United States Environmental Protection Agency Air and Energy Engineering Research Laboratory Research Triangle Park NC 27711 Research and Development EPA/600/S7-85/003 Apr. 1985 &EPA Project Summary The Relationship of Fly Ash Composition, Refractive Index, and Density to In-Stack Opacity S. J. Cowen and D. S. Ensor The refractive index, density, and composition of fly ash from coal-fired boilers was investigated. The goals were to determine: (1) the interrelationship of refractive index and composition, and (2) the significance of ash properties on in-stack plume opacity. A survey was made of 14 ash samples repre- senting a wide range of coals. Light absorption was measured using the Integrating Plate Method, which com- pares light absorption through a clean filter to that through a filter with a single layer of aerosol. Ony absorption is meas- ured, while scattered light is integrated equally for both cases. This technique requires fine particles (volume absorb- ers) for easy interpretation of results. The technique was calibrated using an aerosol, methylene blue, with known absorption characteristics. The real part of the refractive index was measured by an oil immersion technique. The real refractive index and density were found to be highly correlated with composition with a multilinear regression equation. The absorbing refractive index was well correlated with ash carbon content. The modeling of in-stack opacity showed a weak dependence on ash optical properties for the range of ashes studied .The effect of the real part of the refractive index on opacity tends to be counterbalanced by particle density effects. Furthermore, except for very high carbon ashes, fly ash absorbs relatively little light. This Project Summary was developed by EPA's Air and Energy Engineering Research Laboratory, Research Triangle Park, NC, to announce key findings of the research project that is fully docu- mented in a separate report of the same title (see Project Report ordering infor- mation at back). Introduction Opacity limitations of air pollution emissions are an important aspect of stationary source regulations. However, the engineering approaches needed to design control equipment to meet opacity limits are still under development. Ensor (1972) established the relationship of plume opacity to mass concentration as a function of log-normal particle size distri- butions of the emission for ideal condi- tions. More recently, it was determined that the particle size distributions down- stream of emission control equipment are usually not log-normal. As a result, development of calculator programs to allow prediction of expected plume opac- ity from particle size distribution data and mass concentration was the topic of a study by Cowen, Ensor, and Sparks (1980). However, the secondary variables affecting plume opacity (e.g., particle density and refractive index) have not been systematically measured under conditions useful for plume opacity pre- diction The usual practice has been to assume nominal values of refractive index and particle d&nsity. The present research has two objec- tives: (1) to measure refractive index and particle density with supporting chemical composition for a wide selection of ashes ------- from utility boilersfiring bituminous coal, and (2) to compute the sensitivity of plume opacity to the variation of particle refractive index and density using these data. The survey nature of this study allowed the use of bulk samples taken from ash hoppers at utility plants. In no previous investigations have all the physical properties required for plume opacity prediction been measured oh the same sample of fly ash. Examples of typical fly ash characterization research include determination of the chemical composition of ashes from the major coal fields in the U.S. by the Bureau of Mines (Gluskoter et al., 1977) and measure- ments of composition and particle density in size-segregated samples for a single sample of fly ash by Fisher et al. (1978). It should be noted that the refractive index of a material is a complex number: the real part describes the bending of light, and the imaginary part describes the absorption of light with subsequent con- version to heat in the material. Two totally different measurements are required to determine this physical property. The measurement of real refractive index is a fairly common practice for mineral and small particle identification (McCrone et al., 1967). Limited measurements of absorptive refractive index have been reported for fly ash: Volz (1973) measured absorption of fly ash in the infrared wavelengths, and Nolan (1977) reported the visible light absorption of ash samples at a university heating plant boiler under limited conditions with the Integrating Plate Method (IPM). The IPM, developed by Lin et al. (1973), involves measuring light transmission through the particle sample on a membrane filter and an opal glass diffuser. The reduction in the light transmission can be related to the ab- sorption coefficient and the imaginary refractive index. Thus, an important con- tribution of the present research is that a battery of previously developed analytical methods were used on a fairly wide range of