There is growing interest to move beyond fine particle mass concentrations (PM 2.5 ) when evaluating the population health impacts of outdoor air pollution. However, few exposure models are currently available to support such analyses. In this study, we conducted large-scale monitoring campaigns across Montreal and Toronto, Canada during summer 2018 and winter 2019 and developed models to predict spatial variations in (1) the ability of PM 2.5 to generate reactive oxygen species in the lung fluid (ROS), (2) PM 2.5 oxidative potential based on the depletion of ascorbate (OP AA ) and glutathione (OP GSH ) in a cell-free assay, and (3) anhysteretic magnetic remanence (X ARM ) as an indicator of magnetite nanoparticles. We also examined how exposure to PM oxidative capacity metrics (ROS/OP) varied by socioeconomic status within each city. In Montreal, areas with higher material deprivation, indicating lower area-level average household income and employment, were exposed to PM 2.5 characterized by higher ROS and OP. This relationship was not observed in Toronto. The developed models will be used in epidemiologic studies to assess the health effects of exposure to PM 2.5 and iron-rich magnetic nanoparticles in Toronto and Montreal.
Disparities in exposure to traffic-related air pollution
have been
widely reported. However, little work has been done to simultaneously
assess the impact of various vehicle types on populations of different
socioeconomic/ethnic backgrounds. In this study, we employed an extreme
gradient-boosting approach to spatially distribute light-duty vehicle
(LDV) and heavy-duty truck emissions across the city of Toronto from
2006 to 2020. We examined associations between these emissions and
different marginalization indices across this time span. Despite a
large decrease in traffic emissions, disparities in exposure to traffic-related
air pollution persisted over time. Populations with high residential
instability, high ethnic concentration, and high material deprivation
were found to reside in regions with significantly higher truck and
LDV emissions. In fact, the gap in exposure to traffic emissions between
the most residentially unstable populations and the least residentially
unstable populations worsened over time, with trucks being the larger
contributor to these disparities. Our data also indicate that the
number of trucks and truck emissions increased substantially between
2019 and 2020 whilst LDVs decreased. Our results suggest that improvements
in vehicle emission technologies are not sufficient to tackle disparities
in exposure to traffic-related air pollution.
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