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1 , <br /> PANWHE BURN SITE REMEDIATION <br /> On May 22, 1996, the California EPA duty officer requested the U.S. EPA, Emergency <br /> Response Office to respond to the tire fire. The U.S. EPA mobilized its Superfund Technical <br /> Assessment and Response Team (START) consultant and met with fire agencies to determine <br /> a course of action. At the time of the fire, the 1 million exposed tires were in contact with the <br /> 2 million buried tires because soil was only placed over the top of the tire pile. As a result, <br /> the tire fire spread from the exposed tires to the buried tires in the upper canyon. At the <br /> meeting, the agencies decided to allow the tire fire to burn and to control and contain the fire <br /> and pyrolytic oil runoff. During Phase I of the emergency removal action, the U.S. EPA <br /> authorized $200,000 for its Emergency Response Cleanup Service (FRCS) contractor to <br /> perform the following tasks: <br /> Prevent the pyrolytic oil from discharging into the creek by constructing a temporary <br /> check dam at the base of the canyon <br /> ➢ Excavate and extinguish the tires under combustion at the interface between the buried <br /> tires and the fire <br /> Prevent the further spread of the fire into the buried tire area by constructing an earthen <br /> embankment to act as a firebreak <br /> Several agencies were involved with the fire including CDF, DTSC, California Office of <br /> Emergency Services, Fresno County Community Health Department, U.S. EPA Region IX, <br /> California Air Resources Board, San Joaquin Valley Unified Air Pollution Control District, <br /> Department of Fish and Game (DFG), PG&E, and the CIWMB. <br /> The fire left approximately 4 acres of steep canyon walls contaminated with burn ash and steel <br /> belts. The U.S. EPA's sampling indicated the burn ash contained elevated levels of heavy <br /> metals, primarily zinc at 32,000 mg/kg and petroleum hydrocarbons at 25,000 mg/kg. Based <br /> on limited exploration during Phase I, the contaminated material appeared to be approximately <br /> 1 foot deep on the canyon slopes and 2 feet deep along the base of the canyon. A synopsis of <br /> the tire fire is provided in Appendix A, the U.S. EPA Federal On-Scene Coordination Report. <br /> 1 .4 Site Conditions <br /> Initial reports indicated there were approximately 4 acres of tire ash, 1 to 2 feet deep. The <br /> burn tire residue was light gray and was composed of about 50 percent ash and 50 percent <br /> steel belts. The ash was extremely dry and hydrophobic (i.e., unable to dissolve in water). <br /> Because of the extreme heat from the tire fire, the steel belts were heavily oxidized and <br /> brittle. Steel belts, up to one-half inch, ruptured when bent by hand. <br /> The pyrolytic oil generated from the tire fire burned as it traveled down the canyon. A small <br /> check dam approximately halfway up the canyon held the oil. The pooled oil behind the <br /> check dam created enough heat to partially melt the corrugated steel pipe at the base of the <br /> check dam. Only a small amount of oil was observed at the outlet side of the pipe. <br /> CIWMB 4 <br />