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ARCHIVED REPORTS_2011_26
Environmental Health - Public
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ARCHIVED REPORTS_2011_26
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Last modified
7/17/2020 8:17:55 PM
Creation date
7/3/2020 10:56:23 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2011_26
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_26.tif
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EHD - Public
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Construction Air Permit <br /> media vessel in adsorption operation while the other media vessel is idle or going through its <br /> regeneration cycle. During this adsorption cycle, the solid media will adsorb organic siloxane <br /> compounds, and much of the other NMOCs that are typically present in LFG. The resulting <br /> "clean" LFG will provide fuel for the reciprocating IC engines. After an adjustable length of <br /> time, the adsorption media vessels will become saturated and be switched with the standby <br /> vessels to allow a regeneration cycle to begin. The maximum regeneration cycle (including <br /> warm up and cool down cycle) for one vessel will not exceed %2 of the time of the adsorption <br /> cycle,which is expected to be between 24 and 36 hours. <br /> The media regeneration system includes electric heater units, air compressors, and associated <br /> piping and system controls. During the regeneration cycle, ambient air(about 1,300 scfm at 4 <br /> psig)will be heated with an electric heater to approximately 450 'F and purge the media bed of <br /> siloxanes and other collected contaminants(primarily VOCs and sulfur compounds). This purge <br /> air will contain higher concentrations of organic constituents at the beginning of the regeneration <br /> cycle and mostly air at the end of the cycle, and all purge air will be directed to the small <br /> enclosed flare for destruction. This variability in the purge air, as the media bed goes through its <br /> regeneration cycle, is problematic for source testing since the constituents in the purge air will <br /> vary throughout the regeneration cycle. Likewise,the waste gas flare must be designed <br /> differently than normal enclosed LFG flares where this type of variability is not encountered. <br /> Because extremely low concentration levels of siloxane degrade the reduction efficiency of the <br /> back end control equipment, Ameresco will include a second stage siloxane cleaning system <br /> called the Fixed Bed Polisher. This system includes two non-regenerative vessels containing <br /> activated carbon to remove any remaining organic contaminants before fueling the reciprocating <br /> engines. <br /> The flare for the SRS regeneration off-gas is an enclosed 30 foot high ground flare firing <br /> approximately 100- 200 scfm of LFG at approximately 50%methane to maintain the required <br /> destruction temperatures. The flare has a minimum combustion temperature of 1,500 °F (1,500 <br /> to 2,100 °F with 1,800 °F nominal), and a minimum residence time of 1.0 second. It is rated at <br /> 5.64 MMBtu/hr with an exhaust gas flow rate of 10,653 actual cubic feet per minute (acfm). <br /> This flare uses about 68 scfh of propane to ignite. It is equipped with fully modulating air <br /> dampeners for primary air mixing. The combustion chamber is round with a cross sectional area <br /> of 8.7 square feet and a chamber volume of 261 cubic feet. A process flow diagram of the gas <br /> pre-treatment system is provided in Appendix D. <br /> S <br />
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