Laserfiche WebLink
SSS§ 5.2. As detailed in the original Studies completed for the Preston Pipelines project, a deep <br /> boring was completed near the subject area to determine subsurface soil characteristics and depth to <br /> groundwater. Rust mottling was observed in the test boring at the ten-foot depth indicating seasonal <br /> soil saturation. Soil saturation may be beneficial for the promotion of denitrification potential. <br /> NLS§ 1.1, 1.2. As noted on the A&L Laboratory Soil Analysis Reports found in Appendix B, <br /> chemical analyses of the soil samples from the disposal area quantify several constituents that will <br /> influence nitrate loading from this Blue Rhino project. The important parameters for nitrate loading <br /> assessment are the organic matter, pH, cation exchange capacity(CEC), clay content percentage, and <br /> nitrate-nitrogen content. <br /> The organic matter in the soil is low in both samples. However, the nitrate-nitrogen concentrations <br /> are medium at the 2-foot depth, but very high at the 42-inch depth. This high nitrate-nitrogen <br /> cone ' n may a from the former Hayers Egg Ranch and suggests a very high potential for <br /> future nitrate-nitrogenTading from Indigenous nitrogen content within the soil. Since septic <br /> effluent is composed predominately of ammonium(NH4), the pH, along with the CEC, are <br /> significant influences on ammonium molecules. The pH of the soil is alkaline which may inhibit <br /> ammonium formation and stability, and may create a propensity for ammonia(NH3) formation. The <br /> CEC measures the ability of the soil to theoretically trap and hold ammonium molecules. Cation <br /> Exchange Capacities of the soil samples are medium for the 2-ft depth, but increase significantly at <br /> the 42-inch depth. This suggests there is some potential for the retention of ammonium molecules <br /> for microbial uptake, and suppression of nitrification. <br /> ss5 _< 3 <br /> NLS§5:3 Table 1 below summarizes the subsurface soil characteristics encountered from the two <br /> sampie-8epths: <br /> TABLE 1 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SAMPLE DEPTHFI'%/o,, <br /> ND Son, SOIL NITROGEN pH AND <br /> CLASSIFICATION CONTENT CATION EXCHANGE <br /> S CAPACITY <br /> 2 FT DEPTH 59%,24%, 16% Sandy Loam 16 ppm NO,-N 7.8 14.7 meq/100g <br /> 42 IN DEPTH % . Loam 59 ppm NO,-N 7.7 27.9 meq/100g <br /> C. PERCOLATION TEST RESULTS <br /> SSS§ 6.2. To assess the permeability of the on-site soils, the percolation test boring was completed <br /> in the proposed leachfield location as depicted in the Site Plan found in Appendix C. The test depth <br /> at 40 inches below existing grade gives a comparatively detailed observation of subsurface <br /> permeability from approximately 34 to 40 inches in depth. The test depth can be considered to <br /> represent the average permeability throughout the effluent receiving soil profile. <br /> L3 <br /> Chesney Consulting <br />