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Extended Site Characterization Report: 7500 West Eleventh Street, Tracy, CA Page 12 <br /> and 50 ft. BGS. These depths and screened intervals were selected to provide, in <br /> conjunction with existing Monitoring Well MW-3, information on groundwater quality at <br /> discrete depths. The boring logs and construction details are included in Appendix A. The <br /> 4 well array MW-3, MW-3A, MW-313 permits comparison of groundwater quality in three <br /> separate intervals: water table to 21 ft. BGS, 35 to 40 ft. BGS, and 45 to 50 ft. BGS. <br /> i <br /> 5.3.2 Eastern Limit - Principal Plume of Affected Groundwater <br /> Monitoring Well MW-8 was originally included in SJC's work plan for the first phase <br /> .:= site characterization program (The San Joaquin Company Inc. 1999), but, as was <br /> discussed previously, at that time, funding for its installation was refused by the USTCF. <br /> . , Its installation was approved during the second phase of the site characterization <br /> program. It is located to the east of Chrisman Road on the northern side of West Eleventh <br /> Street at distance from Well MW-7, which was installed during the first phase of site <br /> _ characterization and is known to contain floating product. Its purpose is to provide a <br /> conservative assessment of the eastern limit of the plume of affected groundwater in that <br /> area. <br /> The log and construction details of Well MW-8 are included in Appendix A. It has a total <br /> depth of 22 ft. and is screened over a 15-ft. interval from just above the groundwater table <br /> to a depth of 21 ft. <br /> Monitoring Well MW-9 (see Figure 2 for location) was installed at the request of the <br /> >> SJCEHD. It has a total depth of 22 ft and is screened from a depth of 7 ft. (at an elevation <br /> > above the groundwater table) to the bottom of the well at a depth of 22 ft. (See Appendix <br /> A for the boring log and well construction details.) <br /> 5.3.3 Down- adient Extent- Principal Plume of Affected Groundwater <br /> A groundwater-quality monitoring well designated as Well MW-10 was installed on the <br /> eastern side of Chrisman Road approximately 265 ft. north of that street's intersection <br /> with West Eleventh Street. (See Figure 2 for location). This well is one of two, the other <br /> being MW-11, that were located so as to investigate the distance that groundwater <br /> affected by fuel hydrocarbons has been transported down the groundwater gradient from <br /> the 7500 West Eleventh Street site. MW-10's location is on a projection of a line from <br /> the center of the pump island area of the former fueling station, beneath, which the <br /> C ! majority of the fuel hydrocarbons that leaked into the subsurface were released, and <br /> Monitoring Well MW-7. <br /> Groundwater in MW-7 is heavily affected by components of both gasoline and diesel. <br /> Based on the hydrogeology and geochemistry of the site, as it was known following <br /> completion of the initial site characterization program, it was concluded that the <br /> alignment from Former Pump Island Location to MW-7 to MW-10 closely followed the <br /> principal axis of the plume of affected groundwater. MW-10 was sited on this alignment <br /> so that any analytes of concern present in the groundwater at that distance from the <br /> source would Iikely be detected. Location of that well further to the south would risk <br /> sic <br />