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Mr.Sandi De Jong <br /> September 25,2003 <br /> Page 12 <br /> r_ <br /> The method utilized for the nitrate loading analysis is based on a simple mass balance formula, <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 the quality of percolating recharge waters. <br /> They believe that their method is a good planning tool and provides useful information to <br /> planners and local officials but with some real limitations. In their article published in Ground <br /> Water,Hantzsche and Finnemore mention that"...the equation ignores dispersion, lateral flow, <br /> and mixing with ground water flow from up-gradient areas. These processes would generally <br /> contribute to additional reduction of nitrate-nitrogen concentrations in ground water to the extent <br /> that the nitrate-nitrogen concentration of ground-water flow from up-gradient 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., over years) on ground-water quality, and is not intended for prediction of <br /> seasonal changes" (Hantzsche and Finnemore, 1992). <br /> The method takes into account development area, soil denitrification factor, rainfall volume, <br /> rainfall nitrate concentration,the waste effluent quantity, and waste effluent nitrate concentration. <br /> The formula, assumptions and calculations used for the analysis are shown on Plates 2 through 4. <br /> The units of nitrate used in the mass balance equation are nitrate-N whose maximum drinking <br /> water contaminate level is 10 mg/L. <br /> 7.1 Quantity of Quality of Domestic Wastewater From Proposed Project <br /> The average total nitrogen concentration of the domestic waste water is normally considered to <br /> be 20-85 mg/L-N with a typical concentration of 45 mg/L-N (Crites and Tchobanoglous, 1998). <br /> We believe a reasonable concentration for nitrate may be about 45 mg/L-N due to the use <br /> blending kitchen wash water with the higher nitrate concentration restroom waste water. <br /> 7.2 Quantity and Quality of Deep Percolating Rain Water <br /> An estimate of the quantity and quality of rainfall was required for the analysis. The estimate of <br /> deep percolation of rain is based on the average monthly precipitation of rain fall and <br /> evapotranspiration for Lodi, California. The estimate first determines whether the average <br /> monthly precipitation exceeds average monthly potential ET. If so, then the difference is <br /> pE RSO <br /> O � <br /> f <br /> �'tSOG <br />