ATMOSPHERIC BEHAVIOR OF POLYCHLORINATED DIBENZO-P-DIOXINS AND DIBENZOFURANS AND THE EFFECT OF COMBUSTION TEMPERATURE

Citation
Dm. Pennise et Rm. Kamens, ATMOSPHERIC BEHAVIOR OF POLYCHLORINATED DIBENZO-P-DIOXINS AND DIBENZOFURANS AND THE EFFECT OF COMBUSTION TEMPERATURE, Environmental science & technology, 30(9), 1996, pp. 2832-2842
Citations number
36
Categorie Soggetti
Environmental Sciences","Engineering, Environmental
ISSN journal
0013936X
Volume
30
Issue
9
Year of publication
1996
Pages
2832 - 2842
Database
ISI
SICI code
0013-936X(1996)30:9<2832:ABOPDA>2.0.ZU;2-J
Abstract
Emissions from the combustion of wood chips treated with pentachloroph enol (PCP), polyvinyl chloride (PVC) plastic pipe shavings, and solid PCP were injected into 25-m(3) outdoor Teflon film chambers and aged i n sunlight under typical atmospheric conditions. The behavior of parti culate and gas-phase polychlorinated dibenzo-p-dioxins and dibenzofura ns (PCDDs and PCDFs) and polycyclic aromatic hydrocarbons (PAHs) was m onitored over time. Only the tetra- and pentachlorinated dioxins and f urans were shown to clearly partition at all into the gas phase in the se experiments, perhaps due to high concentrations of TSP. Little or n o reactivity was observed for PCDDs and PCDFs residing on particles re sulting from high-temperature combustion (760-800 degrees C). Greater photochemical reactivity of particle-bound PCDD/Fs resulted after low- temperature combustion (350-380 PC), where fairly rapid photolysis com peted with a production mechanism believed to begin with PCP. Photolys is rates of PCD D/Fs appeared to increase with decreasing levels of ch lorination, lending evidence to the observed enrichment of the higher chlorinated species in the natural environment. On low-temperature com bustion 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 high-temperature combustion particles unde r 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-tem perature combustion experiments. Experimental particle-phase PAH photo lytic half-lives also increased from between 0.1 and 3.6 h in low-temp erature 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-temperatu re combustion.