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SR0085445_SSNL
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2600 - Land Use Program
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SR0085445_SSNL
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Last modified
10/26/2022 8:50:07 AM
Creation date
10/26/2022 7:52:03 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0085445
PE
2602
STREET_NUMBER
19319
Direction
E
STREET_NAME
OAKWOOD
STREET_TYPE
RD
City
STOCKTON
Zip
95215
APN
18506006
ENTERED_DATE
6/23/2022 12:00:00 AM
SITE_LOCATION
19319 E OAKWOOD RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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exist to the depth of the ground -water aquifer, it is possible that any remaining surface <br />contaminants may be transported to the first saturated zone of the aquifer. <br />Because ground water is so deep in the area (116 to 146 feet bgs), there is potential for <br />significant nitrate attenuation before the effluent reaches ground water. Clay -containing <br />soils, like those found on this Site, also tend to inhibit downward movement of nitrate <br />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 />Percolatina Recharae 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 closest to the CIMIS Manteca station. Data from the Manteca <br />station were available for 2014 through 2021; based on the calculation shown, the <br />estimated rate of recharge from percolating waters for the Manteca station is <br />determined to be 3.21 inches (Plate 12). A statistical error of 54 percent is associated <br />with this value. <br />Quality of Rainwater <br />Hantzsche and Finnemore listed 1 mg/L-N as the nitrate concentration of rainwater for <br />their original calculation; in the past, Live Oak has also utilized this value for the nitrate <br />loading calculation. <br />To determine a more accurate local value, Live Oak has collected rainwater during <br />several recent storm events in Lodi. Each sample was collected in a clean, dry, <br />LOGE 2226 Page 9 <br />
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