Copies of papers are available from John.Veranth@utah.edu.
Dust generator for inhalation studies with limited amounts of
archived particulate matter.
Veranth, J. M., K. R. Smith, A. E. Aust, S. L. Dansie, J. B. Griffith, A. A. Hu, M. L. Huggins and J. S. Lighty (2000). “Coal fly ash and mineral dust for toxicology and particle characterization studies: Equipment and methods for PM2.5- and PM1-enriched samples.” Aerosol Science and Technology 32(2): 127-141.
Laboratory methods to produce particle samples from known, reproducible sources with sufficient mass to perform both detailed characterization and replicated in vitro toxicological assays are described. These samples are being used to study of the ability of inhalable particles to produce abnormal concentrations of intracellular iron, resulting in the production of reactive oxygen species in cultured airway epithelial cells. Bulk samples of size-fractionated particles from laboratory-generated coal fly ash and from simulated fugitive mining tailings and road dust were collected as surrogates for important sources of iron-bearing particles in the ambient air. An Andersen cascade impactor was used to produce particle samples enriched in three size ranges: over 10 µm, 10 to 2.5 µm, and less than 2.5 µm aerodynamic diameter. A multi-jet preseparator and rectangular slot virtual impactor are being used to produce a fraction enriched in particles below 1 µm. Data on the particle production conditions, production rates, and particle sample quality are provided to illustrate the feasibility of the experimental approach. The amount of iron mobilized from particles by a physiologically-relevant chelator does not correlate with the total iron. This supports the hypothesis that particle characteristics and iron speciation are important for the production of abnormally iron concentrations in cultured type A549 human airway epithelial cells. Comparison of results obtained with these surrogate particles to previous work with urban particulate standard reference materials (SRM 1648 and SRM 1649) suggests particle sources and size fractions that should be emphasized for detailed characterization of particle morphology and mineralogy.
Smith, K. R., J. M. Veranth, J. S. Lighty and A. E. Aust (1998). “Mobilization of iron from coal fly ash was dependent upon particle size and source of coal.” Chemical Research in Toxicology 11(12): 1494-1500.
Particulate air pollution, including coal fly ash, contains
iron, and some of the pathological effects after inhalation may be due to
reactive oxygen species produced by iron-catalyzed reactions. The objective of
this study was to determine whether iron, present in coal fly ash, was mobilized, leading to ferritin
induction in human airway epithelial cells, and whether the size of the
particles affected the amount of iron mobilized. Three types of coal were used
to generate the three size fractions of fly ash collected. The
Veranth, J. M., K. R. Smith, A. A. Hu, J. S. Lighty and A. E. Aust (2000). “Mobilization of iron from coal fly ash was dependent upon the particle size and the source of coal: Analysis of Rates and Mechanisms.” Chemical Research in Toxicology 13: 382-389.
The observed iron mobilization rate from size-fractionated coal fly ash is consistent with the model predictions for a limiting case of mass transfer where the dominant resistance is diffusion through a layer of depleted solid on the surface of spherical particles. The mobilization of iron from coal fly ash under physiologically-relevant conditions in vitro was previously shown to depend on the size of the ash particles and on the source of the coal, and these in vitro measurements have been shown to correlate with indirect measurements of excess iron in cultured cells. Existing iron mobilization data was compared to mathematical models for mass transfer and chemical reaction in solid-liquid heterogeneous systems. Liquid-phase diffusion resistance can be ruled out as the rate limiting mechanism for iron mobilization as the model predictions for this case are clearly inconsistent with the measurements. Other plausible hypotheses, such as a rate limited by a heterogeneous surface reaction, cannot be conclusively ruled out by the available data. These mathematical analysis methods are applicable to the design of future experiments to determine the rate-limiting mechanism for the mobilization of iron and of other transition metals from both ambient air samples and from surrogates for major sources of particulate air pollution.
Veranth, J. M., K. R. Smith, J. G. Rohrbough, F. Huggins, A. A. Hu, J. S. Lighty and A. E. Aust (2000). “Mossbauer Spectroscopy Indicates that Iron in an Aluminosilicate Glass Phase Is the Source of the Bioavailable Iron from Coal Fly Ash.” Chemical Research in Toxicology 13: 161-164.
