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ARCHIVED REPORTS_2009_14
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ARCHIVED REPORTS_2009_14
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Last modified
7/17/2020 3:53:32 PM
Creation date
7/3/2020 10:54:48 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2009_14
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
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2009_14.tif
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EHD - Public
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New Historical Intrawell Maximum Values <br /> During the third quarter 2009 monitoring event, the arsenic concentration measured in <br /> well MW-16 (0.0037 mg/L)nominally exceeded the previous maximum value of 0.0036 <br /> mg/L. No other historical Intrawell maximum values were exceeded during the current <br /> monitoring period. <br /> Concentration Limit Thresholds <br /> Data obtained during the third quarter 2009 monitoring period were compared to <br /> concentration limits (CLs) as specified in the RPCMP for the Forward Landfill. Given <br /> the fact that the original CL have never been updated and were calculated using data <br /> collected prior to 1994, CLs were recalculated using data collected between February <br /> 2003 and August 2008. CLs were calculated by Herst&Associates using upper <br /> tolerance limits and are included in Appendix D. Excluding suspected field/laboratory <br /> contaminants, only one CL was exceeded for arsenic in the sample collected from well <br /> MW-19 during the current monitoring period. In accordance with the RPCMP <br /> guidelines, arsenic,bicarbonate, hexavalent chromium, nitrate as nitrogen, and sulfate, <br /> are not considered impact constituents, and therefore,retesting for arsenic is not required. <br /> 2.1.5 Vadose Zone Monitoring <br /> The current vadose-zone monitoring network at the Forward Unit consists of 17 <br /> lysimeters. The lysimeter locations are shown on Figure 2-1. Each accessible lysimeter <br /> was inspected and vacuums were reset to approximately—10 to—25 inches of mercury on <br /> August 13, 2009. On September 10, 2009, the lysimeters were again checked and <br /> positive pressure was applied to evacuate the accumulated sample. As recorded in the <br /> field notes for lysimeters (Appendix C) and summarized on Table 2-5, lysimeters W-2 <br /> and LY-BGl had a sufficient volume of soil-pore liquid for sample collection. However, <br /> due to the limited sample volumes, lysimeter samples were only analyzed for select <br /> inorganic constituents and/or VOCs. As shown in Table 2-6, one VOC (bromoform)was <br /> detected above the PQL in the lysimeter samples collected during the third quarter 2009 <br /> monitoring period. <br /> 2.1.6 Surface Water Monitoring <br /> Site run-on and run-off control facilities are designed to effectively channel surface water <br /> to site stormwater/sedimentation ponds. According to the Operations Manager,no <br /> surface water was discharged from the facility during the reporting period. During the <br /> third quarter 2009, surface-water monitoring stations FSW-1 and FSW-2 were sampled <br /> on August 10, 2009. Table 2-4 summarizes the current analytical results of surface water <br /> samples collected at the Forward Unit. No VOCs were detected in the surface water <br /> samples collected from the Forward Unit during the third quarter 2009 monitoring period. <br /> D:\2009_001" _3W.aoc 6 Geologic Associates <br />
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