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Nitrogen and dissolved organic carbon (DOC) losses from an artificially drained grassland on organic soils

机译:在有机土壤上人工流失的草地中的氮和溶解有机碳(DOC)损失

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pstrongAbstract./strong Nitratea??nitrogen (NOsub3/suba??N) as well as dissolved organic carbon (DOC) and nitrogen (DON) concentrations and losses were studied for three and two years, respectively, in a small catchment dominated by a degraded peatland used as intensive grassland. Concentrations in the shallow groundwater were spatially and temporally very variable, with NOsub3/suba??N being the most dynamic component (7.3 ?± 12.5 mg Lsupa??1/sup) and ranging from 0 to 79.4 mg Lsupa??1/sup. Average NOsub3/suba??N concentrations of 10.3 ?± 5.4 mg Lsupa??1/sup (0 to 25.5 mg Lsupa??1/sup) in the ditch draining the catchment and annual NOsub3/suba??N losses of 19, 35 and 26 kg hasupa??1/sup confirmed drained peatlands as an important source of diffuse N pollution. The highest NOsub3/suba??N losses occurred during the wettest year. Resulting from concentration of 2.4 ?± 0.8 mg Lsupa??1/sup (0.7 to 6.2 mg Lsupa??1/sup), DON added a further 4.5 to 6.4 kg hasupa??1/sup to the N losses and thus formed a relevant (15%) component of the total N losses. Ditch DOC concentrations of 24.9 ?± 5.9 mg Lsupa??1/sup (13.1 to 47.7 mg Lsupa??1/sup) resulted in DOC losses of 66 kg hasupa??1/sup in the wet year of 2006/2007 and 39 kg hasupa??1/sup in the dry year of 2007/2008. Ditch DOC concentration were lower than the groundwater DOC concentration of 50.6 ?± 15.2 mg Lsupa??1/sup (14.9 to 88.5 mg Lsupa??1/sup). Both DOC and N concentrations were governed by hydrological conditions, but NOsub3/suba??N reacted much faster and clearer on rising discharge rates than DOC, which tended to be higher under drier conditions. In the third year of the study, the superposition of a very wet summer and land use changes from grassland to arable land in a part of the catchment suggests that, under re-wetting conditions with a high groundwater table in summer, NOsub3/suba??N would diminish quickly, while DOC would remain on a similar level. Further intensification of the land use, on the other hand, would increase N losses to receiving water bodies./p.
机译:> >摘要。研究了硝酸亚硝酸盐(NO 3 a ?? N)以及溶解性有机碳(DOC)和氮(DON)的浓度和损失。在一个由退化的泥炭地用作集约化草原的小流域,分别进行了三年和两年的耕作。浅层地下水的浓度在空间和时间上变化很大,NO 3 a ?? N是最动态的成分(7.3?±12.5 mg L a ?? 1 )范围为0至79.4 mg L a ?? 1 。 NO 3 a ?? N的平均浓度为10.3?±5.4 mg L a ?? 1 (0到25.5 mg L a ?? 1 )在排水流域的沟中,每年NO, 3 a ?? N损失19、35和26 kg ha a ?? 1 扩散氮污染。在最湿的一年中,NO 3 a ?? N损失最高。由于浓度为2.4?±0.8 mg L a ?? 1 (0.7至6.2 mg L a ?? 1 ),DON进一步增加了4.5至6.4 kg ha <对N个损失进行sup> a ?? 1 运算,从而形成了N个总损失的相关部分(15%)。沟渠DOC浓度为24.9±±5.9 mg L a ?? 1 (13.1至47.7 mg L a ?? 1 )导致DOC损失66 kg ha 在2006/2007湿年中a ?? 1 和在2007/2008旱年中39 kg ha a ?? 1 。沟渠DOC浓度低于地下水DOC浓度50.6±±15.2 mg L a ?? 1 (14.9至88.5 mg L a ?? 1 )。 DOC和N的浓度都受水文条件的影响,但NO 3 α?? N在放电率上升时的反应要快得多,而且比DOC清晰,而DOC在干燥的条件下往往更高。在研究的第三年,夏季非常湿润的叠加以及流域一部分中的土地使用从草地变为耕地的变化表明,在夏季有较高地下水位的重新湿润条件下,NO 3 N将迅速减少,而DOC将保持在相似的水平。另一方面,土地利用的进一步集约化将增加接收水体的氮素损失。

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