in

Greening masks stability loss in drylands


Abstract

Drylands are already undergoing large-scale change due to climate change, yet understanding of this response remains limited by observational gaps, conflicting satellite records and substantial model uncertainty. Here, considering trends and interannual variability based on leaf area index (LAI), we show persistent (1982–2020) greening across global drylands and increasing interannual variability. Greening rates are higher than current dynamic global vegetation models and contradict reports of a recent greening slowdown. The interannual variability increase is spatially coherent, covering about 82% of global drylands, and is characterized by increasing LAI maxima and declining minima. Increasing rainfall sensitivity is the dominant driver of increasing variability with both inter- and intraannual rainfall variability acting as secondary drivers. The dynamic global vegetation models analysed cannot reproduce increasing variability and divergent LAI trajectories. Rising variability may indicate eminent state transitions that could intensify carbon cycle uncertainty and disrupt key dryland ecosystem services.

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Fig. 1: Persistent greening yet increasing variability of annual growing season LAI across global drylands.
Fig. 2: Divergent trajectories of upper and lower bounds of the LAI distribution across global drylands.
Fig. 3: Comparison of observed and modelled trends in LAI versus LAICV.
Fig. 4: Potential drivers of increasing LAICV and comparison of spatial dominance patterns between observational multi-products average and TRENDY ensemble mean.

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Vegetation cover change as a growing driver of global leaf area index dynamics

Increasing sensitivity of dryland vegetation greenness to precipitation due to rising atmospheric CO2

Predictability of abrupt shifts in dryland ecosystem functioning

Data availability

All datasets used in this study are publicly available. The Global Inventory Modeling and Mapping Studies 4th Generation LAI dataset (GIMMS4g LAI) is available via Zenodo at https://doi.org/10.5281/zenodo.8281930 (ref. 79); the Global Mapping (GLOBMAP) LAI version 3 dataset is available via Zenodo at https://doi.org/10.5281/zenodo.4700264 (ref. 80); and the Seoul National University (SNU) LAI dataset is available at https://drive.google.com/drive/folders/1ltwcRgJ7IBEZ3mcc7S1eKzCuOon9mws5. Moderate Resolution Imaging Spectroradiometer (MODIS) version 6.1 LAI product (MOD15A2H) is available at https://www.earthdata.nasa.gov/data/catalog/lpcloud-mod15a2h-061. Eddy covariance GPP measurements were obtained from https://data.fluxnet.org/data/. Daily precipitation data were obtained from the CRU-JRA v2.5 forcing dataset at https://catalogue.ceda.ac.uk/uuid/43ce517d74624a5ebf6eec5330cd18d5. Monthly precipitation, temperature, vapour pressure deficit (VPD) and potential evapotranspiration (PET) data were obtained from the CRU TS v4.08 dataset at https://crudata.uea.ac.uk/cru/data/hrg/cru_ts_4.08/. Annual land-cover data were obtained from the European Space Agency Climate Change Initiative (ESA CCI) Land Cover product v2.1.1 (1992–2020) at https://maps.elie.ucl.ac.be/CCI/viewer/download.php. The Global Land Cover 2000 dataset is available at https://forobs.jrc.ec.europa.eu/products/glc2000/glc2000.php. MODIS land-cover data (MCD12Q1 version 6.1) are available from NASA EARTHDATA at https://doi.org/10.5067/MODIS/MCD12Q1.061. Model-simulated LAI data were obtained from 13 DGVMs participating in the TRENDYv13 model intercomparison project. TRENDY model outputs are publicly available via the TRENDY project repository at https://mdosullivan.github.io/GCB/. AVHRR-LTDR Burned Area Grid product (version 1.1) from the ESA Fire Climate Change Initiative is available at https://data.ceda.ac.uk/neodc/esacci/fire/data/burned_area/AVHRR-LTDR/grid/v1.1/. The minimum dataset required to interpret, verify and reproduce the analyses presented in this study is publicly available via Zenodo at https://doi.org/10.5281/zenodo.21536423 (ref. 81).

