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ARCHIVED REPORTS_2008_22
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ARCHIVED REPORTS_2008_22
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Last modified
7/18/2020 12:56:38 AM
Creation date
7/3/2020 10:53:54 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2008_22
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
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2008_22.tif
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EHD - Public
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Concentration Limit Thresholds <br /> Data obtained during the first quarter 2008 monitoring period were compared to <br /> concentration limits(CLs) as specified in the RPCMP for the Forward Landfill. CLs <br /> were calculated by Herst&Associates and are included in Appendix D. Table 2-4 <br /> summarizes CLs that were exceeded in samples collected from groundwater monitoring <br /> wells during the first quarter 2008. As summarized in this table, CLs were exceeded for <br /> wells MW-lA, MW-2A, MW-3, MW-10, -13,MW-14,MW-15, MW-16, <br /> MW-17, MW-18, and MW-19. In accordance with the RPCMP, wells with CL <br /> exceedances (other than arsenic, bicarbonate, hexavalent chromium, nitrate as nitrogen, <br /> and sulfate, which the RPCMP do not consider impact constituents)will be resampled in <br /> May during the second quarter 2008 sampling event and a second independent sample <br /> will be collected in June 2008. The results of the retesting events will be submitted to <br /> DTSC and RWQCB under separate cover. <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—5 to—25 inches of mercury on <br /> February 6 and 7, 2008. On March 18, 2008,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 E-2, <br /> W-2, LY-A, and LY-BG1 had a sufficient volume of soil-pore liquid for sample <br /> collection. However,due to the limited sample volumes,lysimeter samples were only <br /> analyzed for select general chemistry constituents and/or VOCs. As shown in Table 2-6, <br /> a total of two VOCs (both above the PQL), were measured in the lysimeter samples <br /> collected during the first quarter 2008 monitoring period. However, the concentration of <br /> t-butyl alcohol is a suspected field/laboratory contaminant since a similar concentration <br /> was also measured in the QA/QC field blank. <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 quarter. During the <br /> first quarter 2008 monitoring period, surface-water monitoring stations FSW-1 and <br /> FSW-2 were sampled on February 4, 2008. Table 2-8 summarizes the current analytical <br /> results for surface water samples collected at the Forward Unit. No VOCs were detected <br /> in the samples collected from the surface water stations during the first quarter 2008 <br /> monitoring period. A comparison of upgradient(FSW-2)to downgradient(FSW-1) <br /> surface water samples indicates generally similar concentrations suggesting that the <br /> landfill operations are not impacting surface water quality. <br /> D:U007 0043XFA_IQ08.doc <br /> 6 Geologic Associates <br />
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