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首页> 外文期刊>The Science of the Total Environment >Use of stable nitrogen isotope fractionation to estimate denitrification in small constructed wetlands treating agricultural runoff
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Use of stable nitrogen isotope fractionation to estimate denitrification in small constructed wetlands treating agricultural runoff

机译:使用稳定的氮同位素分级法估算处理农业径流的小型人工湿地中的反硝化作用

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Constructed wetlands (CWs) in the agricultural landscape reduce non-point source pollution through removal of nutrients and particles. The objective of this study was to evaluate if measurements of natural abundance of ~(15)NO_3~- can be used to determine the fate of NO_3~- in different types of small CWs treating agricultural runoff. Nitrogen removal was studied in wetland trenches filled with different filter materials (T1 - sand and gravel; T3 - mixture of peat, shell sand and light-weight aggregates; T8 - barley straw) and a trench formed as a shallow pond (T4). The removal was highest during summer and lowest during autumn and winter. Trench T8 had the highest N removal during summer. Measurements of the natural abundance of ~(15)N in NOi showed that denitrification was not significant during autumn/winter, while it was present in all trenches during summer, but only important for nitrogen removal in trench T8. The ~(15)N enrichment factors of NO_3~- in this study ranged from -2.5 to -5.9%. (T3 and T8, summer), thus smaller than enrichment factors found in laboratory tests of isotope discrimination in denitrification, but similar to factors found for denitrification in groundwater and a large CW. The low enrichment factors compared to laboratory studies was attributed to assimilation in plants/microbes as well as diffusion effect. Based on a modified version of the method presented by Lund et al. [Lund LJ, Home AJ, Williams AE, Estimating denitrification in a large constructed wetland using stable nitrogen isotope ratios. Ecol Engineer 2000; 14: 67-76], denitrification and assimilation were estimated to account for 53 to 99 and 1 to 47%, respectively, of the total N removal during summer. This method is, however, based on a number of assumptions, and there is thus a need for a better knowledge of the effect of plant uptake, microbial assimilation as well as nitrification on N isotopic fractionation before this method can be used to evaluate the contribution of dinitrification in CWs.
机译:农业景观中的人工湿地(CW)通过去除养分和颗粒物来减少面源污染。这项研究的目的是评估〜(15)NO_3〜-的自然丰度的测量是否可用于确定处理农业径流的不同类型小型CW中NO_3〜-的命运。在充满不同过滤材料(T1-沙和砾石; T3-泥炭,贝壳砂和轻质骨料的混合物; T8-大麦秸秆)和形成为浅水池(T4)的沟槽的湿地沟槽中研究了氮的去除。去除率在夏季最高,秋季和冬季最低。 T8沟在夏季的N去除率最高。测量NOi中〜(15)N的自然丰度表明,秋/冬季反硝化作用不明显,而夏季所有沟渠中都存在反硝化作用,但仅对除去T8沟中的氮很重要。本研究中NO_3〜-的〜(15)N富集系数在-2.5%至-5.9%之间。 (T3和T8,夏季),因此比反硝化中同位素歧视的实验室测试中发现的富集因子要小,但与地下水和大型连续水中反硝化的发现因子相似。与实验室研究相比,低富集因子归因于植物/微生物的同化以及扩散作用。基于Lund等人提出的方法的修改版本。 [Lund LJ,Home AJ,Williams AE,使用稳定的氮同位素比率估算大型人工湿地中的反硝化作用。 Ecol工程师2000; 14:67-76],据估计,夏季反硝化和同化分别占总氮去除量的53%至99%和1%至47%。但是,该方法基于许多假设,因此,在此方法可用于评估贡献之前,需要更好地了解植物吸收,微生物同化以及硝化对氮同位素分馏的影响。连续波的反硝化作用

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