Plant ecology, resources and taxonomy

Characteristics of Land Cover Change in the Yellow River Estuary Nature Reserve from 1992 to 2010

  • HOU Xue-Hui ,
  • LI Xin-Hua
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  • (Shandong Institute of Agriculture Sustainable Development, Jinan 250100, Shandong China)

Received date: 2015-08-11

  Revised date: 2016-01-15

  Online published: 2015-12-10

Abstract

The characteristics of land cover and land cover change(LUCC) in nature reserve of Yellow River estuary were analyzed by using three phases landsat remote sensing images of 1992, 2000 and 2010. The results showed that the spatial distribution of land cover types in the natural reserve was sympathetic and the main land covers were the sea, tidal flats and dry land during the periods of 1992—2010. The proportion of the same land cover types in the nature reserve all had changed in different degrees. On the whole, the changes of dry land, reservoir, residential land and other land types were not obvious but there are interannual fluctuations. Although the grassland area decreased continuously, the overall change was not obvious. The changes of the shrub area were also not obvious which varied greatly in the interannual. The reed area was reduced especially in the 1992—2000 years, in which a large number of reeds were transformed into dry land types. The aquaculture area increased widely of 6.24×103 hm2, the increased area mainly formed by development of the beach, Tamarix wetlands and Salsa wetlands in 20 years. The changes of sea area were violent, and the main reason for the reduce of the sea area was the conversion of the sea area to the tidal flat. The LUCC in the natural reserve had changed the structure and reduced the ecological service function of the nature reserve. The reasons for the change of LUCC in the Yellow River estuary were both natural factors and human factors, but the driving forces of LUCC in this area were mainly human activities.

Cite this article

HOU Xue-Hui , LI Xin-Hua . Characteristics of Land Cover Change in the Yellow River Estuary Nature Reserve from 1992 to 2010[J]. Subtropical Plant Science, 2015 , 44(04) : 309 -314 . DOI: 10.3969/j.issn.1009-7791.2015.04.009

References

[1] 刘新卫,陈百明,史学正. 国内LUCC研究进展综述[J]. 土壤, 2004,36(2): 132—135.
[2] 王红,宫鹏,刘高焕. 黄河三角洲土地利用土地覆盖变化研究现状与展望[J]. 自然资源学报, 2004,19(1): 110—118.
[3] 马倩. 新疆甘家湖湿地土地利用变化及其生态环境效应[J]. 干旱区资源与环境, 2012,26(1): 189—193.
[4] 尹占娥,许世远. 上海浦东新区土地利用变化及其生态环境效应[J]. 长江流域资源与环境, 2007,16(4): 430—434.
[5] 王丹桂,胡克,马鹏飞,王铭晗,刘霞. 双台河口自然保护区30 a间土地利用/覆被变化及其驱动力分析[J]. 海洋学研究, 2015,33(1): 51—61.
[6] Cui B S, Yang Q C, Yang Z F, Zhang K J. Evaluating the ecological performance of wetland restoration in the Yellow River Delta, China[J]. Ecological Engineering, 2009,35: 1090—1103.
[7] 袁莉蓉,齐婷,喻光明. 内陆湿地土地利用变化的生态效应——以斧头湖为例[J]. 海洋湖沼通报, 2014(1): 129—136.
[8] Matthias B K, Emily W B. Integrative methods to study landscape changes[J]. Land Use Policy, 2001,18: 9—16.
[9] Kelly N M. Changes to the landscape pattern of coastal North Carolina wetlands under the Clean Water Act, 1984—1992[J]. Landscape Ecology, 2001,16: 3—16.
[10] 田家怡,王秀凤,蔡学军,曹桂荣,张红进,万秀敏. 黄河三角洲湿地生态系统保护与恢复技术[M]. 青岛: 中国海洋大学出版社, 2005: 1—26.
[11] 汪小钦,王钦敏,励惠国,刘高焕. 黄河三角洲土地利用/覆盖变化驱动力分析[J]. 资源科学, 2007,29(5): 175—180.
[12] 许学工,陈晓玲,郭洪海,林辉平. 黄河三角洲土地利用与土地覆被的质量变化[J]. 地理学报, 2001,56(6): 640—648.
[13] 王薇,陈为峰,王燃藜,甘运贤. 黄河三角洲新生湿地景观格局特征及其动态变化——以垦利县为例[J]. 水土保持研究, 2010,17(1): 33—38.
[14] 王薇,王昕,黄乾,孙力. 黄河三角洲土地利用时空变化及驱动力研究[J]. 中国农学通报, 2014,30(32): 172—177.
[15] 张成扬,赵智杰. 近10年黄河三角洲土地利用/覆盖时空变化特征与驱动因素定量分析[J]. 北京大学学报(自然科学版), 2015,51(1): 151—158.
[16]刘艳芬,张杰,马毅,单凯,靳晓华,王进河. 1995-1999年黄河三角洲东部自然保护区湿地景观格局变化[J]. 应用生态学报, 2010,21(11): 2904—2911.
[17] 刘庆生,刘高焕,黄翀,宗秀影. 黄河三角洲自然保护区动态变化遥感监测研究[J]. 中国农学通报, 2010,26(16): 376—381.
[18] 何宏谋,陈红莉,刘争胜,张永. 黄河三角洲地区水资源利用研究[J]. 海岸工程, 2000,19(4): 52—58.
[19] 曹建荣,于洪军,徐兴勇,刘衍军,陈华. 黄河三角洲水资源变化特征及其优化配置[J]. 人民黄河, 2010,32(6): 71—72.
[20] 唐娜,崔保山,赵欣胜. 黄河三角洲芦苇湿地的恢复[J]. 生态学报, 2006,26(8): 2616 —2624.
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