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应用生态学报 ›› 2026, Vol. 37 ›› Issue (1): 235-242.doi: 10.13287/j.1001-9332.202601.023

• 研究论文 • 上一篇    下一篇

基于最小累积阻力及重力模型的黄河上游甘青段生态安全格局识别及优化

闫子梦1,2, 童华丽1*   

  1. 1西北师范大学地理与环境科学学院, 兰州 730070;
    2中国环境科学研究院, 北京 100085
  • 收稿日期:2025-06-10 修回日期:2025-11-10 发布日期:2026-07-18
  • 通讯作者: *E-mail: tonghl@nwnu.edu.cn
  • 作者简介:闫子梦, 女, 2002年生, 硕士研究生。主要从事生态评估研究。E-mail: yanm925@163.com
  • 基金资助:
    国家自然科学基金项目(42161043,42461038)

Identification and optimization of ecological security pattern in Gansu-Qinghai section of the upper Yellow River based on minimum cumulative resistance and gravity models

YAN Zimeng1,2, TONG Huali1*   

  1. 1College of Geography and Environmental Science, Northwest Normal University, Lanzhou 730070, China;
    2Chinese Research Academy of Environmental Sciences, Beijing 100085, China
  • Received:2025-06-10 Revised:2025-11-10 Published:2026-07-18

摘要: 识别和保护关键的生态要素,构建区域生态安全格局,能够为生态系统提供稳定的空间结构,对维护区域生态系统稳定性具有重要作用。本研究以黄河上游甘青段为例,基于生态敏感性分析,结合高程、坡度、土地利用类型及植被覆盖等数据,综合运用最小累积阻力模型及重力模型,刻画出研究区的生态安全格局,并提出优化方案。结果表明: 2023年,黄河上游甘青段识别生态源地18块,以草地、水域和林地为主,其面积占研究区总面积的10.6%,构成了区域生态屏障的核心空间;构建了由重要廊道(23条)、一般廊道(130条)、重要节点(82个)及一般节点(378个)组成的复合生态网络,结构基本完整但仍存在优化空间;黄河上游甘青段属于典型的高原型阻力面,对西部草地退化带、中部水源涵养-城镇发展交错带和东部城镇扩张显著区域应重点监控。将黄河上游甘青段划分为生态保护区、生态修复核心区、生态管控区及生态保育区4类功能单元,明确各分区空间管控规则,实施差异化生态保护策略,以期实现区域的生态保护修复和空间优化。

关键词: 黄河上游甘青段, 生态安全格局, 重力模型, 最小累积阻力模型, 敏感性分析

Abstract: Identifying and protecting key ecological elements to construct a regional ecological security pattern can provide stable spatial structure for ecosystems, with consequences on regional ecosystem stability. Taking Gansu-Qinghai section of the upper Yellow River as a case, we integrated ecological sensitivity analysis with multi-source data, including elevation, slope, land use type, and NDVI by using the minimum cumulative resistance model and gravity model to delineate the ecological security pattern and propose optimization strategies. Eighteen ecological sources were identified in the Gansu-Qinghai section of the upper Yellow River, primarily comprising grasslands, water body, and forests, accounting for 10.6% of the total area and forming the core space of the regional ecological barrier. We constructed a composite ecological network, consisting of 23 important corridors, 130 general corridors, 82 important nodes, and 378 general nodes, with a structurally complete yet optimizable configuration. The Gansu-Qinghai section of the upper Yellow River exhibited a typical plateau resistance surface, requiring focused monitoring grassland degradation zone in the western region, the interlaced zone of water conservation and urban development in the central region, and the significant area of urban expansion in the eastern region. The functional units of Gansu-Qinghai section of the upper Yellow River could be classified into ecological conservation zones, core restoration zones, ecological management zones, and ecological preservation zones. We should clarify spatial governance principles and implement differentiated ecological protection strategies to achieve regional ecological restoration and spatial optimization.

Key words: Gansu-Qinghai section of the upper Yellow River, ecological security pattern, gravity model, minimum cumulative resistance model, sensitivity analysis