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ARCHIVED REPORTS_SITE CONCEPTUAL MODEL 2009
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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 /> A-Zone <br /> Groundwater Flow System <br /> The A-zone behaves as a semi-confined or leaky aquifer (Weiss, 1995a). Model calibrated <br /> hydraulic conductivity values for the A-zone ranged from 70ft/d (Geomatrix, 1996) to 125 ft/d <br /> (RUST, 1994). Using the same horizontal gradient and porosity as for the B-zone groundwater <br /> calculations, but the higher K, groundwater velocities on the order of 1 to 2 ft/d are estimated <br /> for the A-zone. Vertical gradients are typically downward from the A-zone to the Intermediate <br /> Aquifer zones (Appendix B). <br /> 4.4.2 Intermediate Aquifer <br /> The Intermediate Aquifer is composed of alluvial and fluvial sediments of Upper Turlock Lake <br /> Formation, and therefore high groundwater yields are expected. Water levels are similar to <br /> those in the Upper Aquifer, where a mound in the potentiometric surface exists in the vicinity of <br /> the WWTF lagoons, with groundwater flow northward, north of the lagoons, westward west of <br /> the lagoons towards pumping at Neenah Paper Company wells PW-6, PW-7, and PW-8, and <br /> southward, towards the Stanislaus River (Appendix F). <br /> The horizontal groundwater flow direction in the Intermediate Aquifer (based on measured <br /> water levels in January and July 2008 for wells penetrating both C1- and C2-zones) had a <br /> radial pattern, with a similar water level distribution to those observed for the Upper Aquifer <br /> Zone in January and July 2008 (Appendix F). This suggests that much of the recharge to the <br /> Intermediate Aquifer occurs near the WWTF and Neenah Paper Company lagoons. The <br /> steepest horizontal gradients are from the area of recharge (on the Neenah Paper Company <br /> property in January 2008) northward along Stockton Avenue, from TH-8 to M-8C1 <br /> (approximately 1,250 feet), where the water level difference was 5.94 feet, enhanced by <br /> drawdown from pumping at Nestle extraction well E-6. <br /> Strong downward gradients develop between the Intermediate Aquifer and Lower Aquifer, and <br /> are highest during the summer months. As shown in the hydrographs for the M-23 well cluster <br /> (Appendix B), the water level in M-23C was 5.18 feet higher than that measured in M-23D <br /> during the February 2007 monitoring event. This difference increased to 13.40 feet by the July <br /> event. The higher vertical gradients occur in the summer months presumably because of <br /> irrigation pumping and increased municipal pumping. The thickness of the Corcoran Clay at M- <br /> 23D is approximately 20 feet, based on the clay interval described as "moderately plastic and <br /> sticky" in the boring log, between 197 and 217 feet bgs. If the 13.40 feet head difference is <br /> applied across this 20 feet thick layer, the downward gradient is calculated as 13.4 feet/20 feet <br /> = 0.67 ft/ft. <br /> AMEC Geomatrix, Inc. <br /> I:\Doc_Safe\9000s\9837.005\4000 REGULATORY\SCM_01.30.09\1_text\SCM Report Final.doc 36 <br />
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