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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, east and west is rural residential, all on septic systems <br /> and wells. To the south is an auto dismantling company. <br /> SSS§3.1,3.2,3.3,3.4,3.5,3.6,3.7,6.8. Application permits found in EHD online files were <br /> available for review to determine the number of permits issued for repairs/replacements/additions <br /> to existing systems found on Carpenter Road exclusively. As noted in Appendix J, the number of <br /> permits are quite extensive on this Road alone. A total of 31 permits were found. Given the <br /> hardpan/clay content of the on-site and surrounding soils, septic system longevity can be <br /> considered limited without installing deeper septic system structures, such as sumps and preferably <br /> seepage pits. Many of the permits for repairs/replacements are decades old. This indicates that <br /> originally installed systems were insufficient in size to manage ultimate effluent flow volumes, in <br /> addition to being installed in the shallow, slowly permeable soils. <br /> Found in Appendix I, are the EHD permits pertaining exclusively to the subject property. Aerial <br /> photos illustrate the locations of the on-site wells and existing septic systems. <br /> B. SOIL PHYSICAL CHARACTERISTICS AND ANALYTICAL TEST RESULTS <br /> SSS§ 5.2. The United States Department of Agriculture -Natural Resource Conservation Service <br /> (USDA-NRCS) indicates the property soils are 85% Jacktone clay, 4%Archerdale clay, <br /> 3% Unnamed, 3% Hollenbeck clay and 3% Stockton clay. <br /> NLS§ 1.1, 1.2. Auger cuttings were sampled from the bottom of the 42 inch, 12-ft and 25-ft perc <br /> test borings for chemical analysis. As noted on the A&L Laboratory Soil Report in Appendix C, <br /> analyses of the soil sample quantifies a number of constituents that influence nitrate loading for <br /> this project. The important parameters for nitrate loading assessment are the organic matter,pH, <br /> cation exchange capacity(CEC), and the nitrate-nitrogen content of the soil. <br /> As noted, the organic matter from all three depths starts at 0.6%at 42 inches, followed by 0.5%at <br /> 12 ft and 0.6%at the 25-ft depth. This translates to an Estimated Nitrogen Release(ENR)of <br /> approximately 40 lbs N/acre. This is an insignificant concentration of nitrogen release over a one <br /> acre area. The soil nitrate-nitrogen concentration at the three depths was determined to be an <br /> average of 9 ppm, which can be considered a concentration in equilibrium. <br /> Because septic effluent is composed predominately of ammonium(NHA the pH, along with the <br /> CEC, are significant influences on the ammonium molecules. The pH of the soil is alkaline at the <br /> proposed soil-effluent interface which has a positive effect in promoting ammonia and not the nitrate <br /> substrate ammonium within the alkaline soil environment. The CEC measures the ability of the soil <br /> to theoretically trap and hold ammonium molecules. The CEC illustrates a high potential for the clay <br /> fraction of the soil profile to retain ammonium molecules that remain as ammonium in the soil <br /> environment. Nitrification is also hindered due to the alkaline pH and the anaerobic clay micro-sites. <br /> Page -2- <br /> Chesney Consultin; <br />