Ecology and Environmental Sciences ›› 2025, Vol. 34 ›› Issue (12): 1841-1852.DOI: 10.16258/j.cnki.1674-5906.2025.12.002
• Original article [Ecology] • Previous Articles Next Articles
ZHANG Yan1,2,*(
), ZHANG Shaojuan1,2, LÜ Tao1,2, HE Huiting1,2
Received:2025-04-18
Online:2025-12-18
Published:2025-12-10
张艳1,2,*(
), 张少娟1,2, 吕韬1,2, 贺慧汀1,2
通讯作者:
*
作者简介:张艳(1978年生),女,副教授,博士,研究方向为土地资源管理、生态安全。E-mail: zyzhangyan@chd.edu.cn
基金资助:CLC Number:
ZHANG Yan, ZHANG Shaojuan, LÜ Tao, HE Huiting. Research on the Coupling and Synergistic Relationship between Landscape Ecological Risk and Habitat Quality in the Yellow River Basin (Inner Mongolia Section)[J]. Ecology and Environmental Sciences, 2025, 34(12): 1841-1852.
张艳, 张少娟, 吕韬, 贺慧汀. 黄河流域(内蒙古段)景观生态风险与生境质量的耦合协同关系研究[J]. 生态环境学报, 2025, 34(12): 1841-1852.
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URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2025.12.002
| 土地利用类型 | 生境适宜性 | 相对敏感程度 | ||
|---|---|---|---|---|
| 耕地 | 建设用地 | 未利用地 | ||
| 耕地 | 0.5 | 0.3 | 0.4 | 0.4 |
| 林地 | 1 | 0.45 | 0.8 | 0.2 |
| 草地 | 0.7 | 0.45 | 0.6 | 0.3 |
| 水域 | 0.9 | 0.6 | 0.8 | 0.3 |
| 建设用地 | 0 | 0 | 0 | 0 |
| 未利用地 | 0.2 | 0.2 | 0.2 | 0.2 |
Table1 The suitability of each habitat type and its sensitivity to threat factors
| 土地利用类型 | 生境适宜性 | 相对敏感程度 | ||
|---|---|---|---|---|
| 耕地 | 建设用地 | 未利用地 | ||
| 耕地 | 0.5 | 0.3 | 0.4 | 0.4 |
| 林地 | 1 | 0.45 | 0.8 | 0.2 |
| 草地 | 0.7 | 0.45 | 0.6 | 0.3 |
| 水域 | 0.9 | 0.6 | 0.8 | 0.3 |
| 建设用地 | 0 | 0 | 0 | 0 |
| 未利用地 | 0.2 | 0.2 | 0.2 | 0.2 |
| 威胁因子 | 最大影响距离/km | 权重 | 衰退类型 |
|---|---|---|---|
| 耕地 | 4 | 0.6 | 线性 |
| 建设用地 | 10 | 1 | 线性 |
| 未利用地 | 2 | 0.5 | 线性 |
Table 2 Threat factors and their weights
| 威胁因子 | 最大影响距离/km | 权重 | 衰退类型 |
|---|---|---|---|
| 耕地 | 4 | 0.6 | 线性 |
| 建设用地 | 10 | 1 | 线性 |
| 未利用地 | 2 | 0.5 | 线性 |
| 土地利用类型 | 面积/km2 | 占比/% | |||||
|---|---|---|---|---|---|---|---|
| 2000年 | 2010年 | 2020年 | 2000-2010年 | 2010-2020年 | 2000-2020年 | ||
| 耕地 | 21281.695 | 23793.661 | 20975.804 | 13.73 | 15.35 | 13.53 | |
| 林地 | 6541.095 | 6611.267 | 7403.776 | 4.22 | 4.267 | 4.78 | |
| 草地 | 83584.713 | 80371.011 | 81723.641 | 53.93 | 51.86 | 52.73 | |
| 水域 | 3835.290 | 3624.804 | 3885.915 | 2.47 | 2.34 | 2.51 | |
| 建设用地 | 3947.397 | 4361.625 | 5831.003 | 2.55 | 2.81 | 3.76 | |
| 未利用地 | 35793.758 | 36221.454 | 35162.917 | 23.10 | 23.37 | 22.69 | |
Table 3 Area and proportion of land use in the Yellow River Basin (Inner Mongolia section)
| 土地利用类型 | 面积/km2 | 占比/% | |||||
|---|---|---|---|---|---|---|---|
| 2000年 | 2010年 | 2020年 | 2000-2010年 | 2010-2020年 | 2000-2020年 | ||
| 耕地 | 21281.695 | 23793.661 | 20975.804 | 13.73 | 15.35 | 13.53 | |
| 林地 | 6541.095 | 6611.267 | 7403.776 | 4.22 | 4.267 | 4.78 | |
| 草地 | 83584.713 | 80371.011 | 81723.641 | 53.93 | 51.86 | 52.73 | |
| 水域 | 3835.290 | 3624.804 | 3885.915 | 2.47 | 2.34 | 2.51 | |
| 建设用地 | 3947.397 | 4361.625 | 5831.003 | 2.55 | 2.81 | 3.76 | |
| 未利用地 | 35793.758 | 36221.454 | 35162.917 | 23.10 | 23.37 | 22.69 | |
| 生态风险等级 | 面积/km2 | 变化量/km2 | |||||
|---|---|---|---|---|---|---|---|
| 2000年 | 2010年 | 2020年 | 2000-2010年 | 2010-2020年 | 2000-2020年 | ||
| 低 | 28059.093 | 22821.737 | 23661.174 | −5237.357 | 839.437 | −4397.920 | |
| 较低 | 48665.446 | 39099.514 | 38986.373 | −9565.932 | −113.142 | −9679.073 | |
| 中等 | 31759.915 | 39004.622 | 39895.155 | 7244.706 | 890.533 | 8135.239 | |
| 较高 | 24690.396 | 31165.011 | 29894.906 | 6474.614 | −1270.105 | 5204.509 | |
| 高 | 21808.864 | 22892.833 | 22546.109 | 1083.969 | −346.724 | 737.245 | |
Table 4 Landscape ecological risk area and variation in the study area from 2000 to 2020
| 生态风险等级 | 面积/km2 | 变化量/km2 | |||||
|---|---|---|---|---|---|---|---|
| 2000年 | 2010年 | 2020年 | 2000-2010年 | 2010-2020年 | 2000-2020年 | ||
| 低 | 28059.093 | 22821.737 | 23661.174 | −5237.357 | 839.437 | −4397.920 | |
| 较低 | 48665.446 | 39099.514 | 38986.373 | −9565.932 | −113.142 | −9679.073 | |
| 中等 | 31759.915 | 39004.622 | 39895.155 | 7244.706 | 890.533 | 8135.239 | |
| 较高 | 24690.396 | 31165.011 | 29894.906 | 6474.614 | −1270.105 | 5204.509 | |
| 高 | 21808.864 | 22892.833 | 22546.109 | 1083.969 | −346.724 | 737.245 | |
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