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Speaker 
 Lowell Kessel, P.G. 
 GEO Incorporated - Gas Thermal Remediation Services
Challenging Sites 
 Limited access- no 
excavation 
 Source zone mass removal 
 Complex mix of COCs 
 DNAPL below the water 
table 
 LNAPL smear zones 
 Clay lithology- diffusion 
limited condition 
 Fractured bedrock 
 Other options failed 
Challenging Goals 
 Rapid schedule (<90 days) 
 Low clean-up standards in 
soil, GW or VI 
 High probability of success
 Vapor pressure of organic 
materials increase 
 Viscosity of separate phase 
liquids decrease 
 Increases desorption 
 Diffusion rates increase 
 Solubility increases 
 Increases biodegradation 
 Rates of Hydrolysis 
increase 
 Thermal Oxidation
 Thermal conductivity = measure of the ability of a 
material to conduct heat. How quickly heat 
migrates through it. 
 Thermal Diffusivity = measure of the ability of a 
material to conduct heat relative to its ability to 
store heat. How quickly the temperature of the 
material increases. 
◦ Thermal diffusivity (m2/s) = thermal conductivity 
(W/mK) 
volumetric heat capacity 
4
Heat Transport Equation: 
Soil Thermal conductivity 
(l) 
[W/mK] 
Permeability 
[m2] 
Clay (dry) 0.15-1.8 10-16-10-20 
Water saturated clay 0.6-2.5 
Sand 0.15-0.77 10-10-10-12 
Water saturated sand 2-4 
Gravel (dry) 0.7 10-7-10-9 
Water saturated gravel 1.7-4 
Fractured Bedrock (Granite) 1.4-4.0 
ACE EE 2009 
http://www.engineeringtoolbox.com/thermal-conductivity-d_429.html
 Diffusion limited remediation progress 
◦ Enemy #1 for In Situ Remedies 
 ISCO 
 ISCR 
 MPE / SVE 
 P&T 
1 mm 
[Udell et al. 1999; Alameda Point SEE demonstration] 
Heat transfer occurs 
about 10,000 times 
faster than aqueous 
diffusion in porous 
media and rocks
NAPL 
SOIL 
MINERALS 
ORGANIC 
MATERIAL 
H2O 
Micropores
The influence from enthalpy of 
water vaporization 
Time (Days) 
Temperature (°C)
 Propane/Natural gas/Diesel 
 Closed-loop heating system >> No pollution emissions 
 Soil and groundwater heated by thermal conduction 
 Treatment temperatures from 50°C to >400°C 
 Treat sand, silt, CLAY, Bedrock, and Groundwater 
 Vapor extraction wells remove VOCs 
 VOCs treated by vapor treatment system
Natural gas, propane, 
diesel, gasoline, 
ethanol, etc 
National Avg: April 2014 
Natural Gas per kWh is ~$0.05 
Propane per kWh is ~$0.07 
AC per kWh is ~$0.10 
http://www.eia.gov/electricity/monthly/epm_table_grapher.cfm?t=e 
pmt_5_6_a 
http://www.consumersenergy.com/apps/gasvalues/index.aspx?ekfr 
m=1654 
Flexibility has been key for many 
projects internationally!
Outer tube Inner tube
Level of 
Heating & 
Contaminant 
Target 
Treatment 
Temperature 
(°C) 
Heating 
Well 
Spacing 
(m) 
Desiccation 
of Zone? 
Range of 
Costs (all 
inclusive) 
($/m3) 
1. VOCs: 
Gentle 
Heating 
(BTEX, CVOCs) 
<100 4 – 6 No 40-200 
2. VOCs 
(CVOCs, BTEX) 
>100 2 – 4 Depends 60-300 
3. SVOCs 
(PCBs, PAHs, 
BaP, dioxins) 
200-300 1.5 – 3 Yes 150-600
 Faster (Rapid mobilization, 
smaller footprint, & usually no 
electrical installation required) 
 Scalable (Can be applied to very 
small and very large projects) 
 Pilot Tests for less than 
$200,000 
 Full Scale for less than 
$500,000
N 
 Vapor Treatment system 
permitted with BAAQMD 
 Onsite Liquid Treatment 
 Utilities? 
