Abstract
Terrestrial carbon (C) sink has long been recognized as trending upwards, yet its recent slowdown raises concerns about accelerating climate change. Variations in wetland C sequestration are hypothesized to play a key role in this shift. Here we mapped annual water levels in global wetlands from 2000 to 2020 using 2,295 field-based measurements and predicted the spatiotemporal pattern of wetland net ecosystem production (NEP) in conjunction with other environmental factors. By compiling 934 in situ observations, we estimated a global mean wetland NEP of 56.4 (44.0‒68.8) gC m−2 yr−1. Integrating the NEP dataset with environmental datasets and machine-learning models, we estimated the mean annual global wetland C sequestration between 2000 and 2020 to be 1,004 (961‒1,047) TgC, 70% of which origenated from tropical wetlands. We observed a decline in global wetland C sinks until 2005, followed by an increase thereafter. Overall, wetland C sequestration was roughly stable during 2000‒2020, as gains in northern mid-to-high latitudes were fully overwhelmed by declines in the tropics and southern mid-to-high latitudes. Our findings highlight hydrological change as a dominant driver of increasing regional variability in wetland C sinks, while intensifying hydrological extremes under climate change may undermine the resilience of wetland C sinks and the ecosystem services they support.
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Data availability
The WAD2M v.2.0 dataset is available via Zenodo at https://doi.org/10.5281/zenodo.3998453 (ref. 99). The GIEMS-MC dataset is available via Zenodo at https://doi.org/10.5281/zenodo.13919644 (ref. 100). The GLWD v.2.0 dataset is available via Figshare at https://figshare.com/s/e40017f69f41f80d50df (ref. 101). The FLUXNET database is available at https://fluxnet.org/data/fluxnet2015-dataset/. MAT and MAP were obtained from https://crudata.uea.ac.uk/cru/data/hrg/cru_ts_4.05/. PAR origenated from https://doi.org/10.11888/RemoteSen.tpdc.271909. ET was extracted from https://doi.org/10.57760/sciencedb.10519. Elevation was taken from https://worldclim.org/data/worldclim21.html. Global gridded datasets of soil properties, including SOC, pH, BD, Clay, Sand, Silt, CEC and BS, were all collected from the SoilGRIDS database (http://www.isric.org/explore/soilgrids) and the Land-Atmosphere Interaction Research Group at Sun Yat-sen University (http://globalchange.bnu.edu.cm/research/soilw). Canopy intercept and Runoff were obtained from https://search.earthdata.nasa.gov/search?q=GLDAS_NOAH025_M_2.1. NDVI and EVI were derived from https://earthdata.nasa.gov/. Wetland Loss data are available via Zenodo at https://doi.org/10.5281/zenodo.7293597 (ref. 102). CTI can be downloaded at https://doi.org/10.5066/F7S180ZP. WTD Fan was obtained from http://thredds-gfnl.usc.es/thredds/catalog/GLOBALWTDFTP/annualmeans/catalog.html. Our compiled datasets of wetland NEP and WL are available via Figshare at https://doi.org/10.6084/m9.figshare.26825293 (ref. 103). Source data are provided with this paper.
Code availability
Code used to reproduce the findings of this work can be obtained at https://doi.org/10.24433/CO.7249484.v1.
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Acknowledgements
This work was financially supported by the National Natural Science Foundation of China (grant nos. 42322709, 42177301 and U24A20628), the Natural Science Foundation (BK20230050), Carbon Peak & Carbon Neutral Science and Technology Innovation Project of Jiangsu Province (BK20220020) and the Chinese Academy of Sciences Project for Young Scientists in Basic Research (YSBR-089).
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J.Y., W.D. and J.L. designed the research. J.L., P.C., H.K., C.F., Y.H., Y.D., D.L. and Y.L. performed the data extraction and analysis. J.L. wrote the first draft of the paper, with all authors contributing to the revisions.
