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SR0081495 SSNL
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Last modified
9/1/2020 4:19:25 PM
Creation date
1/23/2020 10:16:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0081495
PE
2602
FACILITY_NAME
SAN JOAQUIN DELTA COMMUNITY COLLEGE
STREET_NUMBER
5298
Direction
E
STREET_NAME
BRUNSWICK
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
19704006
ENTERED_DATE
12/6/2019 12:00:00 AM
SITE_LOCATION
5298 E BRUNSWICK RD
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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Soil Suitability/ Nitrate Loading Study Irerracon <br /> Manteca Farm Improvement Manteca, California <br /> October 29, 2019 Terracon Project No. NA197073 <br /> 1.4 Groundwater Information <br /> 1.4.1 Groundwater Depth and Gradient <br /> Groundwater was not encountered within our borings which were advanced between 3.5 and 10.0 <br /> feet below grade surface (bgs). Based on a review of a Geotechnical Engineering Investigation <br /> Proposed Delta Farm Improvements dated April 26, 2019 prepared by Krazan &Associates Inc. <br /> (Krazan) Project No. 072-19013, groundwater was encountered at approximately 34.5 feet bgs. <br /> According to the California Department of Water Resources, Groundwater Information Center <br /> Interactive Map Spring and Fall 2018 depth to groundwater was reported between approximately <br /> 30 and 40 feet bgs. Groundwater appeared to flow in a northeasterly direction. The groundwater <br /> flow direction and the depth to shallow, unconfined groundwater, if present, would likely vary <br /> depending upon seasonal variations in rainfall and other hydrogeological features. Without the <br /> benefit of on-site groundwater monitoring wells surveyed to a datum, groundwater depth and flow <br /> direction beneath the site cannot be directly ascertained. <br /> 1.4.2 Potential Groundwater Contamination Issues <br /> Potential groundwater contamination can occur from a number of sources including historical <br /> petroleum hydrocarbon use, agricultural activities, dairies, septic systems, and storm water <br /> infiltration. As per EHD requirements nitrate as N and 1,2-dibromo-3-chloropropane (DBCP) have <br /> been included as part of the SSS discussion. Identifying potential groundwater contamination <br /> other than nitrates and DBCP is beyond the scope of work for this report. <br /> The presence of nitrates is not uncommon in shallow groundwater aquifers in San Joaquin County <br /> and other parts of the Central Valley. Nitrate in groundwater occurs as a result of the application <br /> of fertilizers, livestock waste, and untreated septic tank waste. Nitrate is mobile and often <br /> accumulates in the shallow groundwater zones. <br /> In the early 1900s, natural levels of nitrate in groundwater were measured in forty-three (43)wells <br /> throughout the Sacramento Valley by Kirk Bryan (1923). It was thought that groundwater at that <br /> time was close to "natural" conditions. Based on the work by Bryan, it is estimated that under <br /> "natural" conditions, groundwater concentration containing nitrate is no more than about 13.5 <br /> milligrams per liter(mg/L) nitrate (NO3) or (3 mg/L-N). Areas having 24.75 mg/L-NO3 (5.5 mg/L- <br /> N) or more, are those in which nitrate concentrations may be increasing (Hull, 1984). <br /> DBCP (dibromochloropropane) is a nematocide and soil fumigant for vegetables and grapes. It <br /> is thought to cause health problems consisting of kidney damage, liver damage, and cancer. The <br /> use of DBCP was discontinued in 1979. <br /> Based on a review of the State Water Resources Control Board online map, there were no nitrate <br /> impacted wells identified within 2,000 feet of the site. Based on the historical information, the <br /> Responsive■ Resourceful ■ Reliable 8 <br />
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