 Existing Natural Gas 
Connection 
 Existing Electrical 
Connection
Bathroom 
TCU-1-2 
(Before July 8, 2012) 
TCU-1 
(After July 8, 2013) 
TCU-2 
T9 Wall 
SVE-1 TCU-3 
SVE-2 
SVE-3 
SVE-4 
SVE-5 
SVE-6 SVE-12 
SVE-7 
SVE-8 
SVE-10 
SVE-9 
TCU-1 SVE-11 
(Before July 8, 2013) 
TCU 1-2 
(After July 8, 2013) 
T10 Wall 
T1 
T2 
T3 
T5 
T4 
T6 
T7 
T8 
TCU-1-1 
TCU-3-1 
TCU-3-2 
TCU-2-1 
TCU-2-2 
0 40 
Scale In Inches 
 100°C target 
treatment 
temperature 
 9 GTR Heater Wells 
 12 Vapor Extraction 
Points (dual nested) 
 10 TPMPs
0" 
20" 
40" 
60" 
80" 
100" 
120" 
14(May" 
21(May" 
28(May" 
4(Jun" 
11(Jun" 
18(Jun" 
25(Jun" 
2(Jul" 
9(Jul" 
16(Jul" 
23(Jul" 
30(Jul" 
6(Aug" 
13(Aug" 
20(Aug" 
27(Aug" 
3(Sep" 
10(Sep" 
17(Sep" 
24(Sep" 
1(Oct" 
8(Oct" 
15(Oct" 
22(Oct" 
29(Oct" 
5(Nov" 
12(Nov" 
19(Nov" 
26(Nov" 
3(Dec" 
10(Dec" 
17(Dec" 
24(Dec" 
31(Dec" 
7(Jan" 
PPMV$ 
Influent$Vapor$Sampling$Results$ 
PCE" 
0" 
50" 
100" 
150" 
200" 
250" 
300" 
350" 
400" 
12(May" 1(Jul" 20(Aug" 9(Oct" 28(Nov" 
Well$Head$VOC$Data$in$Parts$Per$Million$by$Volume$(PPMV)$ 
SVE$Well$Head$VOC$Data$ 
Head$VOC$Data$in$Parts$Per$Million$by$Volume$(PPMV)$ 
300" 
sve"1" 
sve"2" 
sve"3" 
250" 
sve"4" 
sve"5" 
sve"6" 
sve"7" 
sve"8" 
150" 
sve"9" 
sve"10" 
sve"11" 
Well$100" 
sve"12" 
50" 
0" 
12(May" 1(Jul" 20(Aug" 9(Oct" 200" 
350" 
400" 
Individual SVE Wells 
SVE$Well$Head$VOC$Data$
 100°C Treatment Temperature in Vadose Soils Maintained for 
185 days. 
 2,938 Pounds of PCE, cis-1,2-DCE, and Vinyl Chloride 
Recovered as DNAPL from vapor treatment (condensation) 
system 
 1 month post-remediation vapor results 180 ug/m3. 
 3 month post-remediation vapor results 70 ug/m3. 
 825 pore volume steam exchanges (calculated) in treatment 
zone. 
 5,944 gallons aqueous phase liquid (water) recovered and 
treated onsite.
 Specialized Equipment Needed to Access 
Interior Through Standard 3ft wide Door. 
 High resolution site characterization is key to 
design and cost management 
 Site remediation goals driven by Vapor Intrusion 
Risk and achieved!
 Benzo(a)pyrene and related MGP COCs, 
Naphthalene, TPH-g, TPH-d impacts above residential 
limits, TPH-mo impacts also present. 
 Impacts from surface to 15 ft bgs. 
 Sandy, gravely soils; GW at >90 ft bgs. 
