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Soil Suitability / Nitrate Loading Study Irerracon <br />JPM u Lathrop, Califomia <br />May 24, 2022 n Terracon Project No. NA227026 <br />As the facility is proposed to be open daily year-round, a long-term average daily flow rate was <br />not calculated. The total maximum daily flow rate for Phase I and proposed Septic System 1 is <br />1,275 gpd (Section 1.3.7). <br />The average total nitrogen concentration of domestic wastewater is normally considered to be 20 <br />to 85 mg/L-N with 35 to 45 mg/L-N being typical (Crites and Tchobanoglous, 1998, Table 4-14). <br />It is estimated that commercial use will have higher concentrations of total nitrogen when <br />compared to residential use. For the purposes of the nitrate loading estimate, it is estimated that <br />the average concentration for total nitrogen in wastewater for the project is approximately 85 <br />mg/L-N. <br />2.3.4.2 Denitrification Estimate <br />Denitrification is an important process which occurs within the leach field whereby certain bacteria <br />utilize the oxygen in the nitrate (NO3) and release nitrogen gas (N2) to the atmosphere. <br />Denitrification is expressed as a percentage, and the normally accepted range is 10 percent to 35 <br />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 to 15 percent. <br />Based on the results of the shallow and deep soil borings, the proposed leach field is expected to <br />be located within silty sandy; therefore, a denitrification estimate of 15 percent was selected. <br />2.3.5 Nitrate Loading Scenario <br />A nitrate loading scenario was performed to determine the impact from the proposed project. The <br />scenario utilizes the variables discussed previously which represent the estimated conditions and <br />uses associated with this project. The following table presents a summary of the nitrate loading <br />calculation for the site. A copy of the nitrate loading calculation is included in Appendix F. <br />Table 10. <br />Summary of Nitrate Mass Balance Equation. <br />Maximum contaminant level (MCL) for nitrate in drinking water is 10 mg/L-N <br />Based on the nitrate loading balance, nitrate levels for the proposed Phase I development is <br />anticipated to increase nitrate levels to 3.3 mg/L-N for the project area which is below the MCL of <br />10 mg/L-N. <br />Responsive ■ Resourceful ■ Reliable 17 <br />Average <br />Effluent <br />Leachfield <br />Net Rainfall <br />Proposed <br />Result (Nc)' <br />Acres <br />Daily Flow <br />Concentration <br />Denitrification <br />Recharge <br />Development <br />(mglL-N) <br />(A) <br />(Q) (9Pd) <br />(Nw) <br />(d) <br />(infyear) (R) <br />(mg/L-N) <br />Phase I — Septic <br />3.3 <br />92.39 <br />1,275 <br />85 <br />15% <br />5.58 <br />System 1 <br />Maximum contaminant level (MCL) for nitrate in drinking water is 10 mg/L-N <br />Based on the nitrate loading balance, nitrate levels for the proposed Phase I development is <br />anticipated to increase nitrate levels to 3.3 mg/L-N for the project area which is below the MCL of <br />10 mg/L-N. <br />Responsive ■ Resourceful ■ Reliable 17 <br />