Profiles of PAH emission from steel and iron industries.

In order to characterize the polycyclic aromatic hydrocarbons (PAHs) emission from steel and iron industries, this study measured the stack emission of twelve steel and iron plants in southern Taiwan to construct a set of source fingerprints. The study sampled the emissions by the USEPA's sampling method 5 with the modification of Graseby for the gas and particulate phase PAH and, then, used Hewlett-Packard 5890 gas chromatograph equipped with mass spectrometer detector to analyze the samples. The steel and iron industries are classified into three categories on the basis of auxiliary energy source: Category I uses coal as fuel, Category II uses heavy oil as fuel and Category III uses electric arc furnace. The pollution source profiles are obtained by averaging the ratios of individual PAH concentrations to the total concentration of 21 PAHs and total particulate matter measured in this study. Results of the study show that low molecular weight PAHs are predominant in gas plus particulate phase for all three categories. For particulate phase PAHs, however, the contribution of large molecular weight compounds increases. Two-ring PAHs account for the majority of the mass, varying from 84% to 92% with an average of 89%. The mass fractions of 3-, 4-, 5-, 6-ring PAHs in Category I are found to be more than those of the other two categories. The mass of Category III is dominated by 7-ring PAHs. Large (or heavy) molecular weight PAHs (HMW PAHs) are carcinogenic. Over all categories, these compounds are less than 1% of the total-PAH mass on the average. The indicatory PAHs are benz[a]anthracene, benzo[k]fluoranthene, benzo[ghi]perylene for Category I, benzo[a]pyrene, acenaphthene, acenaphthylene for Category II and coronene, pyrene, benzo[b]chrycene for Category III. The indicatory PAHs among categories are very different. Thus, dividing steel and iron industry into categories by auxiliary fuel is to increase the precision of estimation by a receptor model. Average total-PAH emission factors for coal, heavy oil and electric arc furnace were 4050 microg/kg-coal, 5750 microg/l-oil, 2620 microg/kW h, respectively. Carcinogenic benzo[a]pyrene for gas plus particulate phase was 2.0 g/kg-coal, 2.4 microg/l-oil and 1.4 microg/kW h for Category I, II and III, respectively.

[1]  N. R. Khalili,et al.  PAH source fingerprints for coke ovens, diesel and, gasoline engines, highway tunnels, and wood combustion emissions , 1995 .

[2]  E. S. Gibson,et al.  Lung cancer mortality in a stell foundry. , 1977, Journal of occupational medicine. : official publication of the Industrial Medical Association.

[3]  Wen-Jhy Lee,et al.  PAH emission from the incineration of waste oily sludge and PE plastic mixtures , 1995 .

[4]  C. Rolff,et al.  Flux estimates and pattern recognition of particulate polycyclic aromatic hydrocarbons, polychlorinated dibenzo-p-dioxins, and dibenzofurans in the waters outside various emission sources on the Swedish Baltic coast , 1992 .

[5]  C. Gestel,et al.  Enrichment of polycyclic aromatic hydrocarbons in forest soils near a blast furnace plant , 1996 .

[6]  G. Gordon,et al.  Receptor models. , 1988, Environmental science & technology.

[7]  W. Lee,et al.  Partitioning coefficients of polycyclic aromatic hydrocarbons in stack gas from a municipal incinerator , 1995 .

[8]  Barbara Zielinska,et al.  Characterizing PM2.5 emission profiles for stationary sources: comparison of traditional and dilution sampling techniques , 2000 .

[9]  Jiun-Horng Tsai,et al.  Pah characteristics in ambient air within a steel industrial complex , 1996 .

[10]  Wen-Jhy Lee,et al.  PAH emission from various industrial stacks , 1998 .

[11]  B. Tomkins,et al.  Influence of carbonaceous particles on the interaction of coal combustion stack ash with organic matter. , 1986, Environmental science & technology.

[12]  R. P. Hangebrauck Sources of polynuclear hydrocarbons in the atmosphere , 1967 .

[13]  R. Kamens,et al.  The use of polycyclic aromatic hydrocarbons as source signatures in receptor modeling , 1993 .

[14]  C. Schwab,et al.  In-stack dilution technique for the sampling of polycyclic organic compounds. Application to effluents of a domestic waste incineration plant , 1984 .

[15]  Lloyd Jw,et al.  Long-term mortality study of steelworkers. V. Respiratory cancer in coke plant workers. , 1971 .

[16]  P. T. Crisp,et al.  The analysis of organic matter in coke oven emissions , 1991 .

[17]  A. Bjørseth Handbook of polycyclic aromatic hydrocarbons , 1983 .

[18]  Glen R. Cass,et al.  A Dilution Stack Sampler for Collection of Organic Aerosol Emissions: Design, Characterization and Field Tests , 1989 .

[19]  P. Lioy,et al.  Profiles of organic particulate emissions from air pollution sources: status and needs for receptor source apportionment modeling. , 1986, Journal of the Air Pollution Control Association.