Biodiv Sci ›› 2025, Vol. 33 ›› Issue (3): 24346.  DOI: 10.17520/biods.2024346  cstr: 32101.14.biods.2024346

• Original Papers: Animal Diversity • Previous Articles     Next Articles

Research on the optimization of wildlife passage spatial layout in Xinjiang

Mengdi Fu1, Yanpeng Zhu1, Yueheng Ren1, Shuang Li1, Le Qin1, Zhengjun Xie2, Qingchun Wang3, Libo Zhang1*   

  1. 1 State Key Laboratory of Environmental Criteria and Risk Assessment, Key Laboratory of Regional Eco-Process and Function Assessment of the Ministry of Ecology and Environment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China 

    2 Xinjiang Lop Nor Wild Camel National Nature Reserve Administration, Urumqi 830011, China 

    3 School of Ecology and Nature Conservation, Beijing Forestry University, Beijing 100083, China

  • Received:2024-07-30 Revised:2024-09-30 Online:2025-03-20 Published:2025-02-22
  • Contact: Libo Zhang

Abstract:

Aims: The rapid expansion of linear infrastructure poses a significant threat to biodiversity. Developing large-scale optimization pathways for wildlife passages is crucial for regional biodiversity conservation. 

Method: We employ the Maximum Entropy (MaxEnt) model, with emphasis on representative wildlife species in Xinjiang, to predict potential habitats and assess the importance of each. The minimal cumulative resistance (MCR) model computes the least-cost paths influenced by linear infrastructure. We then accurately pinpoint the necessary locations and numbers of passages by integrating current and planned roads and fences to improve habitat connectivity, ultimately proposing an optimized spatial layout for wildlife passages. 

Results: Our findings reveal notable ecological differences in the habitat distributions of various representative species. Carnivores are predominantly found in alpine and subalpine regions, while large herbivores show a preference for arid desert areas. High-resistance zones are mainly located where railways and highways intersect protected areas. Our analysis identified 2,494.98 km of passage regions and 4,314 individual passages. Higher technical grades of road are associated with longer passage regions and a greater number of passages. The total length of passages in important regions surpasses that of key regions, but passage density is significantly higher in key regions. 

Conclusion: Given these findings we suggest implementing differentiated passage construction based on the technical grade of linear infrastructure. Further, enhancing passage layout optimization outside protected areas to effectively preserve regional ecological connectivity is necessary to maintain biodiversity.

Key words: wildlife passage, road, fence, MaxEnt model, MCR model