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ARCHIVED REPORTS_2006_6
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ARCHIVED REPORTS_2006_6
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Last modified
7/17/2020 3:53:24 PM
Creation date
7/3/2020 10:52:08 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2006_6
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_2006_6.tif
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EHD - Public
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® summarizes CLs that were exceeded in samples collected from groundwater monitoring <br /> wells during the third quarter 2006. As summarized in this table, CLs were exceeded for <br /> wells MW-1,MW-2A,MW-3, MW-10, MW-13, MW-14, MW-15, MW-16, <br /> MW-17, MW-18,MW-19, and MW-21. In accordance with the RPCMP,wells with <br /> exceedances of concentration limits(other than arsenic,bicarbonate,hexavalent <br /> chromium,nitrate as nitrogen, and sulfate)will be resampled in November during the <br /> fourth quarter 2006 sampling event and a second independent sample will be collected in <br /> December 2006. The results of the retesting events will be submitted to DTSC and <br /> RWQCB under separate cover. <br /> 2.1.5 Vadose Zone Monitoring <br /> The current vadose-zone monitoring network at the Forward Unit consists of 16 <br /> lysimeters. The lysimeter locations are shown on Figure 2-1. Each accessible lysimeter <br /> was inspected and vacuums were reset to approximately—80 to—40 centibars on August <br /> 28, 2006. On September 26, 2006, 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, only lysimeter LY-BG1 <br /> contained soil-pore liquid and was submitted for VOC analysis. The analytical results <br /> indicates only one VOC (t-butyl alcohol) was detected in the sample collected from <br /> lysimeter LY-BG-1 at a concentration of 35 µg/L. <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 lined holding and evaporation ponds on site. According to the Operations Manager, no <br /> surface water was discharged from the facility during the reporting quarter. During the <br /> third quarter 2006 monitoring period surface water stations FSW-1 and FSW-2 were <br /> sampled on August 29, 2006. Table 2-6 summarizes the analytical results for surface <br /> water samples collected at the Forward Unit. A comparison of upgradient(FSW-2)to <br /> downgradient(FSW-1) surface water samples indicates slightly elevated general <br /> chemistry and metals constituent concentrations in the downgradient surface water <br /> sample. However,with the exception of dibromochloromethane(a confirmed laboratory <br /> contaminant),no VOC were detected at either surface water station during the third <br /> quarter 2006 monitoring period. Further monitoring is necessary to evaluate the <br /> significance of the elevated general chemistry and metals in downgradient surface water <br /> station FSW-1. <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 third <br /> quarter 2006, leachate was observed at holding areas WMW-DO1,WMU-D02, <br /> WMU FU-03, WMU FU-04, and WMU FU-05. The other holding areas were reported to <br /> be dry by Forward Landfill personnel. Freeboard at WMU F ranged from approximately <br /> D:U003 02IWorwerdAn <br /> - - 7 Geologic Associates <br />
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