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A summary of the perc test results with corresponding application rates in gallons of effluent <br /> accepted per square foot of soil per day are illustrated in Table 2: <br /> TABLE 2 <br /> PERCOLATION TEST RESULTS WITH CORRESPONDING SOIL TYPE, <br /> PERCOLATION RATES AND APPLICATION RATES IN GALLONS/FT /DAY <br /> 24 INCH DEEP PERC TEST BORING 5.5 min/inch / 1.20 gallons/ft2/day <br /> LOAMY SAND <br /> PERCOLATION RATE/APPLICATION RATE <br /> 42 INCH DEEP PERC TEST BORING 4.7 min/inch / 0.85 gallons/ft2/day <br /> SAND <br /> PERCOLATION RATE/APPLICATION RATE <br /> Application Rate adapted from EPA 615'R-!N'008 Onsite Wanewmer 7reatment Systems Mmmal and is based on the soil classification. <br /> D. GROUNDWATER INFORMATION <br /> NLS§ 2,1, SSS§ 4. . Groundwater depths and elevations throughout San Joaquin County are <br /> illustrated on s published by the County Flood Control and Water Conservation District. The <br /> Fall 2014 Ines of Equal Depth Map indicate the groundwater depth to be approximately 10 feet <br /> below grade. The Fall 2014 Lines of Equal Elevation Map illustrates the groundwater directional <br /> flow to be in a northeasterly direction. <br /> NGLS§ 2 3.1,SSS 2.1, .2. Since the surrounding properties were farmed for a number of <br /> decades,the potentihYt"or nitrate contamination to the upper groundwater aquifers can be considered <br /> significant. However, from extensive studies conducted for EHD, high nitrate groundwater has not <br /> been observed in areas near large bodies of water, or near rivers. Both a large body of water and the <br /> San Joaquin River exist to the south and southwest of the property. Correspondingly, the on-site <br /> well has a nitrate concentration of 0 ppm(Below Detectable Limits - BDL) as nitrate. <br /> NLS§ 2 SS ,4.4,4.5, 4. The 10-inch diameter, on-site domestic was sampled from- <br /> a directly the south of the well. The water was allowed to run for3CTm'mutes with the <br /> p cycling several times to ensure that aquifer formation water was sampled and not stagnant <br /> well casing water. A nitrate water sample was drawn into a one-quarter liter plastic bottle and the <br /> DBCP/EDB sample was drawn into three VOC glass vials. The four sample containers were placed <br /> in a cooled ice chest and then stored under refrigeration until delivery to the laboratory, under the <br /> attached Chain of Custody found in Appendix E. The constituents tested were for nitrate and <br /> Dibromochloropropane (DBCP) and Ethylenedibromide(EDB), with the test results illustrated below: <br /> 4 <br />