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Soil Suitability / Nitrate Loading Study Irerracon <br /> Jeremy Winery Lodi, CA <br /> May 7, 2019 Terracon Project No. NA197008 <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 percent to 15 percent. <br /> Based on the results of the shallow soil borings, the proposed new leach field is expected to be <br /> located within sandy silt soils that are stiff and cemented with depth. Based on the soils <br /> encountered during our borings and anticipated slow percolation rate, a denitrification estimate of <br /> 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 11. <br /> Summary of Nitrate Mass Balance Equation. <br /> Result Average Effluent Leachfield Deep <br /> Acres Concentration Percolation <br /> Land Use (Nc)* (A) Daily Flow (Nw) Denitrification of Rainfall <br /> (mg/L-N) (a) 19Pd1 (mg/L-N) (d) (R) (in) <br /> Proposed Winery 6.0 16.41 416.10 85 15% 4.49 <br /> Maximum contaminant level(MCL)for nitrate in drinking water is 10 mg/L-N. <br /> Based on the nitrate loading balance calculation, nitrate levels for the proposed development is <br /> anticipated at 4.9 mg/L N below the MCL of 10.0 mg/L-N. <br /> 2.3.6 Impact of Nitrate Loading to Nearby Water Sources <br /> The Mokelumne river is located to the south of the site, approximately 120+ feet south of the <br /> proposed leach field area which will meet OWTS setback requirements of 100 feet. Based on the <br /> topographic maps, the site is situated approximately 20 to 25 feet higher than the river with a <br /> westerly topographic gradient. The addition of 25 foot deep seepage pits (if applicable) would <br /> place the pits at an elevation equal to the river. Groundwater was reported at depths greater than <br /> or equal to 90 feet bgs; therefore, if seepage pits were to be utilized, there would be a significant <br /> buffer of soil mass between the bottom of the seepage pit and groundwater. Based on depth to <br /> Responsive ■ Resourceful ■ Reliable 17 <br />