Articles | Volume 25, issue 23
https://doi.org/10.5194/acp-25-17889-2025
© Author(s) 2025. This work is distributed under the Creative Commons Attribution 4.0 License.
Pathway-specific responses of isoprene-derived secondary organic aerosol formation to anthropogenic emission reductions in a megacity in eastern China
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- Final revised paper (published on 08 Dec 2025)
- Supplement to the final revised paper
- Preprint (discussion started on 15 May 2025)
- Supplement to the preprint
Interactive discussion
Status: closed
Comment types: AC – author | RC – referee | CC – community | EC – editor | CEC – chief editor
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RC1: 'Comment on egusphere-2025-1909', Anonymous Referee #1, 18 Jul 2025
- AC1: 'Reply on RC1', Yue Zhao, 10 Sep 2025
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RC2: 'Comment on egusphere-2025-1909', Anonymous Referee #2, 18 Jul 2025
- AC2: 'Reply on RC2', Yue Zhao, 10 Sep 2025
Peer review completion
AR – Author's response | RR – Referee report | ED – Editor decision | EF – Editorial file upload
AR by Yue Zhao on behalf of the Authors (11 Sep 2025)
Author's response
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ED: Publish as is (29 Oct 2025) by Jason Surratt
AR by Yue Zhao on behalf of the Authors (31 Oct 2025)
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AA – Author's adjustment | EA – Editor approval
AA by Yue Zhao on behalf of the Authors (27 Nov 2025)
Author's adjustment
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EA: Adjustments approved (05 Dec 2025) by Jason Surratt
This study presents measurements of isoprene and its SOA products in Shanghai across summer and wintertime in 2015, 2019, 2021. The study examines isoprene SOA response to emissions reductions, particularly the hydroperoxy pathway (IEPOX-SOA) and NOx-dominated pathway (HMML, MAE). CMAQ modeling captures some trends in experimental data, including a decreasing IEPOX-SOA over the study period. The study concludes that emissions reductions can decrease biogenic SOA in urban areas, and that a deeper understanding of isoprene-derived SOA is needed.
I have major technical concerns about the manuscript that should be addressed prior to reconsideration for publication. Additionally, there are numerous opportunities for more thorough comparisons of the modeled and experimental data. Similarly, there is opportunity for thorough and meaningful comparisons of the current study to literature more specific to urban areas.
a. Recent work demonstrates that use of reversed phase liquid chromatography (RPLC) with mass spectrometry (MS) can caused significant underestimation of some isoprene-derived organosulfates (OS) with little retention on reversed phase LC columns (Liang et al. 2025, pubs.acs.org/doi/10.1021/acs.est.5c01846). OS co-elute from the RPLC column with sulfate and other inorganic ions, which can suppress OS signal. Changes to the aerosol matrix can thus be misinterpreted as changes in OS concentrations. Because the author’s OS measurement method is likely subject to matrix suppression, there is concern about the validity of the OS concentrations and relative ratios presented in this study.
b. There are additional concerns about C5 alkene-triols being artifacts of gas chromatography (GC) MS analysis (Frauenheim, et al. doi/10.1021/acs.estlett.2c00548). The extent to which these may be artifacts in the current study should be considered, especially following the result that they are the dominant product observed by GCMS.
c. Taken together, the suppression of OS and potential artifact formation of C5 alkene triols raises questions to the validity of the paragraph that discusses “the dominance of iSOA polyol tracers over OS tracers…” With one signal being enhanced and the other suppressed, such comparisons have very large uncertainties.
d. The potential for bias in measurements mentioned should be thoroughly considered and discussed in downstream calculations and comparisons, including SOA estimates, relative ratios of isoprene SOA products, correlation analysis, model comparisons, etc.
e. The current treatment of matrix effects is insufficient at lines 221-225. While the expected extent of matrix effects may be informative, correction factors are not valid across studies. The authors must discuss the relevance of the sample matrix in the study by Bryant et al. (2021) and their work. Similarly, it is not a valid approach to extrapolate relative ionization efficiencies observed by others (i.e. Bryant et al. (2021, line 169)) across studies, because ionization changes day-to-day within an instrument, and depends upon specific instrumental conditions and mobile phase composition. Ratios of relative responses are reported to 2-3 significant figures at lines 169-173, while in reality these estimates are known with much less certainty.
a. Extend Figure 2 be expanded to also show PM2.5 mass, OC (or OM), sulfate, nitrate, and other relevant PM component or atmospheric parameters (NOx, O3). This would be a useful way to provide context for understanding changes in isoprene SOA that are discussed subsequently.
b. In figures 6 and 7, include experimental data be for comparison to modeled values.
c. Also in figures 6 and 7 – the x-axis labels are confusing. Can they be simplified?