Emissions from the combustion of wood chips treated with pentachlorophenol (PCP), polyvinyl chloride (PVC) plastic pipe shavings, and solid PCP were injected into 25-m 3 outdoor Teflon film chambers and aged in sunlight under typical atmospheric conditions. The behavior of particulate and gas-phase polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDDs and PCDFs) and polycyclic aromatic hydrocarbons (PAHs) was monitored over time. Only the tetra-and pentachlorinated dioxins and furans were shown to clearly partition at all into the gas phase in these experiments, perhaps due to high concentrations of TSP. Little or no reactivity was observed for PCDDs and PCDFs residing on particles resulting from hightemperature combustion (760-800°C). Greater photochemical reactivity of particle-bound PCDD/Fs resulted after low-temperature combustion (350-380°C), where fairly rapid photolysis competed with a production mechanism believed to begin with PCP. Photolysis rates of PCDD/Fs appeared to increase with decreasing levels of chlorination, lending evidence to the observed enrichment of the higher chlorinated species in the natural environment. On low-temperature combustion particles, model results showed that TCDD half-lives increased from 0.4 under North Carolina summer outdoor conditions to 17 h under wintertime conditions. For hightemperature combustion particles under similar outdoor conditions, half-lives ranged from 6.8 to 62 h. For these same conditions, model OCDD half-lives increased from 5 and 38 h in low-temperature combustion experiments to 36 and 257 h in high-temperature combustion experiments. Experimental particle-phase PAH photolytic half-lives also increased from between 0.1 and 3.6 h in low-temperature combustion experiments to between 4.4 h and stability on high-temperature combustion particles. These differ-ences may be explained by differences in the particles generated from low-and high-temperature combustion.