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ti <br /> CLEAKWATER <br /> • n R O S P <br /> $nveronmertf of Services <br /> In January 1999, Clearwater supervised the installation of three additional groundwater monitoring <br /> wells (MW-4 through MW-6) to delineate the extent of dissolved-phase contamination and performed <br /> a sensitive receptor survey The results of the investigation indicated that the extent of sorbed-phase <br /> contamination was delineated and existed from approximately 10 to 25 feet bgs near the former USTs <br /> Results of the groundwater samples indicated that the extent of dissolved-phase contamination <br /> remained undelineated downgradient from the former UST system However, high contaminant <br /> concentrations in cross-gradient position of wells suggested that off-site sources may be contributing to <br /> contamination detected beneath the site Initial inquiries suggested and was later confirmed that there <br /> is existing fuel transport line in the area if the site, and that it is currently filled with nitrogen gas <br /> Based on this information, Clearwater recommended additional investigation along South Fresno <br /> Avenue to better understand the distribution of contamination and possible contribution from potential <br /> off-site sources The results of this phase of investigation were presented in Clearwater's Well <br /> Installation and Groundwater Monitoring Report - First Quarter 1999 <br /> In March 2000, Clearwater supervised the completion of one hydropunch, six soil borings, the <br /> destruction of MW-5, and three of the borings were converted into monitoring wells (MW-5B, MW-7, <br /> and MW-8) All three wells were placed on the downgradient portion of the plume to help determine <br /> the downgradient extent of contaminants The hydropunch was performed in the former UST location to <br /> assess the vertical extent of groundwater contamination at 36 feet bgs Three soil bongs were <br /> performed to define the lateral extent of soil and groundwater contamination on the northeastern <br /> portion of the site and assess possible off-site sources A total of three soil samples and one groundwater <br /> sample were analyzed from each boring Soil concentrations of TPHg and BTEX were only detected in <br /> boring MW-5B The highest soil concentration of TPHg (1,000 mg/kg) was detected at 25 feet bgs in <br /> MW-5B This sample was also analyzed for TPH as Jet Fuel and contained 55 mg/kg Detectable <br /> concentrations of BTEX were present in soil samples collected from boring MW-5B at 25 feet and 35 feet <br /> bgs MTBE was not detected by EPA method 8260 in any of the soil samples analyzed Groundwater <br /> concentrations of TPHg and BTEX were detected in bongs SB-9, MW-5B, MW-7 and MW-8 The <br /> highest groundwater concentration of TPHg (9,700 µg/L) was detected in MW-5B MTBE was not <br /> detected by EPA method 8260 in any of the groundwater samples analyzed <br /> GROUNDWATER MONITORING AND SAMPLING ACTIVITIES <br /> Date of groundwater sampling May 30,2001 <br /> Wells gauged MW-1 through MW-8 <br /> Wells purged and sampled MW-1 through MW-8 <br /> Analytes tested TPHg/BTEX/MTBE(EPA Method 8015M/8020) <br /> Laboratory Entech Analytical Labs, (Sunnyvale, CA) <br /> Remarks None <br /> GROUNDWATER MONITORING AND SAMPLING RESULTS <br /> Depth to groundwater 8 86 (MW-2) to 10 94 (MW-8) feet below top of casing <br /> Flow direction Southeast at 0 005 ft/ft <br /> TPHg concentration range < 50 gg/L (MW-2, MW-4) to 15,000 gg/L(MW-5B) <br /> Benzene concentration range <0 50 lig/L (MW-2, MW-4) to 2,600 µg/L (MW-5B) <br /> MTBE concentration range <5 0 gg/L (MW-2,MW-3,MW-4,MW-7) to 42 gg/L (MW-1) <br /> ZB 178C-2QTOI 2 June 8, 2001 <br />