The co-benefits of a low-carbon future for PM<sub>2.5</sub> and O<sub>3</sub> air pollution in Europe

<p>There is considerable academic interest in the potential for air quality improvement as a co-benefit of climate change mitigation. Few studies use regional air quality models for simulating future co-benefits, but many use global chemistry–climate model output. Using regional atmospheric ch...

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Main Authors: C. J. Clayton, D. R. Marsh, S. T. Turnock, A. M. Graham, K. J. Pringle, C. L. Reddington, R. Kumar, J. B. McQuaid
Format: Article
Language:English
Published: Copernicus Publications 2024-09-01
Series:Atmospheric Chemistry and Physics
Online Access:https://acp.copernicus.org/articles/24/10717/2024/acp-24-10717-2024.pdf
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author C. J. Clayton
D. R. Marsh
S. T. Turnock
S. T. Turnock
A. M. Graham
K. J. Pringle
C. L. Reddington
R. Kumar
J. B. McQuaid
author_facet C. J. Clayton
D. R. Marsh
S. T. Turnock
S. T. Turnock
A. M. Graham
K. J. Pringle
C. L. Reddington
R. Kumar
J. B. McQuaid
author_sort C. J. Clayton
collection DOAJ
description <p>There is considerable academic interest in the potential for air quality improvement as a co-benefit of climate change mitigation. Few studies use regional air quality models for simulating future co-benefits, but many use global chemistry–climate model output. Using regional atmospheric chemistry could provide a better representation of air quality changes than global chemistry–climate models, especially by improving the representation of elevated urban concentrations. We use a detailed regional atmospheric-chemistry model (WRF-Chem v4.2) to model European air quality in 2050 compared to 2014 following three climate change mitigation scenarios. We represent different climate futures by using air pollutant emissions and chemical boundary conditions (from CESM2-WACCM output) for three shared socioeconomic pathways (SSP1-2.6, SSP2-4.5 and SSP3-7.0: high-, medium- and low-mitigation pathways respectively).</p> <p>We find that in 2050, following SSP1-2.6, mean population-weighted PM<span class="inline-formula"><sub>2.5</sub></span> concentrations across European countries are reduced by 52 % compared to 2014. Under SSP2-4.5, this average reduction is 34%. The smallest average reduction is 18 %, achieved following SSP3-7.0. Maximum 6-monthly-mean daily-maximum 8 h (6mDM8h) ozone (O<span class="inline-formula"><sub>3</sub></span>) is reduced across Europe by 15 % following SSP1-2.6 and by 3 % following SSP2-4.5, but it increases by 13 % following SSP3-7.0. This demonstrates clear co-benefits of climate mitigation. The additional resolution allows us to analyse regional differences and identify key sectors. We find that the mitigation of agricultural emissions will be key for attaining meaningful co-benefits of mitigation policies, as evidenced by the importance of changes in NO<span class="inline-formula"><sub>3</sub></span> aerosol mass to future PM<span class="inline-formula"><sub>2.5</sub></span> air quality and changes in CH<span class="inline-formula"><sub>4</sub></span> emissions to future O<span class="inline-formula"><sub>3</sub></span> air quality.</p>
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spelling doaj-art-c4f57c0bc7d84ceb906de71259ce869e2025-08-20T01:55:02ZengCopernicus PublicationsAtmospheric Chemistry and Physics1680-73161680-73242024-09-0124107171074010.5194/acp-24-10717-2024The co-benefits of a low-carbon future for PM<sub>2.5</sub> and O<sub>3</sub> air pollution in EuropeC. J. Clayton0D. R. Marsh1S. T. Turnock2S. T. Turnock3A. M. Graham4K. J. Pringle5C. L. Reddington6R. Kumar7J. B. McQuaid8Institute of Climate and Atmospheric Science, University of Leeds, Woodhouse, Leeds, LS2 9JT, United KingdomSchool of Physics and Astronomy, University of Leeds, Woodhouse, Leeds, LS2 9JT, United KingdomMet Office