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II. SOIL SUITABILITY STUDY FINDINGS <br />A. SUBJECT PROPERTY AND SURROUNDING STUDY AREA INFORMATION <br />SSS§ 1.1. Land use to the north, south, east and west is agricultural production and very sparse <br />rural residential. The City of Tracy is located five miles to the southwest. <br />SSS§ 3.1, 3.2, 3.3, 3.4, 3.5, 3.6, 3.7, 6.8. Applications for Repairs/Additions Permits in EHD files <br />were reviewed to determine life spans of surrounding septic systems. Five permits on Delta Ave. <br />exclusively were issued. Considering sparse rural development, this can be considered a high <br />number of permits. Copies of these Applications are found in Appendix F. <br />The project site has level terrain; consequently, there is no need to incorporate design <br />considerations for slopes within the effluent disposal area. <br />B. SOIL PHYSICAL CHARACTERISTICS AND ANALYTICAL TEST RESULTS <br />SSS§ 5.2. The UC Davis Soil Web designates the soil as a Merritt silty clay loam, partially <br />drained (# 197). Texture analysis by A&L Labs confirms the surface and subsurface soils to be a <br />clay loam. <br />NLS§ 1.1, 1.2. The surface and subsurface soil investigation began on June 2, 2019 with the <br />drilling of one 36 -inch deep perc test boring and a 36" deep boring in the cropland for soil <br />comparison purposes. Auger cuttings were sampled from the referenced depths for chemical <br />analysis. As noted on the A&L Laboratory Soil Report in Appendix B, analysis of the soil samples <br />quantifies a number of constituents that influence nitrate loading from this project. The important <br />parameters for nitrate loading assessment are the organic matter, pH, cation exchange capacity <br />(CEC), and the nitrate -nitrogen content of the soil. <br />As noted, the organic matter is 2.9% at 0"-6""for both sample sites, but declines to 1.4% and 1.7% <br />at.30"-36" which translates to an Estimated Nitrogen Release (ENR) of 89 lbs. of N/acre for the <br />surface soils and approximately 60 lbs. N/acre for the deeper soils. The soil nitrate -nitrogen <br />concentration is 11 ppm (0"-6") and 8 ppm (30"-36") in the leachfield soils, illustrating <br />denitrification. A very low nitrate -nitrogen concentration of 1 ppm at both depths in the cropland <br />soil indicates the existing grain crop has assimilated the applied nitrogen fertilizer exceedingly <br />well. <br />Because septic effluent is composed predominately of ammonium (NH4), the pH, along with the <br />CEC, are significant influences on the ammonium molecules. The pH of the soil profile is acidic in <br />the surface soils and alkaline in the subsurface soils. At these pHs, ammonium will have a <br />propensity to remain as NH4 but convert to the ammonia fraction in the deeper soils. The CEC <br />measures the ability of the soil to theoretically trap and hold ammonium molecules. The CECs <br />throughout the soil profile for both locations is a medium exchange capacity. Therefore, there is a <br />medium potential for the clay soil to retain ammonium molecules within the soil environment. <br />Page -2- <br />Chesney Consulting <br />