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ARCHIVED REPORTS_2011 REVISED FEASABILITY STUDY
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ARCHIVED REPORTS_2011 REVISED FEASABILITY STUDY
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Last modified
2/5/2020 2:26:35 PM
Creation date
2/5/2020 10:37:50 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2011 REVISED FEASABILITY STUDY
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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Nestle USA, Inc.—Ripon, CA January 28, 2011 <br /> 2011 Revised Feasibility Study <br /> 9.2.2.1 Effectiveness <br /> There is a general consensus that the barrier must be installed to terminate in a <br /> low permeability soil layer to prevent vertical migration of groundwater (and <br /> COCs) from within the contained area, to beneath and outside of the contained <br /> area. It is important to ensure that no conduit wells penetrating the low <br /> permeability soil layer exist in the vicinity of the containment area, which could <br /> prevent sufficient containment of CDCs. However, if surface recharge over the <br /> containment area is minimal, due to climatic factors or engineering controls, and <br /> the containment area is completely encapsulated by low permeability walls, <br /> horizontal groundwater flow can be diverted around the source area with minimal <br /> vertical movement of groundwater within the contained area. Therefore, <br /> impermeable barriers could be effective for controlling the migration of COCs in <br /> groundwater and therefore this technology is retained for further evaluation. <br /> 9.2.2.2 Implementability <br /> Physical containment of groundwater using impermeable barriers is generally <br /> limited to shallower depths (i.e. <100 feet bgs) and smaller areas than those <br /> under discussion in this Revised FS. Furthermore, access issues and utility <br /> conflicts can be serious obstacles to the implementation of this technology. For <br /> these reasons, an impermeable barrier is considered to be implementable if the <br /> containment area is confined to the Site, and to depths of less than 100 feet bgs, <br /> and if access issues (i.e. sufficient clearance between buildings, roadways, and <br /> other obstacles) and utility conflicts can be cleared. Because the area of higher <br /> TCE concentrations (i.e. above 1,000 µg/L) is confined to the northern portion of <br /> the 230 Industrial Avenue parcel, and to depths of less than 60 feet bgs, an <br /> impermeable barrier around this area would likely be implementable. <br /> 9.2.2.3 Relative Cost <br /> The relative cost of an impermeable barrier surrounding the area of higher TCE <br /> concentrations beneath 230 Industrial Avenue (approximately 1,000 linear feet) <br /> to an average depth of 70 feet bgs would be classified as medium (< <br /> $2,500,000). <br /> 9.2.2.4 Conclusion <br /> The installation of an impermeable barrier has been retained for further <br /> evaluation for the Upper Aquifer beneath the Site, but will not be considered <br /> further for the Intermediate and Lower Aquifers, or for other off-site areas due to <br /> the implementability limitations discussed in 9.2.2.2. <br /> 9.2.3 Permeable Reactive Barriers <br /> PRBs, also known as "treatment walls", are generally installed across the flow <br /> path of impacted groundwater, where COCs are removed by reaction with <br /> amendments contained within the PRB. PRBs, like impermeable barriers, can be <br /> designed to limit the mass discharge from a source zone. However, unlike <br /> impermeable barriers, PRBs can also be effective technologies far downgradient <br /> of the source zone to contain the leading edge of a dissolved COC plume, <br /> 28 <br />
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