Articles | Volume 19, issue 17
https://doi.org/10.5194/gmd-19-8447-2026
© Author(s) 2026. This work is distributed under the Creative Commons Attribution 4.0 License.
Integrating ozone–vegetation damage schemes into SSiB4/TRIFFID: evaluation of six parameterizations and refinement of ozone decay process across plant functional types
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- Final revised paper (published on 10 Sep 2026)
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Comment types: AC – author | RC – referee | CC – community | EC – editor | CEC – chief editor
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RC1: 'Comment on egusphere-2026-1335', Anonymous Referee #1, 24 Apr 2026
- AC1: 'Reply on RC1', Lingfeng Li, 09 Jun 2026
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RC2: 'Comment on egusphere-2026-1335', Anonymous Referee #2, 16 May 2026
- AC2: 'Reply on RC2', Lingfeng Li, 09 Jun 2026
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AR – Author's response | RR – Referee report | ED – Editor decision | EF – Editorial file upload
AR by Lingfeng Li on behalf of the Authors (09 Jun 2026)
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ED: Referee Nomination & Report Request started (08 Jul 2026) by Amos Tai
RR by Anonymous Referee #2 (27 Jul 2026)
RR by Anonymous Referee #1 (03 Aug 2026)
ED: Publish subject to minor revisions (review by editor) (08 Aug 2026) by Amos Tai
AR by Lingfeng Li on behalf of the Authors (17 Aug 2026)
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ED: Publish as is (31 Aug 2026) by Amos Tai
AR by Lingfeng Li on behalf of the Authors (31 Aug 2026)
Li et al. “Integrating Ozone-vegetation Damage Schemes into SSiB4/TRIFFID: Evaluation of Six Parameterizations and Refinement of Ozone Decay Process Across Plant Functional Types”
This study incorporates six ozone–vegetation damage parameterizations into the SSiB4/TRIFFID model and systematically evaluates ozone-induced reductions in GPP across China. Estimated GPP losses range from 15% to 31% across schemes. Benchmarking against observational ozone sensitivity indicates that the L2024 and LMA-based schemes perform relatively better. Moreover, refining the L2024 scheme to better represent the decay of cumulative ozone damage across plant functional types improves the spatiotemporal fidelity of GPP simulations. The topic of this study is helpful for the development of ozone vegetation damage scheme. However, some issues need to be addressed before the study can be considered for publication in GMD.
GENERAL
First, the key characteristics and differences among the six ozone damage schemes are not clearly presented. The authors introduce L2015, L2024, S2007, CS2007, LMAgrid, and LMApft separately in the methods, but a side-by-side comparison is missing. For example, which metric (CUO, PODy, or instantaneous ozone uptake) does each scheme rely on? Are the effects on photosynthesis and stomatal conductance treated in a coupled or decoupled manner? Is CS2007 simply a recalibrated version of S2007 with lower ozone damage sensitivity coefficients and a simplified treatment for three PFTs? The distinction between LMAgrid and LMApft is also unclear. Including a summary table in the methods that highlights the essential features and differences of all six schemes would greatly improve clarity.
Second, the conceptual framework regarding ozone dose metrics is confusing, and the distinction between mechanistic use and analytical use is not properly addressed. The authors employ three concepts – PODy (Phytotoxic Ozone Dose over a threshold of y), CUO (Cumulative Uptake of Ozone), and instantaneous ozone uptake -- without clearly defining or differentiating them. The description confuses PODy with CUO, and the relationship between PODy and instantaneous uptake is not explained. In the results, the authors introduce a dose-response analysis between GPP and ozone, in which the simulated annual cumulative stomatal ozone uptake is directly defined as PODy. The authors should clarify the physical meaning of each metric and specify how each is used in the research.
Third, the description of the original L2024 scheme is misleading, and the true contribution of the authors’ proposed improvement remains unclear. Section 2.2 describes L2024 as a PODy-dependent scheme, but Section 2.3.2 introduces CUO when discussing the modification of the ozone decay process, creating an inconsistency. Moreover, the claim that extending the decay process to all PFTs is an improvement is problematic: in the original L2024 (Eq. 5 in Li et al., 2024), the decay process already applies to all PFTs (leaf longevity for evergreens, LAI change for deciduous plants). Thus, this is not an innovation of the present study. Similar issues appear in the description of the Ma et al. (2023) schemes (see specific comments). The authors should clearly distinguish between parameter updates and structural improvements, and accurately restate their own contribution.
SPECIFIC
Throughout the abstract, main text, captions, and supplementary materials, there are multiple formatting errors: inconsistent terms for ‘O3’ or ‘ozone’, and/or missing subscripts. Please check each instance carefully. In addition, please standardize the format of dashes ‘-’ throughout the manuscript.
Line 47: NOx subscript.
Lines 83-86: Reference format errors. Are the re-calibrated S2007 and LMA schemes from the same paper? The sentence is unclear.
Line 121: H2O (m s-1) font error. Please check similar issues throughout this section.
Line 122: Missing period ‘.’
Line 127: FO3_A and FO3_g do not match the formulas.
Line 146: Typo: ‘O3-modification‘.
Line 157: Could be more explicit: ‘stomatal flux-based O3 damage framework‘.
Line 164: Ambiguous wording. The sentence ‘Following Feng et al. (2018), we set x = 0.019 based on the observations’ is from the scheme setting of Ma et al. (2023). The distinction between LMAgrid and LMApft is unclear; they differ in LMA format and α.
Line 170: Abbreviation not used (many such errors throughout; please check).
Line 172: Missing subscript (many such errors throughout).
Table 2: The L2024modify scheme could also be included.
Line 262: The sentence ‘Figure 1 shows... are shown in the supplementary materials (Fig. S4)’ is unclear. Please rephrase.
Figure 2: Why was GOSIF chosen for spatial validation but not FLUXCOM? Are panels (a), (b), (c) for the whole year or growing season? Experiment names in figures should match the main text (e.g., ‘O3OFF’ vs ‘O3 OFF’, ‘O3ON’ vs ‘O3 ON’). Please check all figures.
Figure 3: Why the inter-scheme difference have just one value instead of six?
Figure 4: Why does L2024 show the strongest GPP damage in Fig. 4 but not the strongest LAI damage in Fig. S7? Similarly, why does LMApft show the strongest GPP damage in southeastern China (f) but no corresponding LAI damage? Is this related to how GPP and LAI are calculated in the model? Could absolute and relative damage values be marked on the figures? Figure caption is separated from the figure.
Figure 5: Are these results for China or globally? Growing season or annual? Please clarify in each caption. The x-axis has errors.
Figure 5 clearly shows the relationship between RGPP and PODy. Figures 6 and 7 discuss ‘ozone sensitivity’ based on this relationship. However, the captions of Figures 6 and 7 do not explicitly state that sensitivity refers to the slope in Figure 5. Please clarify to avoid confusion.
Lines 319-326: Could the mismatch between stomatal ozone uptake and GPP damage across schemes be further explained? For example, L2015 decouples these two calculations.
Line 328: The explanation of RGPP has already been given above.
Line 418: Does the observational ozone sensitivity for each PFT attributed to Li et al. (2024) in Figure 6 correspond to the slopes calculated in Figure S3? This could be clarified.
Lines 425-426: The criticism of S2007 in the discussion is not accurate, as S2007 may have biases in sensitivity parameters instead of problems in the physical mechanisms.