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ARCHIVED REPORTS_1995
EnvironmentalHealth
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4400 - Solid Waste Program
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PR0440004
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ARCHIVED REPORTS_1995
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Last modified
7/17/2020 3:53:09 PM
Creation date
7/3/2020 10:41:03 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
1995
RECORD_ID
PR0440004
PE
4433
FACILITY_ID
FA0004517
FACILITY_NAME
FOOTHILL LANDFILL
STREET_NUMBER
6484
Direction
N
STREET_NAME
WAVERLY
STREET_TYPE
RD
City
LINDEN
Zip
95236
APN
09344002
CURRENT_STATUS
01
SITE_LOCATION
6484 N WAVERLY RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440004_6484 N WAVERLY_1995.tif
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EHD - Public
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12. 0 LANDFILL GAS CONTROL AND MONITORING <br /> Decomposition of organic waste in a landfill produces various <br /> gases, principally methane and carbon dioxide. When organic waste <br /> is initially placed in a landfill, it contains oxygen and <br /> decomposes aerobically for a short time, producing carbon dioxide, <br /> methane, nitrates, and minor amounts of other gases. After the <br /> oxygen is depleted, anaerobic decomposition takes place, and both <br /> methane and carbon dioxide are produced. The concern over landfill <br /> gas production stems from methane's combustibility in <br /> concentrations of 5 to 15 percent in air. <br /> The potential for lateral gas migration beyond the landfill <br /> boundaries and dilution of the gas to the combustible range near <br /> on-site or off-site structures must be considered in the landfill <br /> design. Studies of gas flow through various soils and experience <br /> at landfill sites have determined that flow is less in lower- <br /> permeability soils and greater in granular soils. Subsurface gas <br /> migration from landfills therefore depends greatly on the natural <br /> soils or lining systems beneath and surrounding the wastes. <br /> A Calderon Air Quality Solid Waste Assessment Test (ASWAT) , dated <br /> July 1988, has been completed for the site to comply with the <br /> Calderon amendments to the Health and Safety Code, Section 41805. <br /> The ASWAT included installation of four gas monitoring probes <br /> around the perimeter of the active fill area and near the on-site <br /> structures (Figure 13) . Figure 14 shows a typical cross section of <br /> the gas probes that were installed at the site for the ASWAT. <br /> The ASWAT was performed to determine (1) the effect of landfill <br /> gases on ambient air at the active site boundary (2) the <br /> composition of the gas stream within the landfill, and (3) whether <br /> gas is migrating off-site. Results of the ASWAT are summarized <br /> below. <br /> Volatile Organic Compound (VOC) concentrations at the Foothill <br /> Sanitary Landfill are relatively similar in upwind and downwind <br /> ambient air. In particular, downwind VOC concentrations do not <br /> appear to be higher than upwind VOC concentrations except for <br /> methyl chloride and trichloroethylene, which were detected at only <br /> 0.9 ppb and 0.2 ppb, respectively. The concentrations of benzene, <br /> perch lorethylene, carbon tetrachloride, 1, 1, 1-trichloroethane, and <br /> trichloroethylene fall at or below their respective detection <br /> limits. <br /> In areas of buried municipal refuse, the major gas components <br /> detected in the gas probes were methane and carbon dioxide, which <br /> are refuse decomposition by-products. Methane concentrations were <br /> 63 to 76 percent by volume. The results of the integrated surface <br /> walks indicated a methane concentration of 3 ppm in the active <br /> landfill area on the west side of the landfill site and 23 ppb in <br /> the active landfill area on the northwest side. <br /> 32 <br />
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