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      Sources of ambient PM 2.5 exposure in 96 global cities

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          Abstract

          To improve air quality, knowledge of the sources and locations of air pollutant emissions is critical. However, for many global cities, no previous estimates exist of how much exposure to fine particulate matter (PM 2.5), the largest environmental cause of mortality, is caused by emissions within the city vs. outside its boundaries. We use the Intervention Model for Air Pollution (InMAP) global-through-urban reduced complexity air quality model with a high-resolution, global inventory of pollutant emissions to quantify the contribution of emissions by source type and location for 96 global cities. Among these cities, we find that the fraction of PM 2.5 exposure caused by within-city emissions varies widely (μ = 37%; σ = 22%) and is not well-explained by surrounding population density. The list of most-important sources also varies by city. Compared to a more mechanistically detailed model, InMAP predicts urban measured concentrations with lower bias and error but also lower correlation. Predictive accuracy in urban areas is not particularly high with either model, suggesting an opportunity for improving global urban air emission inventories. We expect the results herein can be useful as a screening tool for policy options and, in the absence of available resources for further analysis, to inform policy action to improve public health.

          Highlights

          • The contributions of different air pollution sources vary widely among cities.

          • The contributions of within-city vs. external emission sources to a city's air pollution also varies widely among cities.

          • The contributions above cannot be accurately predicted without air quality modeling.

          • An opportunity exists to improve global emission inventories in urban areas.

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          Most cited references31

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          The contribution of outdoor air pollution sources to premature mortality on a global scale.

          Assessment of the global burden of disease is based on epidemiological cohort studies that connect premature mortality to a wide range of causes, including the long-term health impacts of ozone and fine particulate matter with a diameter smaller than 2.5 micrometres (PM2.5). It has proved difficult to quantify premature mortality related to air pollution, notably in regions where air quality is not monitored, and also because the toxicity of particles from various sources may vary. Here we use a global atmospheric chemistry model to investigate the link between premature mortality and seven emission source categories in urban and rural environments. In accord with the global burden of disease for 2010 (ref. 5), we calculate that outdoor air pollution, mostly by PM2.5, leads to 3.3 (95 per cent confidence interval 1.61-4.81) million premature deaths per year worldwide, predominantly in Asia. We primarily assume that all particles are equally toxic, but also include a sensitivity study that accounts for differential toxicity. We find that emissions from residential energy use such as heating and cooking, prevalent in India and China, have the largest impact on premature mortality globally, being even more dominant if carbonaceous particles are assumed to be most toxic. Whereas in much of the USA and in a few other countries emissions from traffic and power generation are important, in eastern USA, Europe, Russia and East Asia agricultural emissions make the largest relative contribution to PM2.5, with the estimate of overall health impact depending on assumptions regarding particle toxicity. Model projections based on a business-as-usual emission scenario indicate that the contribution of outdoor air pollution to premature mortality could double by 2050.
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            Historical (1750–2014) anthropogenic emissions of reactive gases and aerosols from the Community Emissions Data System (CEDS)

            We present a new data set of annual historical (1750–2014) anthropogenic chemically reactive gases (CO, CH 4 , NH 3 , NO x , SO 2 , NMVOCs), carbonaceous aerosols (black carbon – BC, and organic carbon – OC), and CO 2 developed with the Community Emissions Data System (CEDS). We improve upon existing inventories with a more consistent and reproducible methodology applied to all emission species, updated emission factors, and recent estimates through 2014. The data system relies on existing energy consumption data sets and regional and country-specific inventories to produce trends over recent decades. All emission species are consistently estimated using the same activity data over all time periods. Emissions are provided on an annual basis at the level of country and sector and gridded with monthly seasonality. These estimates are comparable to, but generally slightly higher than, existing global inventories. Emissions over the most recent years are more uncertain, particularly in low- and middle-income regions where country-specific emission inventories are less available. Future work will involve refining and updating these emission estimates, estimating emissions' uncertainty, and publication of the system as open-source software.
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              Estimates of global terrestrial isoprene emissions using MEGAN (Model of Emissions of Gases and Aerosols from Nature)

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                Author and article information

                Contributors
                Journal
                Atmos Environ (1994)
                Atmos Environ (1994)
                Atmospheric Environment (Oxford, England : 1994)
                Pergamon
                1352-2310
                1352-2310
                01 October 2022
                01 October 2022
                : 286
                : 119234
                Affiliations
                [a ]Department of Agricultural and Biological Engineering, University of Illinois at Urbana-Champaign, Urbana, IL, United States
                [b ]Department of Environmental and Occupational Health, George Washington University, Washington, DC, United States
                [c ]C40 Cities Climate Leadership Group Inc., New York, NY, United States
                [d ]Department of Mechanical Engineering, University of Colorado, Boulder, CO, United States
                [e ]Orbis Air, LLC, Concord, MA, United States
                [f ]Department of Civil and Environmental Engineering, University of Washington, Seattle, WA, United States
                [g ]Department of Civil and Environmental Engineering, University of Illinois at Urbana-Champaign, Urbana, IL, United States
                Author notes
                []Corresponding author. ctessum@ 123456illinois.edu
                [∗∗ ]Corresponding author. mtessum@ 123456illinois.edu
                Article
                S1352-2310(22)00299-0 119234
                10.1016/j.atmosenv.2022.119234
                9297293
                36193038
                ab3d0f21-fbff-4786-b9ac-76683c5a145f
                © 2022 The Authors

                This is an open access article under the CC BY license (http://creativecommons.org/licenses/by/4.0/).

                History
                : 9 January 2022
                : 3 June 2022
                : 6 June 2022
                Categories
                Article

                environmental policy,fine particulate matter,air quality,pollution,metropolitan,air quality modeling,chemical transport modeling

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