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Last modified
9/28/2016 9:33:35 AM
Creation date
9/30/2015 6:25:21 PM
Metadata
Fields
Template:
Official Documents
Official Document Type
Report
Approved Date
03/11/2003
Control Number
2003-063
Agenda Item Number
11.H.1.
Entity Name
PBS & J
Subject
February 2003, IRC Central Wastewater Treatment Facility Odor Control St
Archived Roll/Disk#
3160
Supplemental fields
SmeadsoftID
3185
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ODOR CONTROL STUDY <br /> improvements on overall plant emissions , mass sulfur emission rates were estimated for <br /> each of these improvements . Applying measured Sludge Storage Tank emission flux <br /> rates to the area of the Aerobic Digesters provided an approximate reduction of Aerobic <br /> Digester emissions . An estimated 3 .4 pounds of sulfur per day was eliminated for each <br /> Aerobic Digester. <br /> Applying the Sludge Storage Tank emission flux rate to the area of the belt filter presses <br /> provided an approximate reduction in fugitive emissions collected by the hoods and <br /> covers . Approximately 1 . 0 pound of sulfur per day will be eliminated when the covers <br /> and hoods are completed . Of course these estimates are soft because the sources <br /> were not available for direct measurements . The hoods and covers over the belt filter <br /> presses should also reduce ambient concentrations of H2S in the Dewatering Building . <br /> However, open grating over the filtrate sump will likely allow significant emissions to <br /> escape into the Dewatering Building . Based on the observations made , the filtrate sump <br /> must be eliminated or covered in order to further reduce H2S concentrations in the <br /> Dewatering Building . <br /> Taken altogether, it is estimated that the elimination of the Filtrate Equalization Basin <br /> and Aerobic Digesters , and the enclosure of the belt filter presses , have reduced total <br /> plant emissions by approximately 9 . 6 pounds of sulfur per day. Figure 11 shows that <br /> this reduction represents an approximate 25 to 33 % reduction in sulfur emissions . <br /> How-ever, approximately 18 . 3 pounds of sulfur are still being emitted from the Central <br /> WWTF . As shown in Figure 12 , the highest mass sulfur emissions were found to <br /> originate from the RSF Scrubber, the Anoxic Tank, and the Sludge and Septage <br /> Storage Tanks (fugitive emissions) . These three sources represent approximately 97 <br /> percent of the total mass emissions that are currently emitted from the Central WWTF . <br /> 2 . 3 . 6 Other Minor and Transient Sources <br /> Other relatively minor and transient odorous sources were observed at the Central <br /> WWTF . Emission estimates were not prepared for these sources . However, based on <br /> engineering judgment , these source are not believe to create measurable off-site odor <br /> impacts . These include : <br /> • Open doors in the bar screen dumpster area . Inadequate ventilation in this area <br /> reportedly prevents the closure of these doors . <br /> • Openings at slide gates and bar screens on top of the Headworks Structure . <br /> Rubber gaskets can be used to seal these openings . <br /> • Grit removal units , dumpsters , and a mechanical sludge thickener are open to <br /> the atmosphere at the Sludge Storage Tanks . Emissions from these sources are <br /> transient, but highly odorous . Ceasing operations or enclosing these sources are <br /> the only methods of eliminating emissions from these sources . <br /> •"9 13 Indian River County, Central Wastewater Treatment Facility <br /> 1 PBSU #071230, February 2003 <br />
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