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Mr Harlm Knoll <br /> May 6, 1999 <br /> Page 2 of 3 <br /> Groundwater samples were submitted to Argon Laboratories (FLAP #1873) for analysis of TPHg <br /> and BTEX utilizing EPA methods 8015 modified and 8020, respectively <br /> Groundwater samples collected from wells MW 1 and MW5 contained elevated levels of <br /> petroleum hydrocarbons TPHg and BTEX were detected in well NMI at concentrations of 63 <br /> parts per billion (ppb), 0 8 ppb, <0 5 ppb, 1 0 ppb, and 1 5 ppb, respectively MW5 contained <br /> TPHg and BTEX at concentrations of 65,000 ppb, 10,000 ppb, 5,000 ppb, 1,500 ppb, and 9,500 <br /> ppb, respectively No petroleum hydrocarbon constituents were detected in wells MW3, MW4 or <br /> MW8 Figure 3 shows the estimated extent of dissolved benzene in groundwater Analytical <br /> results are summarized in Table 3 Laboratory data sheets and chain of custody documentation <br /> are included in Attachment B <br /> SUMMARY AND CONCLUSIONS <br /> • MTBE has not been detected above 7 ppb at the site, which is below the Department of <br /> Health Services advisory level of 13 ppb A summary of MTBE levels is presented in Table 4 <br /> • Concentrations of dissolved gasoline constituents beneath the site have decreased or remained <br /> stable, with exception of well MW5, since the USTs were removed in 1987 and secondary soil <br /> contamination was excavated in 1990 In well MW5, the trend since December 1996 is one of <br /> decreasing concentrations <br /> • Downgradient wells MW8 and MW4, located approximately 105 and 85 feet, respectively, <br /> from well MW5 do not contain petroleum hydrocarbons above laboratory detection limits <br /> • Well MW1, located immediately downgradient of the former tanks and approximately 85 feet <br /> from well MW5, contains benzene (0 8 ppb), toluene (<0 5 ppb), ethylbenzene (1 0 ppb), and <br /> toluene (1 5 ppb) at concentrations below Maximum Contaminant Levels (MCLS) <br /> • The areal extent of the dissolved contaminant plume has been largely defined and has <br /> generally decreased in dimension since 1992 <br /> • Twelve years after the USTs were removed (1987) and nine years after contaminated soil was <br /> excavated (1990), groundwater meets Basin Plan objectives approximately 80-100 feet <br /> downgradient of the original release <br /> • Additional soil and groundwater remediation at the site is considered technically and/or <br /> ecomonically infeasible <br /> • The shallow aquifer in the Stockton area is generally not used as a drinking water source due <br /> to saltwater intrusion from the delta and general poor water quality <br /> • Although the nearest known water supply well is located approximately 300 feet in the <br /> downgradient direction from the site, this well does not appear to be active and would not be <br /> expected to be impacted by the dissolved contaminant plume at the site, which appears to be <br /> shrinking and does not appear to extend off-site <br /> Although detectable concentrations of BTEX in the vicinity of monitoring well MW5 are likely to <br /> remain above MCLS for many years, the current or future beneficial uses of surface or drinking <br /> 1knowles hamheporW1 qm 1999 doc <br />