Abstract
Afforestation can influence evapotranspiration (E) and precipitation (P), thereby altering water availability (known as P − E) on land. However, such effects on P − E have rarely been examined in the context of seasonal and spatial variations in background P − E conditions. Here we show the impacts of global tree restoration on P − E under spatiotemporally varying P − E conditions. Afforestation amplifies seasonal contrasts in P − E, resulting in higher P − E in the high P − E season and/or lower P − E in the low P − E season, over approximately two-thirds of the land area. Afforestation also amplifies spatial contrasts in P − E, leading to higher P − E in the high P − E regions but lower P − E in the low P − E regions. This study underscores the importance of considering background P − E conditions when evaluating the hydrological effects of afforestation, with important implications for both forestry and water management.
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Data availability
The dataset mapping the existing tree cover is from Hansen et al.64 (https://doi.org/10.1126/science.1244693; available on request). The dataset mapping the global tree restoration potential is from Bastin et al.31 (https://doi.org/10.1126/science.aax0848; available on request). The dataset mapping the biophysical effects of vegetation cover changes is available at https://jeodpp.jrc.ec.europa.eu/ftp/jrc-opendata/ECOCLIM/Biophysical-effects-vgt-change/v2.0/. The moisture tracking dataset developed by Link et al.34 is available at https://doi.org/10.1594/PANGAEA.908705. The moisture tracking dataset developed by Tuinenburg et al.35 is available at https://doi.org/10.1594/PANGAEA.912710. The GLEAM dataset is available at https://www.gleam.eu/. The MSWEP dataset is available at https://www.gloh2o.org/mswep/. The Global Aridity Index and Potential Evapotranspiration Database is available at https://doi.org/10.6084/m9.figshare.7504448.v5 (ref. 37). The Gridded Population of the World version 4 dataset is available at https://sedac.ciesin.columbia.edu/data/collection/gpw-v4/sets/browse.
Code availability
The data used in this study were processed by the software MATLAB. The processing MATLAB codes are available at https://box.nju.edu.cn/f/f2ad9e2bc1e84741b41e/.
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Acknowledgements
This research is supported by the Natural Science Foundation of China (42375115 awarded to J.G. and 42105023 awarded to B.Z.). J.G. also acknowledges support from the Fundamental Research Funds for the Central Universities (2024300330) and the Jiangsu Collaborative Innovation Center of Climate Change.
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J.G. and J.W. conceived and designed the overall study. B.Z. and J.G. performed the data analysis with help from M.M., Q.S., X.L. and J.W. in the interpretation of the results. B.Z. drafted the paper. J.G. and J.W. edited the paper. All the authors discussed and revised the paper.
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Extended data
Extended Data Fig. 1 The hydrological effects of afforestation.
a–c, Impacts of afforestation on annual evapotranspiration (E) (a), precipitation (P) (b) and water availability (P–E) (c). The pie chart insets show the proportion (%) of land area with a positive (green) or negative (yellow) response. The land area is calculated using a spatially weighted mean to account for the change in pixel size with latitude. d–f, Latitudinal and monthly variations in the responses of E (d), P (e) and P–E (f) to afforestation. The latitudinal value is averaged over land. The results are calculated based on the Duveiller et al.33 and Link et al.34 datasets.
Extended Data Fig. 2 Seasonal contrasts in the response of water availability (P–E) to afforestation.
a, Seasonal variations in the multi-year (2001–2018) mean P − E (yellow line) and the P − E response to afforestation (green line) at a selected location of 6° N, 72° W. b–d, Impacts of afforestation on the annual range of P − E ((P − E)range) (b), the wet season P–E ((P–E)wet) (c) and the dry season P–E ((P–E)dry) (d) are shown. The violet star in b denotes the selected location of 6° N, 72° W. The pie chart insets show the proportion (%) of land area with a positive (green) or negative (yellow) response. The land area is calculated using a spatially weighted mean to account for the change in pixel size with latitude. e, Combined impacts of afforestation on (P–E)wet and (P–E)dry, and the corresponding proportions (%) of land area are shown in the pie chart inset. The results are calculated based on the Duveiller et al.33 and Link et al.34 datasets.
Extended Data Fig. 3 Spatial contrasts in the hydrological effects of afforestation.
Responses of evapotranspiration (E) (a), precipitation (P) (b) and water availability (P–E) (c) to afforestation and the proportion (%) of land area with a negative P–E response to afforestation (d) binned as a function of P–E. The land pixels are sorted and divided into 20 bins at intervals of 5% according to their monthly or annual P–E. Hatching in panels a–c denotes that changes in E (a), P (b) or P–E (c) are statistically significant (P < 0.05) according to two-sided Student’s t test. For panel d, the land area is calculated using a spatially weighted mean to account for the change in pixel size with latitude. The first 12 columns denote monthly values, and the last column (labeled as Y) denotes annual values. The results are calculated based on the Duveiller et al.33 and Link et al.34 datasets.
Extended Data Fig. 4 Changes in the P–E contrast between afforested pixels and their downwind footprints (δ(P–E)).
a, b, Maps of δ(P–E) when afforested pixels are in the wet (a) and dry (b) seasons, respectively. The pie chart insets show the proportion (%) of land area with a positive (green) or negative (yellow) value of δ(P–E). The land area is calculated using a spatially weighted mean to account for the change in pixel size with latitude. c, d, The proportion (%) of downwind land area in the wet season when the upwind afforested pixel is in the wet (c) or dry (d) P–E season. e, f, The proportion (%) of downwind land area in the dry season when the upwind afforested pixel is in the wet (e) or dry (f) season. The results are calculated based on the Duveiller et al.33 and Link et al.34 datasets.
Extended Data Fig. 5 Impacts of afforestation on country-level water availability (P–E).
The insets show seasonal variations in the water gain (yellow line), water loss (green line) and water budget (black line) for 14 selected countries that are among the top 30 countries ranked by tree restoration area. The water gain is the amount of precipitation in a country resulting from afforestation outside the country. The top country where the water comes from is shown in the top left corner of the inserts, and the corresponding monthly water amounts are shown in green bars. The water loss is the amount of evapotranspiration resulting from afforestation in a country that eventually precipitates outside the country. The top country to which the water flows is shown in the bottom left corner of the inserts, and the corresponding monthly water amounts are shown in brown bars. The water budget is the difference between the water gain and loss and is roughly equivalent to the P–E change. The results are calculated based on the Duveiller et al.33 and Link et al.34 datasets. Note that the European Union is included here, although it is not a country.
Extended Data Fig. 6 Global map of the aridity index (AI).
The AI is defined as the ratio of precipitation to potential evapotranspiration.
Extended Data Fig. 7 Spatial contrasts in the hydrological effects of afforestation and tree cover changes.
Potential changes in evapotranspiration that would occur if all grasslands and/or croplands in a pixel were converted to trees (a) and tree cover changes (b) binned as a function of P–E. The land pixels are sorted and divided into 20 bins at intervals of 5% according to their monthly or annual P–E. In panel a, hatching denotes that potential changes in evapotranspiration are statistically significant (p < 0.05) according to two-sided Student’s t test. The first 12 columns denote monthly values, and the last column denotes annual values.
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Zan, B., Ge, J., Mu, M. et al. Spatiotemporal inequality in land water availability amplified by global tree restoration. Nat Water 2, 863–874 (2024). https://doi.org/10.1038/s44221-024-00296-5
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DOI: https://doi.org/10.1038/s44221-024-00296-5
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