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ARCHIVED REPORTS_2010_13
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ARCHIVED REPORTS_2010_13
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Last modified
7/17/2020 3:53:35 PM
Creation date
7/3/2020 10:55:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2010_13
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_2010_13.tif
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EHD - Public
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Concentration Limit Thresholds <br /> Data obtained during the first quarter 2010 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 2010. As summarized in this table, CLs were exceeded for <br /> wells MW-10, MW-14,MW-19, and MW-22. In accordance with the RPCMP, wells <br /> with CL exceedances of impact constituents (as defined in Table 5-3 of the RPCMP) will <br /> be resampled in May during the second quarter 2010 sampling event and a second <br /> independent sample will be collected in June 2009. The results of the retesting events <br /> will be submitted to DTSC and RWQCB under separate cover. As discussed above, <br /> GLA prepared a letter report dated February 14, 2001 (RWQCB Case No. 2209), to <br /> assess the source and potential impacts of low-level VOCs in groundwater adjacent to the <br /> Forward Landfill. The letter report concluded that the sporadic detection of low-level <br /> VOCs in groundwater at the Forward Unit are most likely due to landfill gas from <br /> unlined unit WMU-B. Since low-level VOCs have been confirmed at the Forward Unit, <br /> retesting will be performed for inorganic constituents only from background well <br /> MW-22. <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 water on <br /> March 24, 2010. On March 31, 2010, the lysimeters were again checked and positive <br /> pressure was applied to evacuate the accumulated sample. As recorded in the field notes <br /> for lysimeters (Appendix C) and summarized on Table 2-5, all lysimeters were reported <br /> dry, and as a result,no soil-pore liquid samples were collected during the monitoring <br /> 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 quarter. During the <br /> first quarter 2010 monitoring period, no surface-water was observed at monitoring <br /> stations FSW-I and FSW-2, and as a result, surface water samples were not collected. <br /> 2.1.7 Leachate Monitoring <br /> Leachate sumps are inspected for the presence of leachate and observations are recorded <br /> at least weekly by Forward Landfill personnel, If leachate is detected in a sump, it is <br /> pumped into the surface impoundment(WMU F) for evaporation. During the first <br /> quarter 2010, leachate was observed at all of the holding areas except WMU D-88 and <br /> D:U01 0001 3\FA-1 Q I O.doc <br /> 7 GeoLogic Associates <br />
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