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EXECUTIVE SUMMARY <br /> The objectives of this investigation were to assess the lateral extent of impacted groundwater <br /> and to establish a groundwater monitoring capability at the site To achieve these objectives, <br /> three on-site groundwater table monitoring wells were permitted, installed, surveyed, monitored <br /> and sampled The on-site water supply well was also sampled during the investigation <br /> Due to the unavailability of water well completion reports for San Joaquin County at the <br /> California Department of Water Resources (DWR), the proposed water well survey will be <br /> completed and documented in a subsequent quarterly groundwater monitoring report <br /> Soils observed during the drilling of the three monitoring well borings to a maximum depth of 87 <br /> feet bgs consisted mostly of massive intervals of clay, silt and fine sand mixtures interrupted by <br /> thin (i e, less than five feet thick) intervals of poorly-graded fine sand Laterally continuous sand <br /> sequences were observed at approximately 15 feet bgs and at 75 to 80 feet bgs Other sand <br /> intervals were observed as laterally discontinuous across the site <br /> During drilling, saturated soil and groundwater were first encountered between 79 5 and 80 1 <br /> feet bgs One week later, the static depth to the groundwater table, as measured in the three <br /> groundwater monitoring wells, ranged from 77 40 feet bgs in MW-1 to 78 23 feet bgs in MW-3 <br /> As such, groundwater does not appear to present under significant confining conditions <br /> The groundwater surface elevation ranged from a high of 22 64 feet (arbitrary datum) at MW-2 <br /> to a low of 22 42 feet (arbitrary datum) at MW-1 The resulting groundwater surface appears as <br /> a regular plane dipping to the north-northeast at a gradient of approximately 0 0037 foottfoot <br /> The 12 soil samples, three monitoring well groundwater samples, and the domestic water supply <br /> well sample collected during the investigation did not contain detectable concentrations of any of <br /> the gasoline constituent compounds analyzed <br /> Based on the results of previous subsurface investigation, soil and groundwater beneath the <br /> north end of the former middle UST are impacted by relatively low concentrations of gasoline <br /> hydrocarbons Most of the petroleum hydrocarbon mass remains concentrated in soil <br /> immediately below the north end of the former middle UST Vertically, the concentrations of <br /> gasoline hydrocarbons decrease rapidly with depth, and are defined between 65 and 80 feet <br /> bgs Based on the results from soil samples collected during the drilling of MW-1, MW-2 and <br /> MW-3, the lateral extent of impacted soil appears to be defined to the area of the former USTs <br /> Impacts to groundwater at the water table are defined to the northwest (MW-1), west (MW-2), <br /> and east (MW-3) The plume of impacted groundwater appears to be undefined to the south <br />' and north-northeast (downgradient) of the former USTs <br /> Based on these conclusions, Ramage Environmental recommends the following course of <br /> environmental corrective action <br /> 1 Continue to monitor and sample groundwater at the site on a quarterly basis <br /> 2 Complete the sensitive receptor survey for the site vicinity <br /> 3 Determine if an additional monitoring well is needed downgradient of the former USTs <br /> r <br /> 4 <br />