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2900 - Site Mitigation Program
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PR0501477
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Last modified
11/20/2024 9:09:40 AM
Creation date
1/24/2020 2:21:48 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0501477
PE
2965
FACILITY_ID
FA0005116
FACILITY_NAME
SMS BRINERS INC
STREET_NUMBER
17750
Direction
E
STREET_NAME
STATE ROUTE 4
City
STOCKTON
Zip
95206
APN
18314010
CURRENT_STATUS
01
SITE_LOCATION
17750 E HWY 4
P_LOCATION
99
QC Status
Approved
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2.0 HYDROGEOLOGIC CHARACTERIZATION <br /> The regional geologic setting in the vicinity of the SMS Briners facility is typical of the <br /> northern San Joaquin Valley and was discussed in the Interim Ground-Water Monitoring <br /> Network and Program, SMS Briners, Stockton, California (LSCE, 1985),the Interim <br /> ` Monitoring Report and Work Plan for Operational Revisions and Verification Monitoring <br /> (LSCE, 1989), the Monitoring Program Status Update Report and Work Plan for Source <br /> Control, Operational Revisions and Ongoing Monitoring(LSCE, 1990), and the <br /> Underground Injection Control Program, Permit Application for a CLASS I Injection Well <br /> (LSCE, 1991). These documents can be referenced to obtain a detailed discussion of the <br /> regional geologic setting. Informal,descriptive subdivisions of Quaternary alluvium,based on <br /> local lithostratigraphic characteristics, were presented in the Corrective Action Program <br /> (LSCE, 1992), and hydrostratigraphic designations were given. <br /> 2.1 Shallow Zone Groundwater Conditions <br /> Groundwater levels in shallow zone monitoring wells have fluctuated between depths of <br /> about 100 to 140 feet since 1992. Water level elevations in the shallow and deep zones, as <br /> measured in well clusters MW3A/313 and MW4A/4B,typically differ by less than a foot. <br /> Contours of equal groundwater elevations prepared for the shallow zone from August 1990 <br /> to present generally indicate that flow in the immediate vicinity of the facility predominantly <br /> occurs to the northwest (west-northwest to north-northwest)to northeast depending on the <br /> operation of local extraction wells. Since Spring 2002 when discharge from well P5 was <br /> discontinued,the general flow pattern in the shallow zone has been primarily to the <br /> northwest as shown on Figure 2-1 (LSCE, 2003a, 2004a, 2005a). <br /> r. <br /> Historical groundwater flow to the northeast, east, and east-southeast directions were <br /> primarily due to the operation of MW 1 as an extraction well for remedial purposes, Well A, <br /> and P5 (prior to Spring 2002). Flow to the northeast has most frequently been observed from <br /> 1996 to Spring 2001 after MWl started operating as an extraction well (LSCE, 2001a). Prior <br /> to 1996 the direction of flow exhibited a seasonal pattern, west and northwest during the <br /> winter and spring months (typically referred to as the wet season) and an east to northeast <br /> direction during the summer and early fall months (typically referred to as the dry season) as <br /> a result of seasonal pumping (LSCE, 1992 and 1995). Northwesterly gradients are typically <br /> on the order of 0.001 ft/ft and have ranged from about 0.0004 to 0.002 in the last three years. <br /> r <br /> 2.2 Deep Zone Groundwater Conditions <br /> Groundwater levels in the deep zone have fluctuated between depths of 100 to 125 feet since <br /> 1992. Contours of equal groundwater elevations prepared for the deep zone from March <br /> 1985 to present show that, in absence of obvious pumping impacts, the flow direction in the <br /> immediate vicinity of the facility ranges from westerly to northerly. However, stable or <br /> © LUHOORFF & SCALMANINI <br /> CONSULTING ENGINEERS 2 <br />
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