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71tappearts that the maximum mound height.that may occur under the flter bed, and above the <br /> current satic water table depth is 1,8 feet. This would leave a marginal distance of approximately <br /> five feet between the soilleffluent interface and the top of the mound (soiUeffluent interface z2 ft <br /> below grade + 5 ft separation distance= 7 ft, which the mound may rise to this depth: 9.0 ft minus <br /> 1.8 ft rise of mound z 7 ft.) For wastewater treatment to occur, the distance effluent must travel <br /> under unsaturated conditions through the soil environment is generally regarded to be five feet. <br /> Wastewater treatment in this respect is taken to be destruction of bacteria and viruses. <br /> If it is determined at some point in the future that mounding effects are preventing proper effluent <br /> treatment and disposal, the area designated as 100%replacement area may have to be activated. <br /> This may occur prior to attaining 1;050 gpd effluent flow volumes,but is unlikely. <br /> The nitrate concentration of the water table is over twice the MCL Drinking Water Standard. Total <br /> Dissolved Solids is over saline water, which is generally accepted to be 1,000 mg/L. Total <br /> alkalinity plays a significant role in nitrate formation. A concentration of 444 mg/L can be <br /> considered high for groundwater. It is normally the domestic water supply and the alkalinity in the <br /> wastewater effluent that determines nitrification potential. <br /> E. SURFACE WATER INFORMATION <br /> The surface water retention pond for the existing and future development of the project is located <br /> at the west and'south areas of the project. There should be no impact to impoundment water from <br /> the proposed new filter bed. The south pond is upgradient and somewhat crossgradient to the <br /> proposed filter bed and the addition of runoff water-percolating into the top aquifer mixing layer <br /> may create a dilution effect. <br /> Climatic Data: Rainfall versus Evapotranspiration <br /> It is generally regarded that when precipitation exceeds evapotranspiration (Eto), deep percolation <br /> of surface rainwater impoundment may occur. Evapotranspiration refers to water evaporation that <br /> takes place both at the soil surface and transpiration by plants, and is defined as water loss from a <br /> large field of 4-to-7 inch tall, cool-season grass that is not water stressed. <br /> A number of factors determine deep percolation and ultimately groundwater recharge, primarily <br /> domestic irrigation volumes and stormwater subsurface storage. The following chart illustrates <br /> rainfall and evapotranspiration for the Tracy area. Precipitation data was obtained from the Soil <br /> Survey of San Joaquin County. The "2 years in 10" data was used and not the "average rainfall" <br /> data. Evapotranspiration data was obtained from the California Irrigation Management <br /> Information System (CIMIS): <br /> 7 <br /> Chesney Consulting <br />