Iron speciation by Mössbauer
spectroscopy indicates that ferric iron in an aluminosilicate
glass phase is the source of the bioavailable iron in
coal fly ash, and that this iron species is associated with combustion
particles, but not with fugitive dust derived from soil minerals. Urban particulate has been shown to be a
source of bioavailable iron and have been shown to be
able to induce the formation of reactive oxygen species in cell culture
experiments. Laboratory generated coal fly ash and crustal
dust have been studied as surrogates for two sources of metal-bearing particles
in ambient air. As much as a 60-fold difference in iron mobilization by a
citrate chelator was observed between fly ash and crustal dust samples with similar total iron content. The
iron mobilization by citrate in vitro has been shown to correlate with indirect
measures of excess iron in cell culture and with assays for reactive oxygen
species generation. Mössbauer spectroscopy of
Smith, K. R., J. M. Veranth, A. A. Hu, J. S. Lighty and A. E. Aust (2000). “Interleukin-8 levels in human lung epithelial cells are increased in response to coal fly ash and vary with bioavailability of iron, as a function of particle size and source of coal.” Chemical Research in Toxicology 13: 118-125.
Particulate air pollution contains iron, and some of the
pathological effects after inhalation may be due to radical species produced by
iron-catalyzed reactions. We tested the hypothesis that iron present in coal
fly ash (CFA) could induce the expression and synthesis of the inflammatory
cytokine interleukin-8 (IL-8). CFA, containing as much as 14% iron, was used as
a model combustion source particle. Three coal types were used to generate
three size fractions enriched in particles [submicron (<1 micrometer), fine
(<2.5 micrometer), or coarse (2.5-10 micrometer]), as well as the fraction
of >10 micrometer. Treatment of human lung epithelial (A549) cells for 4 h
with CFA from
Lighty, J. S., J. M. Veranth and A. F. Sarofim (2000). “Combustion aerosols: Factors governing their size and composition and implications to human health.” Journal of the Air & Waste Management Association 50: 174-227.
Particulate
matter (PM) emissions from stationary combustion sources burning coal, fuel
oil, biomass, and waste, and PM from internal combustion engines burning
gasoline and diesel are a significant source of primary particles smaller than
2.5 µm (PM2.5)
in urban areas. Combustion-generated particles are generally smaller than
geologically produced dust, and have unique chemical composition and
morphology. The fundamental processes affecting formation of combustion PM and
the emission characteristics of important applications are reviewed. Particles containing
transition metals, ultrafine particles, and soot are emphasized because
these types of particles have been studied extensively, and the emissions are
controlled by the fuel composition and the oxidant-temperature-mixing history
from the flame to the stack. There is a need for better integration of the
combustion, air pollution control, atmospheric chemistry, and inhalation health
research communities. Epidemiology has demonstrated that susceptible
individuals are being harmed by ambient PM. Particle surface area, number of ultrafine particles, bioavailable
transition metals, PAH and other particle-bound organic compounds are suspected
to be more important than particle mass in determining the effects of air
pollution. Time- and size-resolved PM measurements are needed for testing
mechanistic toxicological hypotheses, for characterizing the relationship
between combustion operating conditions and transient emissions, and for source
apportionment studies to develop air quality plans. Citations are provided to
more specialized reviews, and the concluding comments make suggestions for further research.
Ball, B. Ryan, K. R. Smith J. M. Veranth, and A. E. Aust (2000): “Bioavailability Of Iron From Coal Fly Ash: Mechanisms Of Mobilization And Of Biological Effects.” Inhalation Toxicology 12: 209-225.
