the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Global natural wetland methane emissions (2000–2025)
Abstract. Wetlands are the largest natural source of atmospheric methane (CH4), yet comprehensive global budgets are typically delayed by several years, preventing a timely understanding of CH4 sources, sinks, and their trends. To reduce this delay, we present a model emulator-driven framework and accompanying workflow that enable timely, continuous emission updates and applying the framework to a global dataset of natural vegetated wetland CH4 emissions to extend the most recent Global Methane Budget (GMB; Saunois et al., 2025) record through 2025 at monthly 1°x1° resolution. We developed a machine-learning emulator to reconstruct spatially explicit monthly emission fields (global R2 =0.65 ± 0.003 (mean ± 95 % CI, hereafter) and RMSE=5.49 ± 0.12 ×10-3 Tg CH4/year in test data which is ~30 % of the total data). The emulator is trained on 35 GMB model estimates (22 process-based model estimates and 13 atmospheric inversion estimates) paired with 10 ensemble realizations of 11 gridded climate predictor variables from atmospheric reanalyses. While the global mean predicted wetland CH4 emissions for 2021–2025 (157.83 ± 2.38 Tg CH4/year) are only marginally higher (~0.05 Tg CH4/year) than the 2000–2020 baseline, this stability masks a significant hemispheric redistribution of emissions. We detect a surge in Northern Hemisphere emissions in 2021–2025, with mid- and high-latitudes increasing by 0.76 ± 0.07 (z-score: 2.21) and 0.35 ± 0.03 Tg/year (z-score:1.01), respectively, while the tropics and Southern Hemisphere extratropics show offsetting negative trends (-0.95 ± 0.19 and -0.11 ± 0.02 Tg/year with z-scores of -2.81 and -0.34, respectively). The predicted emissions capture the low emissions in 2023 in South America linked to El Niño-related drought, as reported by recent studies (Ciais et al., 2026; Quinn et al., 2025). Post-2020 growth rates of emission anomalies are a magnitude higher than that in 2000–2025, suggesting an intensification of emission variability. Furthermore, we identify a distinct seasonal amplification of global emission growth peaking in late boreal summer. This new dataset and operational framework bridge the gap between latest updated budgets and low-latency monitoring, providing a scalable capacity to frequently update global emission estimates and critical early warnings of regional wetland feedback loops. The data are publicly available at https://doi.org/10.5281/zenodo.18870108 (Li et al., 2026).
Competing interests: At least one of the (co-)authors is a member of the editorial board of Earth System Science Data.
Publisher's note: Copernicus Publications remains neutral with regard to jurisdictional claims made in the text, published maps, institutional affiliations, or any other geographical representation in this paper. While Copernicus Publications makes every effort to include appropriate place names, the final responsibility lies with the authors. Views expressed in the text are those of the authors and do not necessarily reflect the views of the publisher.- Preprint
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Status: open (until 18 Apr 2026)
- RC1: 'Comment on essd-2026-176', Anonymous Referee #1, 17 Mar 2026 reply
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RC2: 'Comment on essd-2026-176', Anonymous Referee #2, 26 Mar 2026
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The manuscript “Global natural wetland methane emissions (2000-2025)” uses a machine- learning emulator to estimate monthly methane emissions from global natural wetlands for the period 2000-2025. The emulator was trained on 35 GMB model estimates for 2000-2020 and the results show that the emulator, XGBoost models, reproduced both the magnitude and spatial pattern of the 2000-2020 GMB estimates very well. The XGBoost was able to extend the global emissions beyond 2020 to 2025 (2021-2025) with high confidence. The results from the machine-learning technique highlight multiple spatial and temporal patterns in the global methane emissions data. Since efforts to synthesize global methane emission estimates using BU and TD models lead to lags of multiple years, the paper proposes use of the XGBoost model to monitor global methane emissions from wetlands in almost "real time" and at lower computational costs.
I highly recommend it for publication in ESSD once the authors have addressed the following minor comments and suggestions.
Specific comments:
- Title: The title may be rephrased to “Global methane emissions from natural wetlands (2000-2025) using a machine-learning approach”
- Line 126: Insert “extent” in the sentence......Hydrology, often summarized by water table depth, soil moisture and inundation extent, controls oxygen...
- Line 127: Insert “CH4” in the sentence .... thereby influencing wetland CH4 production and oxidation (Cui et al., 2024; .........
- Lines 180-183: Could you please clarify on the advantages of the fact that all BU models compute wetland extent internally? Like you mentioned that contributes to inter-model spread. If a reliable dataset of the wetland extents, maybe from simulations by one specialized model, was used for all BU models, would that help to reduce the spread? Inaccurate representation of wetland extents has also been associated with failures of process-based models (Lin et al., 2024 - Nature Communications vol. 15: 10894).
- Line 252: Rewrite the mean flux of CH4. It is not clear, but I believe it should read 1x10-15 kg CH4/m2/s. Is this value 30,000 or 300,000 times lower than the global mean of 157 Tg/yr?
- Line 271-273, Line 277, Line 290, Line 337-339: Can you clarify on which predictor variables were identified and retained as important after the Boruta feature screening? If the key predictor variables changed from one cell to another, how reproduceable is this step? Can the key predictor variables be grouped based on geographical regions (e.g., southern vs northern hemisphere) or latitudinal bands?
