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Scale-dependent linkages between nitrate isotopes and denitrification in surface soils: implications for isotope measurements and models

机译:表层土壤中硝酸盐同位素与反硝化之间的尺度相关联系:对同位素测量和模型的影响

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Natural abundance nitrate (NO3 (-)) isotopes represent a powerful tool for assessing denitrification, yet the scale and context dependence of relationships between isotopes and denitrification have received little attention, especially in surface soils. We measured the NO3 (-) isotope compositions in soil extractions and lysimeter water from a semi-arid meadow and lawn during snowmelt, along with the denitrification potential, bulk O-2, and a proxy for anaerobic microsites. Denitrification potential varied by three orders of magnitude and the slope of delta O-18/delta N-15 in soil-extracted NO3 (-) from all samples measured 1.04 +/- 0.12 (R (2) = 0.64, p 0.0001), consistent with fractionation from denitrification. However, delta N-15 of extracted NO3 (-) was often lower than bulk soil delta N-15 (by up to 24 aEuro degrees), indicative of fractionation during nitrification that was partially overprinted by denitrification. Mean NO3 (-) isotopes in lysimeter water differed from soil extractions by up to 19 aEuro degrees in delta O-18 and 12 aEuro degrees in delta N-15, indicating distinct biogeochemical processing in relatively mobile water versus soil microsites. This implies that NO3 (-) isotopes in streams, which are predominantly fed by mobile water, do not fully reflect terrestrial soil N cycling. Relationships between potential denitrification and delta N-15 of extracted NO3 (-) showed a strong threshold effect culminating in a null relationship at high denitrification rates. Our observations of (1) competing fractionation from nitrification and denitrification in redox-heterogeneous surface soils, (2) large NO3 (-) isotopic differences between relatively immobile and mobile water pools, (3) and the spatial dependence of delta O-18/delta N-15 relationships suggest caution in using NO3 (-) isotopes to infer site or watershed-scale patterns in denitrification.
机译:天然丰富的硝酸盐(NO3(-))同位素是评估反硝化作用的有力工具,但是同位素与反硝化之间关系的规模和背景依赖性却很少受到关注,尤其是在表层土壤中。我们测量了融雪期间半干旱草甸和草坪的土壤提取物和溶渗水中的NO3(-)同位素组成,以及反硝化潜力,大块O-2和厌氧性微场所的替代物。从所有样品中测得的土壤样品中NO3(-)中的反硝化潜能变化了三个数量级,δO-18 /δN-15的斜率是1.04 +/- 0.12(R(2)= 0.64,p <0.0001) ,与反硝化过程中的分馏相一致。但是,提取的NO3(-)的δN-15通常低于散装土壤的δN-15(最多达24 aEuro度),这表明硝化过程中的分馏作用因反硝化作用而部分覆盖。溶渗仪水中的平均NO3(-)同位素与土壤提取物的差异在O-18三角洲高达19 aEuro度,在N-15三角洲高达12 aEuro度,表明相对于土壤微场所而言,相对流动的水具有独特的生物地球化学过程。这意味着主要由流动水供给的河流中的NO3(-)同位素不能完全反映陆地土壤的氮循环。潜在的反硝化作用与提取的NO3(-)的δN-15之间的关系显示出很强的阈值效应,最终在高反硝化率下达到了无效关系。我们的观察结果是:(1)在氧化还原非均质表层土壤中硝化和反硝化的竞争性分级分离;(2)相对不流动和可移动的水池之间存在较大的NO3(-)同位素差异;(3)和δO-18 /的空间依赖性δN-15关系建议在使用NO3(-)同位素推断反硝化过程中的位点或分水岭尺度模式时要谨慎。

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