 Residential Goals: 
◦ Combined B(a)P, Naphthalene, and MGP SVOCs: >0.9 mg/kg 
◦ TPH-d: >1,000 mg/kg 
◦ TPH-mo: >10,000 mg/kg
 14 GTR Heater Wells 
 15 Vapor Extraction Points 
 4 TPMPs 
 Onsite Liquid Treatment 
 C2 Technology Vapor Condensation Unit 
(100 scfm) with VGAC 
 Adjacent, Existing Natural Gas Connection 
 Adjacent, Existing Electrical Connection
TC-1 
TCU 
11 
TC-2 
TC-3 
TCU 
5 
TC-4 
CHINA ALLEY 
BT01 BT02 
Holding 
Tank 
Chiller 
Skid 
SVE 
Skid 1 
VGAC2 
Heater 
Fan 
VGAC1 
TCU 
TCU 1 
2 
TCU 
TCU 
12 
TCU 14 
3 
TCU 
10 
TCU 
8 
TCU 
7 
TCU 
4 
TCU 
6 
TCU 
13 
SVE 
SVE 
Skid 2 
TCU 
9 
LGAC 
TITLE: 
TCH Equipment As Built 
SVE Skid 1: After Cooler 
Knock Out Tank 
Chiller Skid: Chiller 
Knock Out Tank 
SVE Skid 2: Blower 
After Cooler 
LGAC: 200 lbs 
VGAC 1: 400 lbs 
VGAC 2: 200 lbs 
Holding 
Tank: 650 gal Tank 
BT01: 2500 gal Tank 
BT02: 1000 gal Tank 
Legend 
TCH / Co-Located Vapor 
Extraction Well (Total: 14) 
Vapor Extraction Well 
1 10 
Scale in Feet 
Pilot Test Treatment Zone 
Conveyance Line 
Equipment 
* Well and Equipment Locations are Approximate
0 
5 
10 
15 
20 
0 100 200 300 400 500 600 
T1 60day T2 60day T3 60day T4 60day 
T1 120day T2 120day T3 120day T4 120day 
°C 
T4 
T2 
T1 
T3 
Depth (ft bgs.)
100 
10 
1 
0.1 
0.01 
BaP BaP Eq. 
10000 
1000 
100 
Max. Conc. 
(mg/kg) Pre- 
Treatment 
Max. Conc. 
(mg/kg) Post- 
Treatment 
10 
1 
TPH-d TPH-mo 
Target 
Treatment 
goal lines 
Max. Conc. 
(mg/kg) Pre- 
Treatment 
Max. Conc. 
(mg/kg) Post- 
Treatment
60 
40 
20 
0 
1 
0.1 
0.01 
0.001 
Post = 
0.01 lbs 
before = 
51.43 lbs 
BaP Equivalent TPH 
Post = ND 
before = 
1.47 lbs 
BaP Equivalent mass (lbs) 
TPH mass (lbs) 
Remedial Objectives Exceeded by Order of Magnitude in 130 Days of ISTD Operation.
1. Greater than expected water content of soil (20% versus anticipated 
10%) and higher water production impacted heating schedule for 
superheated phase. 
2. Electrical interruption caused down time, and thereby impacted 
system heating capabilities (downed power line offsite) – recommend 
providing backup generators 
3. Longer heating duration increased heat lost to surface – installed 
thermal blankets. Recommend higher R value ‘air entrained’ material 
to improve overall thermal efficiencies
GTR© ISTCH Individual Burner System: 
1. Applicability: soil temperatures < 70°C to > 325°C 
2. Speed: Mobilize and commence GTR operations in 
Weeks not months 
3. Scalability: small pilots to acre size projects 
4. Economics: No waiting/paying for electrical 
utilities, transformers, switchgear, third party 
inspections. 
