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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 immediate north and east is industrial facilities an lie Stockton <br /> Metropolitan Airport. To t south is-predominately faunLand with ran and ranchettes. To the <br /> immediate west, i a stilling basin for the South Fork of Little Johns Creek his basin is less than <br /> six feet deep; therefore,t e leachfield setbac� is 1 ft. Further west is the town of French Camp. e <br /> i J <br /> SSS§3.1,3.2,3.3,3.4,3.5,3.6,3.7, 6.8. Applications for Permit in the EHD microfiche files were <br /> reviewed to determine life spans of surrounding septic systems. Since rural development is sparse in <br /> the surrounding areas, the town of French Camp was reviewed, specifically the French Camp School. <br /> From February 1961, up through June 1991 were there no repairs completed. Only one other repair <br /> was completed in the surrounding one mile radius from the subject property. Therefore, it appears <br /> that systems in this locale possess reasonable life spans. Copies of these Applications are found in <br /> Appendix F. <br /> The project site has level terrain; consequently, there is no need to incorporate design considerations <br /> for slopes within the effluent disposal area. <br /> B. SOIL PHYSICAL CHARACTERISTICS AND ANALYTICAL TEST RESULTS <br /> SSS§ The UC avis Soil Web esignates the soil as Ja nne( la 0 . Texture analysis <br /> - — <br /> by &L La s fin t e s t 20 below grade (b.g.)to be a hea clay, ut at the 42 depth, <br /> the soi is classified as loam(silt <br /> NLS§ 1.1, 1.2. The surface and subsurface soil investigation began on January 3,2019 with the <br /> drilling of one 40-inch deep perc test boring. Auger cuttings were sampled from the 20" depth and <br /> the 40" depth. As noted on the A&L Laboratory Soil Report in Appendix C, chemical analysis of the <br /> soil samples quantifies a number of constituents that influence nitrate loading for this project. The <br /> important parameters for nitrate loading assessment are the organic matter, pH, cation exchange <br /> capacity(CEC), and the nitrate-nitrogen content of the soil. In addition,the carbon:nitrogen(C:N) <br /> ratio was also determined. <br /> As noted, the organic matter is 2.4% at 20", but declines to 1.1%at 40" which translates to an <br /> Estimated Nitrogen Release(ENR) of 51 lbs. of N/acre. This is an insignificant concentration of <br /> nitrogen over a one acre area. The soil nitrate-nitrogen concentration is very low at 4 ppm at the 20" <br /> depth and declines to 1 ppm at 40", illustrating denitrification. <br /> Because septic effluent is composed predominately of ammonium (NH4),the pH, along with the CEC, <br /> are significant influences on the ammonium molecules. The pH of the soil profile is alkaline at over 8. <br /> At this pH, ammonium will have a propensity to convert to the ammonia formation. The CEC <br /> measures the ability of the soil to theoretically trap and hold ammonium molecules. The CEC at 20" <br /> is very high at 35.0 and lowers to a still significantly high 27.4 meq/100g. This indicates a high <br /> potential for the clay and silt soil to retain ammonium molecules within the soil environment. <br /> Page-2- <br /> Chesney Consulting <br />