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• <br /> LFR Inc. <br /> 1.3 Site Geology and Hydrogeology <br /> Soils encountered at the Site during previous investigations consist of silty gravel with <br /> interbedded clayey silt lenses to a depth of approximately 25 feet below the average <br /> gravel pit elevation. Silt and sand with varying amounts of gravel and clay occur at a <br /> depth of 25 to 300 feet below ground surface (bgs). The Corcoran Clay is encountered <br /> at depths ranging from 300 to 380 feet bgs (Ecology and Environment, Inc. 2002). <br /> The soil encountered during drilling activities for monitoring wells MW-6 and MW-7 <br /> and soil borings SB-01 and SB-02 from the surface to approximately 25 feet bgs <br /> consisted of silty gravel with minor layers of fines (resembling alluvial fan deposits). <br /> From approximately 25 feet to 125 feet bgs, the soils generally consisted of silt and <br /> sands with varying amounts of clay and gravels assumed to be part of the Tulare <br /> Formation. A 10-foot-thick clay layer was noted in the cliff face from 85 to 95 feet bgs <br /> but was not detected in the intermittent soil samples collected from borings. <br /> Groundwater occurs in two water-bearing zones at the Site: an upper water-bearing <br /> zone and a lower water-bearing zone. The upper water-bearing zone (i.e., the water <br /> table) is encountered at an approximate depth of 75 feet bgs. The lower water-bearing <br /> unit is encountered at an approximate depth of 380 feet bgs, and is separated from the <br /> upper zone by the Corcoran Clay (Ecology and Environment, Inc. 2002). Regionally, <br /> recharge of the upper water-bearing unit is primarily from irrigation and seepage of <br /> surface water through the alluvium with little contribution from rainwater (U.S. <br /> Geological Survey 1971). The project site receives an approximate average of 10.5 <br /> inches of precipitation per year and has a total estimated evapotranspiration rate of 61 <br /> inches per year as measured 3 miles south of the Site. Based on data collected from six <br /> on-site groundwater monitoring wells during a recent groundwater sampling event, <br /> groundwater flow within the upper water-bearing unit is toward the northwest, with a <br /> calculated gradient of approximately 0.001 (Figure 3). <br /> The nearest surface-water features to the project site are Corral Hollow Creek to the <br /> north, an intermittent natural drainage course; the Delta-Mendota Canal, an irrigation <br /> canal; and the California Aqueduct. The topographic nature of the Site precludes it as a <br /> potential source of runoff to any of these water features. Because the Site is a former <br /> gravel mine, it is essentially a closed basin with no outfall. All rainwater that falls onto <br /> the Site infiltrates into the soil substrate and serves as local groundwater recharge. <br /> "The Water Quality Control Plan, Sacramento River and San Joaquin River Basins" <br /> ("Basin Plan"; Regional Water Quality Control Board 1998) designates beneficial uses, <br /> establishes water-quality objectives, and contains implementation plans and policies for <br /> all waters of the Basin. The designated beneficial uses of the groundwater, as specified <br /> in the Basin Plan, are domestic and municipal, agricultural, and industrial supply. As <br /> stated previously, there is no surface-water flow into or out of the project site because <br /> it is located in an excavated pit. <br /> Page 2 wp-MW-08_Insult-Feb06-final-0902506.dm:LFR <br />