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SR0080542 SSNL
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SR0080542 SSNL
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Last modified
1/2/2020 9:58:40 AM
Creation date
1/2/2020 9:47:24 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0080542
PE
2602
FACILITY_NAME
ABEL MARTINEZ
STREET_NUMBER
9216
Direction
W
STREET_NAME
LORRAINE
STREET_TYPE
RD
City
TRACY
Zip
95377
APN
24806024
ENTERED_DATE
4/29/2019 12:00:00 AM
SITE_LOCATION
9216 W LORRAINE RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Sources of Nitrate <br /> Dairies, orchards that require fertilization in sandy soils, and septic systems have been <br /> found to be the most significant sources of nitrate in ground water. <br /> Percolating Recharge Waters <br /> One of the most determinant factors in the Hantzsche and Finnemore equation is the <br /> rate of recharge from percolating waters, which mix with the downward-percolating <br /> effluent generated by on-site septic systems. In the original Hantzsche and Finnemore <br /> paper, only "average recharge rate of rainfall" was considered. For the Chico area, <br /> Hantzsche and Finnemore present an average rainfall of 22.5 inches per year and an <br /> estimated recharge of 16.8 inches per year. <br /> Based on San Joaquin County Environmental Health Department policy (personal <br /> communication, March 18, 2019), the recharge input for the Hantzsche and Finnemore <br /> equation should be derived from average monthly precipitation of rainfall and <br /> evapotranspiration rates for the area; the data should be obtained from the California <br /> Irrigation Management Information System (CIMIS), preferably from stations located <br /> within San Joaquin County. Recharge is calculated by first determining whether the <br /> average monthly precipitation exceeds average monthly potential evapotranspiration. If <br /> so, then the difference is the percolating recharge water into the aquifer. Runoff and <br /> stream infiltration drainage are not factored into the calculation. This approach likely <br /> under-estimates recharge to the aquifer and, consequently, over-estimates nitrate <br /> loading. <br /> For the project Site, the local percolation and evapotranspiration rates are presented in <br /> Plate 12. The Site is located closest to the CIMIS Ripon station (249). Data for the <br /> Ripon station were available for 2017 and 2018; based on the calculation shown, the <br /> estimated rate of recharge from percolating waters for the Ripon station is determined to <br /> be 3.12 inches. A statistical error of 46% is associated with this value. <br /> The nitrate concentration of the recharge waters was estimated to be 1 mg/L-N <br /> (Hantzsche and Finnemore). <br /> Quantity and Quality of Domestic Wastewater <br /> Mr. Martinez indicated that he plans to construct a two-bedroom house on the Site. A <br /> one-bedroom house is currently located on the Site. <br /> Crites and Tchobanoglous (1998) list a typical flow rate of 50 to 70 gallons per person <br /> per day for an individual residence. The San Joaquin County Environmental Health <br /> Department has indicated that maximum flow and double occupancy within each <br /> bedroom should be considered for the nitrate loading assessment; as a result, a value <br /> LOGE 1914 Page 9 <br />
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