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ARCHIVED REPORTS_2017
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ARCHIVED REPORTS_2017
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Last modified
7/17/2020 3:53:46 PM
Creation date
7/3/2020 10:59:30 AM
Metadata
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Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2017
RECORD_ID
PR0440005
PE
4433
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106001-3, 5
CURRENT_STATUS
01
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_.tif
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2017 Corrective Action Evaluation Report-Austin Road Unit <br /> Forward Landfill <br /> Forward will begin installing _ more perimeter monitoring probes around the Austin Unit in <br /> August 2017 to evaluate the effectiveness of the existing LFG extraction system. <br /> 6.0 COMPARISON OF CURRENT TO MODELED GROUNDWATER QUALITY <br /> The August 8, 2001 Revised Engineering Feasibility Study for Austin Rood Landfill (hereafter, <br /> EFS) presented projected isoconcentration contour maps for select VOCs in groundwater based <br /> on computer modeling simulations. The four VOCs that were modeled were PCE, <br /> trichloroethene (TCE), cis-1,2-dichloroethene (cis-1,2-DCE), and vinyl chloride. These <br /> simulations projected how the concentrations of individual VOCs could potentially change <br /> following the initiation of recharge within the artificial basin. The EFS presented projected <br /> maps corresponding to each year following the initiation of recharge. <br /> In past Annual Corrective Action Evaluation Reports, these projected isoconcentration maps <br /> were compared to maps based on contemporary data collected from the same monitoring <br /> wells utilized in modeling. However, the EFS simulations projected that none of the modeled <br /> VOCs would be detected above 1 µg/L by 2012 after nine years of recharge from the recharge <br /> basin. Accordingly, there are no projected isoconcentration maps available for comparison to <br /> current results. <br /> Consistent with past Annual Corrective Action Evaluation Reports, isoconcentration maps for <br /> the four modeled VOCs are presented in Appendix D using the second quarter monitoring <br /> results. The maps in Appendix D utilize a contour interval of 10 µg/L and do not include values <br /> less than 1 µg/L. <br /> Figure D-1 presents PCE results in ARU groundwater monitoring wells from May 2017. The May <br /> 2017 results indicate that PCE concentrations exceed 1 µg/L at CAP monitoring wells AMW-1 <br /> and AMW-13; detection monitoring wells AMW-6 and AMW-12; domestic supply wells 7898-A <br /> and 8106-A; and in EMP/CAP wells AMW-13, AMW-13B, AMW-186, AMW-19, AMW-19BR, <br /> AMW-21, AMW-21S, AMW-22, AMW-22S, AMW-24R, AMW-26R, AMW-29, AMW-31, and <br /> AMW-31S. The highest concentration of PCE was measured at 23 µg/L in well AMW-22S. <br /> Figure D-2 presents TCE results in ARU groundwater monitoring wells from May 2017. The May <br /> 2017 results indicate that TCE concentrations exceed 1 µg/L at CAP monitoring wells AMW-1 <br /> and AMW-13; domestic supply well 8106-A; and in EMP/CAP wells AMW-21, AMW-22, AMW- <br /> 22S, AMW-26R, and AMW-29. The highest concentration of TCE was measured at 20 µg/L in <br /> well AMW-22S. <br /> Project No 5017.1030 ( 2017 Corrective Action Evaluation Report-Austin Road Unit 5 <br /> Forward Landfill <br />
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