Regional Sustainability ›› 2026, Vol. 7 ›› Issue (5): 100391.doi: 10.1016/j.regsus.2026.100391
• Research article • Previous Articles Next Articles
SHI Hana,b,c, PENG Xia,d,e, GUO Jingjinga,d,e, ZHAO Ruxiaa,c,d,e, HAO Guangyoua,d,e,*(
)
Received:2025-07-07
Revised:2026-03-05
Accepted:2026-09-20
Published:2026-09-30
Online:2026-10-12
Contact:
HAO Guangyou
E-mail:haogy@iae.ac.cn
SHI Han, PENG Xi, GUO Jingjing, ZHAO Ruxia, HAO Guangyou. Insights into climatic adaptability of Acer truncatum and Quercus mongolica in typical sandy lands of China using the Maximum Entropy (MaxEnt) model[J]. Regional Sustainability, 2026, 7(5): 100391.
Fig. 1.
Study region and occurrence records of Acer truncatum Bunge and Quercus mongolica Fisch. ex Ledeb. in China (a) and photos of Acer-Quercus sparse forest grassland in sandy regions (b and c). The boundaries of the four major sandy lands were delineated using the 1:100,000 desert (sand) distribution dataset in China (https://data.tpdc.ac.cn/en/data/122c9ac2-53ee-4b9a-ae87-1a980b131c9b; Wang et al., 2013) and land cover data from the Resource and Environmental Science Data Center Platform of the Chinese Academy of Sciences (http://www.resdc.cn/), following the methods described by Yu et al. (2018). Species occurrence records were compiled from the Global Biodiversity Information Facility (GBIF), the Chinese Virtual Herbarium (CVH), published literature (e.g., Wang et al., 2022; Tang et al., 2023; Shi et al., 2024; Tian et al., 2024), and field surveys. Note that the figure is based on the standard map (GS(2024)0650) from the National Platform for Common Geospatial Information Services (https://cloudcenter.tianditu.gov.cn/administrativeDivision) issued by the Ministry of Natural Resources of the People’s Republic of China, and the boundary of the standard map has not been modified."
Table 1
Percentage contributions of the environmental variables used to predict the potential geographic distribution included in the Maximum Entropy (MaxEnt) model for Acer truncatum Bunge and Quercus mongolica Fisch. ex Ledeb."
| A. truncatum | Q. mongolica | ||||
|---|---|---|---|---|---|
| Variable | Description | Contribution (%) | Variable | Description | Contribution (%) |
| bio3 | Isothermality | 2.00 | bio1 | Annual mean temperature | 23.30 |
| bio4 | Temperature seasonality | 23.50 | bio2 | Mean diurnal range | 7.70 |
| bio5 | Max temperature of warmest month | 4.00 | bio3 | Isothermality | 6.30 |
| bio13 | Precipitation of wettest month | 28.50 | bio7 | Temperature annual range | 2.90 |
| bio14 | Precipitation of driest month | 2.10 | bio8 | Mean temperature of wettest quarter | 1.30 |
| bio15 | Precipitation seasonality | 13.50 | bio13 | Precipitation of wettest month | 34.20 |
| elev | Elevation | 25.90 | bio14 | Precipitation of driest month | 18.60 |
| t_texture | Topsoil texture (0-30 cm) | 0.60 | bio15 | Precipitation seasonality | 1.80 |
| elev | Elevation | 2.10 | |||
| t_texture | Topsoil texture (0-30 cm) | 1.90 | |||
Fig. 2.
Current (1970-2000) habitat probability in China (a and d), current potential suitable habitats in China (b and e), and current potential suitable habitats in the four major sandy lands (c and f) for A. truncatum and Q. mongolica. CI, confidence interval. Note that these figures are based on the standard map (GS(2024)0650) from the National Platform for Common Geospatial Information Services (https://cloudcenter.tianditu.gov.cn/administrativeDivision) issued by the Ministry of Natural Resources of the People’s Republic of China, and the boundary of the standard map has not been modified."
Fig. 3.
Future potential suitable habitats of A. truncatum (a-f) and Q. mongolica (g-l) in China under the Shared Socioeconomic Pathway (SSP)126, SSP245, and SSP585 scenarios in 2050 (2041-2060) and 2090 (2081-2100). Note that these figures are based on the standard map (GS(2024)0650) from the National Platform for Common Geospatial Information Services (https://cloudcenter.tianditu.gov.cn/ administrativeDivision) issued by the Ministry of Natural Resources of the People’s Republic of China, and the boundary of the standard map has not been modified."
