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`. KLEINFELDER <br /> LNe=AWN, (1-D) + (Nb R <br /> AW+R <br /> Where: <br /> L Ne = Average calculated nitrate-nitrogen in groundwater resulting from domestic sources <br /> L — and precipitation—mg/1, as N. <br /> A Number of dwelling units per acre on septic tanks (unit/acre) = 0.37 (estimated <br /> based on two homes on each of the ten lots divided by 54.7 acres.) <br /> L <br /> W = Annual wastewater loading per dwelling unit per acre (inches) = 2.0 inches (per year <br /> per dwelling unit assuming a flow of 150 gal./day/dwelling unit.) <br /> 6. Nw = Nitrate concentration of nitrified leachfield effluent (mg/1) =35 mg/1 (Hantzsche and <br /> Finnemore (1992)). Percent denitrification selected based on depth to groundwater <br /> and presence of interbedded low-percable soil strata. <br /> 6 D = Percent dentrification of leachfield effluent = 0.35 percent (0.1 to 0.35 percent <br /> typical per Hantzsche and Finnemore (1992). 0.35 selected given the large depth to <br /> groundwater(90+ feet). <br /> 6. R = Annual deep percolation of precipitation (inches) = 8.4 inches (representing 70 <br /> percent of average annual rainfall of approximately 12 inches in project area. <br /> Remaining 30 percent of rainfall is assumed to drain off-site into natural or <br /> L manmade drainages.) <br /> Nb = Background nitrate nitrogen concentration of rainfall recharge at the water table = <br /> 0.5 mg/1 (per Technical Memorandum, Hydrologic and Soil Investigation for the <br /> L Chico Urban Area, page 6, Dames and Moore, April 1996) <br /> Our calculation is as follows: <br /> L Ne = 0.37(2)(35)(l -0.35) +0.5(8.4) = 16.84+4.2 = 2.3 mg/l asN <br /> 0.37(2)+8.4 0.74 +8.4 <br /> L CONCLUSIONS <br /> As shown above, we calculate 2.3 mg/1 of nitrate-nitrogen (1) in groundwater resulting from the <br /> ` proposed leach fields, a result that is below the state standard of 10 mg/l. Based on this <br /> relatively low level of nitrate-nitrogen, we anticipate that the impact from the proposed <br /> construction on surrounding wells will be minimal. Little Johns Creek is the nearest natural <br /> L water body to the site and is located approximately 0.7 miles down gradient from the site. Based <br /> on this distance and the relatively low nitrate-nitrogen levels calculated, we anticipate that the <br /> impact to water bodies will be minimal <br /> The results of our percolation tests for Lots 1, 8, and 26 indicate that the near surface soils (at a <br /> depth of about 3 to 3'/2 feet) exhibit suitable percolation characteristics. A suitable soil condition <br /> for a test at this depth is defined as a stratum capable of percolating water at a rate of 60 min/inch <br /> or faster. A conventional septic tank/leach trench sewage disposal system designed per SJCEHD <br /> Lcriteria should adequately serve the proposed residences. <br /> L <br /> L32585.G01/ST03R1168 November 26,2003 <br /> L ©2003 Kleinfelder,Inc. Page 5 of 6 <br />