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San Joaquin '%..,zy Air Pollution Control District <br /> Page 2 <br /> UST removal operations and soil samples collected from beneath the removed USTs and <br /> dispensers revealed significant levels of petroleum hydrocarbon constituents. As an interim <br /> abatement measure, the tank excavation was lined with 6-mil plastic sheeting and the soil was <br /> returned to the hole. <br /> On September 23, 1998, Jim Thorpe Oil, Inc. excavated approximately 166 cubic yards of <br /> impacted soil. The soil was transported directly to Forward Inc. landfill for disposal. A strong <br /> petroleum odor and some visible discoloration were noted in the upper portion of the removed <br /> soil. As soil removal continued, the bottom of the excavation began to clean up, and the west <br /> and south walls appeared to have only occasional areas of minor contamination. The north and <br /> east walls still showed evidence of discoloration. The removal of the contaminated soil was <br /> supervised by William J. Hunter, RG, of Wm J. Hunter & Associates. On September 23 & 24, <br /> 1998, approximately 369 cubic yards of clean fill dirt and 54 cubic yards of gravel base was <br /> brought in to fill the excavation.. The soil was compacted as required by San Joaquin County. <br /> Subsurface Investigation <br /> Subsurface assessments were performed by Ground Zero between November 1998 and July 2004 <br /> to evaluation the extend of contamination in soil and groundwater beneath the site. The <br /> investigations consisted of drilling two pilot borings using a CPT rig to identify subsurface <br /> stratigraphy, advancing additional soil borings as necessary to collect soil and groundwater <br /> samples, installing and sampling fifteen groundwater monitoring and/or extraction wells <br /> including three deeper zone wells, and initiating free product recovery and groundwater <br /> extraction. Groundwater was initially encountered at a depth of approximately 56-58 feet below <br /> ground surface (bgs) and is currently measured at a depth of approximately 68-74 feet bgs in site <br /> wells. Borings and well locations are shown on Figure 2. <br /> Extent of Hydrocarbons in Soil and Groundwater <br /> Laboratory analysis of soil samples collected from borings within and peripheral to the former <br /> tank/excavation pit have defined the lateral extent of soil contamination. Vadose soil <br /> contamination of significance was identified only in vadose zone and capillary fringe zone samples <br /> from borings SBI, S132, SB3, MWI, and VW1, each of which was drilled in the vicinity of the <br /> former USTs and dispensers. Soil samples from peripheral borings did not contain contaminants in <br /> the vadose zone, although wells MW2, MW6, and MW 12 contained low levels of hydrocarbons in <br /> soil samples collected from the capillary fringe zone. Relatively minor levels of soil contamination <br /> are present between the bottom of the tank pit excavation (approximately 15-17 feet bgs) and the <br /> water table (currently approximately 70 feet bgs). Below this depth saturated soil appears to be <br /> minimally impacted. Ground Zero has estimated that approximately 500-525 pounds of TPHg and <br /> approximately 40-70 pounds of MTBE are present in the vadose zone soils beneath the site. Soil <br /> analytical results are presented in Tables 1 and 2. <br /> Groundwater in wells MWI, MW2, MW3, MW4, MW5, MW6, MW12, EW2, and VWI in the <br /> shallow aquifer beneath the site have been impacted with MTBE, but only wells MW 1, MW2, and <br /> VW1 are impacted with TPI-Ig and BTEX constituents. The wells with greatest impact are wells <br /> MWI, MW3, MW4, and VW1, with lower Ievels of contaminants in wells MW2, MWS, MW6 <br /> GAGROUNDZE\TULESURGNapor Extraction perrnits\VEScvrltr.DOC <br />