南京林业大学学报(自然科学版) ›› 2016, Vol. 59 ›› Issue (01): 135-141.doi: 10.3969/j.issn.1000-2006.2016.01.022

• 研究论文 • 上一篇    下一篇

贵州山区公路沿线生态系统服务价值变化

郜红娟1,罗绪强1*,韩会庆1,王后阵2   

  1. 1.贵州师范学院地理与旅游学院,贵州 贵阳 550018;
    2.贵州师范大学地理与环境科学学院,贵州 贵阳 550001
  • 出版日期:2016-02-18 发布日期:2016-02-18
  • 基金资助:
    收稿日期:2015-04-06 修回日期:2015-10-06
    基金项目:国家自然科学基金项目(41563007); 贵州省环境科学教学团队基金项目(黔教高[2012]426号)
    第一作者:郜红娟(cgp1963@126.com)。*通信作者:罗绪强(xuqiangluo@163.com),教授,博士。
    引文格式:郜红娟,罗绪强,韩会庆,等. 贵州山区公路沿线生态系统服务价值变化[J]. 南京林业大学学报(自然科学版),2016,40(1):135-141.

The change of ecosystem service value along the road in mountainous region— a case study of provincial road 309 in Majiang County, Guizhou Province

GAO Hongjuan1,LUO Xuqiang1*, HAN Huiqing1,WANG Houzhen2   

  1. 1.College of Geography and Tourism, Guizhou Normal College, Guiyang 550018, China;
    2.College of Geography and Environmental Sciences, Guizhou Normal University, Guiyang 550001, China
  • Online:2016-02-18 Published:2016-02-18

摘要: 为探讨山区公路沿线土地利用变化对生态系统服务价值(ecosystem service value, ESV)的影响,以贵州省麻江县309省道为例,基于1992年、2002年、2012年和2032年土地利用数据和中国陆地生态系统服务单位面积ESV系数,对309省道沿线土地利用变化所引起的ESV变化进行估算。结果表明:①研究期间,耕地和草地持续减少,建设用地不断增加,而不同时期的林地、水域和未利用地或增或减。②1992—2032年间,除情景B外,情景A和C的ESV均不断增加。各地类的ESV变化趋势与各地类面积变化一致。除情景B外,情景A和C的各种ESV均不断增加。越靠近公路的缓冲区(距公路0~500 m区域),ESV变化越剧烈,不同时期各缓冲区ESV变化存在差异。③快速经济发展、退耕还林政策、地形限制等是影响公路沿线ESV变化的主要因素。

Abstract: In order to discuss the effects of land use change along the road in mountains region on the ecosystem service value, we took provincial road 309 in Majiang county in Guizhou Province as an example, and analyzed the change of ecosystem service value along the road resulting from land use change based on land use data 1992, 2002, 2012 and 2032 and ecosystem service value coefficient per unit area in China. The results showed that: ① farmland and grassland were consistently decreasing, construction land would keep increasing, while forest land, water body and unused land underwent a positive or negative change during the study period. ② Ecosystem services value for scenario A and C increased except for scenario B. The variation trend of each ecosystem services value was in accordance with the change trend of each land use type. Each category of ecosystem services value continued to increase for scenario A and C except for scenario B. The change rate of ecosystem service value in 0-500 m buffer was bigger than that in the other buffers. In addition, there were differences between different periods for the change of ecosystem service value in four buffers. ③ Rapid economic development, grain for green policy and terrain were the main factors influencing the change of ecosystem service value along the road in mountains region.

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