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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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Impact Report Pa <br /> Draft Environmental Imp e IV.F-12 p g <br /> Forward Inc. Landfill Expansion <br /> Groundwater quality at the Forward Landfill is summarized in the quarterly and annual <br /> monitoring per the RWQCB Cleanup and Abatement Order R5-2008-0714. Reports are <br /> submitted to the RWQCB and DTSC and can be viewed by the public on the California <br /> ' Geotracker system (http://geotracker.swrcb.ca.gov/). The current groundwater contamination <br /> from the Forward operations exhibits a large but diffuse plume of VOCs, specifically the key <br /> compounds of concern tetrachloroethene (PCE);trichloroethene (TCE); cis-1,2-dichloroethene <br /> (DCE);and vinyl chloride (VC). Within the plume, PCE and TCE have been the primary <br /> chemicals with concentrations above regulatory standards since monitoring was initiated in <br /> 1977 at the Forward landfill unit. This plume is shown on Figure IV.F-3. <br /> ! .�. The groundwater-monitoring system at the Forward Landfill is designed to detect the presence <br /> of contaminants in groundwater by analyzing groundwater chemistry at point-of-compliance <br /> wells. The monitoring system currently consists of 36 groundwater-monitoring wells, which <br /> G meet the requirements of the landfill's Detection Monitoring (DMP) for groundwater <br /> monitoring and the Corrective Action Program (CAP)for groundwater contamination. <br /> Currently VOC's are detected at low concentrations in selected well monitoring the Forward <br /> and Austin landfill units (disused in detail in water quality section below). Until their <br /> abandonment in 1993, VOCs were most commonly detected in monitoring wells MW-5A and <br /> MW-5B, near the southern border of WMU B (Figure IV.F-1). Since then, VOCs have been most <br /> commonly detected in the northeast corner of the Forward Landfill,in the main entrance <br /> facilities area. <br /> i <br /> In September 2000, the RWQCB requested that Forward assess the source and potential impacts <br /> of low-level VOC concentrations in the groundwater adjacent to the landfill. The assessment <br /> was performed by GeoLogic Associates (GLA)and summarized in the Low-Level VOC <br /> Detections in Monitoring Wells letter report (February 2001). The report found that, excluding <br /> acetone and methyl chloride (common laboratory contaminants), VOCs were detected in <br /> samples from 8 monitoring wells during 1999 and 2000. VOCs were most commonly detected <br /> at trace levels and in samples obtained from wells MW-13, MW-14, and MW-21, in the <br /> Fn northeastern corner of the existing Forward Landfill. The most frequently detected VOCs in <br /> groundwater include:benzene, cis-1,2-dichloroethene,tetrachloroethene, toluene, 1,1- <br /> dichloroethane, and 1,1,1-trichloroethane. The concentrations at which these analytes were <br /> �r <br /> detected did not exceed state or federal drinking water standards. <br /> Based on a review of the existing data, the GLA report finds that several combined factors <br /> indicate that landfill gas production in WMU B is a significant contributing source of VOCs in <br /> the groundwater at the existing Forward Landfill. These factors include: the locus of VOC <br /> detections near unlined landfill cell WMU B, the erratic pattern of low VOC detections,the <br /> relative long list of VOCs that are detected, the detection of VOCs in both upgradient and <br /> f downgradient monitoring wells, and the consistency of inorganic water quality in both <br /> upgradient and downgradient wells near the site. GLA concluded that the potential impacts <br /> associated with the VOCs in the groundwater appear to be small because the concentrations of <br /> FVOCs are well below drinking water standards and the absence of VOCs at offsite monitoring <br /> locations indicate that VOCs degrade or disperse within a relatively short distance of the <br /> landfill boundary. <br /> At the Austin Road Landfill unit where a Solid Waste Quality Assessment Test in 1989 found a <br /> significant groundwater quality impacts as a result form the unlined nature of the(Class III) <br /> landfill, the subsequent remediation at the north side of the landfill has resulted in insignificant <br /> increases in the VOC contamination, although concentrations are still above regulatory limits. <br /> This has been documented in the various monitoring reports and additional corrective action <br /> studies completed up through 2008. <br />
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