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FINDINGS AND DISCUSSION <br /> The nitrate loading concentration from the residential units determined in the referenced Studies <br /> has subsequently been recalculated and is now 14 ppm nitrate-nitrogen, still 4 ppm over the <br /> MCL. Another nitrate loading equation parameter changed was the wastewater volume in <br /> average daily flow(ADF)from 450 gallons per day(gpd)to 400 gpd, which equates to 146.000 <br /> gallons per year. <br /> The recalculated average concentration of nitrate-nitrogen in the recharge water of 14 ppm <br /> equates to 0.000116702 lbs of nitrate-nitrogen per U.S. gallon. Multiplying, we find a potential <br /> total nitrate-nitrogen concentration in the recharge wastewater, in lbs,to equal: 0.000116702 lbs <br /> NO -N/gallon x 146,000 gallons (Total wastewater flow volume)= 17 lbs of nitrate-nitrogen in <br /> the recharge water. <br /> Mr. Thornton applies 275 units (pounds per acre)of nitrogen fertilizer each growing season(or <br /> per year), based upon his average yield of 2,750 lbs almond kernels/ac. Nitrogen applied is <br /> primarily in the ammonium form from synthetic N fertilizers injected through his irrigation <br /> system (fertigation) and contributions of N from his irrigation water. His irrigation system is <br /> composed of microsprinklers and he applies 3.0 ft of irrigation water per season. <br /> Taking the subject parcel acreage of 1.37 acres x 325,851 gallons/acre-fl =446,416 gallons per <br /> foot of irrigation water applied x 3.0 ft total = 1,339,248 gallons applied. Converting 275 lbs N <br /> applied/ac x 1.37 ac = 377 lbs N applied_ 1,339,248 gals irrigation water applied=0.000282 lbs <br /> N/gallon of irrigation water. 0.000282 lbs N/gallon= 33.9 ppm N in the applied irrigation water. <br /> However, the almond trees utilize a percentage of this nitrogen concentration,with the remaining <br /> fraction potentially entering the groundwater. This is referred to as the Nitrogen Use Efficiency <br /> (NUE)Factor. It is the fraction of applied nitrogen that is absorbed and used by the plant. It is <br /> generally regarded by regulatory agencies to be 70% for almond trees (See Ref. 2, Pg 28).' <br /> Therefore,taking 70%of 33.9 ppm N utilization=33.9 x (1- 0.70)= 10.2 ppm N that may <br /> potentially enter the groundwater. <br /> CONCLUSIONS <br /> The nitrogen loading calculations above illustrate that whether the subject Parcel is planted in <br /> almonds, or developed with a primary and second unit dwelling, the loading from both sources <br /> exceeds the drinking water MCL of 10 mg/L N. <br /> It is my professional opinion that given the surrounding agricultural land use that will not change <br /> for decades, and the fact that both agricultural sources and domestic wastewater sources exceed <br /> the MCL, nitrogen loading mitigation does not warrant pressurizing the effluent from the <br /> proposed second unit dwelling. It is my professional opinion that increasing the size of the septic <br /> tank from a 1,600 gallon to a 2,000 gallon tank, thus potentially increasing the total N removal <br /> up to 30%(See Ref. 1, Pg. 12), is a much more plausible approach to decrease nitrogen loading <br /> than effluent pressurization. <br /> Page 2 of 3 <br /> Chesney Consulting <br />