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ARCHIVED REPORTS_2013_6
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ARCHIVED REPORTS_2013_6
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Last modified
7/17/2020 3:53:43 PM
Creation date
7/3/2020 10:57:18 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2013_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
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2013_6.tif
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EHD - Public
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Concentration Limit Thresholds <br /> As specified in the RPCMP and RWQCB Order No. R5-2003-0049 for the Forward <br /> Landfill, the routine inorganic monitoring data obtained during the second quarter 2013 <br /> monitoring period were compared to established intrawell concentration limits (CLs) <br /> calculated for the Forward Unit. The CLs are summarized in Table 2-4 and compared to <br /> the analytical results collected during the second quarter 2013. As summarized in this <br /> table, CLs were exceeded for chloride at wells MW-2A and MW-13; nitrate as nitrogen <br /> (nitrate) at well MW-14; for sulfate at wells MW-14 and MW-15; and for sodium at <br /> background well MW-24. Trend analyses were performed for wells and constituents that <br /> exceeded respective CLs. Statistically significant increasing temporal trends were <br /> identified for nitrate-N concentrations in well MW-14, sulfate concentrations in well <br /> MW-15, and sodium concentrations in background wells MW-24. Trend analyses are <br /> included in Appendix D. Previously submitted No Release Demonstrations (NRDs) for <br /> these common inorganic constituents at the Forward Unit have concluded that the CL <br /> exceedances are not the result of a release from the Forward Unit, and as a result, <br /> retesting is not performed for these common inorganic constituents. The increasing trend <br /> for sodium at background well MW-24 suggests increases in sodium concentrations <br /> upgradient of the landfill. <br /> 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 0 <br /> was inspected and vacuums were reset to approximately—25 inches of mercury on <br /> May 21, 2013 at each suction lysimeter. On May 28, 2013, the lysimeters were again <br /> checked and positive pressure was applied to evacuate the accumulated sample. As <br /> recorded in the field notes for lysimeters (Appendix C) and summarized on Table 2-5, <br /> lysimeters were reported dry, and as a result,no soil-pore liquid samples were collected <br /> during the current monitoring period. Of note, there was no access port to inspect pan <br /> lysimeters WMW-DO1N, WMW-DO1S, and WMW-D02. GLA and Del-Tech will be <br /> working with Forward to access these pan lysimeters for future monitoring. <br /> 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 second <br /> quarter 2013, 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 3.58 to 7.25 feet <br /> during the second quarter 2013 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, temperature, and turbidity. Results of monthly field monitoring <br /> measurements for the second quarter 2013 are presented in Table 2-6. <br /> C:\2013-0021\FA_2Q13.doc 6 Geo-Logic Associates <br />
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