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SITE GEOLOGY AND HYDROLOGY <br /> The Sebastiani Vineyards/Woodbridge Cellars site is located on a broad, <br /> flat, alluvial plain at an elevation of approximately 20 feet above mean <br /> sea level (MSL). The site is located approximately 3 1/2 miles southwest <br /> Of the Mokelumne River and is bordered (Zn three sides by vineyards and to <br /> the north by Turner School. A Western Pacific rail line runs northwest <br /> to southeast across the western side of the site, <br /> Soils encountered during drilling and excavation activities at the site <br /> consisted of a slightly moist, clayey silt to silty sand unit to a depth <br /> Of approximately eight feet below ground surface, underlain by a moist, <br /> silty, sandy clay that extended to an approximate depth of 17 feet. A <br /> saturated, moderately-well sorted, well rounded, fine grained sand to <br /> silty sand unit extended from 17 feet to 34 feet on the eastern side of <br /> "-x the area of investigation. <br /> encountered at <br /> increasingly shallower depths h toward the west ande bottom of thiss wass encountered at <br /> approximately 25 feet on the western side of the investigation area. A <br /> silty, slightly sandy, moist to ve slightly moist clay unit was <br /> encountered beneath the silty sand in all the monitor we <br /> �t the _circ s un was encountered at approximately R� S drilled <br /> 34 feet below <br /> ground surface in borings located on the castsideof the investigation <br /> MIN area and, as drilling activities progressed in a southwesterly direction, <br /> it was encountered at a depth averaging approximately 25 feat, This clay <br /> unit extended to the total depth of all monitor well borings. IC's <br /> thickness was not determined, but it is at least 5 feet thick throughout <br /> the area explored. Generalized geologic cross sections which depict the <br /> lithologic units encountered at the site and a cross section reference map <br /> Of the investigation area are presented in Figures 4, 5, and 6. <br /> Groundwater level measurements were made at each monitor well on June 2, <br /> 1989, after a minimum 12-hour equilibration period following construction <br /> of monitor wells MW-9 and -10. A second sounding round was performed on <br /> .FWDJune 19, 1989, allowing over two weeks for equilibration following well <br /> construction. The depth to water in each well was measured with an <br /> electric sounder. As shown in Table 3, groundwater surface elevations <br /> across the site varied by approximately 0.68 feet, The normal licit of <br /> accuracy for this method of measurement is 0.02 feet. <br /> groundwater contours developed from the June 19, 1989, A map of <br /> water level <br /> sounding measurements is shown on Figure 7. The contours suggest that <br /> groundwater at the site is moving in a southwesterly direction. <br /> ANALYTICAL RESULTS <br /> As previously stated, analytical services for the site assessment work <br /> were provided by Weston Analytical Laboratory of Stockton, California and <br /> McLaren Analytical Laboratory of Rancho Cordova, California. These <br /> laboratories are certified by the State of—California <br /> f --- - __.__—Health-Services -for hazardous waste testing. '- LePartmant_-of ---- <br /> 13 <br />