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2001_0813_packet
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AUG-01-2001 1 2 17 INDUSTRIAL EQUIPMENT 1TV 407 886 5990 P.03/12 <br /> Introduction <br /> Background <br /> The United States EPA is required to set emission standards for the "other solid waste <br /> incinerators" (OSWI) category referenced under Section 129(aXl#) of the amended Clean Air <br /> Act. This category currently contains pathological waste incinerators and human crematories. A <br /> representative human crematory, located at the Woodlawn Cemetery in the Bronx, New York, <br /> was tested in support of setting these emission standards. Testing was conducted in <br /> collaboration with the Cremation Association of North America (CANA). <br /> Although emissions data are available from tests at another facility, the unit tested did not have <br /> emission controls and the body containers (caskets) may not have been representative. Thus, the <br /> Woodlawn facility. which involves a representative human crematory having emission controls, <br /> was selected for baseline ("best controlled similar unit") emissions testing. Additionally, this <br /> test project would help determine the effects of secondary chamber temperature on emission <br /> levels. <br /> Scope <br /> This EPA work assignment was conducted in collaboration with the Cremation Association of <br /> North America (CANA) and resttits of testing for both patties are combined in this report. <br /> Emissions testing for polychlorinated dibenzo-dioxins (KDDs) and polychlorinated dibenio- <br /> furans (PCDFs) and process monitoring was conducted under the EPA work assignment. In <br /> conjunction with EPA testing, emissions testing for total particulate matter (PM), hydrogen <br /> chloride MCI), cadmium (Cd), mercury (Hg), lead (Pb), sulfur dioxide (S%), oxides of nitrogen <br /> (NOA and carbon monoxide (CO), and visual observation of opacity was conducted for CANA. <br /> Testing was conducted for three conditions, where secondary chamber temperature was varied at <br /> 1,4Q0°, 1,600°,and 1,800°F per test. Each test consisted of three sampling runs at the sctubbcr <br /> inlet and outlet simultaneously with similar container materials, 8s available, being used for 0 <br /> runs. Each sampling Nn covered an entire cycle of about 2 hours. <br />
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