Code availability

The code for the analyses is available via Zenodo at https://doi.org/10.5281/zenodo.21541318 (ref. 82).

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Acknowledgements

We would like to acknowledge the Global Carbon Project, which is responsible for the Global Carbon Budget, and we thank the land modelling groups for producing and making available their model outputs that were used in this analysis. Any use of trade, firm or product names is for descriptive purposes only and does not imply endorsement by the US Government. Any opinions, findings and conclusions or recommendations expressed in this material are those of the authors and do not necessarily reflect the views of our shareholders or sponsors. United States Department of Agriculture (USDA) is an equal-opportunity provider.

Funding

W.Z., W.K.S., B.P., S.C.R. and N.M. acknowledge funding for this research provided by the National Aeronautics and Space Administration (NASA) Carbon Cycle Science Program (grant 80NSSC23K0109). W.Z., R.L.S. and W.K.S acknowledge funding provided by the US Department of Agriculture (USDA; cooperative agreement 58–2022–2–001). Several authors also acknowledge funding provided by the NASA Terrestrial Ecology Program to scope a dryland field campaign (grant 80NSSC23K1420). N.M. acknowledges the support of the Natural Sciences and Engineering Research Council of Canada (NSERC) (funding reference numbers RGPIN/05249-2023 and DGECR/00302-2023). Cette recherche a été financée par le Conseil de recherches en sciences naturelles et en génie du Canada (CRSNG) (numéros de références RGPIN/05249-2023 et DGECR/00302-2023). N.M. acknowledges support from the Wolfe–Western Fellowship At-Large for Outstanding Newly Recruited Research Scholars Endowment Fund. Y.K. acknowledges support from the NASA Early Career Investigator Program (award number 80NSSC24K1562).

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Contributions

W.Z. and W.K.S. conceived the idea. W.Z., W.K.S and D.J.P.M. designed the study and participated in the early-stage discussion. W.Z. performed the analysis and wrote the first draft of the manuscript. D.J.P.M., Y.L., N.M., A.F.F., C.R.S., Y.K., J.K.G., B.P., M.J., R.L.S., Z.S., Y.R., S.J. and S.C.R. contributed to the interpretation of the results and revised the manuscript.

Corresponding authors

Correspondence to
Wen Zhang or William K. Smith.

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Nature Climate Change thanks Scott Collins, Xuanlong Ma and the other, anonymous, reviewer(s) for their contribution to the peer review of this work. Peer reviewer reports are available.

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Extended data

Extended Data Fig. 1 Spatial patterns of long-term trends in annual growing season LAI (1982–2020) from three individual satellite products.

a, GIMMS4g; b, GLOBMAP; c, SNU. Colors show trend magnitude (% yr⁻1); black dots mark grid cells with significant trends (two-sided t-test, p < 0.05). Insets report the area fractions of significant greening (blue), significant browning (brown), and non-significant change (grey). Basemaps were generated with python3.12-mpltoolkits.basemap (version 2.0.0, https://matplotlib.org/basemap/stable/).

Extended Data Fig. 2 Decomposition of LAIcv Into standard deviation (std) and mean.

a, Time series of LAI std (left axis, purple) and mean (right axis, teal) based on multi satellite product average across global drylands using the 15-yr moving-window analysis (1982–2020). b, Joint map of trends in LAI std and mean. Slopes were estimated using linear regression applied to the global mean time series. Statistical significance was assessed using two-sided t-tests. Basemap in b was generated with python3.12-mpltoolkits.basemap (version 2.0.0, https://matplotlib.org/basemap/stable/).

Extended Data Fig. 3 Spatial patterns of long-term trends in LAIcv (1982–2020) across three individual satelite products using a 15-year moving window.

