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Anthropogenic modification of the nitrogen cycling within the Greater Hangzhou Area system, China

机译:中国大杭州地区系统内氮循环的人为改变

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Based on the mass balance approach, a detailed quanti. cation of nitrogen (N) cycling was constructed for an urban-rural complex system, named the Greater Hangzhou Area (GHA) system, for this paper. The GHA is located in the humid climatic region on the southeastern coast of China, one of the earliest regions in the Yangtze Delta to experience economic development. Total N input into the GHA was calculated at 274.66 Gg/yr (1 Gg = 10 9 g), and total output was calculated at 227.33 Gg/yr, while N accumulation was assessed at 47.33 Gg/yr (17.2% of the total N input). Human activity resulted in 73% of N input by means of synthetic fertilizers, human food, animal feed, imported N containing chemicals, fossil fuel combustion, and other items. More than 69.3% of N was released into the atmosphere, and riverine N export accounted for 22.2% of total N output. N input and output to and from the GHA in 1980 were estimated at 119.53 Gg/yr and 98.30 Gg/yr, respectively, with an increase of 130% and 131%, respectively, during a 24-year period (from 1980 to 2004). The N input increase was influenced by synthetic fertilizers (138%), animal feed (225%), N-containing chemicals (371%), riverine input (311%), and N deposition (441%). Compared to the N balance seen in the arid Central Arizona-Phoenix (CAP) system in the United States, the proportion of N transferred to water bodies in the humid GHA system was found to be 36 times higher than the CAP system. Anthropogenic activity, as it typically does, enhanced the flux of N biogeochemistry in the GHA; however, a lack of an N remover (N pollutant treatment facilities) causes excess reactive N (N-r; such as NH3, N2O, NOx), polluting water bodies and the atmosphere within the GHA. Therefore many challenges remain ahead in order to achieve sustainable development in the rapidly developing GHA system.
机译:基于质量平衡方法,进行了详细的定量分析。本文针对城乡复杂系统(称为大杭州地区(GHA)系统)构建了氮(N)循环阳离子。 GHA位于中国东南沿海潮湿的气候区域,这是长江三角洲最早经历经济发展的地区之一。 GHA的总氮输入量为274.66 Gg /年(1 Gg = 10 9 g),总输出量为227.33 Gg /年,而氮积累量估计为47.33 Gg /年(占总N的17.2%输入)。人类活动通过合成肥料,人类食品,动物饲料,进口的含氮化学品,化石燃料燃烧和其他物品产生了73%的氮输入。超过69.3%的氮被释放到大气中,河流氮的出口占氮总产量的22.2%。在1980年至1980年的24年中,GHA的氮输入和输出估计分别为119.53 Gg /年和98.30 Gg /年,分别增长了130%和131%。 。氮素输入量的增加受到合成肥料(138%),动物饲料(225%),含氮化学品(371%),河流输入量(311%)和氮素沉积(441%)的影响。与美国干旱的亚利桑那州中部凤凰城(CAP)系统中的氮平衡相比,在潮湿的GHA系统中转移到水体中的氮比例比CAP系统高36倍。人为活动通常会增加GHA中N生物地球化学的通量。但是,缺乏脱氮剂(N个污染物处理设施)会导致过量的反应性N(N-r;例如NH3,N2O,NOx),污染水体和GHA中的大气。因此,为了在快速发展的GHA系统中实现可持续发展,仍然存在许多挑战。

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