 255 1
Benzo(k)fluoranthene 240 1
Carbazole 6,750 2
Chrysene 870 3
Dibenzo(a,h)anthracene 60 0
Dibenzofuran 3,850 7
Ethylbenzene 40 0
Fluoranthene 3,750 11
Fluorene 5,150 7
Indeno(1,2,3-cd)pyrene 220 1
Naphthalene 29,500 63
Phenanthrene 10,850 21
Pyrene 2,550 8
Toluene 130 0
Xylenes (total) 225 0
TPH-DRO soil C10-C28* 118,000 243
TPH-GRO soil C6-C10 1,300 7
Compound
Average Concentration (mg/kg)
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CLIQUEZ ET MODIFIEZ LE TITRE
GTR© - Gas·Thermal·Remediation
IN-SITU AND EX-SITU THERMAL DESORPTION APPLICATIONS
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How it Works
More information at:
www.tpsthermal.com
Closed-loop in-situ
thermal conductive
heating system;
Co-located vapor
extraction and heating
wells;
Treatment
temperatures from
~100°C to >400°C
Small Case Study: ISTT Underneath Building
Contaminants : Petroleum and Heavy Hydrocarbons
Max. Concentration: 15,000 mg/kg Depth: 21 ft bgs
Geology: Sand, silt Volume: 400 m3
Treatment Time: 25 days Target Temperature: 200°C
Challenges: Difficult access in basement; Rapid schedule RE transaction
Remedial Goal: < 300 ppm Remedial Result: Avg. Concentrations < 90 ppm
Both Performance and Time Guarantees Achieved Turnkey ISTD Cost: $168 / cu yd (note: larger areas generally less costly)
Reuse of TCH Wells: Geothermal Heat Storage
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Water in
Water out
When the commercial building was
redeveloped to residential apartments, the
heating wells were left in place and converted
to geothermal heat storage wells with PTFE
tubing. The system harnesses the constant
temperature of the subsurface to preheat
municipal water prior to the building’s boiler
system. The use of the wells in this manner
also contributes to a more rapid reduction in
in-situ soil temperatures.
Current, Select “Small” Projects (North America)
Chlorinated Solvents: 900 cu yards ISTD (indoor installation) San Francisco 3,100 cu yards ISTD (active facility) Toronto
BTEXs 2,700 cu yards ISTD (former petrol station) Sacramento 3,000 cu yards Ex-Situ Thermal Treatment in Wyoming
PCBs 1,300 cu yards ISTD (to residential goals) in California
Dioxins 1,900 cu yards Ex-Situ Thermal Treatment near Phoenix
Coal Tar 2,500 cu yards ISTD (to residential goals) in Illinois
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PCB Pilot Study (Commenced June 2012) Initial Soil Concentrations: Average 5,900 mg/kg (Aroclors 1242, 1260)
Design Remedial Goal: Average samples < 10 mg/kg
Design Duration > 250° C: 72 hours (64 days total heating duration)
CEM: ambient air and emissions monitoring (reason for tent)
Full Scale: project is > 10,000 cubic yards (combination of in situ and ex situ soils); estimated start date January 2013.
PCB Pilot Study (Vadose + Saturated Zones) Three Phases of Thermal Conduction Heating: First: Heating from ambient to boiling point of water (100°C) Second: Boiling, evaporation of groundwater in TTZ (steam stripping and removal of mobile DNAPL) Third: Superheating from 100°C to 250°C (thermal destruction of residual DNAPL)
PCB Pilot Study (Initial Results) Final results will be published in a scientific journal Spring 2013.
Lessons Learned:
1. High temperature hydrolysis effected significant dechlorination of PCBs during remediation and likely acts as a positive polishing effect (more in our article).
2. Significant mass was extracted as NAPL and vapour off-gas. C3 Technology vapor condensation system specified for full scale treatment.
3. ND levels of dioxins and furans measured (low potential for indoor air quality impacts). Levels of dioxins and furans are now being measured in soil and groundwater for pre- vs. post-treatment quantification.
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Cool (or Hot) New Idea
Post-Remediation use of ISTT Infrastructure to support Geothermal Heat Pump for HVAC
Considered for Frontier Fertilizer site but big box retailer decamped
Reportedly part of plan post-ISTT at industrial facility in Bordeaux, France
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Vendor Contact Information –
Additional Case Studies
Terratherm
- terratherm.com
- Ralph Baker – 978-730-1200
Thermal Remediation Services
thermalrs.com
David Fleming – 425-396-4266
Current Environmental Solutions
Cesiweb.com
Joe Pezzullo – 215-262-7855
McMillan-McGee
Mcmillan-Mcgee.com
Bruce McGee – 403-569-5101
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Vendor Contact Information (cont.)
RF Heating Ray Kasevich [email protected] 413-528-4651
STAR Technology Gavin Grant, Geosyntec [email protected] 919-822-2230
Gas Thermal Remediation TPS Tech America Grant Geckeler [email protected] 858-603-1838