Particulate air pollution contains iron that may be involved in the pathological effects after inhalation. This article reviews work demonstrating that ambient particulate samples (Standard Reference Material [SRM] 1648 and SRM 1649, from the National Institute of Science and Technology) contain iron that can be mobilized from the particle in vitro and inside human lung epithelial (A549) cells. The mobilized iron can then catalyze the formation of reactive oxygen species (ROS). Work is also reviewed on the generation and size fractionation of coal fly ash (CFA) from three commercially important coal types, as well as size fractionation of three types of noncombustion particles. The availability of iron from these particles to A549 cells was measured by citrate mobilization in vitro and induction of the iron storage protein ferritin in particle-treated cells. The amount of bioavailable iron decreased with increasing particle size. The ability of particles to induce synthesis of the proinflammatory cytokine interleukin-8 (IL-8) was also determined. As with the bioavailability of iron, there was an inverse correlation with size. Further work showed that iron in CFA is responsible for IL-8 induction. Mössbauer spectroscopy of a CFA sample before and after desferrioxamine B treatment to remove bioavailable iron showed that the bioavailable iron was associated with the glassy aluminosilicate fraction of the particle. In conclusion, this work shows that bioavailable iron is responsible for ROS production by SRMs and IL-8 induction by CFA in A549 cells. The source of this bioavailable iron in CFA is glassy aluminosilicates, which are found at higher levels in smaller sizes of CFA.
D. Stephenson, G. Seshadri and J. M. Veranth, American Industrial Hygiene Association Journal, 64:4 p516-521, 2003. [13]
Particle emissions from
manual shielded metal arc welding of carbon steel were sampled in a
typical industrial maintenance
and metal fabrication workplace environment. Particle number measurements over
the size range from 14 nm to 10 mm using a scanning mobility particle sizer and
an optical particle counter showed that welding produced an approximately
lognormal particle mode with a 120 nm count median and a geometric standard
deviation of 2.07. This study produced welding particle number concentrations
on the order of 23105/cm3 in the building air 8.5 m away from the welding. Workplace
exposure samples were below the current 8-hour American Conference of
Governmental Industrial Hygienists mass concentration threshold limit value of
5 mg/m3. Submicron particles comprised 80% of the total aerosol mass collected
by a cascade impactor during welding. The
concentration of larger particles was indistinguishable from indoor background.
Microscopy showed that the welding emissions are dominated by clusters formed from ,0.1
mm primary spheres. These data
on the particles resulting from aerosol transformation by natural dilution
inside an industrial building can be compared with laboratory-scale studies of
welding particulate. The particle number characteristics observed in this study
are significant because toxicological hypotheses suggest that number or surface
area may be a better metric than mass when evaluating the health effects of
fine particles.
J. M. Veranth, R. Gelein and G. Oberdörster, Aerosol Science and Technology 37 pp. 603-609, 2003.
An
evaporation/condensation particle generator produced 30–50 nm count median
diameter particles from both pure hydrocarbons and from a complex mixture—used motor
oil—at a concentration above 1x106/cm3.
The objective was to generate ultrafine aerosols for
inhalation toxicology studies using specified organic components as surrogates
for the particulate emissions generated by diesel internal combustion engines.
This nanoparticle generation system, assembled from
commercially available components, produced smaller particle size and higher
particle number concentration than has been previously documented using
Sinclair-La Mer condensation generator technology.
The paper describes both the experiments used to design and characterize the
particle generator and the operating conditions used for a specific inhalation experiment
as an example of the system capability.
Veranth, J. M., C. A. Reilly, M. M. Veranth, T. A. Moss, C. R. Langelier, D. L. Lanza and G. S. Yost (2004). Toxicological Sciences 82: 88-96.
Cultured human lung
epithelial cells (BEAS-2B) were treated in
vitro with PM2.5-enriched particles of soil-derived mineral dust
from nine sites in the western
Veranth,
J. M., T. A. Moss, J. C. Chow, R. Labban, W. K.
Nichols, J. C. Walton, J. G. Watson and G. S. Yost (2006). Environmental Health
Perspectives 114(3): http://ehp.niehs.nih.gov/docs/2005/8360/abstract.html.
