Abstract

[1] Air pollution (ozone and particulate matter in surface air) is strongly linked to synoptic weather and thus is likely sensitive to climate change. In order to isolate the responses of air pollutant transport and wet removal to a warming climate, we examine a simple carbon monoxide–like (CO) tracer (COt) and a soluble version (SAt), both with the 2001 CO emissions, in simulations with the Geophysical Fluid Dynamics Laboratory chemistry-climate model (AM3) for present (1981–2000) and future (2081–2100) climates. In 2081–2100, projected reductions in lower-tropospheric ventilation and wet deposition exacerbate surface air pollution as evidenced by higher surface COt and SAt concentrations. However, the average horizontal general circulation patterns in 2081–2100 are similar to 1981–2000, so the spatial distribution of COt changes little. Precipitation is an important factor controlling soluble pollutant wet removal, but the total global precipitation change alone does not necessarily indicate the sign of the soluble pollutant response to climate change. Over certain latitudinal bands, however, the annual wet deposition change can be explained mainly by the simulated changes in large-scale (LS) precipitation. In regions such as North America, differences in the seasonality of LS precipitation and tracer burdens contribute to an apparent inconsistency of changes in annual wet deposition versus annual precipitation. As a step toward an ultimate goal of developing a simple index that can be applied to infer changes in soluble pollutants directly from changes in precipitation fields as projected by physical climate models, we explore here a “Diagnosed Precipitation Impact” (DPI) index. This index captures the sign and magnitude (within 50%) of the relative annual mean changes in the global wet deposition of the soluble pollutant. DPI can only be usefully applied in climate models in which LS precipitation dominates wet deposition and horizontal transport patterns change little as climate warms. Our findings support the need for tighter emission regulations, for both soluble and insoluble pollutants, to obtain a desired level of air quality as climate warms.

Highlights

  • [2] Air quality is influenced by meteorological conditions and could be sensitive to climate change [e.g., Denman et al, 2007]

  • [3] Most General Circulation Model (GCM) and Chemical Transport Model (CTM) studies of the impact of climate change on air pollutants focus on ozone (O3) and particulate matter (PM) because these two species are of most concern for human health and directly affect both air quality and atmospheric radiative forcing [e.g., Jacob and Winner, 2009]

  • Racherla and Adams [2006] showed that a lower PM burden corresponds to an increase in global precipitation in a future climate, Pye et al [2009] indicated that changes in precipitation are not always the governing factor for PM concentrations

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Summary

Introduction

[2] Air quality is influenced by meteorological conditions and could be sensitive to climate change [e.g., Denman et al, 2007]. Jacob and Winner [2009] argued that precipitation frequency is likely the dominant factor determining PM concentration changes Such disparate results in the literature motivate our investigation into the impact of changing precipitation on soluble pollutants in a warmer climate. They find that interhemispheric exchange times, mixing times, and mean transit times all increase under global warming by about 10% from 1990 to 2000 to 2090–2100, but they consider only advection and diffusion and neglect wet deposition and convection Their tracers have localized (rather than distributed) sources, permitting the identification of transport pathways from specific locations while precluding examination of the impact of spatial patterns in precipitation and ventilation changes over polluted regions.

Methods
Psnow Á snow Rsnow Ásnow
Pf Pf
As mentioned in section
Findings
Conclusions
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