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remediation of both soil and groundwater is required Fourteen remediation technologies were <br /> evaluated according to their performance, reliability, and applicability to the site-specific <br /> I conditions Three of the fourteen technologies screened were deemed feasible for remediation of <br /> both the impacted site soil and groundwater These technologies included In-Situ Air Sparging, <br /> In-Situ Well Aeration, and Enhanced Bioremediation <br />' Treatibihty and pilot testing should be conducted to further evaluate the best remediation <br /> technology for the Canteen Facihty Following evaluation of the pilot test/treatibility data, an <br /> estimate of the duration of the clean up time can be provided and the costs for system <br /> implementation and operation and maintenance can be finalized In addition, a sensitive receptor <br /> survey should be performed <br /> 2.0 SOIL ASSESSMENT ACTIVITIES <br />' 2.1 UST Excavation <br /> On March 31, 1992, a 10,000-gallon UST, which had contained gasohne, was removed from the <br /> site Samples from the excavated soil revealed concentrations of toluene, ethylbenzene, xylene, <br /> and gasoline range (TPH-G) total petroleum hydrocarbons To allow for full use of the area, the <br /> excavated soil was placed back in the tank pit, covered with clean fill and sealed with asphalt <br /> On November 5, 1992 the site of the removed UST was excavated for a second time to remove <br /> the soil that had been returned to the hole The original removed soil was encountered at a depth <br />' of five to six feet bgs That material was placed directly on a dump truck and transported to <br /> Forward, Inc , a disposal facility Due to the limitations of the excavation equipment being used, <br /> work was discontinued even though hydrocarbon staining was still present on the south and east <br />' walls Soil samples taken from the southeast and south walls revealed concentrations of BTEX <br /> and TPH-G The excavation was later filled with clean soil and pea gravel <br />' 2.2 Soil Boring and Monitor Well Installations <br /> On February 1, 1993 sort borings SB-1 through SB-5 were installed around the excavation site <br />' Hydrocarbon constituents were detected in all five soil borings In addition, hydrocarbon <br /> constituents were detected approximately 45 feet below ground surface (bgs) in soil borings SB- <br /> 2, SB-3, and SB-4 In May 1993 monitoring wells MW-1 through MW-4 were installed further <br />' away from the excavation site Benzene, toluene, xylene, and TPH-G were detected in soil <br /> samples from all four monitoring wells <br />' On August 23 and 24, 1994 monitoring wells MW-5, MW-6 and MW-7 were installed No <br /> hydrocarbon components were detected in any of the soil samples submitted for analysis, <br /> indicating that the limits of the soil impact had been defined to the north, west and south <br /> I <br /> 2 <br /> 1 <br />