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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, Michael Kith, <br /> Registered Environmental Health Specialist, Program Coordinator at the San Joaquin <br /> County Environmental Health Department, stated that he has conferred with Norman <br /> Hantzsche (author of the 1992 paper discussed previously), and they have arrived at a <br /> new method to determine flow from residential sources. He indicated that wastewater <br /> flow from a single-family residence should be calculated as 100 gallons per day (gpd) <br /> for the first bedroom and 50 gpd for each additional bedroom; additional residences <br /> should be calculated in the same manner (personal communication, March 4, 2020). <br /> Using this method, the primary residence would contribute 200 gpd, and the second unit <br /> dwelling would contribute 100 gpd (for one bedroom) or 150 gpd (for two bedrooms), for <br /> a total maximum daily flow rate of 300 to 350 gpd. <br /> A typical residential concentration of 35 mg/L of nitrate as N was selected for the <br /> proposed residence (Crites and Tchobanoglous, 1998). <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 On-Site Wastewater Treatment <br /> Systems Standards which incorporate peak and surge flow factors. The estimates used <br /> in the On-Site Wastewater Treatment Systems Standards may be greater than those <br /> discussed here. <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 will may undergo a reduction between 10 percent to 35 percent. Soils with higher <br /> clay 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 35 percent was selected for the Site because of the clayey soil <br /> present at the percolation test location. <br /> Nitrate Loading Estimate <br /> A nitrate loading scenario was employed to determine the impact from the proposed <br /> project to ground water. The scenario utilizes the variables discussed previously, which <br /> represent the estimated conditions and uses associated with this project. <br /> LOGE 20-48 Page 11 <br />