Please join EPA Region 9 and GEO Inc. for a technical presentation on In Situ Gas Thermal Remediation (GTR™) and thermal conductive heating (TCH) that will provide regulators, consultants, and field applicators with an understanding of the primary thermally enhanced contaminant removal mechanisms and will help distinguish three types of In Situ Thermal Remediation available commercially in the U.S. and internationally. Additionally, benefits from heat generation, such as increased rates of naturally occurring processes (including hydrolysis, increased bio-availability, and different forms of bio-degradation at various temperature regimes) will be highlighted. In order to identify when In Situ Thermal is appropriate, important design factors will be discussed for their applicability and operation including developing a comprehensive and high resolution conceptual site model through the use of passive soil gas sampling, MIP, LIF, and other high resolution techniques.
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/mK)
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
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 ~$0.10
http://www.eia.gov/electricity/monthly/epm_table_grapher.cfm?t=e
pmt_5_6_a
http://www.consumersenergy.com/apps/gasvalues/index.aspx?ekfr
m=1654
Flexibility has been key for many
projects internationally!
17. Level of
Heating &
Contaminant
Target
Treatment
Temperature
(°C)
Heating
Well
Spacing
(m)
Desiccation
of Zone?
Range of
Costs (all
inclusive)
($/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
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
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.)
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
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.
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.
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
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
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.
GTH is flexible and can be performed at different temperatures and configurations to meet the contaminant and geological conditions of a site.
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).