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5.2 Description of impact of rainfall contribution of nitrate load to the project site: The <br /> impact of rainfall contribution on the project site was obtained to determine the nitrate load. The <br /> average monthly precipitation and evotranspiration are required to calculate the site nitrate load. <br /> These two values are used to estimate the deep percolation. The deep percolation is estimated by <br /> analyzing the difference between the monthly average precipitation and the evotranspiration,when <br /> the evotranspiration exceeds the monthly average precipitation.The available evotranspiration was <br /> adjusted with an adjustment factor based landscaping on-site. These calculations are attached in <br /> the Appendix. <br /> The data for the potential evotranspiration water was obtained from the California Irrigation <br /> Management Information System (CIMIS). The project is located within an area designated as <br /> Zone 12. Based on the values for this area along with the average monthly precipitation values <br /> obtained from the Western regional Climate Center (Station 242) for the Staten Island region an <br /> estimate of the deep percolation of rain for the project was determined. <br /> The results for the deep percolation at the site were 8.98 in./year. The nitrate concentration is <br /> estimated to be about 1 mg/L-N. (Hantzche and Finnemore, 1992). <br /> 5.3 Description of all current on-site sources of nitrate to soil and groundwater and the <br /> contribution of nitrate load from these sources to the project site: The sources of nitrates are <br /> the existing septic systems in use by an existing parcel for residential uses and office/wine tasting <br /> facility. The existing septic systems were accounted for when determining the approximate nitrate <br /> concentration, the site is expected to produce minor increase of nitrates with the proposed <br /> development. <br /> 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 will remain consistent. It will continue be a winery. The improvements are proposing a new <br /> building that will be built in two phases. The building would only have four fixtures,three of them <br /> being sinks. The maximum number of employees using the building would be six employees <br /> during the harvest season. That number would go down to three during the remainder of the year. <br /> The proposed building improvements are capable of generating 14 gal/person/day of wastewater. <br /> The existing site includes a house for which we expect to see 49 gal/day and an existing wine <br /> tasting facility that could provide capacity for the wastewater generated by 480 people/day. Based <br /> on the duration of visitors on-site and use of Agri-tourism the winery would generate 2 gal/per/day. <br /> The maximum flow generated from the existing home of 49 gals/day and another 84 gals/day from <br /> the proposed building, along with a maximum of 960 gal/day for the winery would total 1,089 <br /> gal/day. Accounting for these existing and proposed improvements the site can sustain a flow of <br /> 1,089 gal/day and not exceed 10 mg/L-N. This method of calculating the nitrate loading <br /> concentration is conservative as it does not include lateral dispersion or mixing of groundwater. <br /> The site is expected to grow in phases, but the additions to the existing site have no significant <br /> impact on the 4.38-acre site. The calculation of the flows generated on-site is conservative as the <br /> winery will not experience 480 people on a daily basis. The site will also only have a maximum <br /> number of workers on-site for a brief seasonal period. Given these factors it is safe to say the site <br /> is capable of sustaining the proposed uses without exceeding l Omg/L-N. <br /> 5 <br />