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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 future use of the <br /> site, if the rezone is approved, will continue to be residential. The existing lot would be divided <br /> into two equal lots,with each lot containing 5 acres. The projected 10 acres will be used for rural <br /> residential purposes. For residential use,the approximate flow rate that is expected to be generated <br /> is between 50 to 70 gallons per person per day (Crites and Tchobanoglous). Calculating the site's <br /> nitrate loads, a conservative value of 70 gallons per person per day was used. This method is <br /> conservative as it does not include lateral dispersion or mixing of groundwater. These factors of <br /> safety are additional to the County's factor of safety. The residential homes both contain 3 <br /> bedrooms. The residential homes are expected generate an approximate of 240 gallons of <br /> wastewater per day. <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 35 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 10-15% of <br /> denitrification. The value used for this site was 15%. <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 each 5-acre parcel would contain a Nitrate <br /> Load (Nc) of 5.41 mg/L-N. Each site would be able to sustain flow of up to 600 gal/day, a flow <br /> surpassing that amount could cause an impact to the site's nitrate load and surpass the maximum <br /> contaminant level (MCL) of 10.0 mg/L-N for 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 are minimal. The Hanztch/Finnemore <br /> equation's factor of lowers those risks, but no major additions should be made beyond a flow of <br /> 600 gal/day without an update to this 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: The project, as described in this report is sustainable by the site in current conditions. <br /> Additions or modifications to the site may require the addition of a waste water treatment system. <br /> At the time an addition is proposed, this report should be updated to ensure the adequate <br /> improvements are made. <br /> 5 <br />