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丽香铁路建设对沿线景观格局影响的尺度效应及其生态风险

王德智1,邱彭华2**,方源敏1   

  1. (1昆明理工大学国土资源工程学院, 昆明 650093; 2海南师范大学地理与旅游学院, 海口 571158)
  • 出版日期:2015-08-18 发布日期:2015-08-18

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

摘要: 高原铁路作为大型廊道工程,线长点多、途经环境敏感,其对沿线生态环境影响评价范围的界定在环评工作实践中易产生争议.本文以丽香铁路唐布至建塘段为研究对象,利用2012年1∶10000土地利用现状图和数字高程模型为数据源,采用缓冲区与景观指数方法,构建了廊道切割度指数和廊道干扰累积作用指数,改进了衡量铁路建设后的生态风险指数.通过定量分析不同空间尺度下铁路建设前后景观格局时空变化特征和演变规律,得到本段铁路最适宜评价尺度,并在该尺度内对铁路建设前后生态风险时空变化特征进行分析.结果表明:廊道切割度指数有效反映出铁路廊道对各种景观类型的切割方式和程度,廊道干扰累积作用指数可衡量铁路风险源与风险受体之间暴露与危害关系;铁路建设后,铁路廊道将对沿线景观产生较大的正中切割作用,边缘切割和内部切割作用较小,林地和草地所受影响最大;景观格局指数在600 m缓冲区内尺度效应最明显,因此设置600 m为本段铁路最适宜生态影响评价范围;铁路建设前,600 m评价区以低生态风险为主,铁路建设后,生态风险显著增加,以中等以上生态风险区域为主;研究区生态风险具有南低北高,多核环形的分布特征.

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.