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Crites and Tchobanoglous (1998) list a typical flow rate of 50 to 70 gallons per person <br /> per day for an individual residence. In the past, San Joaquin County Environmental <br /> Health Department has requested that the flow rate be calculated as 140 gallons per <br /> bedroom per day to reflect maximum usage. On March 4, 2020, however, the San <br /> Joaquin County Environmental Health Department dictated a new procedure for <br /> calculating residential flow, developed in consultation with Norman Hantzsche (author of <br /> the 1992 paper discussed previously). The new procedure required that wastewater <br /> flow from a single-family residence be calculated as 100 gallons per day (gpd) for the <br /> first bedroom and 50 gpd for each additional bedroom; additional residences should be <br /> calculated in the same manner (personal communication, March 4, 2020). <br /> Using this method, the existing four-bedroom house would contribute 250 gpd, and the <br /> proposed two-bedroom ADU would contribute 150 gpd, for a total wastewater flow of <br /> 400 gpd for the Site. <br /> The estimated flow values discussed here should not be used for the design and sizing <br /> of the septic system. The design and sizing of the septic system should utilize the San <br /> Joaquin County Environmental Health Department's On-Site Wastewater Treatment <br /> Systems Standards, which incorporate peak and surge flow factors. The estimates <br /> used in the On-Site Wastewater Treatment Systems Standards may be greater than <br /> those discussed here. <br /> A typical residential concentration of 35 mg/L of nitrate as N was selected for the <br /> residences (Crites and Tchobanoglous, 1998). <br /> Denitrification Reductions <br /> Denitrification is a process that occurs in the septic system drain field whereby certain <br /> bacteria oxidize the nitrate (NO3) in the wastewater and release nitrogen gas (N2) to the <br /> atmosphere. Due to the biologic processes in the shallow soils, nitrogen in the drain <br /> field may undergo a reduction between 10 percent to 35 percent. Soils with higher clay <br /> content, moist soil conditions, high pH, and organic material denitrify by about 35 <br /> percent, and soils with high sand content tend to denitrify at a lower rate of about 10 <br /> percent. <br /> A denitrification factor of 25 percent was selected for the Site because of the clay soil <br /> observed at the percolation test location. <br /> Nitrate Loading Estimate <br /> A nitrate loading scenario was employed to determine the impact from the existing and <br /> proposed development to ground water. The scenario utilizes the variables discussed <br /> previously, which represent the estimated conditions and uses associated with this <br /> LOGE 2637 Page 12 <br />