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The Health Effects of Combustion Generated Ultrafine Particles

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Dioxins have a half-life of 7-10 years and are environmentally stable1 ... Figure 2 Graph of an unaged sample against the standard. Abstract ... – PowerPoint PPT presentation

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Title: The Health Effects of Combustion Generated Ultrafine Particles


1
The Health Effects of Combustion Generated
Ultrafine Particles
Angelina Padilla, David Baston, Bing Guo,
Michelle Werner, Cort Anastasio, Michael
Denison, Ian Kennedy Department of Mechanical
Engineering Department of Environmental
Toxicology Department of Atmospheric Science
University of California, Davis, CA 95616
Abstract Dioxin-like compounds, including
polychlorinated dibenzo-p-dioxins, are generated
in combustion processes and can be adsorbed and
transmitted by particulate matter such as soot
particles generated in the combustion processes.
Transformation and/or transportation of the
dioxin-like compounds carried by soot particles
in the earths atmosphere can affect toxicity
levels and have subsequent health effects. In
order to discover the effect of the atmosphere on
polyaromatic hydrocarbons and dioxins transformed
by reactions induced by sunlight and other
factors in the atmosphere, samples were generated
under specific, controlled, combustion conditions
and were analyzed prior-to and after an
atmospheric aging process. In the atmospheric
aging chamber, soot samples were exposed to
controlled levels of ozone, ultraviolet light,
nitric oxides, humidity and a specified pH-value.
All of the samples were analyzed by means of a
bioassay and their corresponding toxicities were
compared. The bioassay demonstrated evidence of
dioxin-like activities in the samples generated
in this experiment.
  • Introduction
  • Reactions of particles in the earths atmosphere
    can have an effect on the toxicity and health
    effects of ultra fine combustion generated
    aerosol particles that might be inhaled by a
    human. Specifically, polyaromatic hydrocarbons
    and dioxins can be transformed by reactions in
    the atmosphere and by sunlight.
  • Dioxins are known to have carcinogenic potential
    1
  • Dioxins have a half-life of 7-10 years and are
    environmentally stable1
  • Hydrocarbons seem to be formed in the
    post-combustion zone due to incomplete
    incineration of chlorinated plastics 2
  • Experimental
  • Burned controlled levels of Methyl chloride in a
    laminar diffusion flame
  • Preliminary results were collected around 2.5
    inches above a propane fueled flame
  • Later results were collected at room temperature
    with a ethylene fueled flame
  • Particles were collected on a Teflon filter for
    a duration of 3 to 4
  • The samples analyzed by means of bioassay (cell
    culture) for four hours
  • Aging of the samples included exposure to
    specified levels of ozone, ultraviolet light,
    nitric oxides, humidity and a specified pH-value
  • Results
  • Preliminary results have both indicated
    dioxin-like activity and no dioxin-like activity.
    Although the data does not demonstrate a clear
    relationship it does imply a decrease in
    dioxin-like activity after aging.
  • Overall the amount of dioxin-like activity is
    low both before and after aging
  • Higher chlorine concentrations yielded greater
    dioxin concentrations
  • Lower chlorine concentrations demonstrated
    negligible results
  • Aging seems to reduce the amount of dioxin-like
    activity
  • The first graph is of a preliminary sample
    against the standard it indicates positive
    results for dioxin-like activity. The second
    graph is of an unaged sample and its
    corresponding aged sample is number 21 in the
    third figure.

Figure 2 Graph of an unaged sample against the
standard.
Standard Curve
Aged sample
Figure 3 Graph of an unaged sample and one aged
sample against the standard.
Acknowledgements Thank you to Professor Kennedy,
Bing Guo, Dave Baston, Mercedes Piedra and the
UCLEADS Program for all of their guidance and
support. Thank you to Hewlett Packard.
Literature Cited 1) Murkerjee, D. Journal of the
Air and Waste Management Association 1998, 48,
157-165. 2) Sidhu, S. S. Maqsud, L. Dellinger,
B. Mascolo, G. Combustion and Flame 1995, 100,
11-20.
Figure 1 Graph of a preliminary sample against
the standard.
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