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Isotopic composition of nitrate-nitrogen as a marker of riparian and benthic denitrification at the scale of the whole Seine River system

机译:整个塞纳河系统规模的河​​岸底栖反硝化标志物硝态氮的同位素组成

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Nitrogen budgets established for large river systems reveal that up to 60% of the nitrate exported from agricultural soils is eliminated, either when crossing riparian wetlands areas before even reaching surface waters, or within the rivers themselves through benthic denitrification. The study of nitrogen isotope ratios of riverine nitrates could offer an elegant means to assess the extent of denitrification and thus confirm these budgets, as it is known that denitrification results in a natural 15N enrichment of residual nitrates. The results reported here, for the Seine river system (France), demonstrate the feasibility of this isotopic approach at the scale of large watersheds. On the basis of in situ observations carried out in a large storage reservoir in the upstream Seine catchment (Der Lake), where intensive benthic denitrification occurs, as well as on the basis of laboratory experiments of denitrification under controlled conditions, it is shown that the isotopic discrimination associated with benthic denitrification is minimal (ε of NO3-N ranging from −1.5 to −3.6‰), probably because the rate-limiting step of the process consists of nitrate diffusion through the water-sediment interface. Riparian denitrification on the contrary, when it implies nitrate reduction during convective transfer through reducing environements, causes a much more significant isotopic enrichment of 15N of residual nitrate (ε about −18‰). The authors report measurements of nitrogen isotopic composition of nitrate from rivers of various stream orders in the Seine river system under summer conditions. Anomalies in the data with respect to the values expected from the mixture of the various sources of nitrate are here attributed to riparian denitrification. However, the authors show that because of the patchy distribution of actively denitrifying riparian zones within the drainage network, the isotopic signature conferred to residual nitrate in river water intrinsically provides only a minimum estimate of the extent of denitrification.
机译:为大型河流系统制定的氮预算显示,从农业土壤中输出的硝酸盐最多可消除60%,这既可以在甚至到达地表水之前穿越河岸湿地地区时发生,也可以通过底栖反硝化作用而消除在河流内部。研究河流硝态氮的氮同位素比可以为评估反硝化程度提供一个绝妙的方法,从而证实这些预算,因为众所周知,反硝化作用会自然残留15 N的硝态氮。对于塞纳河系统(法国),此处报告的结果证明了这种同位素方法在大流域范围内的可行性。根据在塞纳河上游集水区(Der Lake)发生大型底栖反硝化作用的大型储水库进行的现场观察,以及在受控条件下进行的反硝化作用的实验室实验的基础上,发现与底栖反硝化作用有关的同位素判别极少(NO3 -N的ε在-1.5至-3.6‰之间),这可能是因为该过程的限速步骤包括硝酸盐通过水-沉积物界面的扩散。相反,河岸反硝化意味着对流转移过程中通过减少环境而使硝酸盐减少,从而导致15 N残留硝酸盐的同位素富集得多(ε约为-18‰)。作者报告了夏季条件下来自塞纳河系统各种河流阶流的河流中硝酸盐的氮同位素组成的测量结果。关于各种硝酸盐源的混合物所期望值的数据异常在此归因于河岸脱氮。然而,这组作者表明,由于排水网络内主动反硝化河岸带的分布不规则,赋予河水中残留硝酸盐的同位素特征本质上仅提供了反硝化程度的最小估计。

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