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ODOR CONTROL STUDY <br /> processes . To test the operator' s observations , odor and sulfur mass emissions were <br /> calculated for the Filtrate Equalization Basin and the liquid treatment processes , with <br /> and without filtrate . <br /> At the time of the sampling program , the Filtrate Equalization Basin had been <br /> eliminated , following a recommendation by PBS &J during the site visit in April . <br /> Therefore , in order to assess the impact of eliminating the Filtrate Equalization Basin , <br /> odor and sulfur flux rates were measured in the Filtrate Sump and mass emission rates <br /> were calculated using the flux rate applied over the area of the Filtrate Equalization <br /> Basin . This assessment showed that eliminating the Filtrate Equalization Basin had <br /> eliminated approximately 1 . 7 pounds of sulfur per day. <br /> Odor and sulfur emission rates were also calculated for the Anoxic Tank and the <br /> Oxidation Ditches . Odor and sulfur measurements were taken in the Anoxic Tank and <br /> the pre-oxygen zone and mixed-aerated zone of the oxidation ditch , prior to and after <br /> the introduction of filtrate. The different zones of the oxidation ditch were sampled in <br /> order to obtain representative air samples for areas with different aeration patterns . <br /> Unfortunately, the night before the sampling program , the return activated sludge (RAS ) <br /> pumps failed and did not become operational until 8 : 50 am the day of sampling . The <br /> RAS pumps are used to deliver fresh biological microbes to the Anoxic Tanks as part of <br /> the liquid treatment process . Since the RAS pumps did not work, the Anoxic Tank <br /> appeared to contain only raw wastewater. The lack of return activated sludge allowed <br /> the contents of the Anoxic Tank to become somewhat septic and this affected the <br /> quality of the influent wastewater to the oxidation ditch . This degradation in raw <br /> wastewater appears to have affected the emission rates for all the liquid treatment <br /> process . <br /> Figures 9 and 10 show that the morning samples (which did not contain filtrate) had <br /> higher odor and sulfur emissions than the afternoon samples . Thus , the sampling <br /> program did not confirm the operator' s observations . Problems with the return activated <br /> sludge pumps appear to have prevented the sampling program from discovering the <br /> impact of filtrate on liquid process emissions . However, based on the very low <br /> emissions from the oxidation ditch (even under bad influent conditions ) , filtrate in not <br /> likely to impact emissions from the oxidation ditches . Overall , calculations indicate that <br /> the the oxidation ditch contributes only 0 . 5 % of the total emissions from the Central <br /> WWTF . However, the impact of filtrate on Anoxic Tank emissions remains unknown at <br /> this time . <br /> 2 . 3 . 5 Impact of Recent Improvements on Emissions <br /> As indicated above , the Filtrate Equalization Basin had been eliminated at the time of <br /> sampling and this eliminated an estimated 1 . 7 pounds of sulfur per day compared to <br /> operations in April 2002 . Operators at the plant also eliminated the Aerobic Digesters <br /> and . the construction of hoods and covers in the belt filter press area of the Dewatering <br /> Building were about to be completed . In order to assess the impact of these <br /> 12 Indian River County, Central Wastewater Treatment Facility <br /> PBSU #071230, February 2003 <br />