Resources Ecology

Land-use Change and Its Ecological Effect to the Water in Downstream River Network Area of Dongjiang Basin

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  • 1. a. State Key Laboratory of Earth Surface Processes and Resource Ecology, b. College of Resources Science and Technology, Beijing Normal University, Beijing 100875, China;
    2. China University of Geosciences, Beijing 100083, China

Received date: 2010-04-02

  Revised date: 2010-05-09

  Online published: 2010-08-20

Abstract

Dongguan plays an great important role in the utilization of water resources around the Pearl River Delta and Dongjiang watershed. However, the rapid urbanization leads to severe land use change in this area. It’s necessary to realize land use change characteristics and especially its ecological effect on the water. This kind of research would improve our strategies making on the land use planning and water resources management.Based on the multi-temporal remotely sensed data in 1990, 2000 and 2009, this paper takes a research on the land-use change by using land-use change rate, land-use transfer matrix and land scope indicator. Then through several landscape indicators, the paper also describes water landscape and land-use landscape pattern in the buffer around the river and reservoir, in order to understand land-use change ecological effect to the water in Dongguan City. The conclusions can be drawn as follows:1) In recent two decades, the major land use type has changed into urban construction land from forest and agricultural land rapidly, the ratio of cropland, garden and forest has reduced from 23.56%, 13.39%, 28.73% in 1990 to 11.5%, 3.26%, 17.39% separately; while the urban construction land increases from 20.21% to 53.62% sharply, and the change rate of the land use during 2000-2009 is more severe than that in 1990-2000.2) The agriculture area decreased gradually, and the amount of fertilizer and pesticide use has been cut down by 58.30% and 32.35%, which means agriculture non-point source pollution reduces in recent period, meanwhile the increase of urban construction area leads to more urban non-point source pollution, this situation will be more aggravated accompanied with the expansion of urbanization and reduction in water area.3)Water landscape dominance decreases gradually, and water patch become more fragmentation and distributed;while in the reservoir and riparian buffer zone the proportion of construction land increases, and more artificial river channels lead to the reduction in the diversity of riparian habitat.On all accounts, Dongguan should strengthen the protection and management of water resource. In the water pollution control, based on the management of point source pollution, the city should enhance urban non-point source pollution prevention and control.

Cite this article

XIONG Xing, JIANG Yuan, REN Fei-peng, DONG Man-yu, TIAN Yu-hong, LEI Yi-ming . Land-use Change and Its Ecological Effect to the Water in Downstream River Network Area of Dongjiang Basin[J]. JOURNAL OF NATURAL RESOURCES, 2010 , 25(8) : 1320 -1331 . DOI: 10.11849/zrzyxb.2010.08.009

References

[1] Turner B. Land-use and land-cover change science research plan . IHDP report, 1995. [2] Yuan J, Mu Y K, Qing Z G, et al. Impact of land use on plant biodiversity and measures for biodiversity conservation in the Loess Plateau in China—A case study in hilly-gully region of the northern Loess Plateau [J]. Biodiversity and Conservation, 2003, 12(10): 2121-2133. [3] Yuan J, Mu Y K. Agriculture based identification of land use factors for improving sustainable land resource management in northern Thailand—A case study in the Chiang Mai Province [J]. International Journal of Sustainable Development & World Ecology, 2007(14): 382-390. [4] Allan D. Landscapes and riverscapes: The influence of land use on stream ecosystems [J]. Annual Review of Ecology, Evolution and Systematics, 2004, 35: 257-284. [5] Ahearn D S, Sheibley R W, Dahlgren R A. Land use and land cover influence on water quality in the last free-flowing river draining the western Sierra Nevada, California [J]. Journal of Hydrology, 2005, 313: 234-247. [6] 王介勇, 刘彦随. 三亚市土地利用/覆被变化及其驱动机制研究[J]. 自然资源学报, 2009, 24(8): 1458-1466. [7] 彭静, 王浩, 徐天宝. 珠江三角洲的经济发展与水文环境变迁[J]. 水利经济, 2005, 23(6): 5-9. [8] 陈百明, 周小萍. 《土地利用现状分类》国家标准的解读[J]. 自然资源学报, 2007, 11(6): 994-1003. [9] 史培军, 潘耀忠, 陈晋, 等. 深圳市土地利用/覆被变化与生态环境安全分析[J]. 自然资源学报, 1999, 14(4): 293-299. [10] 朱会义, 李秀彬. 关于区域土地利用变化指数模型方法的讨论[J]. 地理学报, 2003, 58(5): 643-650. [11] 何春阳, 史培军, 陈晋, 等. 北京地区城市化过程与机制研究[J]. 地理学报, 2002, 57(3): 363-371. [12] 周婷, 彭少麟, 任文韬. 东江河岸缓冲带景观格局变化对水体恢复的影响[J]. 生态学报, 2009, 29(1): 231-239. [13] 刘学录, 董旺远, 林慧龙. 景观要素的形状指数与形状特征的关系[J]. 甘肃科学学报, 2000, 12(3): 17-20. [14] 张宏锋, 欧阳志云, 郑华, 等. 新疆玛纳斯河流域景观格局变化及其生态效应[J]. 应用生态学报, 2009, 20(6): 1408-1414. [15] Chattopadhyay S, Rani L A, Sangeetha P V. Water quality variations as linked to water quality variations as linked to landuse pattern: A case study in Chalakudy river basin, Kerala [J]. Current Science, 2005, 89(12): 2163-2169. [16] 季冰, 朱远生. 东莞市水污染现状及其对策探讨[J]. 人民珠江, 2007(2): 56-58. [17] 梁锦发. 东莞运河污染状况分析与整治对策研究. 广州: 暨南大学, 2008. [18] 金辉. 东江干流东莞段水质研究[J]. 环境科学研究, 2001, 14(3): 45-48. [19] 张建春, 彭补拙. 河岸带研究及其退化生态系统的恢复与重建[J]. 生态学报, 2003, 23(1): 56-63. [20] 陈玉成, 李章平, 李章成, 等. 城市地表径流污染及其全过程削减[J]. 水土保持学报, 2004, 18(3): 133-136.
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