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CORRESPONDENCE_2006-2009
Environmental Health - Public
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CORRESPONDENCE_2006-2009
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Entry Properties
Last modified
10/3/2025 2:07:00 PM
Creation date
7/3/2020 10:50:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
2006-2009
RECORD_ID
PR0440005
PE
4433 - LANDFILL DISPOSAL SITE
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
201060013, 5
CURRENT_STATUS
Active, billable
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\cfield
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2006-2009.tif
Site Address
9999 AUSTIN RD MANTECA 95336
Tags
EHD - Public
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Draft Cleanup and Abateme rder No. R5-2008- - 3 - <br /> Forward <br /> 3 - <br /> Forward Landfill <br /> San Joaquin County <br /> GROUNDWATER IMPACTS FROM THE AUSTIN ROAD LANDFILL <br /> 11.Significant volatile organic compound (VOC) groundwater impacts including, but not <br /> limited to, 1,1-dichloroethane, cis-1,2-d ichloroethylene, tetrachloroethylene, and <br /> trichloroethylene are associated with waste discharged to the Austin Road Landfill. <br /> Impacts were initially detected in 1989. By 1991, evaluation monitoring determined <br /> that chlorinated hydrocarbon impacts extended as far as 1,000 feet down-gradient <br /> from the Austin Road Landfill. A corrective action plan, consisting of a phased <br /> approach to remediate the plume, was approved in 1991, but by 1998 it was <br /> apparent that the initial corrective actions had failed to remediate the groundwater <br /> impacts because detections of 1,1-dichloroethane, cis-1,2-dichloroethylene, <br /> tetrachloroethylene, and trichloroethylene were still detected in downgradient <br /> monitoring wells. <br /> 12.The Discharger stated in its 2002 Joint Technical Document that "the VOC polluted <br /> groundwater extends approximately 4,000 feet northeast from the northern border of <br /> the existing Austin Road Landfill. The plume appears to have migrated to a lower <br /> depth at the leading edge of the plume. The primary contaminants of concern are <br /> Tetrachloroethylene and Trichloroethene, with concentrations levels up to 59 and 48 <br /> micrograms per liter, respectively. The highest VOC concentrations are present <br /> within a sand layer that extends beneath the site between approximately 80 to 104 <br /> feet below ground surface." <br /> 13.There are no monitoring wells installed at the downgradient edge (vertically or <br /> laterally) of the plume. <br /> 14.In 2003, the Central Valley Water Board adopted WDRs Orders R5-2003-0049 and <br /> R5-2003-0080 to implement revised corrective actions to remediate groundwater <br /> impacts. The Discharger extracts groundwater from two wells adjacent to the <br /> northern boundary of the Austin Road Landfill, and then runs it through an air <br /> sparger prior to discharging the effluent to an infiltration area. From 1 October <br /> through 31 December 2007, the two wells extracted at an average rate of 209 <br /> gallons per minute or 301,000 gallons per day. Based on the continuing detections in <br /> the downgradient wells, the current extraction rate is insufficient to control the plume <br /> and remediate the release of waste from the landfill. <br /> 15.The Austin Road Landfill corrective action monitoring system includes monitoring <br /> wells AMW 13 and AMW 14. These wells are approximately 1,600 feet directly <br /> downgradient of the two extraction wells EW-1 and EW-2. During the first Quarter <br /> 2008 sampling event the following VOCs concentrations were detected in these <br /> wells: <br />
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