Hadley Centre, Fitzroy Rd, Exeter EX1 3PB, United KingdomMet Office Strategic (LUMOS) Research Group, University of Leeds, Woodhouse, Leeds, LS2 9JT, United KingdomInstitute of Climate and Atmospheric Science, University of Leeds, Woodhouse, Leeds, LS2 9JT, United KingdomSustainable Software Institute, University of Edinburgh, Old College, South Bridge, Edinburgh, EH8 9YL, United KingdomInstitute of Climate and Atmospheric Science, University of Leeds, Woodhouse, Leeds, LS2 9JT, United KingdomNational Center for Atmospheric Research, 1850 Table Mesa Dr, Boulder, CO 80305, USAInstitute of Climate and Atmospheric Science, University of Leeds, Woodhouse, Leeds, LS2 9JT, United Kingdom<p>There is considerable academic interest in the potential for air quality improvement as a co-benefit of climate change mitigation. Few studies use regional air quality models for simulating future co-benefits, but many use global chemistry–climate model output. Using regional atmospheric chemistry could provide a better representation of air quality changes than global chemistry–climate models, especially by improving the representation of elevated urban concentrations. We use a detailed regional atmospheric-chemistry model (WRF-Chem v4.2) to model European air quality in 2050 compared to 2014 following three climate change mitigation scenarios. We represent different climate futures by using air pollutant emissions and chemical boundary conditions (from CESM2-WACCM output) for three shared socioeconomic pathways (SSP1-2.6, SSP2-4.5 and SSP3-7.0: high-, medium- and low-mitigation pathways respectively).</p> <p>We find that in 2050, following SSP1-2.6, mean population-weighted PM<span class="inline-formula"><sub>2.5</sub></span> concentrations across European countries are reduced by 52 % compared to 2014. Under SSP2-4.5, this average reduction is 34%. The smallest average reduction is 18 %, achieved following SSP3-7.0. Maximum 6-monthly-mean daily-maximum 8 h (6mDM8h) ozone (O<span class="inline-formula"><sub>3</sub></span>) is reduced across Europe by 15 % following SSP1-2.6 and by 3 % following SSP2-4.5, but it increases by 13 % following SSP3-7.0. This demonstrates clear co-benefits of climate mitigation. The additional resolution allows us to analyse regional differences and identify key sectors. We find that the mitigation of agricultural emissions will be key for attaining meaningful co-benefits of mitigation policies, as evidenced by the importance of changes in NO<span class="inline-formula"><sub>3</sub></span> aerosol mass to future PM<span class="inline-formula"><sub>2.5</sub></span> air quality and changes in CH<span class="inline-formula"><sub>4</sub></span> emissions to future O<span class="inline-formula"><sub>3</sub></span> air quality.</p>https://acp.copernicus.org/articles/24/10717/2024/acp-24-10717-2024.pdf
spellingShingle C. J. Clayton
D. R. Marsh
S. T. Turnock
S. T. Turnock
A. M. Graham
K. J. Pringle
C. L. Reddington
R. Kumar
J. B. McQuaid
The co-benefits of a low-carbon future for PM<sub>2.5</sub> and O<sub>3</sub> air pollution in Europe
Atmospheric Chemistry and Physics
title The co-benefits of a low-carbon future for PM<sub>2.5</sub> and O<sub>3</sub> air pollution in Europe
title_full The co-benefits of a low-carbon future for PM<sub>2.5</sub> and O<sub>3</sub> air pollution in Europe
title_fullStr The co-benefits of a low-carbon future for PM<sub>2.5</sub> and O<sub>3</sub> air pollution in Europe
title_full_unstemmed The co-benefits of a low-carbon future for PM<sub>2.5</sub> and O<sub>3</sub> air pollution in Europe
title_short The co-benefits of a low-carbon future for PM<sub>2.5</sub> and O<sub>3</sub> air pollution in Europe
title_sort co benefits of a low carbon future for pm sub 2 5 sub and o sub 3 sub air pollution in europe
url https://acp.copernicus.org/articles/24/10717/2024/acp-24-10717-2024.pdf
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