Arid Land Geography ›› 2026, Vol. 49 ›› Issue (9): 1826-1839.doi: 10.12118/j.issn.1000-6060.2025.703
• Ecology and Environment • Previous Articles Next Articles
BI Wenjun1,2(
), YAN Qingwu1,3(
), ZHAO Fuxin3, YI Minghao3, WU Zihao1,3
Received:2025-10-30
Revised:2025-11-21
Online:2026-09-25
Published:2026-09-07
Contact:
YAN Qingwu
E-mail:ts24160142p31@cumt.edu.cn;yanqingwu@cumt.edu.cn
BI Wenjun, YAN Qingwu, ZHAO Fuxin, YI Minghao, WU Zihao. Spatiotemporal evolution and driving factors of landscape ecological risk in the middle section of the Tianshan Mountains based on the XGBoost-SHAP method[J].Arid Land Geography, 2026, 49(9): 1826-1839.
Tab. 1
Driving factor indicators"
| 数据类型 | 数据名称 | 数据来源 |
|---|---|---|
| 自然地 理因素 | NDVI | 国家青藏高原科学数据中心( |
| 坡度 | 由高程在ArcGIS中计算得到 | |
| 降水量 | 国家地球系统科学数据中心( | |
| 气温 | 国家地球系统科学数据中心( | |
| 社会经 济因素 | 人口密度 | 美国能源部橡树岭国家实验室( |
| GDP | 中国科学院资源环境科学数据中心( |
Tab. 2
Calculation of landscape ecological risk-related indices"
| 相关指数 | 计算公式 | 变量含义 |
|---|---|---|
| 景观损失度(Ri) | Ri=Vi×Di | Vi为第i类景观的景观脆弱度;Di为第i类景观的景观干扰度 |
| 景观脆弱度(Vi) | 归一化处理 | 根据前人研究[ |
| 景观干扰度(Di) | Di=a×Ci+b×Ni+c×Fi | a、b和c分别为Ci、Ni和Fi的权重,且a+b+c=1,根据相关研究[ |
| 景观破碎度(Ci) | ni为第i类景观的斑块数量;Ai为第i类景观的总面积(km2) | |
| 景观分离度(Ni) | A为景观总面积(km2) | |
| 景观分维数(Fi) | Pi为第i类景观的周长(km) |
Tab. 3
Area and proportion of landscape ecological risk from 2005 to 2023"
| 景观生态 风险类型 | 2005年 | 2010年 | 2015年 | 2020年 | 2023年 | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 面积/104 km2 | 占比/% | 面积/104 km2 | 占比/% | 面积/104 km2 | 占比/% | 面积/104 km2 | 占比/% | 面积/104 km2 | 占比/% | |||||
| 低风险 | 13.34 | 23.52 | 13.29 | 23.43 | 13.38 | 23.59 | 13.33 | 23.50 | 13.19 | 23.26 | ||||
| 中低风险 | 10.07 | 17.75 | 11.12 | 19.60 | 11.16 | 19.68 | 10.98 | 19.36 | 11.13 | 19.62 | ||||
| 中风险 | 7.13 | 12.57 | 6.13 | 10.81 | 6.00 | 10.58 | 6.21 | 10.95 | 6.32 | 11.14 | ||||
| 中高风险 | 6.50 | 11.46 | 6.34 | 11.18 | 6.18 | 10.89 | 6.11 | 10.77 | 6.21 | 10.95 | ||||
| 高风险 | 19.68 | 34.70 | 19.84 | 34.98 | 20.00 | 35.26 | 20.09 | 35.42 | 19.87 | 35.03 | ||||
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