Abstract

Ambient air pollution from ground-level ozone and fine particulate matter (PM2.5) is associated with premature mortality. Future concentrations of these air pollutants will be driven by natural and anthropogenic emissions and by climate change. Using anthropogenic and biomass burning emissions projected in the four Representative Concentration Pathway scenarios (RCPs), the ACCMIP ensemble of chemistry-climate models simulated future concentrations of ozone and PM2.5 at selected decades between 2000 and 2100. We use output from the ACCMIP ensemble, together with projections of future population and baseline mortality rates, to quantify the human premature mortality impacts of future ambient air pollution. Future air pollution-related premature mortality in 2030, 2050 and 2100 is estimated for each scenario and for each model using a health impact function based on changes in concentrations of ozone and PM2.5 relative to 2000 and projected future population and baseline mortality rates. Additionally, the global mortality burden of ozone and PM2.5 in 2000 and each future period is estimated relative to 1850 concentrations, using present-day and future population and baseline mortality rates. The change in future ozone concentrations relative to 2000 is associated with excess global premature mortality in some scenarios/periods, particularly in RCP8.5 in 2100 (316 thousand deaths/year), likely driven by the large increase in methane emissions and by the net effect of climate change projected in this scenario, but it leads to considerable avoided premature mortality for the three other RCPs. However, the global mortality burden of ozone markedly increases from 382,000 (121,000 to 728,000) deaths/year in 2000 to between 1.09 and 2.36 million deaths/year in 2100, across RCPs, mostly due to the effect of increases in population and baseline mortality rates. PM2.5 concentrations decrease relative to 2000 in all scenarios, due to projected reductions in emissions, and are associated with avoided premature mortality, particularly in 2100: between -2.39 and -1.31 million deaths/year for the four RCPs. The global mortality burden of PM2.5 is estimated to decrease from 1.70 (1.30 to 2.10) million deaths/year in 2000 to between 0.95 and 1.55 million deaths/year in 2100 for the four RCPs, due to the combined effect of decreases in PM2.5 concentrations and changes in population and baseline mortality rates. Trends in future air pollution-related mortality vary regionally across scenarios, reflecting assumptions for economic growth and air pollution control specific to each RCP and region. Mortality estimates differ among chemistry-climate models due to differences in simulated pollutant concentrations, which is the greatest contributor to overall mortality uncertainty for most cases assessed here, supporting the use of model ensembles to characterize uncertainty. Increases in exposed population and baseline mortality rates of respiratory diseases magnify the impact on premature mortality of changes in future air pollutant concentrations and explain why the future global mortality burden of air pollution can exceed the current burden, even where air pollutant concentrations decrease.

Highlights

  • Ambient air pollution has adverse effects on human health, including premature mortality

  • We find that future changes in ozone concentrations are associated with excess global premature mortality due to respiratory diseases in 2030 but avoided mortality by 2100 for all scenarios but RCP8.5 (Fig. 1, Table S5)

  • In all Representative Concentration Pathway scenarios (RCPs) scenarios but RCP8.5, stringent air pollution controls lead to substantial decreases in ozone concentrations through the 21st century, relative to 2000

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Summary

Introduction

Ambient air pollution has adverse effects on human health, including premature mortality. Previous studies have estimated the present-day global burden of disease due to exposure to ambient ozone and/or PM2.5 (e.g., Apte et al, 2015; Evans et al, 2013; Forouzanfar et al, 2015), with several studies estimating this burden using only output of global atmospheric models (Anenberg et al, 2010; Fang et al, 2013a; Lelieveld et al, 2013; Rao et al, 2012; Silva et al, 2013). Studies at local and regional scales have evaluated the mortality impact of changes in air quality due to future climate change (Bell et al, 2007; Chang et al, 2010; Fann et al, 2015; Heal et al, 2012; Jackson et al, 2010; Knowlton et al, 2004, 2008; Orru et al, 2013; Post et al, 2012; Sheffield et al, 2011; Tagaris et al, 2009) but few such studies have evaluated changes beyond 2050

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