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Spanos Property <br /> Page 3 <br /> our Project Number: LG5090501 <br /> April 14, 2009 <br /> The average total nitrogen concentration of domestic waste water is normally considered to be <br /> 20-85 mg/L-N with 35 to 45 mg/L-N being typical (Crites and Tchobanoglous, 1998). It IS <br /> estimated that commercial use will have higher concentrations of total nitrogen when compared <br /> x to residential use. It is estimated that the average concentration for total nitrogen in waste <br /> water for the hotel aspect of the project is near residential use, approximately 45 mg/L-N over <br /> the long term. The service station and commercial/retail aspect of the project 1s approximately <br /> 85 mg/L-N over the long term, and the short order restaurant will have a concentration near <br /> approximately 60 mg/L-N. <br /> The adjusted nitrogen long term average using a weighted average is 58 mg/L-N. Below Is the <br /> long term weighted average of nitrogen in the proposed development waste water. <br /> Weighted Ayeraae ofi TotAl Nitro_ etenn <br /> Hotel: 2,1.00 gpd x 45 Mg/L-N = 94,500 <br /> Restaurant: 1.,050 gpd x 60 mg/1--N = 63,000 <br /> Commercial/retail: 900 gpd x 85 mg/L-N = 76,500 <br /> 234,000 / 4,050 gpd = 58 mg/L-N <br /> Denitrification.Estirnalte <br /> Denitrification is an important process which occurs within the leach field whereby certain <br /> bacteria utilize the oxygen in the nitrate (NO3) and release nitrogen;gas (N7-) to the atmosphere. <br /> Denitrification is expressed as a percentage, and the normally accepted range is 10 percent to <br /> 35 percent. Soils with higher clay content, moist soil conditions, high pH, and organic material <br /> denitrify by about 35 percent, and soils with high sand content and fast percolation rates are <br /> estimated to denitrify at a lower rate, about 10 percent to 15 percent. <br /> A denitrification factor of 35 percent was selected for the Site because of the fine grained <br /> nature of the soils. <br /> Nitrate Loading Scenario <br /> A nitrate loading scenario was performed to determine the impact from the proposed project. <br /> The scenario utilizes the variables discussed previously which represent the estimated <br /> conditions and uses associated with this project. The following tabled presents a summary of the <br /> nitrate loading calculation for the site (also, see Plate 2). <br /> Table 2,. <br /> S mmary of Nitrate Mass Balance E uatiarn <br /> Result Average Effluent Leachfield Deep <br /> Parcel (Nc)* Acres(A) Daily Flow Concentration Denitrification Percolation <br /> (Nw) of Rainfall <br /> (m9/L-N) (Q)(gpd) <br /> (m01LN) (d) (R)(in) <br /> 1 14.1 17.1 4,050 58 35% 5.75 <br /> *Maximum contaminant level(MCL)far nitrate In drinking water is 10 mg/L-N. <br /> 902 Industrial Way•Lodi,CA 95240.7-09.3673701 -Fax 209.369.4-228 92007Ncol0.Anderson&Aosoatare,s,Inc <br />