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三峡库区小流域土地利用结构变化及其氮素输出控制效应:以兰陵溪小流域为例
摘要点击 2889  全文点击 1513  投稿时间:2016-02-05  修订日期:2016-03-30
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中文关键词  三峡库区  退耕还林  土地利用  面源污染  氮素输出
英文关键词  Three Gorges Reservoir Area  returning farmland to forest  land use  non-point pollution  nitrogen output
作者单位E-mail
吴东 中国林业科学研究院森林生态环境与保护研究所, 国家林业局森林生态环境重点实验室, 北京 100091 wudong901116@163.com 
黄志霖 中国林业科学研究院森林生态环境与保护研究所, 国家林业局森林生态环境重点实验室, 北京 100091
南京林业大学南方现代林业协同创新中心, 南京 210037 
hzlin66@163.com 
肖文发 中国林业科学研究院森林生态环境与保护研究所, 国家林业局森林生态环境重点实验室, 北京 100091  
曾立雄 中国林业科学研究院森林生态环境与保护研究所, 国家林业局森林生态环境重点实验室, 北京 100091  
韩黎阳 中国林业科学研究院森林生态环境与保护研究所, 国家林业局森林生态环境重点实验室, 北京 100091  
中文摘要
      基于三峡库区兰陵溪小流域退耕还林后土地利用结构变化分析,结合2015年汛期流域氮素养分输出监测数据,利用逐步回归定量分析土地利用结构特征对氮素输出的控制效应. 结果表明:①退耕还林工程小流域土地利用结构发生改变,林地、园地面积比例分别增加到76.85%和13.87%,园地多以茶园单一类型片状分布,耕地面积比例锐减至1.16%,且零星分布于林地、园地之间. ②小流域部分监测点总氮浓度超过国家Ⅴ类地表水水质标准,各监测点铵态氮(NH4+-N)、硝态氮(NO3--N)和总氮(TN)输出浓度分别为0.089~0.214 mg·L-1、2.925~13.203 mg·L-1以及3.561~14.572 mg·L-1,硝态氮输出浓度占总氮比例超过80%. ③集水区氮素输出浓度与园地和住宅用地极显著正相关,与林地、未利用地则成极显著负相关,住宅用地和园地类型是主要的氮素输出源. ④小流域土地利用结构调整应优先增加林地,适当控制园地发展,且将住宅用地面积比例控制在5%以下,并通过林茶、林果间作等方式改变小流域部分园地单一类型片状分布格局.
英文摘要
      The nitrogen (N) output in Lanlingxi watershed of Three Gorges Reservoir Area in 2015 was monitored and the current land use map was investigated. Cluster analysis and correlation analysis were used to identify the major sources of pollutants and to discriminate the source and the sink land use types. The effects of land use on N exports were quantitatively analyzed by stepwise regression analysis. The results showed that: ① After the returning farmland to forest project the land use structure of this area changed dramatically. The area proportions of forest land and garden plot increased to 76.85% and 13.87% respectively, and the proportion of cultivated land dropped to 1.16%. Cultivated lands were stellate distributed and garden plots in some catchments were flake distributed. ② The content of TN in some monitoring points surpassed the Class V standard of the national groundwater environmental quality. The ammonium-N (NH4+-N) concentrations ranged 0.089-0.214 mg·L-1, 2.925-13.203 mg·L-1 for nitrate-N (NO3--N) and 3.561-14.572 mg·L-1 for total-N (TN). And NO3--N accounted for more than 80% of TN. ③ There were significant positive correlations between garden plot, residential land and N loss, and negative correlations between forest land, unutilized land and N export, which indicated that the former were N sources and the latter were sinks. ④ Forest land area should be increased and garden plot should be controlled, and the area ratio of residential land should be kept below 5% when adjusting land use structure of this watershed. Moreover, forest-tea and forest-fruits modes should be applied to change single land use type of garden plot in some catchments.

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