1. 山西省生态环境研究中心,山西,太原,030009
2. 北京山海础石信息技术有限公司,北京,100012
纸质出版:2019
移动端阅览
宁婷, 郭新亚, 荣月静, 等. 基于RUSLE模型的山西省生态系统土壤保持功能重要性评估[J]. 水土保持通报, 2019,39(6):205-210.
Ning Ting, Guo Xinya, Rong Yuejing, et al. Evaluation of Soil Conservation Function Importance of Ecosystems in Shanxi Province Based on RUSLE Model[J]. Bulletin of Soiland Water Conservation, 2019, 39(6): 205-210.
宁婷, 郭新亚, 荣月静, 等. 基于RUSLE模型的山西省生态系统土壤保持功能重要性评估[J]. 水土保持通报, 2019,39(6):205-210. DOI: 10.13961/j.cnki.stbctb.2019.06.030.
Ning Ting, Guo Xinya, Rong Yuejing, et al. Evaluation of Soil Conservation Function Importance of Ecosystems in Shanxi Province Based on RUSLE Model[J]. Bulletin of Soiland Water Conservation, 2019, 39(6): 205-210. DOI: 10.13961/j.cnki.stbctb.2019.06.030.
[目的
]
分析山西省生态系统土壤保持服务功能的空间分布格局,识别山西省土壤保持功能保护的重点区域,为生态保护红线划定和国土空间规划提供参考。[方法
]
采用修正通用水土流失方程(RUSLE)开展山西省土壤保持功能重要性评估。[结果
]
山西省土壤保持总量为6.52×10
9
t/a,单位面积土壤保持强度平均为416.10 t/(hm
2
·a)。土壤保持功能总体呈现“西北低、东南高,盆地低,丘陵和山地高”的空间分布格局,极重要区、重要区和一般重要区的面积分别占山西省国土面积的23.10%,28.33%和48.57%。[结论
]
山西省土壤保持功能极重要区主要分布在太行山、吕梁山、恒山、五台山、太岳山、中条山等组成的“多”字形山地地区,在晋西黄土丘陵沟壑区也有一定分布。
[Objective] The spatial distribution pattern of soil conservation service function in Shanxi Province was analyzed
and the key areas that need to be protected were identified
in order to provide reference for ecological protection redline delineation and national territorial planning.[Methods] The revised universal soil and water loss equation(RUSLE) was used to analyze the importance of soil conservation function.[Results] The total amount of soil conservation was 6.52×109 t/a
and the average amount of soil conservation per unit area was 416.10 t/(hm2·a) during the study period. The spatial distribution pattern of the ecosystem's soil conservation function was low in northwest and high in southeast
as well as low in basin and high in hills and mountains. The areas of extremely important areas
important areas and general important areas accounted for 23.10%
28.33% and 48.57% of the total area of Shanxi Province
respectively.[Conclusion] The extremely important areas of soil conservation function in Shanxi Province were mainly distributed in Taihang Mountain
Luliang Mountain
Heng Mountain
Wutai Mountain
Taiyue Mountain and Zhongtiao Mountain
and it was also widely distributed in loess hill area of western Shanxi Province.
Zhang Caixia, Zhang Leiming, Li Shimei, et al. Soil conservation of national key ecological function areas[J]. Journal of Resources and Ecology, 2015,6(6):397-404.
李该霞,宋蒙亚,谢丽芳,等.江苏省水土保持功能的重要性评价[J].水土保持通报,2016,36(1):236-241.
Terranova O, Antronico L, Coscarelli R, et al. Soil erosion risk scenarios in the Mediterranean environment using RUSLE and GIS:An application model for Calabria(Southern Italy)[J]. Geomorphology, 2009,112(3/4):228-245.
方广玲,香宝,赵卫,等.基于GIS和RUSLE的拉萨河流域土壤侵蚀研究[J].水土保持学报,2015,29(3):6-12.
冯磊,王治国,孙保平,等.黄土高原水土保持功能的重要性评价与分区[J].中国水土保持科学,2012,10(4):16-21.
张静,曹生奎,曹广超,等.青海湖流域土壤保持量动态变化[J].水土保持通报,2016,36(2):326-331.
刘敏超,李迪强,温琰茂,等.三江源地区土壤保持功能空间分析及其价值评估[J].中国环境科学,2005,25(5):627-631.
刘睿,周李磊,彭瑶,等.三峡库区重庆段土壤保持服务时空分布格局研究[J].长江流域资源与环境,2016,25(6):932-942.
李洋,兰安军,钟九生,等.贵州省水土保持功能的重要性评价[J].贵州农业科学,2018,46(2):148-151.
王治江,李培军,万忠成,等.辽宁省生态系统服务重要性评价[J].生态学杂志,2007,26(10):1606-1610.
生态环境部,国家发展改革委.生态保护红线划定指南[Z].北京:生态环境部,2017.
王彬,郑粉莉.水蚀过程的土壤可蚀性研究述评[J].水土保持研究,2013,20(1):277-286.
吴昌广,李生,任华东,等. USLE/RUSLE模型中植被覆盖管理因子的遥感定量估算研究进展[J].应用生态学报,2012,23(6):1728-1732.
王效科,欧阳志云,肖寒,等.中国水土流失敏感性分布规律及其区划研究[J].生态学报,2001,21(1):14-19.
赵乾坤.山西省水土保持功能分区及生态脆弱性评价[D].山东泰安:山东农业大学,2014.
0
浏览量
906
下载量
9
CSCD
关联资源
相关文章
相关作者
相关机构
京公网安备11010802024621