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SR0081792
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4200/4300 - Liquid Waste/Water Well Permits
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SR0081792
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Last modified
3/16/2020 10:07:23 PM
Creation date
3/16/2020 2:10:34 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4200/4300 - Liquid Waste/Water Well Permits
FileName_PostFix
SSNL
RECORD_ID
SR0081792
PE
2603
FACILITY_NAME
CAIN PROPERTY
STREET_NUMBER
7555
Direction
S
STREET_NAME
COUNTRY
STREET_TYPE
RD
City
STOCKTON
Zip
95215
APN
18514030
ENTERED_DATE
2/25/2020 12:00:00 AM
SITE_LOCATION
7555 S COUNTRY RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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TSok
Tags
EHD - Public
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aquifer, it is possible that any remaining surface contaminants may be transported to <br /> the first saturated zone of the aquifer. <br /> First ground water is predicted at 120 to 134 feet below ground surface for this Site; <br /> consequently, significant nitrate reduction would be anticipated as the septic effluent <br /> percolates downward. Clay soils, like those found on this Site, also tend to inhibit <br /> downward movement of nitrate due to adsorption of the nitrate ions to the soil. <br /> 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, "average recharge rate of rainfall" was utilized. <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). Recharge is calculated by first <br /> determining whether the average monthly precipitation exceeds average monthly <br /> potential evapotranspiration. If so, then the difference is the percolating recharge water <br /> into the aquifer. Runoff and stream infiltration drainage are not factored into the <br /> calculation. This approach likely under-estimates recharge to the aquifer and, <br /> consequently, over-estimates nitrate loading. <br /> The Site is located between the CIMIS stations at Manteca (station 70) and Holt (station <br /> 248); taking both stations into account will yield a value more representative of the Site <br /> area. Data for the Manteca station were available for the past five years; based on the <br /> calculation shown, the estimated rate of recharge from percolating waters for the <br /> Manteca station is determined to be 3.64 inches (Plate 14). A statistical error of 48 <br /> percent is associated with this value. During the past five-year period, data from the <br /> Holt station were only available for 2017 and 2018; based on the calculation shown, the <br /> estimated rate of recharge from percolating waters for the Holt station is determined to <br /> be 3.72 inches (Plate 15). A statistical error of 25 percent is associated with this value. <br /> The two stations are then averaged, for a regional deep percolation value of 3.68 <br /> inches. <br /> LOGE 1946 Page 9 <br />
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