Community time-series epidemiology typically uses either
24-hour integrated particulate matter (PM) concentrations
averaged across several monitors in a city or data
obtained at a central monitoring site to relate PM concentra
tions to human health effects. If the day-to-day variations
in 24-hour integrated concentrations differ substantially
across an urban area (i.e., daily measurements at monitors
at different locations are not highly correlated), then
there is a significant potential for exposure misclassification
in community time-series epidemiology. If the annual
average concentration differs across an urban area, then
there is a potential for exposure misclassification in
epidemiologic studies that use annual averages (or multi-year averages) as an index of exposure across different
cities. The spatial variability in PM2.5 (particulate matter ≤
2.5 μm in aerodynamic diameter), its elemental components,
and the contributions from each source category at 10
monitoring sites in St. Louis, Missouri were characterized
using the ambient PM2.5 compositional data set of the
Regional Air Pollution Study (RAPS) based on the Regional
Air Monitoring System (RAMS) conducted between 1975
and 1977. Positive matrix factorization (PMF) was applied to
each ambient PM2.5 compositional data set to estimate
the contributions from the source categories. The spatial
distributions of components and source contributions to PM2.5
at the 10 sites were characterized using Pearson
correlation coefficients and coefficients of divergence.
Sulfur and PM2.5 are highly correlated elements between
all of the site pairs Although the secondary sulfate is the most
highly correlated and shows the smallest spatial variability,
there is a factor of 1.7 difference in secondary sulfate
contributions between the highest and lowest site on average.
Motor vehicles represent the next most highly correlated
source component. However, there is a factor of 3.6 difference
in motor vehicle contributions between the highest and
lowest sites. The contributions from point source categories
are much more variable. For example, the contributions
from incinerators show a difference of a factor of 12.5 between
the sites with the lowest and highest contributions. This
study demonstrates that the spatial distributions of elemental
components of PM2.5 and contributions from source
categories can be highly heterogeneous within a given
airshed and thus, there is the potential for exposure
misclassification when a limited number of ambient PM
monitors are used to represent population-average ambient
exposures