Nature Geoscience
Article
https://doi.org/10.1038/s41561-025-01742-z
108. Yadav, V. S. et al. Carbon sequestration potential and CO2 fluxes in
a tropical forest ecosystem. Ecol. Eng. 176, 106541 (2022).
109. Houghton, R. A. The annual net flux of carbon to the atmosphere
from changes in land use 1850–1990. Tellus B 51, 298–313 (1999).
110. DeFries, R. S. et al. Carbon emissions from tropical deforestation
and regrowth based on satellite observations for the 1980s and
1990s. Proc. Natl Acad. Sci. USA 99, 14256–14261 (2002).
111. Hamilton, J. G. et al. Forest carbon balance under elevated CO2.
Oecologia 131, 250–260 (2002).
112. Nascimento, H. E. & Laurance, W. F. Total aboveground biomass in
central Amazonian rainforests: a landscape-scale study. For. Ecol.
Manage. 168, 311–321 (2002).
113. Lasco, R. D. & Pulhin, F. B. Philippine forest ecosystems and
climate change: carbon stocks, rate of sequestration and the
Kyoto Protocol. Ann. Trop. Res. 25, 37–52 (2003).
114. Gibbs, H. K., Brown, S., Niles, J. O. & Foley, A. Monitoring and
estimating tropical forest carbon stocks: making REDD a reality.
Environ. Res. Lett. 2, 045023 (2007).
115. Sierra, C. A. et al. Total carbon stocks in a tropical forest
landscape of the Porce region, Colombia. For. Ecol. Manage. 243,
299–309 (2007).
116. Lewis, S. L. et al. Increasing carbon storage in intact African
tropical forests. Nature 457, 1003–1006 (2009).
117. Malhi, Y. & Grace, J. Tropical forests and atmospheric carbon
dioxide. Trends Ecol. Evol. 15, 332–337 (2000).
118. Ngo, K. M. et al. Carbon stocks in primary and secondary tropical
forests in Singapore. For. Ecol. Manage. 296, 81–89 (2013).
119. Wheeler, C. E. et al. Carbon sequestration and biodiversity
following 18 years of active tropical forest restoration. For. Ecol.
Manage. 373, 44–55 (2016).
120. Zaragoza, M. J. G., Aranico, E. C., Tampus, A. D. & Amparado, R. F.
Jr Carbon stock assessment of three different vegetative covers
in Kapatagan, Lanao del Norte, Philippines. Adv. Environ. Sci. 8,
205–220 (2016).
121. Ray, R. et al. Carbon sequestration and annual increase of carbon
stock in a mangrove forest. Atmos. Environ. 45, 5016–5024 (2011).
122. Alongi, D. M. Carbon sequestration in mangrove forests. Carbon
Manage. 3, 313–322 (2012).
123. Alongi, D. M. Carbon cycling and storage in mangrove forests.
Annu. Rev. Mar. Sci. 6, 195–219 (2014).
124. Kauffman, J. B., Heider, C., Norfolk, J. & Payton, F. Carbon stocks
of intact mangroves and carbon emissions arising from their
conversion in the Dominican Republic. Ecol. Appl. 24, 518–527
(2014).
125. Gnanamoorthy, P. et al. Soil organic carbon stock in natural and
restored mangrove forests in Pichavaram south-east coast of
India. Indian J. Geo Mar. Sci. 48, 801–808 (2019).
126. Adame et al. Future carbon emissions from global mangrove
forest loss. Glob. Change Biol. 27, 2856–2866 (2021).
127. Luo, H. et al. Mature semiarid chaparral ecosystems can be a
significant sink for atmospheric carbon dioxide. Glob. Change
Biol. 13, 386–396 (2007).
128. Robinson, D. Implications of a large global root biomass for
carbon sink estimates and for soil carbon dynamics. Proc. R. Soc.
B: Biol. Sci. 274, 2753–2759 (2007).
129. Beier, C. et al. Carbon and nitrogen balances for six shrublands
across Europe. Glob. Biogeochem. Cycles 23, GB4008 (2009).
130. Ruiz-Peinado, R., Moreno, G., Juarez, E., Montero, G. & Roig, S. The
contribution of two common shrub species to aboveground and
belowground carbon stock in Iberian dehesas. J. Arid Environ. 91,
22–30 (2013).
131. Stamati, F. E., Nikolaidis, N. P. & Schnoor, J. L. Modeling topsoil
carbon sequestration in two contrasting crop production
to set-aside conversions with RothC–Calibration issues and
uncertainty analysis. Agric. Ecosyst. Environ. 165, 190–200 (2013).
132. Nie, X. et al. Distribution and controlling factors of soil organic
carbon storage in the northeast Tibetan shrublands. J. Soils
Sediments 19, 322–331 (2019).