5. Performance Guarantees available

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GEO's Presentation on In Situ Thermal Remediation to EPA Region 9

  • 1. Speaker  Lowell Kessel, P.G.  GEO Incorporated - Gas Thermal Remediation Services
  • 2. Challenging Sites  Limited access- no excavation  Source zone mass removal  Complex mix of COCs  DNAPL below the water table  LNAPL smear zones  Clay lithology- diffusion limited condition  Fractured bedrock  Other options failed Challenging Goals  Rapid schedule (<90 days)  Low clean-up standards in soil, GW or VI  High probability of success
  • 3.  Vapor pressure of organic materials increase  Viscosity of separate phase liquids decrease  Increases desorption  Diffusion rates increase  Solubility increases  Increases biodegradation  Rates of Hydrolysis increase  Thermal Oxidation
  • 4.  Thermal conductivity = measure of the ability of a material to conduct heat. How quickly heat migrates through it.  Thermal Diffusivity = measure of the ability of a material to conduct heat relative to its ability to store heat. How quickly the temperature of the material increases. ◦ Thermal diffusivity (m2/s) = thermal conductivity (W/mK) volumetric heat capacity 4
  • 5. Heat Transport Equation: Soil Thermal conductivity (l) [W/mK] Permeability [m2] Clay (dry) 0.15-1.8 10-16-10-20 Water saturated clay 0.6-2.5 Sand 0.15-0.77 10-10-10-12 Water saturated sand 2-4 Gravel (dry) 0.7 10-7-10-9 Water saturated gravel 1.7-4 Fractured Bedrock (Granite) 1.4-4.0 ACE EE 2009 http://www.engineeringtoolbox.com/thermal-conductivity-d_429.html
  • 6.  Diffusion limited remediation progress ◦ Enemy #1 for In Situ Remedies  ISCO  ISCR  MPE / SVE  P&T 1 mm [Udell et al. 1999; Alameda Point SEE demonstration] Heat transfer occurs about 10,000 times faster than aqueous diffusion in porous media and rocks
  • 7. NAPL SOIL MINERALS ORGANIC MATERIAL H2O Micropores
  • 8. The influence from enthalpy of water vaporization Time (Days) Temperature (°C)
  • 9.  Propane/Natural gas/Diesel  Closed-loop heating system >> No pollution emissions  Soil and groundwater heated by thermal conduction  Treatment temperatures from 50°C to >400°C  Treat sand, silt, CLAY, Bedrock, and Groundwater  Vapor extraction wells remove VOCs  VOCs treated by vapor treatment system
  • 10. Natural gas, propane, diesel, gasoline, ethanol, etc National Avg: April 2014 Natural Gas per kWh is ~$0.05 Propane per kWh is ~$0.07 AC per kWh is ~$0.10 http://www.eia.gov/electricity/monthly/epm_table_grapher.cfm?t=e pmt_5_6_a http://www.consumersenergy.com/apps/gasvalues/index.aspx?ekfr m=1654 Flexibility has been key for many projects internationally!
  • 12.
  • 13.
  • 14.
  • 15.
  • 16.
  • 17. Level of Heating & Contaminant Target Treatment Temperature (°C) Heating Well Spacing (m) Desiccation of Zone? Range of Costs (all inclusive) ($/m3) 1. VOCs: Gentle Heating (BTEX, CVOCs) <100 4 – 6 No 40-200 2. VOCs (CVOCs, BTEX) >100 2 – 4 Depends 60-300 3. SVOCs (PCBs, PAHs, BaP, dioxins) 200-300 1.5 – 3 Yes 150-600
  • 18.  Faster (Rapid mobilization, smaller footprint, & usually no electrical installation required)  Scalable (Can be applied to very small and very large projects)  Pilot Tests for less than $200,000  Full Scale for less than $500,000
  • 19.
