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SR0081062 SSNL
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Last modified
11/6/2019 5:06:41 PM
Creation date
11/6/2019 4:53:52 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0081062
PE
2602
STREET_NUMBER
2288
Direction
N
STREET_NAME
MURRAY
STREET_TYPE
RD
City
LINDEN
Zip
95236
APN
10510020,21
ENTERED_DATE
8/20/2019 12:00:00 AM
SITE_LOCATION
2288 N MURRAY RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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4.0 GROUNDWATER ANALYSIS <br /> 4.1 Description of the depth to groundwater, seasonal fluctuations of groundwater depth, <br /> directional flow and gradient: Description of depth to groundwater, seasonal fluctuations of <br /> groundwater,directional flow and gradient are referred to in Section 4 of the Soil Suitability Report <br /> prepared by Dillon& Murphy that is attached in the Appendix. <br /> 4.2 Description/discussion of any existing and/or potential groundwater <br /> contamination issues in the general location of the site: Description of existing or potential <br /> groundwater contamination issues in the general location of the site are referred to in Section 4.2 <br /> of the Soil Suitability Report prepared by Dillon& Murphy that is attached in the Appendix. <br /> 4.3 Description of the current use of groundwater at the site and of the future expected use <br /> of groundwater as related to the proposed development project: <br /> Based on the most recent results from San Joaquin County's "Flood Control and Water <br /> Conservation District"report on groundwater from fall 2017, the estimated depth to groundwater <br /> was determined to be 120 feet below the surface. This information is close to the data collected <br /> from the California Department of Water Resource's Water Data Library. The results of the <br /> historic depth to ground water show that the relative depth has not changed drastically throughout <br /> the years. The proposed improvements will not have a negative effect on the current depth to <br /> ground water. See appendix for the site's depth groundwater tables and diagrams. <br /> 5.0 SOURCES AND CALCULATED IMPACT OF NITRATE TO <br /> GROUNDWATER <br /> 5.1 Description of all current off-site sources of nitrate to soil and groundwater in the general <br /> up gradient area and the contribution of nitrate load from these sources to the project site: <br /> Current off-site sources of nitrate to soil and groundwater in the general up gradient area and the <br /> contribution of nitrate loads are agriculture and neighboring sites with septic systems with minimal <br /> to no current impact to the site. <br /> 5.2 Description of impact of rainfall contribution of nitrate load to the project site: The <br /> impact of rainfall contribution on the project site was completed to determine the nitrate load. The <br /> average monthly precipitation and evotranspiration are required to calculate the site nitrate load. <br /> These two values are used to estimate the deep percolation. The deep percolation is estimated by <br /> adding up the estimated monthly precipitation using 75%as a deep percolation rate.The estimated <br /> total precipitation for the year is (13.41 in) as done by (Crites and Tchobanoglous). The estimated <br /> monthly precipitations were obtained from Station 70 in the California Irrigation Management <br /> Information System (CIMIS) located in Manteca, CA. This is the closest active station to the <br /> project site and is still within the San Joaquin Valley and Zone 12. These calculations are attached <br /> in the Appendix. <br /> The results for the deep percolation at the site were 10.06 in./year. The nitrate concentration is <br /> estimated to be about 1 mg/L-N. (Hantzche and Finnemore, 1992). <br />
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