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ARCHIVED REPORTS_SITE CONCEPTUAL MODEL 2009
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PR0009051
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ARCHIVED REPORTS_SITE CONCEPTUAL MODEL 2009
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Last modified
2/5/2020 2:25:32 PM
Creation date
2/5/2020 10:56:03 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
SITE CONCEPTUAL MODEL 2009
RECORD_ID
PR0009051
PE
2960
FACILITY_ID
FA0000649
FACILITY_NAME
FORMER NESTLE USA INC FACILITY
STREET_NUMBER
230
STREET_NAME
INDUSTRIAL
STREET_TYPE
DR
City
RIPON
Zip
95366
APN
25938001
CURRENT_STATUS
01
SITE_LOCATION
230 INDUSTRIAL DR
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
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amec_"_" <br /> ; <br /> • The WWTF lagoons are situated at a higher water elevation than the adjacent <br /> Stanislaus River, and therefore, some water from the lagoons likely discharges to <br /> the Stanislaus River. <br /> 4.3 RECHARGE AND PUMPING <br /> Groundwater beneath the Study Area is and has been strongly controlled by recharge in the <br /> vicinity of the WWTF and Stanislaus River, and pumping to the north for industrial and <br /> municipal supply, and to the south, for irrigation. Additional information on groundwater <br /> recharge and pumping is provided below. <br /> 4.3.1 Influence of River Stage on Water Levels <br /> Depending on river stage, the reach of the Stanislaus River that crosses the Study Area can <br /> either recharge groundwater or remove groundwater from the aquifer system. When the river <br /> is strongly gaining or losing, it may function as a hydraulic barrier for shallow groundwater <br /> flow, but less so during transitional periods, when the river is not gaining or losing substantial <br /> amounts of groundwater. The Stanislaus River has been characterized as a gaining stream in <br /> the spring of 1964 along the reach encompassing Ripon (DWR, 1965, cited in ECO:LOGIC, <br /> 2005a and Lawrence and Associates, 1991). In general, the Stanislaus River was a gaining <br /> stream prior to 1975, until increased pumping to the north, towards Stockton, lowered the <br /> water table and caused the Stanislaus River to discharge to groundwater, although near the <br /> City of Ripon WWTF lagoons, the Stanislaus River may have been gaining due to local <br /> recharge at the lagoons causing higher groundwater levels. <br /> On September 11, 2006, the water level in the Stanislaus River was surveyed at <br /> approximately 1:30 PM at the location show in Figure 12 (river survey station), and was <br /> reported as 40.06 feet above North American Vertical Datum 1988 (NAVD 88; <br /> http://cdec.water.ca.gov/queryTools.html; Appendix E). This location is approximately 500 feet <br /> east-northeast of Intermediate Aquifer monitoring wells M-30C1 and M-30C2, and <br /> approximately 750 feet south southeast of Neenah Paper Upper Aquifer monitoring well TH-9. <br /> Hourly river stage data is recorded by the Department of Water Resources at a gauging <br /> station located on the Stanislaus River where it is crossed by State Highway 99. The water <br /> levels measured at 1 PM and 2 PM on September 11, 2006 were 40.47 and 40.65 feet above <br /> the DWR datum, respectively. Assuming the river stage at 1:30 PM was the average of these <br /> two values (40.56 feet), an offset of-0.50 feet, when applied to the DWR data, can be used to <br /> estimate historical river stage at the survey location relative to NAVD 88, assuming that an <br /> incremental rise in river stage at the DWR station translates to the same rise at the river <br /> survey station. <br /> Figure 12 includes a plot of estimated river stage at the survey station and water levels in the <br /> nearest monitoring wells (M-30C1, M-30C2, and TH-9). In general, groundwater elevations in <br /> AMEC Geomatrix, Inc. <br /> I:\Doc_Safe\9000s\9837.005\4000 REGULATORY\SCM_01.30.09\1_text\SCM Report Final.doc 28 <br />
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