  • 20. N  Vapor Treatment system permitted with BAAQMD  Onsite Liquid Treatment  Utilities?  Existing Natural Gas Connection  Existing Electrical Connection
  • 21. Bathroom TCU-1-2 (Before July 8, 2012) TCU-1 (After July 8, 2013) TCU-2 T9 Wall SVE-1 TCU-3 SVE-2 SVE-3 SVE-4 SVE-5 SVE-6 SVE-12 SVE-7 SVE-8 SVE-10 SVE-9 TCU-1 SVE-11 (Before July 8, 2013) TCU 1-2 (After July 8, 2013) T10 Wall T1 T2 T3 T5 T4 T6 T7 T8 TCU-1-1 TCU-3-1 TCU-3-2 TCU-2-1 TCU-2-2 0 40 Scale In Inches  100°C target treatment temperature  9 GTR Heater Wells  12 Vapor Extraction Points (dual nested)  10 TPMPs
  • 22. 0" 20" 40" 60" 80" 100" 120" 14(May" 21(May" 28(May" 4(Jun" 11(Jun" 18(Jun" 25(Jun" 2(Jul" 9(Jul" 16(Jul" 23(Jul" 30(Jul" 6(Aug" 13(Aug" 20(Aug" 27(Aug" 3(Sep" 10(Sep" 17(Sep" 24(Sep" 1(Oct" 8(Oct" 15(Oct" 22(Oct" 29(Oct" 5(Nov" 12(Nov" 19(Nov" 26(Nov" 3(Dec" 10(Dec" 17(Dec" 24(Dec" 31(Dec" 7(Jan" PPMV$ Influent$Vapor$Sampling$Results$ PCE" 0" 50" 100" 150" 200" 250" 300" 350" 400" 12(May" 1(Jul" 20(Aug" 9(Oct" 28(Nov" Well$Head$VOC$Data$in$Parts$Per$Million$by$Volume$(PPMV)$ SVE$Well$Head$VOC$Data$ Head$VOC$Data$in$Parts$Per$Million$by$Volume$(PPMV)$ 300" sve"1" sve"2" sve"3" 250" sve"4" sve"5" sve"6" sve"7" sve"8" 150" sve"9" sve"10" sve"11" Well$100" sve"12" 50" 0" 12(May" 1(Jul" 20(Aug" 9(Oct" 200" 350" 400" Individual SVE Wells SVE$Well$Head$VOC$Data$
  • 23.  100°C Treatment Temperature in Vadose Soils Maintained for 185 days.  2,938 Pounds of PCE, cis-1,2-DCE, and Vinyl Chloride Recovered as DNAPL from vapor treatment (condensation) system  1 month post-remediation vapor results 180 ug/m3.  3 month post-remediation vapor results 70 ug/m3.  825 pore volume steam exchanges (calculated) in treatment zone.  5,944 gallons aqueous phase liquid (water) recovered and treated onsite.
  • 24.  Specialized Equipment Needed to Access Interior Through Standard 3ft wide Door.  High resolution site characterization is key to design and cost management  Site remediation goals driven by Vapor Intrusion Risk and achieved!
  • 25.  Benzo(a)pyrene and related MGP COCs, Naphthalene, TPH-g, TPH-d impacts above residential limits, TPH-mo impacts also present.  Impacts from surface to 15 ft bgs.  Sandy, gravely soils; GW at >90 ft bgs.  Residential Goals: ◦ Combined B(a)P, Naphthalene, and MGP SVOCs: >0.9 mg/kg ◦ TPH-d: >1,000 mg/kg ◦ TPH-mo: >10,000 mg/kg
  • 26.  14 GTR Heater Wells  15 Vapor Extraction Points  4 TPMPs  Onsite Liquid Treatment  C2 Technology Vapor Condensation Unit (100 scfm) with VGAC  Adjacent, Existing Natural Gas Connection  Adjacent, Existing Electrical Connection
  • 27. TC-1 TCU 11 TC-2 TC-3 TCU 5 TC-4 CHINA ALLEY BT01 BT02 Holding Tank Chiller Skid SVE Skid 1 VGAC2 Heater Fan VGAC1 TCU TCU 1 2 TCU TCU 12 TCU 14 3 TCU 10 TCU 8 TCU 7 TCU 4 TCU 6 TCU 13 SVE SVE Skid 2 TCU 9 LGAC TITLE: TCH Equipment As Built SVE Skid 1: After Cooler Knock Out Tank Chiller Skid: Chiller Knock Out Tank SVE Skid 2: Blower After Cooler LGAC: 200 lbs VGAC 1: 400 lbs VGAC 2: 200 lbs Holding Tank: 650 gal Tank BT01: 2500 gal Tank BT02: 1000 gal Tank Legend TCH / Co-Located Vapor Extraction Well (Total: 14) Vapor Extraction Well 1 10 Scale in Feet Pilot Test Treatment Zone Conveyance Line Equipment * Well and Equipment Locations are Approximate
  • 28.
