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lot IA <br /> ATC Associates Inc <br /> YVJ%TC <br /> 1117 Lone Palm Avenue, Suite B <br /> Modesto, Cakforma 95351 <br /> 209-579-2221 <br /> • ASSOCIATES i NC fax 209-579-2225 <br /> On September 11 and 12, 2003, a 500-gallon capacity used oil UST was excavated and removed <br /> from the site respectively, by Walton Engineering, Inc Petroleum hydrocarbons and metals were <br /> detected in a soil sample collected from below the former location of the UST from a depth of <br /> approximately seven feet bgs Refer to Grayland Environmental's Underground Storage Tank and <br /> Fuel Dispenser Removal Report, dated October 16, 2003, for more information In September 23 <br /> and 24, 2003, H2OGEOL collected groundwater samples from MW 1 and MW4 through MW8 <br /> Petroleum hydrocarbons were detected in groundwater samples collected from these wells The <br /> reported groundwater flow direction was to the north Refer to 112OGEOL's Third Quarter, 2003 <br /> Groundwater Monitoring Report, dated October 31, 2003, for more information <br /> SAMPLING ACTIVITIES <br /> On August 19, 2004, ATC personnel collected groundwater samples from monitoring wells MW 1 <br /> and MW4 through MW8 Monitoring wells MW2 and MW3 are sampled annually The locations <br /> of the wells are shown on Figure 2 Prior to collection of groundwater samples, the depth to <br /> water, pH, electrical conductivity, and temperature were measured and turbidity was visually <br /> observed in groundwater purged from the monitoring wells and recorded Approximately three <br /> well casing volumes were purged from each monitoring well prior to sampling The wells were <br /> iallowed to recover and samples were collected from each well using disposable polyethylene <br /> bailers <br /> The groundwater samples collected from each well were submitted to State-certified Argon <br /> Laboratories Inc Environmental Laboratory Accreditation Program (FLAP) Cert No 2359, in <br /> Ceres, California for chemical analysis of total petroleum hydrocarbons as gasoline (TPHg) <br /> utilizing EPA method 8015M, benzene, toluene, ethylbenzene, and xylenes (BTEX) utilizing EPA <br /> method 8021B, and methyl tertiary butyl ether (MTBE), ethyl tertiary butyl ether (ETBE) di- <br /> isopropyl ether (DIPE), tertiary amyl ether (TAME), tertiary butyl ether (TBA), 1,2- <br /> dichloroethane (1,2-DCA), and 1,2-dibromoethane (EDB) utilizing EPA method 8260B <br /> Groundwater well purge and sample logs are contained in Attachment 1 <br /> GROUNDWATER FLOW DIRECTION <br /> Water levels were measured in wells MW1 through MW8 on August 19, 2004 Depth to water in <br /> the shallow aquifer ranged from 5 78 to 7 80 feet below the tops of the well casmg elevations, <br /> representing an average decrease in the shallow water table elevation of approximately 1 15 feet <br /> since March 2 04 The water level data were used to develop the groundwater elevation contour <br /> map (Figure YX Shallow groundwater flow in the uppermost aquifer beneath the site is towards <br /> the north The average hydraulic gradient on August 19, 2004 was calculated to be 0 0026 ft/ft <br /> or approximately 14 ft/mile A summary of groundwater monitoring data is presented in Table 1 <br /> Yq <br /> I <br /> s lenvuumeenW\25847M371rep \39r-2004 doc 3 <br /> I <br />