Comparison of Particle Size Distributions and Elemental Partitioning from the Combustion of Pulverized Coal and Residual Fuel Oil

ABSTRACT U.S. Environmental Protection Agency (EPA) research examining the characteristics of primary PM generated by the combustion of fossil fuels is being conducted in efforts to help determine mechanisms controlling associated adverse health effects. Transition metals are of particular interest, due to the results of studies that have shown cardiopulmonary damage associated with exposure to these elements and their presence in coal and residual fuel oils. Further, elemental speciation may influence this toxicity, as some species are significantly more water-soluble, and potentially more bio-available, than others. This paper presents results of experimental efforts in which three coals and a residual fuel oil were combusted in three different systems simulating process and utility boilers. Particle size distributions (PSDs) were determined using atmospheric and low-pressure impac-tion as well as electrical mobility, time-of-flight, and light-scattering techniques. Size-classified PM samples from this study are also being utilized by colleagues for animal instillation experiments. Experimental results on the mass and compositions of particles between 0.03 and >20 μm in aerodynamic diameter show that PM from the combustion of these fuels produces distinctive bimodal and trimodal PSDs, with a fine mode dominated by vaporization, nucleation, and growth processes. Depending on the fuel and combustion equipment, the coarse mode is composed primarily of unburned carbon char and associated inherent trace elements (fuel oil) and fragments of inorganic (largely calcium-alumino-silicate) fly ash including trace elements (coal). The three coals also produced a central mode between 0.8- and 2.0-μm aerodynamic diameter. However, the origins of these particles are less clear because vapor-to-particle growth processes are unlikely to produce particles this large. Possible mechanisms include the liberation of micron-scale mineral inclusions during char fragmentation and burnout and indicates that refractory transition metals can contribute to PM <2.5 μm without passing through a vapor phase. When burned most efficiently, the residual fuel oil produces a PSD composed almost exclusively of an ultrafine mode (~0.1 μm). The transition metals associated with these emissions are composed of water-soluble metal sulfates. In contrast, the transition metals associated with coal combustion are not significantly enriched in PM <2.5 μm and are significantly less soluble, likely because of their association with the mineral constituents. These results may have implications regarding health effects associated with exposure to these particles.

[1]  J. Wendt,et al.  Metal Aerosol Formation in a Laboratory Swirl Flame Incinerator , 1994 .

[2]  Jost O.L. Wendt,et al.  Toxic metal emissions from incineration: Mechanisms and control , 1993 .

[3]  A. Sarofim,et al.  Influence of char fragmentation on ash particle size distributions , 1989 .

[4]  J. Wendt,et al.  Mechanism and kinetics of lead capture by kaolinite in a downflow combustor , 2000 .

[5]  J. Wendt,et al.  Hazardous waste incineration: The in-situ capture of lead by sorbents in a laboratory down-flow combustor , 1992 .

[6]  J. Lighty,et al.  Mobilization of iron from coal fly ash was dependent upon the particle size and the source of coal. , 1998, Chemical research in toxicology.

[7]  H. L. Goldstein,et al.  Particulate Emissions From Residual Fuel Fired Boilers: Influence of Combustion Modification , 1977 .

[8]  L. Baxter Char fragmentation and fly ash formation during pulverized-coal combustion , 1992 .

[9]  C. W. Siegmund,et al.  Influence of heavy fuel oil composition and boiler combustion conditions on particulate emissions. , 1976, Environmental science & technology.

[10]  J. Wendt,et al.  Fine Particle Emissions from Heavy Fuel Oil Combustion in a Firetube Package Boiler , 1998 .

[11]  J. Wendt,et al.  Sorbent capture of nickel, lead, and cadmium in a laboratory swirl flame incinerator☆☆☆ , 1995 .

[12]  John D. Spengler,et al.  Particles in our air : concentrations and health effects , 1996 .

[13]  Richard D. Smith,et al.  Characterization and formation of submicron particles in coal-fired plants , 1979 .

[14]  D. Dockery,et al.  An association between air pollution and mortality in six U.S. cities. , 1993, The New England journal of medicine.

[15]  Jost O.L. Wendt,et al.  Trace metal transformation mechanisms during coal combustion , 1994 .

[16]  G. Huffman,et al.  Speciation of elements in NIST particulate matter SRMs 1648 and 1650 , 2000, Journal of hazardous materials.

[17]  Risto Hillamo,et al.  On the Performance of the Berner Low Pressure Impactor , 1991 .

[18]  G. Huffman,et al.  Nickel and Chromium Speciation of Residual Oil Combustion Ash , 1998 .

[19]  D. Ensor,et al.  Size Distribution of Fine Particles from Coal Combustion , 1982, Science.

[20]  C. Piantadosi,et al.  HUMIC-LIKE SUBSTANCES IN AIR POLLUTION PARTICULATES CORRELATE WITH CONCENTRATIONS OF TRANSITION METALS AND OXIDANT GENERATION , 1996 .

[21]  G. Huffman,et al.  Chemical speciation of nickel in residual oil ash , 1998 .

[22]  C. Sabbioni,et al.  Characterization of the particulate emission by a large oil fuel fired power plant , 1983 .

[23]  Jost O.L. Wendt,et al.  Sodium partitioning in a pulverzed coal combustion environment , 1996 .

[24]  T. T. Shen,et al.  Characterization of Particulates from Power Plants , 1976 .

[25]  J. Wendt,et al.  Partitioning of arsenic, selenium, and cadmium during the combustion of Pittsburgh and Illinois #6 coals in a self-sustained combustor , 2000 .

[26]  D. Costa,et al.  Soluble transition metals mediate residual oil fly ash induced acute lung injury. , 1997, Journal of toxicology and environmental health.

[27]  FINE PARTICLE EMISSIONS FROM RESIDUAL FUEL OIL COMBUSTION: CHARACTERIZATION AND MECHANISMS OF FORMATION , 2000 .

[28]  Esko I. Kauppinen,et al.  Coal combustion aerosols: a field study , 1990 .