Fig. 4.
Changes in the potential suitable habitats of A. truncatum (a-f) and Q. mongolica (g-l) in China under the SSP126, SSP245, and SSP585 scenarios in 2050 and 2090. Note that these figures are based on the standard map (GS(2024)0650) from the National Platform for Common Geospatial Information Services (https://cloudcenter.tianditu.gov.cn/administrativeDivision) issued by the Ministry of Natural Resources of the People’s Republic of China, and the boundary of the standard map has not been modified."
Table 2
Changes in potential suitable habitat areas for A. truncatum and Q. mongolica in China and the four major sandy lands under the Shared Socioeconomic Pathway (SSP)126, SSP245, and SSP585 scenarios."
| Climate scenario | Year | Potential suitable habitat area of A. truncatum (×105 km2) | |||||
|---|---|---|---|---|---|---|---|
| In China | In the four major sandy lands | ||||||
| Gain area | Loss area | Stable area | Gain area | Loss area | Stable area | ||
| SSP126 | 2050 | 2.99 | 0.82 | 8.45 | 0.57 | 0.09 | 0.36 |
| 2090 | 2.49 | 1.67 | 7.59 | 0.67 | 0.01 | 0.44 | |
| SSP245 | 2050 | 2.25 | 0.79 | 8.47 | 0.58 | 0.01 | 0.44 |
| 2090 | 4.28 | 0.26 | 9.01 | 0.81 | 0.00 | 0.45 | |
| SSP585 | 2050 | 3.07 | 0.31 | 8.95 | 0.79 | 0.00 | 0.45 |
| 2090 | 4.50 | 0.45 | 8.82 | 0.71 | 0.01 | 0.44 | |
| SSP126 | 2050 | 2.78 | 2.01 | 7.90 | 0.40 | 0.47 | 0.64 |
| 2090 | 3.52 | 1.75 | 8.15 | 0.13 | 0.04 | 1.07 | |
| SSP245 | 2050 | 2.97 | 2.64 | 7.26 | 0.18 | 0.16 | 0.95 |
| 2090 | 2.16 | 4.10 | 5.80 | 0.37 | 0.25 | 0.85 | |
| SSP585 | 2050 | 5.84 | 2.29 | 7.61 | 0.91 | 0.00 | 1.11 |
| 2090 | 4.23 | 6.48 | 3.42 | 0.77 | 0.49 | 0.62 | |
Fig. S1.
Current (1970-2000) habitat suitability probability for Acer truncatum Bunge (a and b) and Quercus mongolica Fisch. ex Ledeb. (c and d) in China based on occurrence records thinned at a 20-km spatial resolution. CI, confidence interval. Note that these figures are based on the standard map (GS(2024)0650) from the National Platform for Common Geospatial Information Services (https://cloudcenter.tianditu.gov.cn/administrativeDivision) issued by the Ministry of Natural Resources of the People’s Republic of China, and the boundary of the standard map has not been modified."
Fig. S2.
Spearman’s correlation coefficients for 19 bioclimatic variables in the distribution of A. truncatum (a) and Q. mongolica (b). bio1, annual mean temperature; bio2, mean diurnal range; bio3, isothermality; bio4, temperature seasonality; bio5, max temperature of warmest month; bio6, min temperature of coldest month; bio7, temperature annual range; bio8, mean temperature of wettest quarter; bio9, mean temperature of driest quarter; bio10, mean temperature of warmest quarter; bio11, mean temperature of coldest quarter; bio12, annual precipitation; bio13, precipitation of wettest month; bio14, precipitation of driest month; bio15, precipitation seasonality; bio16, precipitation of wettest quarter; bio17, precipitation of driest quarter; bio18, precipitation of warmest quarter; bio19, precipitation of coldest quarter."
Fig. S3.
Optimization results of the Maximum Entropy (MaxEnt) model for A. truncatum (a) and Q. mongolica (b) using different feature constraints and regularization multipliers (RMs). L, linear features; Q, quadratic features; P, product features; T, threshold features; H, Hinge features. The delta Akaike Information Criterion (AIC) values were used to test the MaxEnt model complexity under different feature constraints and RMs, with delta AIC=0 indicating the most accurate model predictions."
