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of the ground-water aquifer, it is possible that any remaining surface contaminants may <br /> be transported to the first saturated zone of the aquifer. <br /> Because ground water is so deep in the area (125 to 153 feet bgs), there is potential for <br /> significant nitrate attenuation before the effluent reaches ground water. Clay-containing <br /> soils, like those observed on the Site, also tend to inhibit downward movement of nitrate <br /> due to adsorption of the nitrate ions to the soil. <br /> Sources of Nitrate <br /> Dairies, orchards that require fertilization in sandy soils, and septic systems have been <br /> found to be the most significant sources of nitrate in ground water. The Site is located <br /> within a small rural residential neighborhood surrounded by orchards. <br /> Percolating Recharge Waters <br /> One of the most determinant factors in the Hantzsche and Finnemore equation is the <br /> rate of recharge from percolating waters, which mix with the downward-percolating <br /> effluent generated by on-site septic systems. In the original Hantzsche and Finnemore <br /> paper, "average recharge rate of rainfall" was utilized. <br /> Based on San Joaquin County Environmental Health Department policy (personal <br /> communication, March 18, 2019), the recharge input for the Hantzsche and Finnemore <br /> equation should be derived from average monthly precipitation of rainfall and <br /> evapotranspiration rates for the area; the data should be obtained from the California <br /> Irrigation Management Information System (CIMIS), preferably from stations located <br /> within San Joaquin County. Recharge is calculated by first determining whether the <br /> average monthly precipitation exceeds average monthly potential evapotranspiration. If <br /> so, then the difference is the percolating recharge water into the aquifer. Runoff and <br /> stream infiltration drainage are not factored into the calculation. This approach likely <br /> under-estimates recharge to the aquifer and, consequently, over-estimates nitrate <br /> loading. <br /> The closest CIMIS stations to the Site are Manteca (station 70) and Holt (station 248). <br /> Data for the Manteca station were available for the past 12 years; based on the <br /> calculation shown, the estimated rate of recharge from percolating waters for the <br /> Manteca station is determined to be 3.83 inches (Plate 14). A statistical error of 53 <br /> percent is associated with this value. Data for the Holt station were available for the <br /> past nine years; based on the calculation shown, the estimated rate of recharge from <br /> percolating waters for the Holt station is determined to be 3.99 inches (Plate 15). A <br /> statistical error of 54 percent is associated with this value. The values for the two <br /> stations were then averaged, for an average rate of recharge of 3.91 inches for the <br /> vicinity of the Site. <br /> LOGE 2614 Page 9 <br />