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ARCHIVED REPORTS_1997
Environmental Health - Public
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4400 - Solid Waste Program
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PR0505006
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ARCHIVED REPORTS_1997
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Last modified
7/18/2020 5:07:51 AM
Creation date
7/3/2020 11:16:42 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
1997
RECORD_ID
PR0505006
PE
4445
FACILITY_ID
FA0006475
FACILITY_NAME
TRACY MATERIAL RECOVERY/TRANSF
STREET_NUMBER
30703
Direction
S
STREET_NAME
MACARTHUR
STREET_TYPE
DR
City
TRACY
Zip
95376
APN
25313019
CURRENT_STATUS
01
SITE_LOCATION
30703 S MACARTHUR DR
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4445_PR0505006_30703 S MACARTHUR_1997.tif
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EHD - Public
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Odor Impact Minimization Plan-Compost Facility <br /> Tracy Material Recovery Facility and Transfer Station <br /> 30703 S. MacArthur Drive, Tracy, California 95377 <br /> Biofilters are also constructed and properly sized and maintained for the <br /> processing of exhaust air in the negatively-aerated ASP systems. The biofilters <br /> are highly effective in the removal of odors, volatile organic compounds, and <br /> greenhouse gasses from the exhaust air; they are constructed with irrigation <br /> systems to maintain proper moisture levels and monitored regularly to assure the <br /> filter media is replaced in a timely manner. <br /> Bioaerosols: The primary feedstock for the compost process is green waste. <br /> Potential adverse health effects associated with airborne fungal spores, <br /> specifically Aspergillus fumigatus and or Aspergillus flavus, have raised concerns <br /> by some Californians during the siting and operation of compost facilities. The <br /> staff of the CalRecycle, in cooperation with the California Department of Health <br /> Services, and Cal/EPA's Office of Environmental Health Hazard Assessment <br /> prepared a technical bulletin during 1993, and released the summary of findings <br /> in LEA Advisory No. 6 dated December 16, 1993. A properly operated compost <br /> facility should not present a health risk from Aspergillus fumigatus. Sound <br /> management practices include maintaining moisture, temperature and pH levels, <br /> aerating, turning and mixing. Reducing the dispersal of dust and spores is best to <br /> control exposure. The uses of water sprays or mists while turning piles, and <br /> refraining from turning on windy days will help accomplish this. The operator <br /> plans to follow the best management practices (BMP's) outlined in LEA Advisory <br /> No 6. These include: <br /> • Maintaining the windrows in an aerobic condition through regular aeration and <br /> mixing with a compost turner. <br /> • Maintaining windrow moisture content between 45 and 60 percent <br /> • Maintaining adequate windrow temperatures (above 55 C) throughout the <br /> pathogen reduction period (as mandated by 14 CCR §17868.3). <br /> Drainage issues: Standing water is a potential source of odors. The pad will be <br /> constructed of asphalt concrete or concrete and is sloped to drain at a minimum <br /> of 1%. Differential settlement of the pad and storage areas will be minimized <br /> through regrading of surfaces as needed. The pad will be maintained to prevent <br /> ponding. <br /> On-site drainage is controlled by use of drainage ditches surrounding the <br /> perimeter of the facility and directing all surface water flow toward the storm <br /> water retention basin adjacent to the compost pad, which is maintained to <br /> prevent sedimentation and organic loading that could potentially cause odors. <br /> Windrows are constructed perpendicular to the slope to facilitate drainage and <br /> prevent ponding. <br /> Operations Procedures: The maximum storage time is 7 days for incoming green <br /> materials feedstock and 48 hours for incoming food waste. The compost cycle <br /> will be 90 to 120 days. Should complaints be filed and verified, the storage time <br /> could be reduced at certain times of the year when there is a higher percentage <br /> 15 <br />
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