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SU0007861
Environmental Health - Public
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SU0007861
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Entry Properties
Last modified
1/6/2020 11:37:03 AM
Creation date
9/4/2019 10:03:24 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0007861
PE
2675
FACILITY_NAME
PA-0800105
STREET_NUMBER
9999
Direction
S
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
APN
20106003
ENTERED_DATE
8/11/2009 12:00:00 AM
SITE_LOCATION
9999 S AUSTIN RD
RECEIVED_DATE
7/24/2009 12:00:00 AM
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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FilePath
\MIGRATIONS\A\AUSTIN\9999\EIR PA-0800105\NOP.PDF
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EHD - Public
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r <br /> Draft Environmental Impact Repot Page IV.F-15 <br /> Forward Inc. Landfill Expansion <br /> so as to achieve concentration meeting drinking water standards or to treat the water through <br /> activated carbon filters to remove the VOCs. This plan is currently under review by the RWQCB. <br /> It is possible that the VOC impacts in groundwater at the existing Austin Road Landfill are <br /> attributable to landfill gas. VOC concentrations have been trending downward recently, and <br /> leachate analyses from the existing Austin Road Landfill indicate no significant VOCs. VOCs <br /> are detected,however, in landfill gas samples. Forward is currently assessing landfill gas and <br /> groundwater issues at the existing Austin Road Landfill and, as required by the RWQCB,the <br /> last revised Engineering Feasibility Study(EFS) has been prepared for the Corrective Action <br /> Program (HA/AEE, 2001)is currently being updated per the recent 2008-0712 Water Board <br /> Order. <br /> The revised EFS involved review of available data and preparation of a detailed groundwater r <br /> flow and transport model to assess the most efficient means of controlling groundwater impacts <br /> at the existing Austin Road Landfill. The model incorporated hydrogeologic and <br /> hydrochemical information that were collected in previous investigations of the landfill, and <br /> included data collected in aquifer pumping tests that were completed at the site. <br /> • Based on the groundwater modeling that was completed for the EFS, it was concluded <br /> that the most effective response to groundwater impacts at the site would include the <br /> following: Enhanced landfill gas extraction. <br /> • Continued groundwater pumping from the two groundwater extraction wells along the <br /> north side of the facility. <br /> • Continued groundwater treatment using the facility's air-stripper unit. <br /> • Artificial recharge of the aquifer by treated groundwater <br /> Artificial recharge of the aquifer by treated groundwater was recommended over increased <br /> remedial pumping because the re-introduction of pumped water to the aquifer is expected to <br /> minimize the impact on an already overdrafted aquifer and would avoid increased energy <br /> consumption associated with increased pumping. In combination with plans for an enhanced <br /> landfill gas collection system, re-introduction of treated water to the aquifer is expected to <br /> reduce existing VOC impacts below Maximum Contaminant Levels(MCLS) (drinking water <br /> standards)within five years and below the Water Standard (1 part per billion) within nine <br /> years. <br /> Project Area Groundwater Quality <br /> The source of the groundwater contamination at the Forward and Austin landfill units is fairly <br /> well understood,being attributed first and foremost to contamination originating from <br /> chemicals are leached out over time form the refuse that accumulated at the landfills. In the case <br /> of the unlined Forward unit, the leachate generate had a more direct path to the subsurface <br /> environment and groundwater, not initially having the protective leachage collection system <br /> that the Forward unit did. The most prevalent and persistent of these chemicals of concern are <br /> the chlorinated solvents (referred to as VOCs), common to hundreds of consumer products. <br /> The VOCs can be retained in solid state media (by adhering to clay particles as they move down <br /> in the unsaturated zone), in soluble form(as a dissolved fraction in surface water or <br /> groundwater),or in the form of a gas (circulating in the flux of the other common landfill gases, <br /> methane and carbon dioxide). The VOCs can transform easily from the solid, soluble, or gas <br /> form depending on the circumstances. Thus, the origin of the VOCs in the water that creates <br /> the landfill leachate is likely the result of a long process of household hazardous waste <br /> containing common solvents such as PCE and TCE leaching into the environment. <br />
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