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EMIL <br /> Mr James L Barton <br /> October 29, 2004 <br /> Page 2 <br /> Groundwater measurements recorded on July 12, 2004 from wells screened to Unit A were used <br />' to construct the groundwater elevation contour map included as Figure 3 The groundwater flow <br /> direction for Unit A was generally to the northeast, with a hydraulic gradient of approximately <br /> 0 002 feet per foot (ft/ft) <br />' Groundwater measurements recorded on July 12, 2004 from wells screened in Unit B were used <br /> to construct the groundwater elevation contour map included as Figure 4 The groundwater flow <br /> direction for Unit B was generally to the east, with a hydraulic gradient of approximately 0 006 ft/ft <br /> Groundwater measurements recorded on July 12, 2004 from wells screened to Unit D were used <br /> to construct the groundwater elevation contour map included as Figure 5 The groundwater flow <br />' direction for Unit D was generally to the northeast, with a hydraulic gradient of approximately <br /> 0 0002 ft/ft <br />' Copies of the groundwater sampling information sheets are included as Attachment B Tabular <br /> results of recent depth to water (DTW) measurements are summarized in Table 1 A tabular <br /> summary of well construction details is included as Attachment C <br />' Groundwater Sampling and Analytical Results <br /> Groundwater samples were collected on July 14 through July 22, 2004 Groundwater samples <br /> were submitted to California Laboratory Services (CLS) in Rancho Cordova, California, for <br /> analyses of total petroleum hydrocarbons as gasoline (TPHg) by EPA Method 8015 Modified, <br /> and volatile organic compounds (VOCs) by EPA Method 8260B Tabular results of recent <br />' groundwater sampling analytical results are summarized in Table 1 A summary of <br /> groundwater elevations measured to date is presented in Table 2. Cumulative groundwater <br /> sampling analytical results are summarized to Table 3 Maps depicting dissolved <br />' concentrations of TPHg and benzene in groundwater are included as Figure 6 through <br /> Figure 13 Laboratory analytical results with chain-of-custody documentation are included in <br />' Attachment D <br /> Site Conceptual Modell Update <br />' In a letter dated February 8, 2002, the RWQCB requested completion of an updated SCM for <br /> this site The initial SCM was submitted to the RWQCB in an Environmental Audit Incorporated <br /> (EAI) report titled "Supplemental Investigation Report, Problem Assessment Report, and Work <br /> Plan, Cleanup and Abatement Order No 5-00-707, Montgomery Ward Auto Service Center and <br /> OS <br /> Former uriocar Site, 05400 a;rd SSPac+bc Avenue, Stnrktnn, C:alrfnrnra " dated October 13, <br /> 2000 <br />' Site stratigraphy is segregated into four hydro-stratigraphic units that generally correspond to <br /> screened intervals of site wells The shallowest wells are screened in the hydro-stratigraphic <br /> unit designated as Unit A and the deepest wells are screened across hydro-stratigraphic Unit D <br /> A cross-section location map, cross section A-A', cross section B-B', and cross section C-C' are <br /> IlDcsacramentolprojeclsTrojectsko6940M98 293TinaWeportslQuartedy Momtonng Reports15098 3rd Qtr D4-QMR doc <br /> �?1BC13'lr1C�^ YPc�r' ' XCP! rCr^ In <br /> E"? 1r0r merlra7 SP <br /> I <br />