Fig. S4.
Predicted suitable habitats of A. truncatum (a-c) and Q. mongolica (d-f) in China under different threshold criteria using the MaxEnt model. Panels a and d represent predictions based on the minimum training presence logistic threshold, panels b and e on the 10.00% training presence logistic threshold, and panels c and f on the equal training sensitivity and specificity logistic threshold. Grey shading denotes the current provincial distribution of species documented in iPlant of China (http://www.iplant.cn/). Note that these figures are based on the standard map (GS(2024)0650) from the National Platform for Common Geospatial Information Services (https://cloudcenter.tianditu.gov.cn/administrativeDivision) issued by the Ministry of Natural Resources of the People’s Republic of China, and the boundary of the standard map has not been modified."
Fig. S6.
Future habitat probability distributions for A. truncatum (a-f) and Q. mongolica (g-l) in China under the Shared Socioeconomic Pathway (SSP)126, SSP245, and SSP585 scenarios in 2050 (2041-2060) and 2090 (2081-2100). Note that these figures are based on the standard map (GS(2024)0650) from the National Platform for Common Geospatial Information Services (https://cloudcenter.tianditu. gov.cn/administrativeDivision) issued by the Ministry of Natural Resources of the People’s Republic of China, and the boundary of the standard map has not been modified."
Table S1
Environmental predictors used for the Maximum Entropy (MaxEnt) model to predict the suitable habitats of species distribution under current and future climate scenarios."
| Variable | Description | Unit |
|---|---|---|
| bio1 | Annual mean temperature | °C |
| bio2 | Mean diurnal range | °C |
| bio3 | Isothermality | - |
| bio4 | Temperature seasonality | °C |
| bio5 | Max temperature of warmest month | °C |
| bio6 | Min temperature of coldest month | °C |
| bio7 | Temperature annual range | °C |
| bio8 | Mean temperature of wettest quarter | °C |
| bio9 | Mean temperature of driest quarter | °C |
| bio10 | Mean temperature of warmest quarter | °C |
| bio11 | Mean temperature of coldest quarter | °C |
| bio12 | Annual precipitation | mm |
| bio13 | Precipitation of wettest month | mm |
| bio14 | Precipitation of driest month | mm |
| bio15 | Precipitation seasonality | - |
| bio16 | Precipitation of wettest quarter | mm |
| bio17 | Precipitation of driest quarter | mm |
| bio18 | Precipitation of warmest quarter | mm |
| bio19 | Precipitation of coldest quarter | mm |
| elev | Elevation | m |
| t_texture | Topsoil texture (0-30 cm) | - |
Table S2
Variance inflation factor (VIF) among the retained bioclimatic variables for Acer truncatum Bunge and Quercus mongolica Fisch. ex Ledeb."
| A. truncatum | Q. mongolica | ||
|---|---|---|---|
| Variable | VIF | Variable | VIF |
| bio3 | 1.76 | bio1 | 9.55 |
| bio4 | 1.98 | bio2 | 9.98 |
| bio5 | 1.54 | bio3 | 8.36 |
| bio13 | 2.94 | bio7 | 3.31 |
| bio14 | 4.50 | bio8 | 8.89 |
| bio15 | 5.18 | bio13 | 4.22 |
| bio14 | 4.52 | ||
| bio15 | 6.92 | ||
Table S3
Area under the curve (AUC) values for the predicted potential distribution of A. truncatum and Q. mongolica across different periods under the Shared Socioeconomic Pathway (SSP)126, SSP245, and SSP585 scenarios."
| Species | Period | Scenario | AUC |
|---|---|---|---|
| A. truncatum | Current (1970-2000) | 0.902 | |
| Future (2050) | SSP126 | 0.906 | |
| SSP245 | 0.907 | ||
| SSP585 | 0.905 | ||
| Future (2090) | SSP126 | 0.907 | |
| SSP245 | 0.905 | ||
| SSP585 | 0.907 | ||
| Q. mongolica | Current (1970-2000) | 0.910 | |
| Future (2050) | SSP126 | 0.911 | |
| SSP245 | 0.909 | ||
| SSP585 | 0.905 | ||
| Future (2090) | SSP126 | 0.903 | |
| SSP245 | 0.909 | ||
| SSP585 | 0.909 |
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