133. Zhao, M. et al. Assessing the effects of ecological engineering
on carbon storage by linking the CA-Markov and InVEST models.
Ecol. Indic. 98, 29–38 (2019).
134. Chen, X., Hutley, L. B. & Eamus, D. Carbon balance of a tropical
savanna of northern Australia. Oecologia 137, 405–416 (2003).
135. Hutley, L. B., Leuning, R., Beringer, J. & Cleugh, H. A. The utility of
the eddy covariance techniques as a tool in carbon accounting:
tropical savanna as a case study. Aust. J. Bot. 53, 663–675
(2005).
136. Grace, J., Jose, J. S., Meir, P., Miranda, H. S. & Montes, R. A.
Productivity and carbon fluxes of tropical savannas. J. Biogeogr.
33, 387–400 (2006).
137. Blaser, W. J., Shanungu, G. K., Edwards, P. J. & Olde Venterink, H.
Woody encroachment reduces nutrient limitation and promotes
soil carbon sequestration. Ecol. Evol. 4, 1423–1438 (2014).
138. Fei, X. et al. Eddy covariance and biometric measurement s show
that a savanna ecosystem in Southwest China is a carbon sink.
Sci. Rep. 7, 41025 (2017).
139. Conant, R. T., Paustian, K. & Elliott, E. T. Grassland management
and conversion into grassland: effects on soil carbon. Ecol. Appl.
11, 343–355 (2001).
140. Derner, J. D., Boutton, T. W. & Briske, D. D. Grazing and ecosystem
carbon storage in the North American Great Plains. Plant Soil 280,
77–90 (2006).
141. Guzman, J. G. & Al-Kaisi, M. Landscape position and age of
reconstructed prairies effect on soil organic carbon sequestration
rate and aggregate associated carbon. J. Soil Water Conserv. 65,
9–21 (2010).
142. DeLuca, T. H. & Zabinski, C. A. Prairie ecosystems and the carbon
problem. Front. Ecol. Environ. 9, 407–413 (2011).
143. Ampleman, M. D., Crawford, K. M. & Fike, D. A. Differential soil
organic carbon storage at forb- and grass-dominated plant
communities, 33 years after tallgrass prairie restoration. Plant Soil
374, 899–913 (2014).
144. Salemme, R. K., Olson, K. R., Gennadiyev, A. N. & Kovach, R. G.
Effects of land use change, cultivation, and landscape position
on prairie soil organic carbon stocks. Open J. Soil Sci. 8, 163–173
(2018).
145. Fisher, M. J. et al. Carbon storage by introduced deep-rooted
grasses in the South American savannas. Nature 371, 236–238
(1994).
146. Post, W. M. & Kwon, K. C. Soil carbon sequestration and land‐use
change: processes and potential. Glob. Change Biol. 6, 317–327
(2006).
147. Archer, S. et al. (eds) in Global Environmental Change in the Ocean
and on Land 359–373 (Terrapub, 2004).
148. Vågen, T. G., Lal, R. & Singh, B. R. Soil carbon sequestration in
sub‐Saharan Africa: a review. Land Degrad. Dev. 16, 53–71 (2005).
149. Boutton, T. W., Liao, J. D., Filley, T. R. & Archer, S. R. Belowground
carbon storage and dynamics accompanying woody
plant encroachment in a subtropical savanna. Soil Carbon
Sequestration Greenhouse Eff. 57, 181–205 (2009).
150. Maia, S. M., Ogle, S. M., Cerri, C. E. & Cerri, C. C. Effect of
grassland management on soil carbon sequestration in Rondônia
and Mato Grosso states, Brazil. Geoderma 149, 84–91 (2009).
151. Räsänen, M. et al. Carbon balance of a grazed savanna grassland
ecosystem in South Africa. Biogeosciences 14, 1039–1054 (2017).
152. Awuah, J., Smith, S. W., Speed, J. D. & Graae, B. J. Can seasonal
fire management reduce the risk of carbon loss from wildfires in a
protected Guinea savanna? Ecosphere 13, e4283 (2022).
153. Zhou, Y. Soil carbon in tropical savannas mostly derived from
grasses. Nat. Geosci. 16, 710–716 (2023).
Nature Geoscience
Article
https://doi.org/10.1038/s41561-025-01742-z
Acknowledgements
C.T., Z.B. and P.T. were supported by the NKFIH K 146137, FK 142428
and KKP 144068 grants, respectively. The support of the János Bolyai
Research Scholarship of the Hungarian Academy of Sciences and
the New National Excellence Program of the Ministry for Culture and
Innovation from the source of the National Research, Development and
Innovation Fund (ÚNKP-23-5-SZTE-697) are also acknowledged. V.M.T.
was supported by the German Ministry for Education and Research
(BMBF) and by the state of Lower Saxony. F.A.O.S. was supported
by grants from FAPEMIG. Á.B.-F. was supported by the János Bolyai
Research Scholarship of the Hungarian Academy of Sciences. This work
has been implemented by the National Multidisciplinary Laboratory for
Climate Change (RRF-2.3.1-21-2022-00014) project within the framework
of Hungary’s National Recovery and Resilience Plan supported by the
Recovery and Resilience Facility of the European Union.
