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LLM�A <br /> RMa, , TMh <br /> 'oOw sco <: ,uDuM,°a p ';Kau p,d <br /> where debris was buried (F'igmc 41. None of the trenches ate visible in air photo taken in 1976, <br /> indicating that use of the (reaches bad been discontinued. Rand on the air photo interpretations <br /> and employee interviews, the debris burial benches consisted of a series or 2 to 3 trenches <br /> thought to range in six fmm 150 R long by 20 n wide to 30 R long by 10 ft wide. The <br /> r tre m depth of these trenches was approximately 10 R. Arrive apor induced and passive <br /> sell vapor surveys were conducted in the area to identify areas of elevated VOCs in soil vapor. <br /> In addition, magnetic and GPR surreys were conducted in the vicinity of the debris burial <br /> trenches to identify areas where metal containers or drums, and Iran containingdebris might be <br /> burned, as well as to help determine the exact locations and sizes of the debris burial trenches. <br /> Based on the results of Ole air photo interpretations, cnployee interviews, and vapor surveys, <br /> and magnetidGPR surveys, six test pits were excavated within the Yastem GSA debris burial <br /> trenches in 1990 to verify the nature of the debris placed in the trenches, and to collect mil <br /> samples to determine nature and extent of contamination in the debris burial ranch area <br /> (Figure 5). As shown on Figure 51 the test pits were located to Correspond Ish vertical magnetic <br /> gradient anomalies. It seas verified that the trenches contained craft shop debris, such as scrap <br /> metal, lathe lumings, porcelain shards, electrical wire, assorted metal pipes, and glass (Figure 6). <br /> Crag shop debris was encountered in Five fthe six test pits. fins material had been mixed with <br /> sail during placement. The results of the magnetidGpR surveys, which indicated that drums or <br /> metal etal container were not present in the trrnewsp was confirmed by the test pit excavations. <br /> Sail samples collected fmm the just pits were analyzed for VOCs. The VOC analytical <br /> results br these soil samples indicated the presence of very law concentrations <br /> of 'ICE <br /> (0.0009mllligrams per kilogram ImglkgD, tmmchlommhrne (PCE) (0.0013 <br /> 1,1,2,2-tetmchlomethane (PCA) (O.On02 mg/kg), dichlorobnmene (0.0002-0.0003mgkg)), <br /> chlomform (0.0005 mg/kg), and Freon 113 (0.0002 mg/kg) in one of the test pits. No other <br /> VOCs were detected above the rcpnrting limit in any of the other test pit mil samples, with the <br /> exception of TICE usua d at the 0.0001 mg/kg reporting limit in used sample been test pit as, <br /> Although craft shop debris was also encountered in three of the other test pits, no VOCs were <br /> detected above the O.00o1 mghg minoring limit in samples from these pits. No debris was <br /> encountered and no VO kg('s were detected above the O.Mill mg reporting limit in the sample <br /> fmmthe .sixth test pit. The concentrations of TCE, PCE, 1,1,2,2-PCA, dichlombenzene, <br /> chloroform, said Freon 113 detected in mil samples fmm the test pits ate all well below the most <br /> recent (June 2015) EPA industrial and residential soil RSLs and the MCL pmtw0on of ground <br /> MIer mil screening levels. <br /> As No of the remedial investigation of the Eastern GSA, IR)E,LI.NL also collected and <br /> analyzed samples of surf ce .mil and subsurface used form borchnles for VOCs and metals, <br /> including samples been within the debris burial trenches. Within the Eastern GSA debris burial <br /> launch area, 52 soil samples were colleetel from the vadose zone (0 to 30 d head in seven <br /> borcholes. All VOC mil detections were below both the residential and industrial soil RSLs <br /> (Juno 2015) that incorporate the recently revised TCB toxicity aloe. OTiny-nine onshe and <br /> oRhite monitor wells were also installed in due Eastern GSA he characterize the vertical and <br /> horizontal extent of ground water contamirmlimn and m determine ground water Raw direction <br /> and gradient. <br /> A Site-Wide Remedial Investigation (SWRI) report that summational e the results of <br /> characterization of Site 300, including the GSA OU, sea sued I, l994. The remedial <br /> mvestigation concluded that the debris in [be burial launches, which was contaminated with small <br />