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ARCHIVED REPORTS_2011_16
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ARCHIVED REPORTS_2011_16
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Last modified
7/17/2020 3:53:37 PM
Creation date
7/3/2020 10:56:00 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2011_16
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_2011_16.tif
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EHD - Public
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0 <br />Concentration Limit Thresholds <br />Data obtained during the third quarter 2011 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 the CLs that were exceeded in samples collected from groundwater <br />monitoring wells during the third quarter 2011. As summarized in this table, CLs were <br />exceeded for DIPE in well MW -2A; PCE and WE in well MW -14; barium and sulfate in <br />wells MW -15; potassium and sodium in well MW -18; chloride in well MW -21; and for <br />potassium and sulfate in well MW -22. In accordance with the RPCMP, only wells with <br />CL exceedances of impact constituents (as defined in Table 5-3 of the RPCMP) need to <br />be resampled, and therefore, retesting for sulfate is not required. Furthermore, a No <br />Release Demonstration (NRD) (Herst, 2011) was performed for CL exceedances of <br />potassium in well MW -18. The results of the NRD indicate that the CL exceedances for <br />potassium are not the result of a release from the facility, and therefore, retesting of <br />potassium will not be performed. In addition, CL exceedances for low-level VOCs are <br />not retested since similar low-level VOCs have been confirmed at the Forward Unit. <br />Therefore, CL exceedances require retesting will be conducted for barium at well <br />MW -15 and sodium at well MW -18. <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 —25 inches of mercury on <br />August 16, 2011. On August 20, 2011, 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 current <br />monitoring period. <br />2.1.6 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 third <br />quarter 2011, leachate was observed at all of the holding areas except WMU D-87 and <br />WMU D-88 A/B. Freeboard at WMU-F ranged from approximately 5.17 to 10.25 feet <br />during the third quarter 2011 monitoring period. Appendix A presents copies of the <br />leachate logs and the freeboard observation logs. <br />Leachate samples were collected on a monthly basis and analyzed in the field for pH, <br />specific conductance, and temperature. Results of monthly field monitoring <br />measurements for the third quarter 2011 are presented in Table 2-6. <br />c:\2011-0050\FA_3Qu.aoa 6 Geo -Logic Associates <br />
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