  • 29.
  • 30. 0 5 10 15 20 0 100 200 300 400 500 600 T1 60day T2 60day T3 60day T4 60day T1 120day T2 120day T3 120day T4 120day °C T4 T2 T1 T3 Depth (ft bgs.)
  • 31. 100 10 1 0.1 0.01 BaP BaP Eq. 10000 1000 100 Max. Conc. (mg/kg) Pre- Treatment Max. Conc. (mg/kg) Post- Treatment 10 1 TPH-d TPH-mo Target Treatment goal lines Max. Conc. (mg/kg) Pre- Treatment Max. Conc. (mg/kg) Post- Treatment
  • 32. 60 40 20 0 1 0.1 0.01 0.001 Post = 0.01 lbs before = 51.43 lbs BaP Equivalent TPH Post = ND before = 1.47 lbs BaP Equivalent mass (lbs) TPH mass (lbs) Remedial Objectives Exceeded by Order of Magnitude in 130 Days of ISTD Operation.
  • 33. 1. Greater than expected water content of soil (20% versus anticipated 10%) and higher water production impacted heating schedule for superheated phase. 2. Electrical interruption caused down time, and thereby impacted system heating capabilities (downed power line offsite) – recommend providing backup generators 3. Longer heating duration increased heat lost to surface – installed thermal blankets. Recommend higher R value ‘air entrained’ material to improve overall thermal efficiencies
  • 34. GTR© ISTCH Individual Burner System: 1. Applicability: soil temperatures < 70°C to > 325°C 2. Speed: Mobilize and commence GTR operations in Weeks not months 3. Scalability: small pilots to acre size projects 4. Economics: No waiting/paying for electrical utilities, transformers, switchgear, third party inspections. 5. Performance Guarantees available

Notes de l'éditeur

  1. it is extremely important to understand the source of the contamination and physical state in order to assess the loading rate. When it is unclear it is required to design on the side of caution and design excess capacity to minimize delays and cost overruns. I’m sure you all recognize this Phase Equilibrium diagram or have seen something similar. The VOCs WILL remain as residual NAPL in the vadose zone or aquifer, adsorb to soil, dissolve in groundwater, or volatize into soil gas to the extent defined by the physical and chemical properties of the individual constituents and the subsurface environment. Our intent is to change the conditions for which these laws operate through the addition of heat.
  2. Thermal conductivity is a measure of the ability to conduct heat. The reciprocal to conductivity is resistivity (aka ERH)! Thermal diffusivity is a measure how quickly the temp of the material increases and related to eachother by volumetric heat capacity of the material.
  3. The Thermal Conductivity of a Wide Range of Soil Materials (gravel, sand, silt, clay) Varies Only by a Factor of ~3 By Contrast: Hydraulic / Pneumatic Conductivities Vary >106 – 108 Electrical Conductivities Vary > 102 TCH Heats the Entire Target Zone – No Locations are Bypassed or Unaffected Soil Immediately Adjacent to TCH Wells Dries, Creating Permeability, Assisting Efficient Vapor Recovery TCH Heaters Can Be Readily Controlled, to Achieve Low, Moderate or Higher Soil Temperatures as Needed
  4. How do you make LNAPL or DNAPL move through saturated porous media? How do you control where air- vapor - and groundwater are moving when applying traditional MPE or groundwater extraction? How do you handle clay? It’s difficult and imperfect
  5. The system is closed looped. Outer tubes are generally a mild steel alloy (other types are available for corrosive environments). Inner tubes are generally a combination of refractory cement and stainless steel alloy.
  6. GTH is flexible and can be performed at different temperatures and configurations to meet the contaminant and geological conditions of a site.
  7. California-Specific Point = SCAQMD Various Locations Permits pending (each permit is for 500 scfm size and each would allow for 40 – 60 heating wells, depending on design. Can combine both permits at single site for double the capacity since we would operate less than six months under the combined permits).