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Effect of antecedent soil moisture conditions on emissions and isotopologue distribution of N2O during denitrification

机译:前期土壤水分条件对反硝化过程中N2O排放和同位素分布的影响

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The present study determined the influence of initial moisture conditions on the production and consumption of nitrous oxide (N2O) during denitrification and on the isotopic fingerprint of soil-emitted N2O. Sieved arable soil was pre-incubated at two different moisture contents: pre-wet at 75% and pre-dry at 20% water-filled pore space. After wetting to 90% water-filled pore space the soils were amended with glucose (400 kg C ha(-1)) and KNO3 (80 kg N ha(-1)) and incubated for 10 days under a He/O-2-atmosphere. Antecedent moisture conditions affected denitrification. N-2 + N2O fluxes and the N2O-to-N-2 ratio were higher in soils which were pre-incubated under dry conditions, probably because mobilization of organic C during the pre-treatment enhanced denitrification. Gaseous N fluxes showed similar time patterns of production and reduction of N2O in both treatments, where N2O fluxes were initially increasing and maximised 3-4 days after fertilizer application, and N2 fluxes were delayed by 1-2 days. Time courses of delta N-15(bulk)-N2O and delta O-18-N2O exhibited in both treatments increasing trends until maximum N-2 fluxes occurred, reflecting isotope fractionation during intense NO3- reduction. Later this trend slowed down in the pre-dry treatment, while delta O-18-N2O was constant and delta N-15(bulk)-N2O decreased in the pre-wet treatment. We explain these time patterns by non-homogenous distribution of NO3- and denitrification activity, resulting from application of NO3- and glucose to the surface of the soil. We assume that several process zones were thus created, which affected differently the isotopic signature of N2O and the N2O and N-2 fluxes during the different stages of the process. We modelled the delta N-15(bulk)-N2O using process rates and associated fractionation factors for the pre-treated soils, which confirmed our hypothesis. The site preference (SP) initially decreased while N2O reduction was absent, which we could not explain by the N-flux pattern. During the subsequent increase in N-2 flux, SP and delta O-18-N2O increased concurrently, confirming that this isotope pattern is indicative for N2O reduction to N-2. The possible effect of the antecedent moisture conditions of the soil on N2O emissions was shown to be important
机译:本研究确定了初始水分条件对反硝化过程中一氧化二氮(N2O)的产生和消耗以及土壤排放的N2O的同位素指纹的影响。将筛分的可耕土壤在两种不同的水分含量下进行预培养:在75%的湿度下预先湿润,在20%的含水孔空间内预先干燥。润湿至90%充满水的孔隙空间后,将土壤用葡萄糖(400 kg C ha(-1))和KNO3(80 kg N ha(-1))修正,并在He / O-2下孵育10天-大气层。先前的水分条件影响反硝化作用。在干燥条件下进行预培养的土壤中,N-2 + N2O通量和N2O与N-2的比率较高,这可能是因为预处理过程中有机碳的移动增强了反硝化作用。在两种处理中,气态氮通量显示出相似的生产和减少N2O的时间模式,其中N2O通量最初在肥料施用后3-4天开始增加并最大化,而N2通量被延迟1-2天。两种处理均表现出δN-15(本体)-N2O和δO-18-N2O的时程增加趋势,直到出现最大的N-2通量,这反映了NO3-强烈还原过程中的同位素分馏。后来,这种趋势在预干燥处理中减慢了,而δO-18-N2O不变,而δN-15(bulk)-N2O在预湿处理中有所降低。我们通过将NO3-和葡萄糖应用到土壤表面而导致的NO3-和-反硝化活性的非均匀分布来解释这些时间模式。我们假设由此创建了多个工艺区域,这些工艺区域在工艺的不同阶段对N2O的同位素特征以及N2O和N-2通量的影响不同。我们使用处理后的土壤的处理速率和相关的分馏因子对N-15(散装)-N2O增量进行了建模,这证实了我们的假设。最初的站点偏好(SP)下降了,而N2O的减少却没有出现,这不能由N流量模式来解释。在随后的N-2通量增加期间,SP和δO-18-N2O同时增加,从而证实该同位素模式指示N2O还原为N-2。结果表明,土壤前期水分条件对N2O排放的可能影响很重要

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