Abstract
Drylands exert a strong influence over global interannual variability in carbon and water cycling due to their substantial heterogeneity over space and time. This variability in ecosystem fluxes presents challenges for understanding their primary drivers. Here we quantify the sensitivity of dryland gross primary productivity and evapotranspiration to various hydrometeorological drivers by synthesizing eddy covariance data, remote sensing products and land surface model output across the western United States. We find that gross primary productivity and evapotranspiration derived from eddy covariance are most sensitive to soil moisture fluctuations, with lesser sensitivity to vapour pressure deficit and little to no sensitivity to air temperature or light. We find that remote sensing data accurately capture the sensitivity of eddy covariance fluxes to soil moisture but largely over-predict sensitivity to atmospheric drivers. In contrast, land surface models underestimate sensitivity of gross primary productivity to soil moisture fluctuations by approximately 45%. Amid debates about the role of increasing vapour pressure deficit in a changing climate, we conclude that soil moisture is the primary driver of US dryland carbon–water fluxes. It is thus imperative to both improve model representation of soil water limitation and more realistically represent how atmospheric drivers affect dryland vegetation in remotely sensed flux products.
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Data availability
All data used for our analyses are publicly available. Eddy covariance tower data are available at ameriflux.lbl.gov, CMIP6 model output are accessible from esgf-node.llnl.gov/search/cmip6/. SMAP L4C, MOD16 and MOD17 data were all obtained using the AppEEARS subsetting tool (https://appeears.earthdatacloud.nasa.gov/). FluxSat data were obtained from the Oak Ridge National Lab Distributed Active Archive Center (https://daac.ornl.gov/VEGETATION/guides/FluxSat_GPP_FPAR.html), and GLEAM data were obtained from https://www.gleam.eu/.
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Acknowledgements
We sincerely thank all flux tower site principal investigators for contributing flux data and the AmeriFlux Management Project team for making these data openly available. Funding for the AmeriFlux data portal was provided by the US Department of Energy. S.A.K. and M.L.B. were supported by the US Department of Energy Environmental System Science program grant number DE-SC0022052. W.R.L.A. acknowledges support from the David and Lucille Packard Foundation, US National Science Foundation grants 1802880, 2003017, 2044937 and IOS-2325700 from the Alan T. Waterman Award. M.P.D. and M.L.B. were supported by NASA SMAP Science Team grant number 80NSSC20K1805.
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S.A.K. initially conceived of the research, with subsequent contributions from all authors. W.R.L.A., M.L.B. and M.P.D. assisted with data extraction. S.A.K. performed all data analysis and wrote the first draft of the manuscript. All authors contributed to subsequent manuscript revisions.
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Extended data
Extended Data Fig. 1 Map of the eddy covariance tower sites used in this analysis.
Color corresponds to the IGBP vegetation type.
Extended Data Fig. 2 Correlation plot representing the coefficient of daily GPP to various environmental drivers.
Each row represents a different flux tower site, while the last row represents the mean across sites. Sites are arranged (top to bottom) in order of decreasing aridity (mean climatic water deficit). Color, point size, and number indicates the Pearson’s R correlation coefficient. Missing values indicate a lack of data for that particular variable. ‘n.s.’ indicates a non-significant relationship (α = 0.05). Deep VWC correlations for US-Whs were excluded due to their limited temporal record.
Extended Data Fig. 3 Correlation plot representing the coefficient of daily ET to various environmental drivers.
Each row represents a different flux tower site, while the last row represents the mean across sites. Sites are arranged (top to bottom) in order of decreasing aridity (mean climatic water deficit). Color, point size, and number indicates the Pearson’s R correlation coefficient. Missing values indicate a lack of data for that variable. ‘n.s.’ indicates a non-significant relationship (α = 0.05). Deep VWC correlations for US-Whs were excluded due to their limited temporal record.
Extended Data Fig. 4 Relative weights for models between GPP/ET and hydrometeorological drivers.
Only a subset of sites were used for this analysis in order to keep relative weights comparable (see Methods). Box plot lines represent the interquartile range and median, while the whiskers represent 1.5 times the interquartile range.
Extended Data Fig. 5 Spearman’s correlation coefficients between daily GPP/ET and environmental drivers.
Environmental drivers include air temperature (TA), vapor pressure deficit (VPD), photosynthetic photon flux density (PPFD), and various layers of volumetric water content (VWC, see Methods for the depths included in each layer). Asterisks indicate where coefficients are significantly different from zero (α = 0.05). Box plot lines represent the interquartile range and median, while the whiskers represent 1.5 times the interquartile range.
Extended Data Fig. 6 Remotely-sensed correlation coefficients.
Pearsons’ R coefficient between various data products (boxplots and points) and a given environmental driver (panels) at each site. Box plot lines represent the interquartile range and median, while the whiskers represent 1.5 times the interquartile range.
Extended Data Fig. 7 Eddy covariance (EC) versus remotely-sensed (RS) coefficients for various environmental drivers.
R2 values are those from a linear model containing all remotely-sensed data products (all models statistically significant at α = 0.05), and the dashed black lines are 1:1 lines. Gray shading indicates the 95% confidence interval.
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Kannenberg, S.A., Anderegg, W.R.L., Barnes, M.L. et al. Dominant role of soil moisture in mediating carbon and water fluxes in dryland ecosystems. Nat. Geosci. 17, 38–43 (2024). https://doi.org/10.1038/s41561-023-01351-8
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DOI: https://doi.org/10.1038/s41561-023-01351-8