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NLS§ 1.2. As noted on the attached Soil Analysis Report,the chemical analyses conducted <br /> quantifies several constituents that influence nitrate loading for this project. The important <br /> parameters for nitrate loading assessment are the organic matter and estimated nitrogen release <br /> (ENR),clay content,pH, cation exchange capacity(CEC), and the nitrate-nitrogen content of the <br /> soil. <br /> The organic matter is medium at 2.6%. The ENR is 81 lbs/ac. This OM and ENR concentrations <br /> suggest there is an upper medium potential for future nitrate forming from organic matter. As <br /> nitrate molecules that may form from the septic effluent percolate downward, these molecules <br /> travel into and through the clay soil. This soil type is generally anaerobic, thus promoting <br /> denitrification and inhibiting nitrification. Since septic effluent is composed predominately of <br /> ammonium(NH4),the pH, along with the CEC, have significant influence on ammonium molecules. <br /> The pH of the soil is alkaline which may have the effect of promoting ammonia formation and not <br /> ammonium formation. Since ammonium is the precursor to nitrate formation, if NH3 is promoted, <br /> this will retard NH4 formation. The CEC measures the ability of the soil to theoretically trap and <br /> hold ammonium molecules and was measured at 21.2 meq/100 g,which is a high value. This <br /> suggests a high potential for the retention of ammonium molecules that may form for microbial <br /> assimilation within the soil. The nitrate-nitrogen is a medium concentration at 18 ppm, indicating a <br /> medium potential for nitrate leaching, but simultaneously a high potential for denitrification within <br /> the high claycontent soil. <br /> NLS§ 3.3. X Table 1 below summarizes the analyzed soil physical and chemical characteristics <br /> from the retrieved soil sample: <br /> TABLE 1 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SAMPLE DEPTH SOILTERTORE SOILNITRATE- pli AND <br /> CLASSIFICATION NITROGEN CONTENT CAI ION EXCHANGE CAPACITY <br /> In meq/100g <br /> 36 IN. DEPTH Clav loam 1 18 ppm NQ-N 7.4 21.2 me /1000 <br /> GROUNDWATER INFORMATION <br /> NLS§ 2.1.�roundwater depths and elevations throughout San Joaquin County are illustrated on <br /> maps published by the County Flood Control and Water Conservation District. The Fall 2016 <br /> Lines of Equal Depth Maps and the Lines of Equal Elevation Maps indicate groundwater depth and <br /> directional flow. Depth to groundwater is approximateV50 A below-grad6and the groundwater <br /> directional flow appears to be in a northeasterly direction. <br /> NLS§ 2.2,3.1. Surrounding agricultural properties are currently farmed and have been for <br /> decades, and surrounding properties have been on septic systems so the potential for nitrate -- <br /> contamination of the underlying groundwater can be considered significant. <br /> Page 2 of 12 <br />