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Examination of nitrate concentration, loading and isotope dynamics in subsurface drainage under standard agricultural cropping in Atlantic Canada

机译:在加拿大大西洋标准农作物种植下进行的地下排水中硝酸盐浓度,负荷和同位素动力学的研究

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Intensive agricultural farming practices have the potential to cause high levels of nitrate—nitrogen (NO_3~-J-N) to be released from tile drainage systems. A better understanding of the temporal dynamics of NOJ-N loading, δ~(15)N and δ~(18)O from standard drainage systems is needed, in order to improve our understanding of NOJ-N transport and transformation processes; particularly, with regards to the imperfectly drained agricultural soils found within Atlantic Canada. Three conventional subsurface drainage plots (48×8 m) placed at a 0.80 m soil depth were monitored over a seven month period on sandy loam soil in Onslow, Nova Scotia. Each plot received similar applications of both organic and inorganic fertilizer. Water samples were obtained and analyzed for NOJ-N concentrations and isotopic signatures of δ~(15)N and δ~(18)O for NO_3~--N. Maximum NO_3~--N loads were observed in the winter and fall, when both discharge and concentration of the NO_3~--N were highest. Mean isotope values in NO_3~ ranged from 3.1 to 8.5%, for δ~(15) N and -3.2 to 17.7‰ for δ~(18)O. Results suggest that NOJ-N from the drainage water was derived from organic sources (i.e. manure and soil organic matter) and that loss via deni-trification does not impart an identifiable signature upon the NO_3~--N pool. The dual isotope approach examined here provides insight into N source and transformation processes which may be contributing to the NO_3~-N found within the drainage water.
机译:集约化农业实践有可能导致瓷砖排水系统释放出高水平的硝酸盐氮(NO_3〜-J-N)。需要更好地了解标准排水系统中NOJ-N负载,δ〜(15)N和δ〜(18)O的时间动态,以增进我们对NOJ-N迁移和转化过程的理解;特别是关于在加拿大大西洋地区发现的排水不完善的农业土壤。在七个月的时间内,对新斯科舍省Onslow的沙质壤土上的三个常规地下排水区(48×8 m)进行了监测,深度为0.80 m。每个地块都接受了有机和无机肥料的相似施用。获得水样并分析NO_3〜--N的NOJ-N浓度和δ〜(15)N和δ〜(18)O的同位素特征。冬季和秋季观测到最大的NO_3〜–N负荷,这时NO_3〜–N的排放量和浓度均最高。对于δ〜(15)N,NO_3〜的平均同位素值在3.1%到8.5%之间;对于δ〜(18)O,在NO_3〜中的平均同位素值在-3.2〜17.7‰之间。结果表明,废水中的NOJ-N来源于有机物(即粪便和土壤有机质),并且通过脱硝作用损失的NOJ-N在NO_3-N池中没有可识别的特征。本文研究的双同位素方法可洞察N的来源和转化过程,这些过程可能有助于排水中发现NO_3〜-N。

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