魏彦强, 胡华伟, 王文颖, 等. 青藏高原自然保护区建设现状及未来规划建议[J]. 自然保护地,2025,5(4):78−94. DOI: 10.12335/2096-8981.2023122802
引用本文: 魏彦强, 胡华伟, 王文颖, 等. 青藏高原自然保护区建设现状及未来规划建议[J]. 自然保护地,2025,5(4):78−94. DOI: 10.12335/2096-8981.2023122802
WEI Y Q, HU H W, WANG W Y, et al. Current status and future planning recommendations for natural reserve construction on the Qinghai-Tibet Plateau[J]. Natural Protected Areas, 2025, 5(4): 78−94. DOI: 10.12335/2096-8981.2023122802
Citation: WEI Y Q, HU H W, WANG W Y, et al. Current status and future planning recommendations for natural reserve construction on the Qinghai-Tibet Plateau[J]. Natural Protected Areas, 2025, 5(4): 78−94. DOI: 10.12335/2096-8981.2023122802

青藏高原自然保护区建设现状及未来规划建议

Current status and future planning recommendations for natural reserve construction on the Qinghai-Tibet Plateau

  • 摘要:
    目的 青藏高原已建立了众多的自然保护区,自然保护区空间分布合理与否是评估物种是否存在保护空缺的重要依据。
    方法 利用已有的各类保护区统计数据,统计分析了其分布类型及特征,并与人类活动强度等分布格局进行空间分析,指出保护区建设中的问题,提出未来规划建议。
    结果 ①截至2020年底,青藏高原已建立国家级自然保护区54个、省级自然保护区61个。总面积约为8.35×105 km2,占青藏高原总面积的32.32%。目前覆盖了大多数的青藏高原特有和珍稀濒危动植物物种,有效保护了青藏高原的珍稀野生动植物物种,保护效果明显改善。②现有保护区空间分布不均,大面积的保护区设立在海拔较高、物种类型单一的无人区;而高原东南部生物多样性丰富,人类活动较强的低海拔沟谷地区人与自然保护区的冲突日渐突出。随着气候变化和人类活动的影响,野生物种的栖息地将受到很大的影响。
    结论 针对性地提出了喜马拉雅东段藏南河谷针叶林雨林区、藏东南高山深谷针叶林区、川西北山地高寒灌丛草甸区等3个未来重点规划和建设的区域。今后应围绕自然保护区建设,及时协调保护区之间和保护区内部的功能,处理好保护区建设与当地经济发展的矛盾,针对气候变化和人类活动对优先保护区的影响进行长期监测,综合评估已建保护区的保护效果并及时做出规划和建设的调整。

     

    Abstract:
    Objectives Numerous nature reserves have been instituted on the Qinghai-Tibet Plateau (QTP). The rationality of their spatial distribution serves as a crucial basis for assessing whether species face conservation gaps.
    Methods Employing the existing statistical data concerning diverse reserve categories, we statistically analyzed their distribution patterns and characteristics, and conducted a spatial analysis with the distribution of human activity intensity, identifying issues in reserve construction and to propose future planning recommendations.
    Results (1) QTP has established 54 national-level and 61 provincial-level nature reserves, encompassing an aggregate area of approximately 8.35×105 km2, constituting 32.32% of the plateau’s total area. These reserves currently provided refuge for the majority of endemic and rare endangered flora and fauna species on the plateau, thereby ensuring the conservation of this precious wildlife and significantly enhancing conservation outcomes. (2) Existing reserves exhibited uneven spatial distribution: large reserves were concentrated in high-altitude, species-poor uninhabited areas, while conflicts between humans and nature reserves were increasingly prominent in the biodiversity-rich, low-altitude valleys of the southeastern plateau with intense human activities. With the impacts of climate change and human activities, wildlife habitats will face significant disruption.
    Conclusions This paper specifically proposed three key areas for future planning and development: the coniferous rainforest zone in the southern Tibetan valleys of the eastern Himalayas, the alpine deep-valley coniferous forest zone in the southeastern plateau, and the high-altitude shrub-meadow zone in the mountainous regions of the northwestern Sichuan. In the future, efforts should be concentrated on the coordination of the functions of reserves, both internally and among themselves. Such efforts should address conflicts between conservation, development, and the local economic growth. Furthermore, a long-term monitoring of the impact of climate change and human activities to nature reserves is highly needed. Integrated assessment of the efficiency of nature reserves should be caried out timely and make adjustments to planning and construction accordingly.

     

/

返回文章
返回