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• ERI 2Q5513 QSR14 Tosco S,.crvgQStation 5 6 t ckt n alt or a <br /> cto r 27 2 <br /> Currently there are three on-site, single-casing groundwater monitoring wells (MW1 through MW3), <br /> four on-site, dual-casing groundwater monitoring wells (MW4S/D through MW7S/D), one on-site UST <br /> cavity well, and nine off-site groundwater monitoring wells (MW8S/I/D through MWIOS/I/D) <br /> consisting of three wells at each nested well location as shown on Plate 2 The purpose of these wells <br /> is to evaluate the lateral and vertical extent of dissolved hydrocarbons detected in groundwater beneath <br /> the site <br /> Based upon data collected during ongoing quarterly groundwater monitoring and sampling, dissolved <br /> hydrocarbons are delineated both laterally and vertically in the vicinity of the site However, dissolved <br /> hydrocarbons continue to be detected in groundwater samples from beneath the site and are <br /> concentrated in the vicinity of the UST cavity <br /> THIRD QUARTER ACTIVITIES <br /> Based upon previous work completed at the site, and in accordance with the correspondence and <br /> request from the County, the following tasks were performed during the third quarter 2000 <br /> • Gettler-Ryan, Inc (GRI) of Dublin, California performed groundwater monitoring and sampling at <br /> the site on August 3 and 4, 2000 The GRI Third Quarter 2000 Groundwater Monitoring and <br /> Sampling Report is provided as Attachment A The results of the third quarter monitoring and <br /> sampling event indicate the following <br /> • Groundwater was measured at approximately 6 6 to 9 5 feet below ground surface (bgs) in <br /> the groundwater monitoring wells (an elevation decrease of approximately 0 6 to 0 9 feet <br /> when compared to the second quarter 2000 groundwater monitoring and sampling event) <br /> During August 2000, groundwater flow direction was towards the southwest at a calculated <br /> hydraulic gradient of approximately 0 004 Historical groundwater flow directions are <br /> shown on the Groundwater Flow Direction Rose Diagram (Plate 3) <br /> • Total purgeable petroleum hydrocarbons as gasoline (TPPHg) and benzene were not <br /> detected at or above laboratory method detection limits in groundwater samples collected <br /> from the groundwater monitoring wells <br /> • Diesel-range hydrocarbons were not detected at or above laboratory method detection limits <br /> in groundwater samples collected from the groundwater monitoring wells with the <br /> exception of wells MW2 and MW3 Diesel-range hydrocarbons were detected in the <br /> groundwater samples collected from wells MW2 and MW3 up to 56 3 parts per billion <br /> (ppb) However, diesel-range hydrocarbons were not detected at or above laboratory <br /> method detection Iimits in the samples after the silica gel clean-up was performed <br /> • MTBE was not detected at or above laboratory method detection limits in groundwater <br /> samples collected from wells MW5D, MW5S, MW7D/MW7S through <br /> MW9S/MW9I/MW9D, MWlOS, and MW1OD MTBE was detected in the remaining <br /> wells ranging from 2 61 ppb to 20,900 ppb using Environmental Protection Agency (EPA) <br /> Method 8260, (ranging from 6 01 ppb to 28,700 ppb using EPA Method 8020) MTBE <br /> was not detected in well MW4S using EPA Method 8020 <br /> • <br /> 3 <br />