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5.4 Discussion of all proposed future on-site sources of nitrate to soil and groundwater and <br />the contribution of nitrate load from these sources to the project site: The existing use for this <br />site is residential. Given the existing three bedroom home, it is expected they generate 100 gals/day <br />for the first room and 50 gals/day for every subsequent room. Assuming a new two bedroom home, <br />that would generate a total of 150 gal/day. This project site can sustain that maximum as shown <br />on the included calculations. <br />The average total nitrogen concentration of domestic wastewater is about 20-85 mg/L-N, <br />although 35-45 mg/L-N is a better approximation (Crites and Tchnobanglous). The value <br />selected for this site was 45 mg/L-N. <br />The site will experience a process of denitrification as the soil naturally treats surface material <br />through natural forms. Denitrification is a process that occurs when bacteria uses oxygen in the <br />nitrate (NO3) and release nitrogen (N2) into the atmosphere. Denitrification can be variable to the <br />type of soils, chemical properties, moisture content and other variables. Based on the sandy loams <br />on site and the high percolation rates, this site's soil has low levels of denitrification. It is expected <br />that a site with soil of these characteristics shall have approximately about 10-20% of <br />denitrification. The value used for this site was 20%. <br />5.5 Calculate mass balance of nitrogen loading considering all potential sources identified <br />using Hanztch/Finnemore equation: <br />Using the data mentioned within this report and the attached Soil Suitability Report the mass <br />balance of nitrogen loading for this site was calculated, this was done using Hanztch/Finnemore <br />formula. Based on the Hanztch/Finnemore equation this 0.51 acre site would contain a Nitrate <br />Load (Nc) of 19.39 mg/L-N. The 350 gal/day flow would require a proprietary measure to avoid <br />the site's nitrate load from surpassing the maximum contaminant level (MCL) of 10.0 mg/L-N for <br />Nitrate in drinking water. <br />6.0 Discussion of nitrate loading results relative to proposed method of <br />wastewater disposal <br />6.1 Discussion of total nitrate impact from proposed project: There are possibilities that the <br />percolating effluent could affect water conditions if nitrates are not reduced. The <br />Hanztch/Finnemore equation has an added to the factor of safety, which is not accounted for, as it <br />does not include lateral dispursment in its calculations diminishing those risks. No additions should <br />be made beyond the proposed improvements mentioned previously without an update to this <br />report. <br />6.2 Description of the methods proposed to mitigate any known or future impact to soil and <br />groundwater from nitrate and/or other constituents of concern, at and/or around the project <br />site: <br />The project, as described without any mitigation efforts, would not be feasible. However, the <br />proprietary measure that will be installed, shall reduce the nitrate loading concentration to <br />acceptable levels. The site is considering several alternatives, subject to cost, maintenance <br />requirements and required area. All the measures being considered have to be EPA ETV approved <br />and have approval of NSF/ANSI Standard 40 test protocol. At the moment, the primary option to <br />treat the nitrate loading concentration would be a HDPE Tank Biofilter. The HDPE Tank Biofilter <br />is ideal for increased nitrogen removal and are pre -assembled for faster and easier installation. The <br />5 <br />