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F <br /> COLATION TEST RESULTS <br /> s were conducted on September 13, 1999 under U.S.E.P.A. and San Joaquin7and <br /> al Health guidelines. Since the soil at the perc test depth of 45 inches is san <br /> six inches of water seeped away after one-half hour, the test was conducted over a one-hour <br /> period. The depth at which the perc test was done represents effluent percolation which normally <br /> takes place at the bottom of a leachline trench. As illustrated on the attached FIELD <br /> PERCOLATION TESTING REPORT, the perc rate increased as a greater hydraulic head was <br /> placed on the water in the perc test boring. In general however, the perc rate slowed over the test <br /> period, signifying the soil was becoming increasingly saturated. The perc test results indicate <br /> rapid percolation of approximately 9.3 min/in at the shallow test depth. <br /> D. GROUNDWATER INFORMATION <br /> Groundwater elevation determinations are delineated on maps published by the San Joaquin <br /> County Flood Control District. The Lines of Equal Elevation map denotes the elevation at 0 feet <br /> mean sea level. As illustrated on the attached USGS map,the ground elevation is approximately <br /> 15 feet above mean sea level. Therefore,the static water table depth should be approximately 15 <br /> feet below grade. However,the capillary fringe was encountered at 22 feet, indicating the water <br /> table depth to be around 25 feet below existing grade. <br /> The groundwater under the subject property is being influenced by the Highway 120 Bypass, <br /> Interstate 5 and the Union Pacific Railroad tracks. This influence on the groundwater by these <br /> structures can be quantified, however,this is beyond the scope of this investigation. As with all <br /> groundwater tables,there are fluctuations in elevation. The critical issue with regards to the <br /> groundwater elevation under the subject property is that there is sufficient distance between the <br /> bottom of the leachline trench(or sump) and the highest anticipated depth to groundwater. This <br /> distance is sufficient for wastewater treatment to occur. <br /> The groundwater directional flow appears to be toward the northwest. As the groundwater is <br /> measured closer to the Delta, the greater the influence in elevation and directional flow. The <br /> directional flow cannot be accurately established because of the referenced influences. <br /> To determine the extent of past nitrate impact to the underlying drinking water aquifers, a water <br /> sample was taken from the well that serves the Cunha Trucking (braying) Company. This well <br /> water contains a nitrate concentration of 3 ppm and a chloride concentration of 28 ppm. Both of <br /> these indicators are very low concentrations and indicates a background nitrate impact to the <br /> respective aquifer(s). A well log was not available for this well. <br /> Chloride was measured to determine septic influence which may have originated from upgradient <br /> residential structures and confined animal facilities. Chloride travels especially well in the <br /> groundwater environment and is one of the primary indicators of septic and/or animal waste <br /> impact. <br /> 3 <br /> Va!!ey Ag Research <br />