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ARCHIVED REPORTS_2013_7
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ARCHIVED REPORTS_2013_7
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Last modified
7/17/2020 3:53:44 PM
Creation date
7/3/2020 10:57:24 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2013_7
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_2013_7.tif
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EHD - Public
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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,there <br /> were no discharges to surface water during the reporting quarter. Samples were collected <br /> from surface water monitoring stations FSW-1 (downstream) and FSW-2 (upstream) on <br /> March 8, 2013 for the first quarter monitoring period. Table 2-7 summarizes the current <br /> analytical results of surface water samples collected at the Forward Unit. As shown on <br /> Table 2-7, no VOCs were detected in either sample. Analytical results for the surface <br /> water samples are similar, suggesting that landfill operations are not impacting surface <br /> water quality. <br /> 2.2 CONSTITUENTS OF CONCERN <br /> During the first quarter 2013 monitoring period, groundwater and surface water samples <br /> from the Forward Unit were analyzed for the five-year COCs listed in RWQCB Order <br /> No. R5-2003-0049 and are summarized in Tables 2-2 and 2-7. As shown in Tables 2-2 <br /> and 2-7, with the exception of one chlorinated herbicide (dicamba)that was measured at <br /> trace concentrations in both surface water samples, no organic COCs were detected in the <br /> groundwater and surface water samples. Since similar concentrations of dicamba were <br /> measured in the upstream and downstream samples, it is believed that the source of the <br /> herbicide is from agricultural activities upsteam of the landfill. <br /> Several inorganic COCs were detected in both up-gradient and down-gradient wells and <br /> surface water stations. The similarity in the concentrations in both up-gradient and <br /> down-gradient wells and surface water stations suggest that the inorganic COCs are <br /> naturally occurring. A comparison of inorganic COCs to Federal and State maximum <br /> contaminant levels (MCLs) for drinking water, indicate that the MCL for antimony <br /> (0.006 mg/L) was exceeded in all groundwater monitoring wells and up-gradient surface <br /> water station FSW-2, and the MCL for nickel (0.1 mg/L)was exceeded at groundwater <br /> monitoring wells MW-3 and MW-15. <br /> 2.3 SUMMARY <br /> Groundwater quality conditions beneath the Forward Unit during the first quarter 2013 <br /> monitoring period are generally similar to those observed in previous monitoring periods. <br /> During the first quarter 2013 monitoring period, non-statistical exceedances for VOCs <br /> were identified at well MW-2A and MW-10. However, trend analyses indicate that there <br /> were no statistically significant increasing temporal trends calculated for the VOCs <br /> detected in wells MW-2A and MW-10. For the routine inorganic monitoring parameters, <br /> CLs were exceeded for constituent concentrations in wells MW-2A, MW-13, MW-14, <br /> MW-15, and MW-23R. With the exception of nitrate-N concentrations in well MW-14 <br /> and sulfate concentrations in well MW-15, trend analyses indicate that there were no <br /> statistically significant increasing trends calculated for the CL exceedances during the <br /> current monitoring period. Previously submitted NRDs for these common inorganic <br /> C:\2013-0021\FA_1Q13.doc 7 Geo-Logic Associates <br />
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