Articles | Volume 25, issue 13
https://doi.org/10.5194/acp-25-7111-2025
© Author(s) 2025. This work is distributed under the Creative Commons Attribution 4.0 License.
Drivers of change in peak-season surface ozone concentrations and impacts on human health over the historical period (1850–2014)
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- Final revised paper (published on 10 Jul 2025)
- Preprint (discussion started on 14 Oct 2024)
Interactive discussion
Status: closed
Comment types: AC – author | RC – referee | CC – community | EC – editor | CEC – chief editor
| : Report abuse
- RC1: 'Comment on egusphere-2024-2732', Anonymous Referee #1, 21 Nov 2024
- RC2: 'Comment on egusphere-2024-2732', Anonymous Referee #2, 02 Dec 2024
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CC1: 'Comment on egusphere-2024-2732', Owen Cooper, 19 Dec 2024
- AC1: 'Reply on CC1', Steven Turnock, 19 Feb 2025
- AC2: 'Author Response to Reviewer Comments on egusphere-2024-2732', Steven Turnock, 19 Feb 2025
Peer review completion
AR – Author's response | RR – Referee report | ED – Editor decision | EF – Editorial file upload
AR by Steven Turnock on behalf of the Authors (19 Feb 2025)
Author's response
Author's tracked changes
Manuscript
ED: Referee Nomination & Report Request started (03 Mar 2025) by John Orlando
RR by Anonymous Referee #2 (06 Mar 2025)
RR by Anonymous Referee #1 (27 Mar 2025)
ED: Publish as is (08 Apr 2025) by John Orlando
AR by Steven Turnock on behalf of the Authors (17 Apr 2025)
A review of egusphere-2024-2732 by Steven Turnock et al.
General Comment:
This paper argues that increases in NOx emissions and CH4 concentrations have played a major role in the historical changes in surface ozone concentrations. Although many previous studies have already shown that these factors have a significant impact on the historical changes in surface ozone, there have been few studies that have analyzed the latest CMIP6 (AerChemMIP) data from this perspective, so to some extent this result is novel. In addition, the authors analyze the health effects of surface ozone changes. Although these results appear to be novel in the same sense, the interpretation of the results is very simplistic and further analysis and discussion of the results are desirable for publication in the journal. I would like the authors to refer to the following comments for revisions.
Major Comment:
The contribution of each driver to historical changes in OSDMA8 is quantitatively estimated in Section 3.2.1. Is it possible to quantitatively estimate the contribution of each driver to health impact in a similar way? With the current descriptions in the manuscript, it is difficult to consistently compare the contribution of each driver to OSDMA8 and its contribution to health impact. If such a comparison could be made, the difference between the impact of each driver on ozone concentration changes and the health impact would be visualized, the factors behind these differences could be discussed further, and suggestions for future countermeasures would become even more meaningful.
Specific Comments:
- Table1: It would be better to more clearly explain what is fixed in each sensitivity scenario. Methane is well described in the caption already, but the other drivers are not clearly explained in the table caption.
- L128: Do all UKESM1 sensitivity experiments use the same initial data?
- L129: heath -> health
- L145-147: The bias correction method for the baseline period should be explained in more detail here. Which was used for the correction: the difference or ratio between RAMP and each model? Did the method correct the 1-hour values and then calculate OSDMA8 or correct the OSDMA8 values directly, etc.?
- L175-177: A brief description is desirable here on the ozone response derived with the method of Wild et al. (2012) using the difference between the equilibrium and prescribed CH4 concentration. Whether the ozone increase or decrease? Are there any regional or temporal characteristics?
- L227: concentration -> remove
- L240-L242: It would be an overstatement that the CMIP6 models have an ability to simulate long-term change in surface ozone based on a comparison at only five remote locations.
- L292: The AF value in Greenland exceeds 10%. Why does it happen where the AF value is quite low at other high latitude regions in the Northern Hemisphere?
- Figure3: Since the average of the three models is mainly discussed in the manuscript, so the average value should also be included in the figure.
- L299: The number in brackets (e.g. 37%) needs an explanation.
- L312-L313: In this experiment, the CH4 concentration is set uniformly within the model domain, but the actual CH4 concentration has a relatively clear difference between the Northern and Southern Hemispheres. How do you think setting the uniform CH4 concentration affects the change in ground-level ozone concentration?
- L348: including -> remove
- L352: Do all models include online calculation of BVOC emissions?
- L354-L355: The UKESM1-0-LL has a smaller ozone sensitivity per unit temperature change (ppb/K) than other models (Zanis et al. 2022), so I guess it is possible that the impact of climate change on OSDMA8 is underestimated in UKESM1-0-LL model. Further discussion on it is desirable here.
- L363: According to the manuscript the sum of individual driver impact on historical OSDMA8 change is 20.4 ppb (8.6+1.5+5.9+0.8+0.8+2.8), and the historical change in OSDMA8 in histSST experiment is 12 ppb (described in L236). I couldn't understand how this number (20% larger) was calculated from these values.
- L377: concs?
- Figure A1: Southern Sub-Saharan Africa is in the wrong colour on the map.