Human
lung epithelial cells, type BEAS-2B, were treated with 10–80 µg/cm2 of
PM2.5-enriched dust derived from soils and road surfaces in the western
Kevin R. Smith, John M. Veranth, Urmila P. Kodavanti, Ann E. Aust, Kent E. Pinkerton. Accepted Toxicological Sciences, 2006
Although primary particle emissions of ash from coal-fired power plants are well controlled, coal fly ash (CFA) can still remain a significant fraction of the overall particle exposure for some plant workers and highly impacted communities. The effect of CFA on pulmonary and systemic inflammation and injury was measured in male Sprague-Dawley rats exposed to filtered air or to CFA for 4 hours/day for 3 days. The concentration of CFA (PM2.5) was 1400 µg/m3, of which 600 µg/m3 was PM1. Animals were examined 18 and 36 hours post exposure. Chemical analysis of CFA detected silicon, calcium, aluminum, and iron, as major components. The total number of neutrophils in bronchoalveolar lavage fluid (BALF) following exposure to CFA was significantly increased along with significantly elevated blood neutrophils. Exposure to CFA caused slight increases in MIP-2, and marked increases in transferrin in BALF. IL-1β and total antioxidant potential in lung tissues were also increased in rats exposed to CFA. Histological examination of lung tissue demonstrated focal alveolar septal thickening and increased cellularity in select alveoli immediately beyond terminal bronchioles. These responses are consistent with the ability of CFA to induce mild neutrophilic inflammation in the lung and blood following short-term exposure at levels that could be occupationally relevant. However, when comparing the effects of CFA with those of concentrated ambient particles, CFA does not appear to have greater potency to cause pulmonary alterations. This study furthers our understanding of possible mechanisms by which specific sources of particulate air pollution affect human health.
Teague, S. V., J. M. Veranth, A. E. Aust and K. E. Pinkerton (2005). Aerosol Science and Technology 39(2): 85-91.
A novel design for a dry aerosol generator that efficiently produces a well-dispersed dust suspension using small quantities of a PM2.5-enriched powder sample is described. The motivation to develop a highly efficient dry aerosol particle generator was to facilitate collaborative projects that combine in vitro cell culture experiments and multiday inhalation exposures using a single batch of well-characterized particles. Premixing of the test particles with larger diameter glass beads permits delivery of aerosol concentrations from 100 - 1000 µg/m3 to an exposure chamber using only milligram quantities of the test powder per hour. Examination of exposure chamber filter samples by scanning electron microscopy showed well-dispersed particles of the test powder free of glass spheres or fragments. Data are presented from experiments using coal fly ash as the test powder to illustrate the system performance.
J. M. Veranth, G. Seshadri and
Vehicle-generated
road dust was measured under stable atmospheric conditions at a flat site in
the
Veranth, J. M., D. Gao and G. D. Silcox (1996). “Field Investigation of the Temperature Distribution in a Commercial Hazardous Waste Slagging Rotary Kiln.” Environmental Science and Technology 30(10): 3053-3060.
Gas and bed temperatures were studied in a 4.4–meter–by–12–meter, co-current flow, slagging rotary kiln at a commercial hazardous waste incinerator. The visual observations used by the kiln operators to control the process are described. These observations were quantified using thermocouples, radiation pyrometers, and phase-change indicators. The objectives were to estimate the peak bed temperature and compare this to measurements at the kiln exit. The maximum bed temperature occurs toward the middle of this type of kiln and not at the discharge. The slag melting temperature and test pellets with known melting points indicate that the peak bed temperature can be 100 to 300 K higher than the kiln exit temperature reported by the permanent instruments at this facility. Both broad-band radiation pyrometers and thermocouples give a qualitative temperature indication that can be used for process control, but the readings depend on the sensor locations relative to the incompletely-mixed air and combustion products. Two-color radiation pyrometer measurements of surface temperature near the kiln exit are higher than actual temperature due to reflected radiation. (Figure 5)
Veranth, J. M., G. D. Silcox and D. Pershing (1997). “Numerical Modeling of the Temperature Distribution in a Commercial Hazardous Waste Slagging Rotary Kiln.” Environmental Science and Technology 31: 534-2539.