Trends in ({mathrm{LAI}}_{mathrm{cv}}) derived from (a) GIMMS4g, (b) GLOBMAP, and (c) SNU LAI. Colors indicate the magnitude of ({mathrm{LAI}}_{mathrm{cv}}) trends (% yr⁻1), and black dots denote grid cells with statistically significant trends (two-sided t-test, p < 0.05). Insets report the area fractions of significant increases in ({mathrm{LAI}}_{mathrm{cv}}) (purple), significant decreases in ({mathrm{LAI}}_{mathrm{cv}}) (green), and non-significant changes (grey). Basemaps were generated with python3.12-mpltoolkits.basemap (version 2.0.0, https://matplotlib.org/basemap/stable/).

Extended Data Fig. 4 Cross-product validation of increasing dryland LAI variability during the MODIS era (2001–2020).

(a) Temporal trends in dryland ({rm{LAI}}_{rm{CV}}) derived from four LAI products (MODIS, GIMMS4g, GLOBMAP, and SNU) during the MODIS era (2001–2020) using a 15-year moving window. Dashed lines indicate linear trends estimated by linear regression of the global mean time series. Statistical significance was assessed using two-sided t-tests; * denotes P<0.05, ** denotes P<0.01 and *** denotes P<0.001. The corresponding P values are 0.024 (MODIS), 1.753× 10⁻4 (GIMMS4g), 0.002 (GLOBMAP) and 3.537× 10⁻4 (SNU). (b–e) Spatial patterns of ({rm{LAI}}_{rm{CV}}) trends derived from (b) MODIS, (c) GIMMS4g, (d) GLOBMAP and (e) SNU during the overlapping period (2001–2020). Colors indicate the magnitude of ({mathrm{LAI}}_{mathrm{cv}}) trends (% yr⁻1), and black dots denote grid cells with statistically significant trends (two-sided t-test, p < 0.05). Basemaps in b–e were generated with python3.12-mpltoolkits.basemap (version 2.0.0, https://matplotlib.org/basemap/stable/).

Extended Data Fig. 5 Robustness of increasing dryland LAI variability across moving-window lengths using MODIS-era observations through 2024 (2001–2024).

a, c, e, Temporal trends in dryland ({rm{LAI}}_{rm{CV}}) derived from the MODIS LAI product using 5-years (a), 10-years (c), and 15-years (e) moving windows, respectively. Dashed lines indicate linear trends estimated by linear regression of the global mean time series. Statistical significance was assessed using two-sided t-tests; *** denotes P<0.001. The corresponding P values are 1.474 × 10⁻6 (5-years), 5.335× 10⁻6 (10-years), and 5.331 ×10⁻6 (15-years). b, d, f, Spatial maps illustrate the corresponding trends in ({rm{LAI}}_{rm{CV}}) for 5-years (b), 10-years (d) and 15-years (f) moving-window respectively. Colors indicate the magnitude of ({rm{LAI}}_{rm{cv}}) trends (% yr⁻1), and black dots denote grid cells with statistically significant trends (two-sided t-test, p < 0.05). Basemaps in b, d and f were generated with python3.12-mpltoolkits.basemap (version 2.0.0, https://matplotlib.org/basemap/stable/).

Extended Data Fig. 6 Partial correlations between LAICV and potential drivers.

Partial correlation between ({mathrm{LAI}}_{mathrm{CV}}) and (a) vegetation rainfall sensitivity (γ), (b) inter-annual rainfall variability (({rm{CV}}_{{rm{inter}}-{rm{rainfall}}})) and (c) intraannual rainfall variability ({rm{CV}}_{{rm{intra}}-{rm{rainfall}}})). Colours indicate correlation strength (blue = positive, red = negative). Only grid cells with significant correlations (two-sided t-test, P<0.05) are shown. Basemaps generated with python3.12-mpltoolkits.basemap (version 2.0.0, https://matplotlib.org/basemap/stable/).

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Zhang, W., Moore, D.J.P., Li, Y. et al. Greening masks stability loss in drylands.
Nat. Clim. Chang. (2026). https://doi.org/10.1038/s41558-026-02733-7

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