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2900 - Site Mitigation Program
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PR0526080
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Last modified
5/18/2020 8:53:58 AM
Creation date
5/18/2020 8:45:51 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0526080
PE
2965
FACILITY_ID
FA0017647
FACILITY_NAME
RIVERBANK WASTEWATER TREATMENT PLNT
STREET_NUMBER
23865
Direction
S
STREET_NAME
SANTA FE
STREET_TYPE
RD
City
RIVERBANK
Zip
95367
CURRENT_STATUS
01
SITE_LOCATION
23865 S SANTA FE RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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Ground water generally flows to the southwest towards the Stanislaus and San Joaquin <br /> rivers. <br /> The unconsolidated sediment aquifer is composed from oldest to youngest of the <br /> Laguna, Turlock Lake containing the Corcoran Clay, Riverbank and Modesto <br /> formations overlain by floodplain deposits of the Stanislaus River. Sediment was <br /> deposited in continental, lacustrine and marsh, and flood-basin environments. The <br /> Corcoran Clay of the Turlock Lake formation is an important aquitard developed in the <br /> San Joaquin Basin. In areas where the Corcoran Clay is not well developed, the Forebay <br /> aquifer (referenced in regional literature) is separated into a shallow and deep. In the <br /> areas east of HWY 99, the shallow aquifer is developed above confining clays of the <br /> Laguna and Mehrten formations and the Corcoran Clay is absent. <br /> f <br /> SITE SPECIFIC HYDROGEOLOGY (Existing Monitoring Network) <br /> The ground water monitoring network has been updated over the years. The original <br /> monitoring wells MW-1 through MW-5, depicted on Figure 2, have been monitored <br /> since 1995. A new monitoring well MW-6 was completed in 2000. This well was <br /> positioned to assist in determining background water quality. In order to support the <br /> expansion of the percolation ponds, four additional wells MW-7 through MW-9 were <br /> completed in July 2002. <br /> Boring logs (132 through B8) from the 2001 Anderson Geotechnical work on site and the <br /> monitoring well boring logs from the available monitoring wells (1\4W-6 through MW- <br /> 9) were used to complete hydrogeologic cross-sections for the site in 2003. These <br /> sections indicate significant changes in the character of the alluvial sedimentation in the <br /> area. River channel migration of gravel deposits associated with the Stanislaus River <br /> deposition. Coarser grained deposits have been encountered along the Southern extent <br /> of the site with finer grained silt deposits dominate the northern portion of the site. <br /> Boring logs from MW-6 through MW-9 and borings B-2 and B-8 depict the poorly <br /> sorted sands and gravel while the boring logs from B-3 through B-7 are finer grained <br /> with dominant clays and silts represented in the borehole logging. These findings were <br /> confirmed by the resent borehole drilling for monitoring wells MW-10 and MW-11 that <br /> are detailed below. <br /> Ground water elevations based on the April round of water quality ranges from 79.35 to <br /> 84.31 ft. Ground water appears to be mounding beneath the site and flows <br /> predominantly toward the Stanislaus River. Local ground water flow is influenced by <br /> mounding beneath the ponds. <br /> City of Riverbank Wastewater Treatment Plant Monitoring Well Installation May 2006 <br /> DE Project No.:109-06 4 Rev.0 <br />
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