Remediation Alternatives Evaluation
Naval Air Station Point Mugu - IRP Site 24

The RT3D software, one of the computer codes used in the Battelle Chlorinated Solvent Design Service, was used in the case study described here to evaluate bioremediation options at Installation Restoration Program (IRP) Site 24 at Naval Air Station (NAS) Point Mugu near Oxnard, California.  This case study was a Remediation Alternatives Evaluation, in which the bioremediation team determined if natural attenuation, accelerated in situ bioremediation, or a combination of the two is needed to remediate the contamination in the plume.  Battelle provides remediation alternatives evaluations and other bioremediation services to clients around the country.

NAS Point Mugu Installation Restoration Program Site 24 with contoured boundaries of chloroethene contamination (5 µg/L contours; yellow is PCE, blue is TCE, green is DCE, and red is VC) at underground storage tank sites 23 and 55.
The Site

Perchloroethene (PCE), trichloro-ethene (TCE), and fuel hydrocarbons have contaminated a portion of the upper aquifer at NAS Point Mugu.  The sources of the contamination were two leaking underground storage tanks (USTs).  Although the tanks and the surrounding soil have been removed, groundwater contamination persists.  Recent data show that contamination extends from the water table (5 ft below ground surface) to a depth of approximately 30 ft, and has an areal extent of approximately 2 acres. The presence of cis-1,2-dichloroethene, vinyl chloride, and ethylene in the groundwater suggests that reductive dechlorination is occurring naturally.

The Scope

Use the RT3D computer code to evaluate the technical feasibility, cost, and clean-up time for remediating the groundwater using:

 [1]  Accelerated anaerobic in situ bioremediation refers to the use of nutrient injection to accelerate reductive dechlorination reactions to convert chloroethenes to ethylene.
The Result

Battelle predicted that in situ bioremediation would save time and money when compared to the pump-and-treat alternative.  The regions surrounding each tank were considered separately since UST Site 23 has significantly more chlorinated solvents than fuels while UST Site 55 had a much larger fuel-to-chloroethene ratio. The fuel-to-chloroethene ratio is an important consideration for evaluating natural attenuation because the fuel serves as an energy source to support reductive dechlorination.  Hence, natural attenuation is the most cost-effective solution for UST Site 55, but is not technically feasible for UST Site 23.

 

Technology Screening Results for NAS Point Mugu IRP Site 24
  UST Site 23 UST Site 23
Technology Cost ($ M) Remediation Time (years) Cost ($ M) Remediation Time (years)
Pump-and-Treat (AS/GAC) 3.1 30 2.8 16
Natural Attenuation NA a NA a 1.6 16
Accelerated anaerobic in situ bioremediation and natural attenuation 2.6 20 1.9 11
a  NA denotes that the technology is not applicable because the technology would be limited by the amount of bioavailable carbon and so is not capable of meeting the treatment objectives.

 
For more information, contact:
Michael Truex
Program Manager
Field Hydrology and Chemistry Group
Battelle
902 Battelle Blvd., K6-96
Richland, WA 99352
USA
509-376-5461
509-372-1704 FAX
mj.truex@pnl.gov


Last Revised:  2002-Jan-07