Abstract

Abstract. The ozone radiative forcings (RFs) resulting from projected changes in climate, ozone-depleting substances (ODSs), non-methane ozone precursor emissions and methane between the years 2000 and 2100 are calculated using simulations from the UM-UKCA chemistry–climate model (UK Met Office's Unified Model containing the United Kingdom Chemistry and Aerosols sub-model). Projected measures to improve air-quality through reductions in non-methane tropospheric ozone precursor emissions present a co-benefit for climate, with a net global mean ozone RF of −0.09 W m−2. This is opposed by a positive ozone RF of 0.05 W m−2 due to future decreases in ODSs, which is driven by an increase in tropospheric ozone through stratosphere-to-troposphere transport of air containing higher ozone amounts. An increase in methane abundance by more than a factor of 2 (as projected by the RCP8.5 scenario) is found to drive an ozone RF of 0.18 W m−2, which would greatly outweigh the climate benefits of non-methane tropospheric ozone precursor reductions. A small fraction (∼ 15 %) of the ozone RF due to the projected increase in methane results from increases in stratospheric ozone. The sign of the ozone RF due to future changes in climate (including the radiative effects of greenhouse gases, sea surface temperatures and sea ice changes) is shown to be dependent on the greenhouse gas emissions pathway, with a positive RF (0.05 W m−2) for RCP4.5 and a negative RF (−0.07 W m−2) for the RCP8.5 scenario. This dependence arises mainly from differences in the contribution to RF from stratospheric ozone changes. Considering the increases in tropopause height under climate change causes only small differences (≤ |0.02| W m−2) for the stratospheric, tropospheric and whole-atmosphere RFs.

Highlights

  • Ozone is a so-called secondary pollutant, being primarily formed by chemical processes within the atmosphere rather than being emitted directly at the surface

  • In a related study focusing on tropical column ozone (Keeble et al, 2017), we find that the change in lower stratospheric ozone scales more strongly with greenhouse gas (GHG) concentration than the change in upper stratospheric ozone: |0.03| vs. |0.02| DU ppmv−1 CO2equivalent, where CO2-equivalent is the concentration of CO2 that would cause the same radiative forcings (RFs) as the mixture of all well-mixed greenhouse gases (WMGHGs)

  • We have focused on the contributions from changes in stratospheric and tropospheric ozone between year 2000 and 2100 due to changes in (i) the physical climate state; (ii) the chemical effects of ozone depleting substances (ODSs); (iii) the chemical effects of non-methane ozone precursor emissions; and (iv) the chemical effects of CH4

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Summary

Introduction

Ozone is a so-called secondary pollutant, being primarily formed by chemical processes within the atmosphere rather than being emitted directly at the surface. Emissions-based estimates of pre-industrial to near present-day (1750–2011) ozone RFs (with 5–95 % confidence ranges) are −0.15 (−0.30 to 0.00) W m−2 due to ODSs and 0.50 (0.30 to 0.70) W m−2 due to ozone precursors (Myhre et al, 2013). This can be compared to a WMGHG forcing of 2.83 (2.54 to 3.12) W m−2 over the same period (Myhre et al, 2013).

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