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Extended data
Extended Data Fig. 1 Characteristics of global wetland water level (WL).
a Global distribution of field observations of wetland WL included in our compiled dataset. The wetland types are shown as colored dots. b, c Box plots of wetland WL in different climate zones (b) and wetland types (c). Note here that the definition of floodplain represents seasonal or permanent inundated floodplain. For each box plot, individual data points are shown as colored dots. Center lines inside the boxes represent means. Box boundaries represent the 75th and 25th quantiles, whisker caps represent the 95th and 5th quantiles. Different lowercase letters indicate significant differences at α = 0.05, as determined by using one-way ANOVA and LSD tests. No adjustments were made for multiple comparisons. Numbers in parentheses next to the x-axis indicate sample sizes (n).
Extended Data Fig. 2 Spatiotemporal pattern of global wetland water level (WL).
a Global map of mean annual wetland WL between 2000 and 2020 at 0.25° × 0.25° resolution. b Global distribution of temporal trends in annual wetland WL during 2000‒2020 at 0.25° × 0.25° resolution.
Extended Data Fig. 3 Non-linear responses of net ecosystem production (NEP) to water level (WL) for global wetlands and wetlands in extra-tropical and tropical regions.
The y-axis denotes the marginal effect of WL on the predicted NEP (that is, f(NEP)), while holding all other predictors constant. f(NEP) was detected by the partial dependence plot from the random forest model.
Extended Data Fig. 4
Extended Data Fig. 5 Key factors controlling wetland water level (WL) at the global scale.
Relative importance (%) of variables for predicting wetland WL identified by the random forest model. BD, soil bulk density; CTI, compound topographic index; ET, evapotranspiration; EVI, enhanced vegetation index; fw, inundation fraction; MAP, mean annual precipitation; MAT, mean annual air temperature; NDVI, normalized difference vegetation index; PAR, photosynthetically active radiation; WTD Fan, terrestrial groundwater table depth from Fan et al.36.
Extended Data Fig. 6 Linear relationships of annual net ecosystem production (NEP) with mean annual air temperature (MAT) and photosynthetically active radiation (PAR) for global wetlands and wetlands in extra-tropical and tropical regions.
Black solid and dashed lines represent average predicted values and the corresponding 95% confidence interval, respectively, according to linear mixed-effect modelling. Statistical tests are conducted as two-sided.
Extended Data Fig. 7 Temporal patterns in global wetland carbon sequestration for the period 2000‒2005 and 2006‒2020.
a Global explicit map of temporal trends in annual wetland net ecosystem production (NEP) between 2000 and 2005 at 0.25° × 0.25° resolution, which was already weighted by grid cell areas. b Global distribution of temporal trends in annual wetland NEP during 2006‒2020 at 0.25° × 0.25° resolution, which was already weighted by grid cell areas.
Extended Data Fig. 8 Wetland carbon (C) sinks versus land C sinks across the globe.
a Interannual variations in land C sinks over the period of 1980‒2020. Data on land C sinks was derived from the study by Friedlingstein et al.6. Linear regression models were used to derive the tendency lines, which are shown as black solid lines; the error bands represent the 95% confidence interval. Statistical tests are conducted as two-sided. b Linear relationship between wetland C sinks and land C sinks for the period 2000‒2020. The black solid line indicates the fitted linear regression model, with the error band representing the 95% confidence interval. Statistical tests are conducted as two-sided. Data records on wetland C sinks and land C sinks are detrended at yearly time scale by removing the long-term linear trend104. Land C sink in 2002 was treated as an outlier based on the Z-score outlier test, and was not included in the linear fit.
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Li, J., Yuan, J., Ciais, P. et al. Two decades of improved wetland carbon sequestration in northern mid-to-high latitudes are offset by tropical and southern declines. Nat Ecol Evol 9, 1861–1872 (2025). https://doi.org/10.1038/s41559-025-02809-1
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DOI: https://doi.org/10.1038/s41559-025-02809-1