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Technology Status Report: In Situ Flushing - CLU-IN

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Table 4 <strong>In</strong> <strong>Situ</strong> <strong>Flushing</strong> - Recovered Contaminant Mass / Economic <strong>In</strong>formation Available<br />

Total Number of Case Studies = 84<br />

GWRTAC Project <strong>Report</strong>ed Contaminant <strong>Report</strong>ed Fraction of Economic Scale of<br />

ID Name Mass Recovered <strong>In</strong>ital Mass Recovered <strong>In</strong>formation Project<br />

FLSH0038 Sindelfingen, Germany Within 18 Months After TCE Spill, 17 Metric<br />

Tons of Chlorinated Hydrocarbons were<br />

Recovered<br />

FLSH0074 SW Tank Farm, Tinker Air Force<br />

Base, OK<br />

FLSH0041 Texas Eastern Transmission<br />

Facility, Delmont, PA<br />

FLSH0042 Thouin Sand Quarry, Quebec,<br />

CA<br />

FLSH0053 U.S. Air Force Plant 4, Fort<br />

Worth, TX<br />

<strong>In</strong>itial Mass Estimates not Available from<br />

Source<br />

Full-<br />

Scale/Commercial<br />

Pilot/Field<br />

Demonstration<br />

0.32 Kg PCBs Unknown At present, no plans exist for further Pilot/Field<br />

surfactant flushing at the site. <strong>In</strong>stead,<br />

recovery and treatment of PCBs at the spring<br />

is planned. The limiting factor controlling the<br />

duration of the surfactant injections presented<br />

above was the ability to effect<br />

Demonstration<br />

992 Kg DNAPL 86% Residual DNAPL Pilot/Field<br />

Demonstration<br />

Project is in Progress; Surfactants may or<br />

may not be Applicable<br />

FLSH0051 U.S. Coast Guard, Traverse City, 3.354 gm PCE Total, 2.757 gm PCE Through<br />

MI<br />

Surfactant-Enhanced Solubilization<br />

FLSH0054 U.S. DOE Gaseous Diffusion<br />

Plnt, Paducah, KY<br />

FLSH0075 U.S. DOE Paducah Gaseous<br />

Diffusion Plant<br />

FLSH0008 U.S. DOE Portsmouth Gaseous<br />

Diffusion Site, Piketon, OH<br />

FLSH0043 Umatilla Army Depot (Lagoons),<br />

Hermiston, OR<br />

FLSH0044 United Chrome Products,<br />

Corvallis, OR<br />

FLSH0083 University of Arizona - HC<br />

Solubilzation and Mobilization by<br />

Biosurfactant<br />

FLSH0082 University of Florida - Two-<br />

Dimensional Flow Experiments<br />

and Simulations<br />

FLSH0081 University of Illinois - Impact of<br />

Surfactant of Configuration of<br />

HC Lens<br />

No <strong>In</strong>crease in TCE Concentration was<br />

Achieved<br />

20 to 40 L (Approximately 5.to 10 Gallons)<br />

DNAPL<br />

Project is in Progress; Surfactants may or<br />

may not be Applicable<br />

Pilot/Field<br />

Demonstration<br />

<strong>In</strong>tial Mass not Known Pilot/Field<br />

Demonstration<br />

No <strong>In</strong>crease in TCE Concentration was<br />

Achieved<br />

Pilot/Field<br />

Demonstration<br />

Laboratory/Bench<br />

Scale<br />

Approximately 50% of Original DNAPL No estimated full-scale cost was available. Pilot/Field<br />

Demonstration<br />

Project is in Progress Project is in Progress Full-<br />

Scale/Commercial<br />

Project is in Progress; Over 3 Years, 9.7 MM<br />

Gallons of Impacted Groundwater Containing<br />

26,732 lbs. of Cr+6 have been Removed<br />

Project is in Progress Cost estimates indicate that treatment costs Pilot/Field<br />

were estimated at $40/lb of Cr+6 removed for Demonstration<br />

the first 25,000 lbs. As Cr+6 concentrations<br />

drop in later phases of operation, it is<br />

estimated that costs will double to $80/lb of<br />

Cr+6 removed.<br />

58% of Residual NAPL (Hexadecane)<br />

Removed Within Three Pore Volumes From<br />

Laboratory Sand Columns<br />

Laboratory/Bench<br />

Scale<br />

Laboratory/Bench<br />

Scale<br />

Laboratory/Bench<br />

Scale<br />

FLSH0052 University of Michigan Project is in Progress Project is in Progress Laboratory/Bench<br />

Scale<br />

Ground-Water Remediation Technologies Analysis Center<br />

Operated by CTC 1-800-373-1973 Page 24<br />

GWRTAC 1998<br />

As of 11/17/98

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