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Existing groundwater quality data from the groundwater monitoring program <br /> indicates that the upper aquifer in the vicinity of the plant is divided into <br /> two distinct units. The shallow groundwater sampled by the plant monitoring <br /> wells is high in nitrates and dissolved solids. A hydraulic barrier which <br /> restricts the vertical movement of groundwater separates the groundwater in <br /> the upper stratum from the groundwater in the Laguna formation. <br /> The domestic well monitoring program samples groundwater at a depth of <br /> approximately 180 ft. During the past 4 years, nitrate concentration for the <br /> domestic wells has averaged 13 mg/l while specific conductance has averaged 420 <br /> umhos/cm. This evidence suggests that the layer of clay between the 50 and <br /> 150 ft level acts as a barrier to prevent mixing of water from the shallow <br /> aquifer with the stratum penetrated by the domestic wells. The lateral extent <br /> of this clay barrier is unknown. Edward Steffani of the Stockton East Water <br /> District maintains that there is some degree of hydraulic continuity between <br /> the shallow surface groundwater and the aquifer in the Laguna formation (4) . <br /> Locally, however, the clay layer appears to act as a barrier to vertical <br /> movement of groundwater. Figure 5 shows the site specific aquifer system. <br /> Table 2* <br /> WATER QUALITY PARAMETERS FOR DOMESTIC WELL MONITORING PROGRAM <br /> Nitrate Conductivity <br /> Year (mq/1 ) (umhos/cm) <br /> 1985 7.9 353 w � jsir �j��d, u ly <br /> 1986 6 326 <br /> 1987 15.5 367 <br /> 1988 8.8 479 <br /> * Average of four samples <br /> It should be noted that well four at 6,383 East Arata yielded water of <br /> relatively poor quality. It appears that this well draws water from the 6�� <br /> shallow groundwater and it was not used in the evaluation of data for Table 2. <br /> Groundwater Gradients <br /> The San Joaquin County Flood Control District has prepared equal elevation <br /> water contour maps biannually for the past decade. Included in the appendix <br /> are the water contour maps for 1985 and 1987. It is evident that the QAP <br /> site is directly overlying the low point of the pumping depression northeast <br /> of Stockton. For this reason the direction of the gradient may shift quite <br /> often. Site specific groundwater gradients estimated on the basis of AMSL <br /> elevations in three monitoring wells indicates that flow is generally to the <br /> east or northeast of the site. Correspondence between gradients shown on the <br /> county equal elevation contour maps and monitoring well data is quite good. <br /> 1-7 <br /> RP033-L <br />