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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�9 <br /> hydraulic depression caused by pumping at 519 Stockton Avenue (extraction well E-6) and <br /> toward well MW-3 pumping, to the northwest. The anthropogenic influence on groundwater <br /> flow is apparent from Figure 16. <br /> January 2006 (Figure 17): At this time, the Stanislaus River water level was near flood stage, <br /> reaching a maximum elevation of approximately 54.29 msl on January 6, 2006. The water <br /> level was measured in nearby well TH-9 on January 23, 2006, and was approximately <br /> 49.41 feet msl; the river stage had subsided to an elevation of 45.50 feet msl by this time. <br /> Groundwater contours shown in Figure 17 indicate that the groundwater flow direction (based <br /> on the hydraulic gradient estimated from water levels in the Intermediate Aquifer monitoring <br /> wells) was northward, from the Stanislaus River beneath the WWTF lagoons, towards <br /> pumping wells (E-6, MW-3 and MW-10). No groundwater mound is evident north of the <br /> WWTF. This scenario is consistent with a large input of river water to the groundwater system, <br /> causing groundwater to flow northward beneath the lagoons, which is opposite to the flow <br /> direction inferred from the July 2006 water levels. Also, there was likely no irrigation pumping <br /> south of the Stanislaus River during this time. The groundwater flow system between the <br /> WWTF lagoons and the Stanislaus River is dynamic system with systematic gradient reversals <br /> due to high river stage that could greatly curtail net groundwater migration over time in this <br /> area. <br /> July 2004 (Figure 18): There were no monitoring wells near the Stanislaus River at this time, <br /> so the flow direction between the WWTF lagoons and the Stanislaus River cannot be <br /> evaluated. However, groundwater flow was generally to the northwest beneath the Study Area <br /> during this time, based on the interpreted Intermediate Aquifer hydraulic gradient shown in <br /> Figure 18. <br /> January 2004 (Figure 19): There were no monitoring wells near the Stanislaus River at this <br /> time, so the flow direction between the WWTF lagoons and the Stanislaus River cannot be <br /> evaluated. However, groundwater flow was generally to the northwest beneath the Study Area <br /> during this time, with an apparent hydraulic mound near the WWTF and Neenah Paper <br /> discharge areas. The water level in well M-1 7C1 is approximately 0.26 feet higher than that <br /> measured for well M-23C1, and similar to well M-20C1, implying a southwesterly flow beneath <br /> the WWTF lagoons. The cause for the apparent high water level within the Intermediate <br /> Aquifer near M-1 7C1 is unknown. <br /> April 1997(Figure 20): Monitoring wells near the Stanislaus River had not yet been installed <br /> at this time, so the flow direction between the WWTF lagoons and the Stanislaus River was <br /> not evaluated. However, the prevailing direction of the hydraulic gradient in the Intermediate <br /> Aquifer was generally to the north and northeast beneath the Study Area during this time, with <br /> AMEC Geomatrix, Inc. <br /> I:\Doc_Safe\9000s\9837.005\4000 REGULATORY\SCM_01.30.09\1_text\SCM Report Final.doc 41 <br />
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