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Handbook of Solvents - George Wypych - ChemTech - Ventech!

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1626 Barry J. Spargo, James G. Mueller<br />

were combined to create an average DNAPL solubility <strong>of</strong> 620,000 mg/L (compared with a<br />

TCE solubility <strong>of</strong> 1,100 mg/L in natural groundwater). The solution was injected over a period<br />

<strong>of</strong> time, in an amount equal to 2.4 pore volumes in the test portion <strong>of</strong> the aquifer.<br />

DNAPL removal was 99 percent (estimated) and surfactant recovery at the extraction wells<br />

was 94 percent. Based on these results, a full-scale system was designed and implemented.<br />

23.2.3.3 Foam-enhanced product recovery<br />

The use <strong>of</strong> foams to remove heavy immiscible fluids such as DNAPL from soil was developed<br />

by the petroleum industry for crude oil production. Subsequently, The Gas Research<br />

Institute developed the use <strong>of</strong> foams to release and mobilized DNAPL contaminants in the<br />

subsurface. Coupled with in situ or ex situ bioremediation, foam-enhanced product recovery<br />

can, potentially, transport CHC contaminants upward in the groundwater, thus reducing<br />

the potential for driving the contamination to previously non-impacted areas.<br />

The use <strong>of</strong> foam for CHC DNAPL is currently viewed as experimental. The delivery<br />

<strong>of</strong> the foam, its sweep front, the foam stability, its ability to release CHC DNAPLs in the<br />

subsurface, and the resultant biodegradability <strong>of</strong> residuals can potentially be aided through<br />

the proper selection <strong>of</strong> foaming agents and nutrients. In theory, the technology can tailor the<br />

foam system to aerobic or anaerobic subsurface environments, depending on the selection<br />

<strong>of</strong> the carrier gas. This allows adequate biodegradation for the particular CHC in the<br />

foam-pollutant system. For example, DCE can be biodegraded aerobically, whereas PCE<br />

needs to be degraded anaerobically.<br />

23.2.3.4 Thermal desorption - Six Phase Heating<br />

Six-Phase Heating TM (SPH) is a polyphase electrical technology that uses in situ resistive<br />

heating and steam stripping to achieve subsurface remediation. The technology was developed<br />

by Battelle’s Pacific Northwest Laboratories for the U.S. Department <strong>of</strong> Energy to enhance<br />

the removal <strong>of</strong> volatile contaminants from low-permeability soils. The technology is<br />

also capable <strong>of</strong> enhancing the removal <strong>of</strong> DNAPLs from saturated zones.<br />

SPH uses conventional utility transformers to convert three-phase electricity from<br />

standard power lines into six electrical phases. These electrical phases are then delivered<br />

throughout the treatment zone by steel pipe electrodes inserted vertically using standard<br />

drilling techniques. Because the SPH electrodes are electrically out <strong>of</strong> phase with each<br />

other, electricity flows from each electrode to the adjacent out-<strong>of</strong>-phase electrodes. In situ<br />

heating is caused by resistance <strong>of</strong> the subsurface to this current movement. In this manner, a<br />

volume <strong>of</strong> subsurface surrounded by electrodes is saturated with electrical current moving<br />

between the electrodes and heated. By increasing subsurface temperatures to the boiling<br />

point <strong>of</strong> water, SPH speeds the removal <strong>of</strong> contaminants such as CHCs via three primary<br />

mechanisms: increased volatilization, steam stripping, and enhanced residual mobility toward<br />

extraction wells via viscosity reduction.<br />

Once subsurface soil and groundwater reach the boiling point <strong>of</strong> water, the in situ production<br />

<strong>of</strong> steam begins. Through preferential heating, SPH creates steam from within silt<br />

and clay stringers and lenses. As this steam moves towards the surface, it strips contaminants<br />

such as CHCs from both groundwater and soil matrix. Released steam can act as a carrier<br />

gas, sweeping CHC out <strong>of</strong> the subsurface and to extraction wells. However, it can also<br />

cause constituent migration and CHC displacement if the steam is allowed to condense prior<br />

to extraction.

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