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Alms*, <br /> 2 <br /> Workplan for Destruction of Groundwater Monitoring Wells <br /> Eggiman Hydaulic Garage <br /> Stockton,California 95205 <br /> July 29,2013 <br /> observed in soil samples collected from the site. The highest concentrations were reported between 10 and 20 feet <br /> bgs and generally attenuate rapidly with depth. Only low concentrations of toluene (0.064 mg/kg) and xylenes <br /> (0.012 mg/kg)were detected at approximately 30 feet bgs in one boring, the maximum depth explored. Attempts <br /> were made to further advance the Geoprobe unit in several of the borings; however probe refusal was encountered <br /> at depths ranging from approximately 16 to 30 feet bgs due to the hardness of the formation. The results of the <br /> subsurface investigation were summarized in Smith Technology's Summary Report, Subsurface Investigation, <br /> dated December 22, 1997. <br /> In April 1999, at the request of the EHD, ATC completed a receptor survey for the subject property. ATC reviewed <br /> EHD groundwater well construction logs, Department of Water Resources (DWR) groundwater well construction <br /> logs, and conducted a site walk in the vicinity of the site to identify any groundwater wells located within a 2,000- <br /> foot radius of the site. This survey revealed 14 wells located within approximately 2,000 feet of the site. The <br /> closest of these wells is located approximately 800 feet upgradient of the project site. The receptor survey findings <br /> are summarized in ATC's Well Survey for Andrew and Edith Trust, for the Property at 1112 East Harding Way, <br /> Stockton, California, dated April 9, 1999. <br /> On April 11, 2000, a single soil boring (S67)was advanced to approximately 65 feet bgs to evaluate whether <br /> groundwater had been impacted at the subject site. Groundwater was initially encountered at approximately 45 <br /> feet bgs and a sample was subsequently collected from the soil boring using a Hydropunch groundwater-sampling <br /> tool. In order to determine the vertical extent of contamination in the most cost-effective manner, the soil boring <br /> was further advanced to a total completion depth of 66.5 feet bgs where field observations suggested the vertical <br /> extent of the petroleum hydrocarbons had been realized. Analytical results and field observations indicated that <br /> soil and groundwater beneath the location of the former USTs were impacted by residual petroleum hydrocarbon <br /> constituents. The vertical extent of impacted soil and groundwater appeared to be defined. However, the lateral <br /> extent of petroleum hydrocarbon constituents at or near the groundwater interface was undefined. Additional work <br /> to further characterize the extent of contamination was requested by the EHD in correspondence dated September <br /> 20, 2000. <br /> On November 15 and 16, 2001, an ATC geologist supervised the advancement of three soil borings to <br /> approximately 54 to 55 feet bgs. Soil borings were then completed as groundwater monitoring wells MW1, MW2, <br /> and MW3. The soil sample collected from boring MW2 at a depth of 35.5 feet bgs contained the highest <br /> concentrations of TPHg, ethyl benzene, and xylenes. The soil samples collected from boring MW2 at depths of 30 <br /> feet bgs and 55 feet bgs contained only trace concentrations of TPHg, ethyl benzene, and/or xylenes. The soil <br /> samples collected from borings MW1 and MW3 at depths of 35 feet bgs contained trace concentrations of xylenes <br /> and TPHg, respectively. The samples collected from borings MW1 and MW3 at depths of 40 feet bgs did not <br /> contain detectable concentrations of TPHg or BTEX. MTBE, t-amyl methyl ether(TAME), t-butanol (TBA), ethyl t- <br /> butyl ether(ETBE), di-isopropyl ether(DIPE), 1,2-dichloroethane (1,2-DCA), or 1,2-dibromoethane (EDB)were not <br /> detected in any soil samples collected from borings MW1, MW2, and MW3, though the detection limits were <br /> elevated in the MW2 sample from 35.5 feet bgs due to the high concentrations of TPHg noted previously. <br /> In July and December 2003, ATC conducted additional subsurface investigation activities at the site that included <br /> cone penetration testing, advancing a soil boring (SB8), and installation of monitoring wells MW4 through MW7. <br /> Petroleum hydrocarbons were detected in soil samples collected from the boreholes of MW5 and MW6, and in the <br /> groundwater samples collected from MW4 through MW-7. <br /> On November 17 and 18, and December 5 and 28, 2005, an ATC geologist supervised the advancement of five soil <br /> borings, S69 through SB 13. The borings were advanced for the purposes of evaluating the horizontal extent of <br /> petroleum hydrocarbon impacted soil and groundwater in the vicinity of the site. Details of these activities are <br /> summarized in ATC's Summary Report of Additional Subsurface Investigation, dated July 12, 2006. <br /> www.cardnoatc.com <br />