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Traylor Shea Precast Page 11 of 14 <br /> Our Project Number: E071WB i <br /> November 29, 2007 <br /> v <br /> For Phase I of the project, the total daily waste water quantity is 371 gallons per day (gpd). <br /> The flow rates selected for the uses associated with Phase II of this project are presented next. <br /> Table 7. <br /> Typical Quantity of Effluent Phase U). <br /> Category Total People Average Quantity per Average Daily Flow per Parcel <br /> per Day Person <br /> Employees 46 13 gal/day/employee (46 employees * 13 gpd * 7) 427 gpd <br /> Note: gpd is gallons per day. <br /> _ For Phase II of the project, the total daily waste water quantity is 427 gallons per day. <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 /> to residential use. It is estimated that the average concentration for total nitrogen in waste <br /> water for the project is approximately 85 mg/L-N over the long term. <br /> I1.3.4.2 Denitrification Estimate <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 (NZ) 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. A typical denitrification <br /> factor of 25 percent was selected for the Site because of the fine grained nature of the soils. <br /> II.3.5 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 table presents a summary of the <br /> nitrate loading calculations for the site, as presented in Plates 10 and 11. <br /> Table 8. <br /> S frimary of Nitrate Mass Balance Equation. <br /> Result Average Effluent Leachfield Deep <br /> Phase of Concentration Percolation <br /> (Nc)* Acres(A) Daily Flow Denitrification <br /> Project (mg/1-N) (Q)(gpd) (Nw) (d) of Rainfall <br /> (m9/�-N) (R)(in) ('i 5 <br /> Phase I 7.9 8.58 371 85 25% 4.67 <br /> Phase II 8.9 8.58 427 85 25% 1 4.67 <br /> * Maximum contaminant level (MCL)for nitrate in drinking water is 10 mg/L-N. <br /> V <br /> 902 Industrial Way•Lodi,CA 95240•209.367.3701 •Fax 209.369.4228 ©2007 Neil O.Anderson&Associates,Inc <br />