Mj. Kleeman et Gr. Cass, SOURCE CONTRIBUTIONS TO THE SIZE AND COMPOSITION DISTRIBUTION OF URBAN PARTICULATE AIR-POLLUTION, Atmospheric environment, 32(16), 1998, pp. 2803-2816
A mechanistic air quality model has been constructed which is capable
of predicting the contribution of individual emissions source types to
the size- and chemical-composition distribution of airborne particles
. This model incorporates all of the major aerosol processes relevant
to regional air pollution studies including emissions, transport, depo
sition, gas-to-particle conversion and fog chemistry. In addition, the
aerosol is represented as a source-oriented external mixture which is
allowed to age in a more realistic fashion than can be accomplished w
hen fresh particle-phase emissions are averaged into the pre-existing
atmospheric aerosol size and composition distribution. A source-orient
ed external mixture is created by differentiating the primary particle
s emitted from the following source types: catalyst-equipped gasoline
engines, non-catalyst-equipped gasoline engines, diesel engines, meat
cooking, paved road dust, crustal material from sources other than pav
ed road dust, and sulfur-bearing particles from fuel burning and indus
trial processes. Discrete primary Seed particles from each of these so
urce types are emitted into a simulation of atmospheric transport and
chemical reaction. The individual particles evolve over time in the pr
esence of gas-to-particle conversion processes while retaining informa
tion on the initial source from which they were emitted. The source- a
nd age-resolved particle mechanics model is applied to the 1987 August
SCAQS episode and comparisons are made between model predictions and
observations at Claremont, CA. The model explains the origin of the bi
modal character of the sub-micron aerosol size distribution. The mode
located between 0.2 and 0.3 mu m particle diameter is shaped by transf
ormed emissions from diesel engines and meat cooking operations with l
esser contributions from gasoline-powered vehicles and other fuel burn
ing. The larger mode located at 0.7-0.8 mu m particle diameter is due
to fine particle background aerosol that has been further transformed
by fog and by other gas-to-particle conversion processes. Smaller cont
ributions to the mode located at 0.7-0.8 mu m particle diameter are ma
de by food cooking and by the fine particle fraction of paved and unpa
ved road dust. Separation of the contributions of particles from diffe
rent sources helps to visualize the effect that different emissions co
ntrol programs would have in advance of their adoption. (C) 1998 Elsev
ier Science Ltd. All rights reserved.