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Scale effect of Li-Xiang Railway construction impact on landscape pattern and its ecological risk.

WANG De-zhi1, QIU Peng-hua2, FANG Yuan-min1   

  1. (1Faculty of Land Resource Engineering, Kunming University of Science and Technology, Kunming 650093, China; 2School of Geography and Tourism, Hainan Normal University, Haikou 571158, China)
  • Online:2015-08-18 Published:2015-08-18

Abstract: As a large corridor project, plateau railway has multiple points and passes various sensitive environments along the railway. The determination of the scope of impact on ecological environment from railway construction is often controversial in ecological impact assessment work. Taking the TangbuJiantang section of LiXiang Railway as study object, and using present land use map (1:10000) in 2012 and DEM as data sources, corridor cutting degree index (CCI) and cumulative effect index of corridor (CCEI) were established by topology, buffer zone and landscape metrics methods. Besides, the ecological risk index used for railway construction was improved. By quantitative analysis of characteristics of the spatiotemporal change of landscape pattern and its evolution style at different spatial scales before and after railway construction, the most appropriate evaluation scale of the railway was obtained. Then the characteristics of the spatiotemporal variation of ecological risk within this scale before and after railway construction were analyzed. The results indicated that the cutting model and degree of railway corridor to various landscape types could be effectively reflected by CCI, and the exposure and harm relations between risk sources and risk receptors of railway can be measured by CCEI. After the railway construction, the railway corridor would cause a great deal of middle cutting effect on the landscape along the railroad, which would influence wood land and grassland landscape most greatly, while would cause less effect of edge cutting and internal cutting. Landscape indices within the 600 m buffer zone demonstrated the most obvious scale effect, therefore, the 600 m zone of the railway was set as the most suitable range of ecological impact assessment. Before railway construction, the low ecological risk level covered the biggest part of the 600 m assessment zone. However, after the railway construction, the ecological risk increased significantly, and the most part of the study area was at the moderate ecological risk level. The ecological risk presented ringshaped and multikernel patterns, and was lower in the southern part than in the northern part of the study area.