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ARCHIVED REPORTS_2011_14
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ARCHIVED REPORTS_2011_14
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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_14
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_14.tif
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EHD - Public
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in accordance with CCR Title 27, Section 20937, Forward continues to install additional <br /> landfill gas extraction wells, as needed. <br /> New Historical Intrawell Maximum Values <br /> During the fourth quarter 2011 monitoring event, a first-time VOC detection, for DIPE, <br /> was measured in the sample collected from well MW-16. All of the other monitoring <br /> parameters were within their historical range of values. <br /> Concentration Limit Thresholds <br /> Data obtained during the fourth 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 CLs that were exceeded in samples collected from groundwater monitoring <br /> wells during the fourth quarter 2011. As summarized in this table, CLs were exceeded <br /> for DIPE at well MW-16, for chloride at upgradient(background) well MW-22, and for <br /> sulfate at wells MW-10, -15, and-22. CL exceedances for non-impact constituents <br /> (arsenic, bicarbonate, hexavalent chromium, nitrate as nitrogen, and sulfate) are not <br /> retested, and therefore, retesting for sulfate is not required. In addition, CL exceedances <br /> for low-level VOCs are not retested since similar low-level VOCs have been confirmed <br /> at the Forward Unit. Therefore, only the CL exceedance for chloride at well MW-22 will <br /> require retesting. <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 /> November 2, 2011. On November 4, 2011,the lysimeters were again checked and <br /> positive pressure was applied to evacuate the accumulated sample. As recorded in the <br /> field notes for lysimeters (Appendix Q and summarized on Table 2-5, lysimeters were <br /> reported dry to moist, and as a result, no soil-pore liquid samples were collected during <br /> the current 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 fourth <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 7.67 to 12.08 feet <br /> during the fourth quarter 2011 monitoring period. Appendix A presents copies of the <br /> leachate logs and the freeboard observation logs. <br /> c:\zooi-0050Tn_4QILdoc 6 Geo-Logic Associates <br />
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