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SR0080203 SSNL
Environmental Health - Public
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SR0080203 SSNL
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Last modified
5/12/2020 4:21:25 PM
Creation date
4/30/2020 8:40:19 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0080203
PE
2602
FACILITY_NAME
PA-1000010
STREET_NUMBER
12
Direction
W
STREET_NAME
LORENZEN
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
23914003
ENTERED_DATE
2/12/2019 12:00:00 AM
SITE_LOCATION
12 W LORENZEN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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D. GROUNDWATER INFORMATION <br /> NLS§2.1, SSS§4.1. Groundwater depths and elevations throughout San Joaquin County are <br /> illustrated on maps published by the County Flood Control and Water Conservation District, found <br /> in Appendix D. The most recent Lines of Equal Depth map (2016) indicates the groundwater <br /> depth to be 30 feet. The Lines of Equal Elevation depict the groundwater flow to be in a <br /> northwesterly direction toward the Delta and in-line with the San Joaquin River. <br /> SSS§2.1, 4.2. Surrounding properties have been intensely farmed for several decades. Thus, the <br /> probability for nitrate contamination in the underlying soil and groundwater can be considered <br /> significant if nitrogen fertilizers were used on this production land. However, soil and well water <br /> analyses indicate very low nitrate concentrations. Again,this may be attributable to denitrification <br /> activity. <br /> Calculation of Alkalinity Requirement for Nitrification <br /> The nitrate-nitrogen loading calculations on Pages 7 and 8 are contingent upon the environmental <br /> factors required for nitrification to occur. These conditions include soil pore-space oxygen content, <br /> soil temperature,pH, electrical conductivity, organic matter, cation exchange capacity, and <br /> alkalinity. Alkalinity in wastewater effluent is derived from the domestic well water supply in <br /> addition to the introduction of wastes. Nitrification-consumes approximately 7.1 mg of alkalinity <br /> for every mg. of ammonia-nitrogen(NH4-N)oxidized. Nitrification of the average Total Nitrogen <br /> (TN)concentration of 90 mg/L, as determined on Page 8 would require: 90 mg/L NH4-N x 7.1 mg <br /> CaCO3 = 639 mg/L alkalinity. The alkalinity in the domestic well water supply was tested to be an <br /> average 153 mg/L. Consequently,nitrification may be inhibited to an indeterminable degree. For <br /> comparison purposes, the average total alkalinity from the City of Stockton groundwater supplies <br /> is 158 mg/L. <br /> E. SURFACE WATER INFORMATION <br /> Storm water management consists of on-site management of runoff flows into the associated bodies of water <br /> and soil percolation. Percolating stormwater may produce dilution effects to constituents of concern, such <br /> as nitrate,within the underlying water table. <br /> Climatic Data: Rainfall versus Evapotranspiration <br /> NLS§3.2. It is generally and scientifically accepted that when precipitation exceeds <br /> evapotranspiration(Eto), deep percolation of surface rainwater may occur. Evapotranspiration <br /> refers to water evaporation that takes place both at the soil surface and transpiration by plants. The <br /> following Table illustrates rainfall and evapotranspiration for the Tracy area, which is the closest <br /> data available. Precipitation data was obtained from the Soil Survey of San Joaquin Countv. The <br /> conservative"2 years in 10"data was used and not the"average rainfall"data. Evapotranspiration <br /> data was obtained from the California Irrigation Management Information System (CIMIS): <br /> Chesney Consulting <br />
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