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January 16,2004- <br /> Job <br /> 004Jab Number: LG03-304 <br /> Page 11 <br /> According to the Environmental Health Department, a double system willberequired with 100 <br /> percent repair/replacement.area: .Each.filte'r bed area is calculated to be 1,396 square feet'in size. <br /> The Site.plan shows one possible configuration of the raised filter beds and reserve area. The <br /> required septic tank size should be 1,394 gallons. One 1,600 gallon septic tank could provide <br /> this volume. In addition, a e uired. The location of the proposed new water <br /> well with-a 100-foot offset from.septic systems is shown in Plate 1. <br /> 7.0 NITRA'T'E LOADING ANALYSIS <br /> Because of the concern of nitrate leaching into ground "water from septic,systems, a nitrate <br /> loading analysis was required by the San Joaquin County P.ubIic Health Services;-Environmental <br /> Health Division.(PHS-EHD), for the proposed facility to measure the potential.concentration of <br /> percolating effluent combined rain fall.over the long term: <br /> The method utilized for the nitrate loading analysis is based on'a simple mass balanceformula, <br /> discussed in a published article by Hantzsche and Finnemore(1992)'which,provides a convenient <br /> and simplified method to estimate long-term-ground-water nitrate impacts on an area-wide basis. <br /> Hantzsche and Finnemore found that-over a long period`of time,water quality.in the upper <br /> saturated ground-water zone closely approximates'fhe quality of percolating recharge waters. <br /> Hantzsche and Finnemore believe that their method is a good planning tool and:provides useful <br /> information to planners and local officials but with'some real limitations. In their article <br /> published in Ground Watdr, Hantzsche and Finnemore mention that "...the equation ignores <br /> dispersion, lateral flow, and mixing'with ground water flow from up-gradient areas. These <br /> processes would-generally contribute to additional reduction of nitrate-nitrogen concentrations in <br /> ground water to the extent that the nitrate-nitrogen concentration of ground-water flow from up- <br /> rgradient'areas is lower." ,. <br /> —The Hantzsche and Fennemore approach-is ...a'conservative(worst case) first approximation of <br /> ground-water'nitrate-nitrogen concentration resulting from'the combined effect of on-site sewage <br /> .disposal systems and precipitation. This (the equation and approach) is.for estimation'of long.- <br /> term effect(i.e., oyer years) on.ground-water quality, and is not intended for,prediction of . <br /> r .seasonal changes" (Hantzsche and Finnemore, 1992). <br /> The method takes into account development area, soil denitrification factor,.rainfall.volume, , <br /> rr4 rainfall nitrate concentration, the waste effluent quantity, and waste effluent nitrate concentration. . <br /> i .'. <br /> . .The formula, assumptions and calculations used for the analysis are'shown on Plate 5. The units <br /> of nitrate used in the mass balance equation are nitrate-N whose maximum drinking water <br /> contaminate level is 10 mglL: <br /> P pE 4S0� I <br />