- Line 342: The sentence “Mean R2 is higher in regions with higher wetland CH4 emissions....” sort of contradicts Line 340-341 because as stated here the northern hemisphere (NH) as a geographical region emits more CH4 than the southern hemisphere (SH), yet the R2 value is higher in the SH than in the NH.
- Line 364: Are the Sudd wetlands in South Sudan within the Congo Basin?
- Lines 459-466: Hydroclimatic drying conditions have been associated with regions that experienced significant decreases in emissions (see Lines 418-428, Lines 449-457), what prompted significant increases (in 9 regions) and no changes (in 4 regions) in emissions? Can this be made clear?
- Lines 494-499: The tropics show emission growth rate of almost zero but with high uncertainty. Is this high uncertainty, also observed using the machine-learning approach, associated with use of limited training data or poor understanding of key biogeochemical and hydroclimatic drivers such as inundation extents in tropical wetlands?
Citation: https://doi.org/10.5194/essd-2026-176-RC2 -
RC3: 'Comment on essd-2026-176', Anonymous Referee #3, 04 Apr 2026
reply
please see attached
Data sets
ERA5 monthly averaged data on single levels from 1940 to present Copernicus Climate Change Service https://doi.org/10.24381/cds.f17050d7
Global natural wetland methane emissions (2000-2025) M. Li et al. https://doi.org/10.5281/zenodo.18870108
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The study by Li et al. entitled “Global natural wetland methane emissions (2000-2025)” uses various bottom-up and top-down estimates of methane emissions from wetlands for the period 2000-2020 in conjunction with a machine-learning approach to model global emissions for the period 2000-2025 and simultaneously project global methane emissions from wetlands for the period 2021-2025. Based on these newer estimates, wetland emissions and growth rates are presented and discussed in relation to latitude, regions and season. Their findings suggest that methane emissions from wetlands in the northern mid-to-high latitudes have increased in recent years. Hence, this machine-learning approach provides the opportunity to model more recent developments of wetland methane emissions, able to investigate possible feedback mechanism and emission changes earlier than global data networks can usually achieve.
This manuscript is a valuable contribution to the research community, and I recommend it for publication in ESSD once the authors have addressed the comments and suggestions raised in this review.
General comments:
The authors should improve the resolution of all figures to at least 300 dpi. After improved resolution, Figures 1, 3, should be increased in size, so that small details can be seen.
Is it possible to write the definitions of all parameters including a “_” with small letters instead (e.g., CH4, pred)?
The gap between top-down and bottom-up approaches for wetland emissions was only recently narrowed by improvements of simulations, adding additional parameters, such as including inland freshwater systems, inundation, accounting for double counting, etc. (e.g., Saunois et al., 2025). The authors state that those are not included in the simulations (line 150). What error is expected regarding those missing emissions?
The uncertainties of the emissions are reported with a CI value of 95%. Highest uncertainties for wetland CH4 emissions correlate with highest emitting regions (e.g., Zhu et al., 2025). This is not reflected by the CI, as can be seen in Figure S1 (0-10%). Did the authors consider uncertainties from the spread of ensemble simulations? Did all BU and TD estimates provide global coverage, or is there a bias in spatial data coverage, influencing uncertainties? Remapping coarser products on finer resolution; have the authors just replicated the mean and uncertainties, or did they used a scaling factor (particularly important for the uncertainty)? The manuscript would benefit from more discussions regarding uncertainties and uncertainty propagation.
Methane experienced a remarkable growth during 2020-2022, coinciding with an unusual La Nina event (triple-peak, Hasan et al., 2022, Nisbet et al., 2023), also supported by observations in the tropics (e.g., Ort et al., 2026; Balasus et al., 2026). Figure 5 shows a strong increase of GMB emission estimates towards 2020, mostly visible in tropical regions, which the XGBoost predictions cannot reproduce. Simultaneously, the Covid-19 pandemic is discussed to had a global influence on CH4 oxidation capacity though the decreased NOx emissions (e.g., Stevenson et al., 2021). However, as Covid-19 influences most likely are not considered by the XGBoost predictions, neither are unusual ENSO phenomena, aren’t they? Sections 3.3, and 3.4 would benefit from more detailed discussions about limitations of the XGBoost predictions, and comparisons of the results with other studies, to better quantify the value of the results provided by this machine-learning approach.
With this machine-learning approach, predictions from 2021-2025 were performed. Why did the authors decide for this time period only, and not included climatological predictions further into the future?
Specific comments:
Technical comments:
Literature:
Zhu et al., 2025, DOI: 10.1088/1748-9326/adad02
Yuan et al., 2024, https://doi.org/10.1038/s41558-024-01933-3
Hasan et al., 2022, https://doi.org/10.3389/fclim.2022.1001174
Nisbet et al., 2023, https://doi.org/10.1029/2023GB007875
Stevenson et al., 2021, DOI: 10.5194/acp-2021-604
Ort et al., 2026, DOI: 10.22541/essoar.177248180.00166712/v1
Balasus et al., 2026, https://doi.org/10.5194/egusphere-2025-6251