The gas, wall, and bed temperatures in a hazardous waste incineration kiln were studied using a commercially available, CFD-based, reacting flow code, which included radiation heat transfer. The model was compared to field measurements made on a co-current flow, 35 MW slagging rotary kiln. Cases were run to determine the sensitivity of the predictions to changes in the model assumptions and to simulate the normal variation in combustion inputs. The model predictions of the peak bed temperature, of the axial temperature profile, and of the gas temperature at the exit-plane were consistent with the measurements at a full-scale waste incinerator during normal operation. The model and the field observations both indicate that the peak bed temperature occurs near the middle of the kiln and that the difference between the peak bed temperature and the exit-plane gas temperature depends on the inlet flows. The geometry of the transition between the kiln and the secondary combustion chamber and the fuel-to-air equivalence ratio have the greatest effect on the calculated temperature distribution. Modeling studies provide useful information such as the relationship between available measurements and the temperature at inaccessible locations inside a full-scale kiln. (Figure 3)
Lighty, J. S. and J. M. Veranth (1998). The Role of Research in Practical Incineration Systems — A Look at the Past and the Future. Twenty-Seventh Symposium (International) on Combustion, Boulder, Colorado, The Combustion Institute, Pittsburgh, PA., 1255-1273.
This paper will cover the changes in incineration technology, research, and regulations over the last 10 years. As research understanding has evolved, regulations have become more stringent, and the need for optimized technology has become more critical. Both hazardous waste and municipal waste incineration are discussed. The paper focuses on pollutant minimization, including dioxin and furan work, criteria pollutants, and the impact of solid waste; process upsets; and system simulations. These topics are presented as case studies and, in each area, future needs are discussed. Finally, future directions are addressed.
Veranth, J. M., D. W. Pershing, A. F. Sarofim
and J. E. Shield (1998). Sources of Unburned Carbon in the Fly Ash Produced
from Low-NOx Pulverized Coal Combustion. 27th
Symposium (International) on Combustion,
The unburned carbon in the fly ash produced from low-NOx pulverized coal combustion is shown to consist of a mixture of soot and coal char. The soot was identified by the presence of chains or aggregates of 10—50 nm diameter primary particles in electron microscope images of both laboratory samples and a sample of fly ash from a power plant operating low-NOx burners. Laboratory samples showed increasing carbon content with decreasing nitrogen oxide (NOx) concentration. The experiments included a high-NOx base case and four low-NOx cases consisting of 1) staged combustion with short (0.5 s) residence time 2) staged combustion with long (1.5 s) residence time, 3) a low-NOx burner with slow mixing, and 4) reburning using coal as the reburning fuel. Comparison of the base case which used premixed coal and air with the long residence time staged combustion case shows a decrease in the NOx from over 900 ppm to below 200 ppm and an increase in the carbon in the ash from 4% to over 30%. The fly ash from staged combustion was a mixture of large soot aggregates, porous char, and spherical particles of mineral ash, while the ash from reburning lacked the large aggregates. For all laboratory conditions the carbon content in the particle fraction with an aerodynamic diameter over 10 µm was higher than in the 1—2.5 µm diameter fraction. Both soot aggregates and char contributed to the high carbon in the large particle fraction. The difference in carbon burnout between the two staging conditions was consistent with published soot oxidation rates. Both char burnout and soot formation need to be considered in studies of the carbon content of pulverized coal fly ash.
Veranth, J. M., T. H. Fletcher, D. W. Pershing and A. F. Sarofim (2000). “Measurement of Soot and Char in Pulverized Coal Fly Ash.” Fuel 79(9): 1067-1075.
The unburned carbon in the fly ash produced by low-NOx pulverized coal combustion has been shown by electron microscopy to be a mixture of porous coal char particles and aggregates of submicron particles, which are thought to be soot. A method for determining the mass of these two carbon morphologies by liquid-suspension gravity separation is described. The mass of soot and char was determined for both laboratory-scale and power plant fly ash samples. For low-NOx, staged, pilot-scale combustion of bituminous coal the soot in the furnace exit ash was estimated to be 0.2 to 0.6% of the fuel carbon, which was about 35% of the total unburned carbon.
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