Author contributions
C.T. conceived the study, Á.B.-F. constructed the models, N.C., Á.B.-F.
and C.T. made the predictions and prepared the figures, C.T. led the
writing of the paper, and all authors critically contributed to the
evaluation of the findings and editing the paper.
Competing interests
The authors declare no competing interests.
Additional information
Extended data is available for this paper at
https://doi.org/10.1038/s41561-025-01742-z.
Supplementary information The online version
contains supplementary material available at
https://doi.org/10.1038/s41561-025-01742-z.
Correspondence and requests for materials should be addressed to
Csaba Tölgyesi.
Peer review information Nature Geoscience thanks the anonymous
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Primary Handling Editor: Tom Richardson, in collaboration with the
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Nature Geoscience Article https://doi.org/10.1038/s41561-025-01742-z Extended Data Table 1 | Predictors used for model construction Predictor type and source Predictor Climatic: WorldClim64 (https://www.worldclim.org/data/bioclim.html)
- Annual mean temperature (°C ×10)
- Mean temperature of wettest quarter (°C × 10)
- Annual precipitation (mm)
- Precipitation seasonality (coefficient of variation)
- Precipitation of the driest quarter of the year (mm) Edaphic: SoilGrids250m65 (https://soilgrids.org/)
- Sand content in the top 15 cm of the soil (%)
- Soil organic carbon stock (g m−2)
- Depth to bedrock (m) GMTED201066 (https://topotools.cr.usgs.gov/gmted_viewer)
- Slope (degree)
- Elevation above sea level (m)
Nature Geoscience Article https://doi.org/10.1038/s41561-025-01742-z 180° 180° 120° E 120° E 60° E 60° E 0° 0° 60° W 60° W 120° W 120° W 180° 180° 30° N 30° N 0° 0° 30° S 30° S 60° N 60° N 60° S 60° S 100 0 % 180° 180° 120° E 120° E 60° E 60° E 0° 0° 60° W 60° W 120° W 120° W 180° 180° 30° N 30° N 0° 0° 30° S 30° S 60° N 60° N 60° S 60° S 100 0 % 180° 180° 120° E 120° E 60° E 60° E 0° 0° 60° W 60° W 120° W 120° W 180° 180° 30° N 30° N 0° 0° 30° S 30° S 60° N 60° N 60° S 60° S 100 0 % 180° 180° 120° E 120° E 60° E 60° E 0° 0° 60° W 60° W 120° W 120° W 180° 180° 30° N 30° N 0° 0° 30° S 30° S 60° N 60° N 60° S 60° S 100 0 % 180° 180° 120° E 120° E 60° E 60° E 0° 0° 60° W 60° W 120° W 120° W 180° 180° 30° N 30° N 0° 0° 30° S 30° S 60° N 60° N 60° S 60° S 100 0 % 180° 180° 120° E 120° E 60° E 60° E 0° 0° 60° W 60° W 120° W 120° W 180° 180° 30° N 30° N 0° 0° 30° S 30° S 60° N 60° N 60° S 60° S 100 0 % 180° 180° 120° E 120° E 60° E 60° E 0° 0° 60° W 60° W 120° W 120° W 180° 180° 30° N 30° N 0° 0° 30° S 30° S 60° N 60° N 60° S 60° S 100 0 % 180° 180° 120° E 120° E 60° E 60° E 0° 0° 60° W 60° W 120° W 120° W 180° 180° 30° N 30° N 0° 0° 30° S 30° S 60° N 60° N 60° S 60° S 100 0 % Forest Shrubland Grassland Wetland Available for restoration Potential total cover A B C D E F G H Extended Data Fig. 1 | Potential distribution of modelled ecosystems (A-D) and the available area for restoration or spontaneous establishment (E-H), predicted using SSP1-2.6 (2061–2080). Color coding indicates the percentage of each ecosystem type (predicted and available) within a 1 × 1 km grid. Thus, ecosystem combinations (for example forest steppes and savanna-forest mosaics) are also allowed in our grid-level restoration planning, although the proportion of each constituting ecosystem type appears on different maps. For example, a savanna-forest mosaic landscape can contain forested, shrubby and grassy parts within a grid cell, and their proportional values are shown on each of the three corresponding maps. We excluded potential restoration activities in intensive agricultural and built-up areas and in biomes with low productivity (polar and arid regions).