干旱区研究 ›› 2025, Vol. 42 ›› Issue (4): 668-681.doi: 10.13866/j.azr.2025.04.09
收稿日期:2024-09-04
修回日期:2025-02-26
出版日期:2025-04-15
发布日期:2025-04-10
作者简介:张艳(1978-),女,博士,副教授,主要从事土地资源管理、生态安全研究. E-mail: zyzhangyan@chd.edu.cn
基金资助:
ZHANG Yan1,2(
), YANG Weixin1,2, LYU Tao1,2
Received:2024-09-04
Revised:2025-02-26
Published:2025-04-15
Online:2025-04-10
摘要:
土地资源是人类生存发展最基本的生产要素,研究土地利用变化驱动因素及未来土地利用情景模拟对区域可持续发展具有重要意义。本文以黄河流域甘肃段为研究区,基于多源数据,采用土地利用转移矩阵、地理探测器(GeoDetector)和混合元胞自动机(MCCA)模型等方法揭示黄河流域甘肃段土地利用演变特征,并开展2035年土地利用多情景模拟。结果表明:(1) 2000—2020年,研究区土地利用覆被以耕地、林地、草地为主,林地草地覆盖度较高,耕地面积显著下降,且耕地和草地之间的转换最为明显。(2) 影响黄河流域甘肃段土地利用变化的主导因素包括高程、气温、降水、距农村居民点距离和人口密度,各驱动因素交互作用后的q值均有所增大。(3) MCCA模型在研究区土地利用模拟过程中有良好的模拟精度,总体精度达到0.903;2035年不同情景模拟结果各异,自然演变情景耕地、未利用地收缩,其余地类均扩张;耕地保护情景保持了耕地现状存量,草地面积下降明显;生态优先情景林地、草地面积上升显著;经济发展情景表现为更积极的开发模式,建设用地显著扩张。研究结果可为黄河流域甘肃段土地管理及高质量发展提供参考。
张艳, 杨维新, 吕韬. 基于GeoDetector-MCCA的土地利用变化驱动因素分析与多情景模拟——以黄河流域甘肃段为例[J]. 干旱区研究, 2025, 42(4): 668-681.
ZHANG Yan, YANG Weixin, LYU Tao. Driving factors analysis and multi-scenario simulation of land use change based on GeoDetector-Mixed-cell Cellular Automata: A case of the Gansu section in the Yellow River Basin[J]. Arid Zone Research, 2025, 42(4): 668-681.
表2
情景构建"
| 情景类型 | 设置依据 | 描述 |
|---|---|---|
| 自然演变情景 | 遵循历史惯性 | 以黄河流域甘肃段2005—2020年土地利用数据为基础利用MCCA模型线性回归模块得到预期土地利用结构占比,不考虑政策等其他约束作用 |
| 耕地保护情景 | 国家粮食安全战略、耕地保护政策 | 严守耕地红线,控制耕地数量,响应国家粮食安全战略,保证区域粮食安全。该情景降低耕地向外转换强度,并减缓建设用地的增长速率 |
| 生态优先情景 | 国土空间生态修复、黄河流域生态保护 | 该情景重点考虑生态环境,强化生态用地保护和多元化利用,将林地、水域预期面积提高5%,且禁止林地、草地、水域转变为建设用地 |
| 经济发展情景 | 城镇化发展动力强劲,建设用地需求增大 | 强调以经济发展和城市建设为核心,保持高速增长的态势,将建设用地预期面积提高至2020年的1.3倍,并减缓耕地、水域的缩减速率 |
表3
模拟情景的转移矩阵"
| 2020— 2035年 | 自然演变 | 耕地保护 | 生态优先 | 经济发展 | |||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| a | b | c | d | e | f | a | b | c | d | e | f | a | b | c | d | e | f | a | b | c | d | e | f | ||||
| a | 1 | 1 | 1 | 0 | 1 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 1 | 1 | 1 | 0 | 1 | 0 | 1 | 1 | 1 | 0 | 1 | 0 | |||
| b | 1 | 1 | 1 | 0 | 0 | 0 | 1 | 1 | 1 | 0 | 1 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 1 | 1 | 1 | 0 | 1 | 0 | |||
| c | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 0 | 1 | 1 | 0 | 0 | 0 | 1 | 1 | 1 | 1 | 1 | 1 | |||
| d | 1 | 0 | 1 | 1 | 1 | 0 | 1 | 0 | 1 | 1 | 1 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 | 0 | 1 | 1 | 1 | 0 | |||
| e | 1 | 0 | 0 | 0 | 1 | 0 | 1 | 0 | 0 | 0 | 1 | 0 | 1 | 0 | 1 | 1 | 1 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | |||
| f | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | |||
表4
2020年与2035年多情景土地利用面积动态变化"
| 土地利用类型 | 2020年 | 2035年 | ||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 利用现状 | 自然演变 | 耕地保护 | 生态优先 | 经济发展 | ||||||||||
| 面积/km2 | 占比/% | 面积/km2 | 占比/% | 面积/km2 | 占比/% | 面积/km2 | 占比/% | 面积/km2 | 占比/% | |||||
| 耕地 | 40377.18 | 28.43 | 38710.09 | 27.26 | 40416.20 | 28.46 | 39016.95 | 27.47 | 39329.49 | 27.69 | ||||
| 林地 | 17864.79 | 12.58 | 17898.04 | 12.60 | 17924.73 | 12.62 | 18323.39 | 12.91 | 18136.55 | 12.77 | ||||
| 草地 | 76359.54 | 53.77 | 77274.01 | 54.41 | 75821.99 | 53.39 | 77316.72 | 54.44 | 76276.51 | 53.71 | ||||
| 水域 | 969.04 | 0.68 | 995.78 | 0.70 | 947.74 | 0.67 | 1009.80 | 0.71 | 1005.10 | 0.71 | ||||
| 建设用地 | 3308.93 | 2.33 | 4153.44 | 2.92 | 3951.87 | 2.77 | 3852.74 | 2.71 | 4285.56 | 3.02 | ||||
| 未利用地 | 3132.55 | 2.21 | 2980.67 | 2.10 | 2949.52 | 2.08 | 2492.42 | 1.76 | 2978.83 | 2.10 | ||||
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