资源生态

黄土高原的景观格局变化与水土流失研究——以黄土高原马莲河流域为例

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  • 1. 西北师范大学 地理与环境科学学院,兰州 730070;
    2. 陇东学院,甘肃 庆阳 745600
张建香(1987- ),女,甘肃庆阳人,硕士研究生,主要研究区域环境与资源开发。E-mail: zhangjianxiang_67@163.com

收稿日期: 2011-01-04

  修回日期: 2011-05-02

  网络出版日期: 2011-09-20

基金资助

国家自然科学基金资助项目(40961038);中国科学院知识创新工程重要方向项目(KZCX2-YW-Q10-4);公益性行业(气象)科研专项(GYHY200806021-07);生态经济学省级重点学科(5001-21)教育部人文社会科学研究规划项目(09YJA770025)。

Landscape Pattern Change and Soil Erosion Research—Take Malian River Basin in Loess Plateau as an Example

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  • 1. College of Geography and Environmental Sciences, Northwest Normal University, Lanzhou 730070, China;
    2. Longdong University, Qingyang 745600, China

Received date: 2011-01-04

  Revised date: 2011-05-02

  Online published: 2011-09-20

摘要

应用RS/GIS技术和景观生态学研究方法,利用通用土壤流失方程(USLE)分析了黄土高原马莲河流域2000年和2007年的景观格局变化与水土流失。结果表明:马莲河流域的景观格局和水土流失方面近8 a发生了重要变化:①建设用地、水域、中高盖度草地以及林地面积增加,低盖度草地、耕地等面积减少,其中超过50%的低盖度草地补充为中高盖度草地;②斑块数量、斑块密度以及多样性指数在减小,说明斑块破碎化程度减小,生态系统趋于稳定化,生态功能逐渐增强;③土壤侵蚀总量减小12 506.76 t,水土流失明显减弱,其变化原因与当地植被恢复、人类活动、人口城镇化、建设用地增加等因素密切相关,尤其是世行项目和国家退耕还林还草政策的有效实施。

本文引用格式

张建香, 张勃, 张华, 张多勇, 戴声佩, 马中华 . 黄土高原的景观格局变化与水土流失研究——以黄土高原马莲河流域为例[J]. 自然资源学报, 2011 , 26(9) : 1513 -1525 . DOI: 10.11849/zrzyxb.2011.09.007

Abstract

Quantitative research on the pattern of landscape changes and soil erosion of Malian River Basin in Loess Plateau was carried out by means of Landsat ETM+ (2000) and Landsat TM (2007) satellite images, and supported by GIS and RS technology and methods in landscape ecology. Landscape pattern analysis software (Fragstats 3.3) was used to calculate all kinds of landscape index. Universal Soil Loss Equation (USLE) was employed to analyze soil erosion. The results are as follows: important changes took place in the past eight years in landscape patterns and soil erosion of the Malian River Basin. On the one hand, for landscape pattern change: 1) we analyzed the patch types from the level of classification. Construction land, water body, high covered grassland and forest area were increasing, especially in high covered grassland,which was increased from 593108.80 hm2 (2000) to 940098.90 hm2 (2007). Rivers, forests, construction land and reservoirs did not significantly increase and their area increases were 21278.82 hm2, 12561.13 hm2, 4863.72 hm2 and 52.11 hm2, respectively. Instead of low covered grassland, farmland areas were decreased, and the low covered grassland decreased greatly. The low covered grassland area was 542020.78 hm2 in 2000, while it was reduced to 219987.30 hm2 in 2007. The arable land, came the next, reduced by 63712.40 hm2. It can be easily found that over 5% of the low-cover grassland before 2000 was added into the high covered one in the course of the entire landscape pattern change. 2) The landscape level analysis shows that: the total number of landscape patches were 1375428 in Malian River Basin in 2000, but it decreased to 805769 seven years later; patch density decreased from 71.98 patch/hm2 in 2000 to 42.21 patch/hm2 in 2007, indicating the reduction of plaque fragmentation; diversity of the index decreased from 1.31 in 2000 to 1.23 in 2007, reflecting the gradual reduction of the number of landscape elements; patch numbers, patch density and diversity index were decreasing. That indicated a reduction for plaque fragmentation, tending to stabilization for ecosystem and gradual increasing of ecological functions. On the other hand, for the quantitative research in the soil erosion, 1) from 2000 to 2007, the landscape soil erosion modulus was decreased except reservoir. The reducing of forest land was the most significant, whose average erosion modulus decrease was 348.38 kg/(hm2·a) from 2000 to 2007. The construction land came the next, the average amount of erosion modulus decreased by 144.25 kg/(hm2·a) during this period of time, other landscape types of soil reducing was not obvious. 2) Total soil erosion decreased by 12506.76 t, which showed a significant reduction of soil erosion. Most area of Malian River Basin fell into the category of slight and mild erosion, especially the forest in the downstream areas of Ziwuling, where soil erosion was clearly changed from the moderate erosion to the ligh erosion. The river erosion in the deposition zone was more serious, and individual regions were severe erosion. The reasons for the change caused by the restoration of the local vegetation, influence of human activities, urbanization, increasing of construction land and other factors, particularly in the World Bank projects, the state policy of returning farmland to forest and grassland and the effective implementation on it.

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