ash samples. Many of the ash samples were also used by Bickelhaupt (1979) to develop mathematical relationships be- tween electrical resistivity and chemical composition. Conclusions and Recommendations A survey of the refractive index, density, and composition of 14 different fly ash samples indicates significant interrela- tionships between their physical and chemical properties. A regression equa- tion was developed with the specific refractivity [(n'-1 )/p] as a function of the major chemical components of the ash. The regression explains 82 percent of the variability of the data. The imaginary refractive index was found to be corre- lated to carbon content of the ash, which explains 80 percent of the variability of the data. The imaginary refractive exper- iments were limited by the accuracy and sample restrictions of the IPM. However, modeling of opacity with typical fly ash size distributions and the ranges of refractive indices indicates that the ab- sorbing refractive index is insignificant. Although pure soot is an effective material for attenuating light, it is usually not of sufficient quantity in boiler emissions to alter the particle size distribution for maximum effect on plume opacity. Opac- ity was more sensitive to particle density than real refractive index for computa- tions using the extremes of each. The IPM is semiquantitative and pro- vides results with sufficient accuracy to fulfill the objectives of this study. How- ever, the technique suffers from several sources of error; e.g., an apparent absorp- tion of known transparent materials from scattered light, and alteration of the reflection of the filter surface by the aerosol sample. Because the method is restricted to submicrometer particles, the ash samples required size segregation. Thus, the chemical composition of the total sample may not be representative of the samples used for the absorption measurement. This problem may be responsible for the scatter observed in the imaginary index carbon correlations. The errors in the method were minimized, however, by the use of an empirical correlation developed with a laboratory aerosol. Continued work would refine the rela- tionship of fly ash specific refractivity to chemical composition. The data base should be expanded to include a wider range of coal ranks and types such as lignite and anthracite. The results of this effort could lend support to studies cor- relating mass emissions to plume opacity. At present, additional work is not justified on the aerosol-absorbing refrac- tive index because the relatively large size of fly ash tends to minimize its effects. However, absorption studies may be worthwhile for sources with submi- crometer emissions. Identification of these processes would be a useful appli- cation of the techniques developed in this study. References Bickelhaupt, R. E.(1979): ATechniquefor Predicting Fly Ash Resistivity. EPA/ 600/7-79/204 (NTIS PB 80-102379). Cowen, S. J., D. S. Ensor, and L. E. Sparks (1980): TI-59 Programmable Calculator Programs for In-Stack Opacity, Venturi Scrubbers, and Electrostatic Precipita- tors. EPA/600/8-80/024 (NTIS PB 80- 193147). Ensor, D. S. (1972): Smoke Plume Opacity Related to the Properties of Air Pollutant Aerosols. Ph.D. Dissertation, University of Washington, Seattle, WA. Fisher, G. L., B. A Prentice, D. Silberman, J. M. Ondov, A. H. Biermann, R. C. Ragaini, and A. R. McFarland (1978): Physical and Morphological Studies of Size Classified Coal Ash. Environ. Sci. Technol., 72,447-451. Gluskoter, H. J., R. R. Ruch, W. G. Miller, R. A. Cahill, G. B. Dreher, and J. K. Kuhn (1977): Trace Elements in Coal: Occurrence and Distribution. EPA/ 600/7-77/064 (NTIS PB 270922). Lin, C., M. Baker, and R. J. Charlson (1973): Absorption Coefficient of At- mospheric Aerosol: A Method for Measurement. Appl. Optics, 12, 1356- 1363. McCrone, W. C., R. G. Draftz, and J. G. Delly (1967): The Particle Atlas. Ann Arbor Science Publishers, Ann Arbor, Ml. Nolan, J. L. (1977): Measurement of Light Absorbing Aerosols from Combustion Sources. M.S. Thesis, University of Washington, Seattle, WA. Volz, F E. (1973): Infrared Optical Con- stants of Ammonium Sulfate, Sahara Dust, Volcanic Pumice, and Fly Ash. Appl. Optics, 12. 564-568. ------- S. J. Cowen is with Atmospheric Research Group, Altadena, CA 91001. andD. S. Ensor is with Research Triangle Institute. Research Triangle Park, NC 27709. Leslie E. Sparks is the EPA Project Officer (see below). The complete report, entitled "The Relationship of Fly A sh Composition, Refractive Index, and Density to In-Stack Opacity," (Order No. PB 85-169 860/AS; Cost: $10.00, subject to change) will be available only from: National Technical Information Service 5285 Port Royal Road Springfield, VA 22161 Telephone: 703-487-4650 The EPA Project Officer can be contacted at: Air and Energy Engineering Research Laboratory U.S. Environmental Protection Agency Research Triangle Park. NC 27711 United States Environmental Protection Agency Center for Environmental Research Information Cincinnati OH 45268 Official Business Penalty for Private Use $300 . •-, '.ItTTi f.Zf.RS'li OCOC329 PS U S ENVIR PROTECTION AGENCY REGION 5 LIBRARY 230 S DEARBORN STREET CHICAGO IL €0604 ------- |