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SR0085175_SSNL
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SR0085175_SSNL
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Last modified
5/25/2022 10:54:03 AM
Creation date
5/25/2022 10:04:02 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0085175
PE
2602
FACILITY_NAME
11662 N HAM LN
STREET_NUMBER
11662
Direction
N
STREET_NAME
HAM
STREET_TYPE
LN
City
LODI
Zip
95240
APN
05925003
ENTERED_DATE
4/20/2022 12:00:00 AM
SITE_LOCATION
11662 N HAM LN
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Quantitv and Qualitv of Domestic Wastewater <br />Approximately 81 mobile homes and a clubhouse are located on the Site. Mr. Wert <br />stated that the manager of the park lives on-site, and the clubhouse is only used by <br />residents. Mr. Wert provided a self-monitoring tables for January 2021 through <br />January 2022. During this time period, the average influent into the septic system was <br />generally 5,000 to 7,000 gallons per day (gpd), with a maximum of 7,356 gpd <br />experienced in June 2021 (Appendix 7). <br />A typical residential concentration of 35 mg/L of nitrate as N was selected for the <br />existing residences (Crites and Tchobanoglous, 1998). It should be noted that the <br />effluent from the existing septic system is being tested and reported quarterly to the <br />California Regional Water Quality Control Board. Mr. Wert provided results from five <br />quarters of effluent sampling in 2022 and 2021, as well as two quarters of effluent <br />sampling in 2020, during which time nitrate was only detected four times total, with <br />values ranging from 0.23 to 11 mg/L-N (Appendix 7). If these values were utilized in the <br />nitrate loading calculation, the predicted maximum buildup of nitrates in the aquifer from <br />the use of the septic system would be substantially lower than that calculated here. <br />Nevertheless, the standard residential concentration of 35 mg/L-N is selected for the <br />calculation to represent the situation if no treatment were taking place. <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 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 35 percent was selected for the Site because of the clayey soil <br />present at the percolation test location and indicated by the Soil Survey. <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 />LOGE 2218 Page 12 <br />
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