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Figure 2. Soil texture was described by the laboratory as clay-loam with 41.6%sand, 20.7%silt, and <br /> 37.7%clay. <br /> Natural Resources Conservation Service data indicates the top soils consist of Capay and Stomar clays, <br /> with 0-2%slopes. <br /> Nitrate Loading Basis and Assumptions <br /> Because there are concerns of nitrate leaching into ground water from septic systems, a nitrate loading <br /> analysis is required by the SJCEHD for approval of the proposed development. The study estimates the <br /> potential concentration of percolating effluent produced by the proposed project over the long term. j <br /> Where percolating effluent leaches into the ground,ground water quality may be adversely impacted to <br /> some degree,should the effluent reach ground water. <br /> The method utilized for the nitrate loading analysis is based on a simple and convenient mass balance <br /> formula,discussed in a published article by Hantzsche and Finnemore(1992). Hantzsche and Finnemore <br /> have found from investigations conducted in the Chico,California area,the water quality in the upper ` <br /> saturated ground-water zone closely approximates the quality of percolating effluent from septic <br /> systems.They have developed a simple method that could be used to estimate the quality of the <br /> percolating effluent from septic systems. The quality of the percolating effluent may represent the <br /> potential worst-case condition the upper aquifer would ever experience from the use of on-site septic <br /> systems. Mixing and dilution in the aquifer as well as adsorption and adhesion in the soil,substantially <br /> reduce the concentration of percolating effluent. - <br /> The Hantzche and Finnemore equation is a conservative approximation of ground water nitrate-nitrogen <br /> concentration resulting from the combined effect of on-site sewage disposal systems and precipitation. <br /> The equation and method is for estimating long-term effect on ground-water quality,and is not <br /> intended for prediction of seasonal changes (Hantzsche and Finnemore, 1992). <br /> The method takes into account the development area,soil denitrification factor, rainfall recharge area, <br /> rainfall nitrate concentration,waste effluent quantity,and waste effluent nitrate concentration from on- <br /> site septic systems. The equation for calculating the project's potential to adversely impact local <br /> groundwater by increasing nitrate concentrations, also defined as long term average concentration of <br /> percolating effluent Nc,shown in Figure 3. <br /> Mass Transport Soil Properties <br /> Preliminary percolation tests at the site have revealed that the soils are permeable.The soil will allow <br /> moderate infiltration of water through the surface soils. Effluent remaining near the ground surface <br /> provides more opportunity for biologic processes to occur. In addition,soil borings at the site <br /> consistently show the presence of numerous lenses of sandy clays in the 0'to 50'depth range. Although <br /> it is not expected that the sandy clays will act as impermeable barriers, it will reduce the rate of <br /> transport and greater dispersion of nitrate. <br /> LBA Nitrate Loading Study/Jan 2017 pg. 3 <br />