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residential wood combustion in a fireplace, and 13,000 times more mutagenic than coal-fired <br /> utility emissions with good combustion efficiency and add-on controls. <br /> A list of 34 target compounds representing the highest potential for inhalation health <br /> impacts from open tire fires was developed by analyzing laboratory test data and open tire <br /> fire data collected at nine tire fires. The list can be used to design an air monitoring plan in <br /> order to evaluate the potential for health risks in future events. <br /> Methods for preventing and managing tire fires are presented. Recommendations are <br /> presented for storage site design, civilian evacuation, and fire suppression tactics. For <br /> example, tire piles should not exceed 6 m (20 ft) in height; maximum outside dimensions <br /> should be limited to 76 m (250 ft) by 6 m (20 ft). Interior fire breaks should be at least 18 m <br /> (60 ft) wide. Civilians should be evacuated when they may be subject to exposure by the <br /> smoke plume. Fire suppression tactics are site and incident-specific and firefighters should <br /> have specialized training to deal effectively with them. <br /> Other Impacts from Open Tire Burning <br /> The scope of this report is limited to airborne emissions. However, significant <br /> amounts of liquids and solids containing dangerous chemicals can be generated by melting <br /> tires. These products can pollute soil, surface water, and ground water and care must be <br /> taken to properly manage these impacts as well. <br /> Controlled Combustion <br /> The results of a laboratory test program on controlled burning of tire-derived fuel <br /> (TDF) in a Rotary Kiln Incinerator Simulator (RKIS) are presented. In all, 30 test conditions <br /> were run, with the TDF feed rate varying from 0 to 21.4% of heat input. The test conditions <br /> were achieved by varying kiln firing rate, combustion air flow rate, and tire feed rate. The <br /> majority of the tests were conducted with a steady-state feed of TDF. However, variations in <br /> the mode of TDF feeding were simulated in two tests to evaluate the impact of transient <br /> operation on air emissions. <br /> Based on the results of the RKIS test program, it can be concluded that, with the <br /> exception of zinc emissions, potentia I emissions from TDF are not expected to be very much <br /> different than from other conventional fossil fuels, as long as combustion occurs in a well- <br /> designed, well-operated and well-maintained combustion device. However, as with most <br /> solid fuel combustors, an appropriate particulate control device would likely be needed in <br /> order to obtain an operating permit in most jurisdictions in the United States. <br /> Test data, from 22 industrial facilities that have used TDF are presented: 3 kilns (2 <br /> cement and 1 lime) and 19 boilers (utility, pulp and paper, and general industrial <br /> applications). All sources had some type of particulate control. In general, the results <br /> indicate that properly designed existing solid fuel combustors can supplement their normal <br /> fuels, which typically consist of coal, wood, coke and various combinations thereof, with 10 to <br /> 20%TDF and still satisfy environmental compliance emissions limits. Furthermore, results <br /> from a dedicated tires-to-energy (100% TDF) facility indicate that it is possible to have <br /> ix <br />