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首页> 外文期刊>Soil Science >Modelling diffusion and reaction in soils: V. Nitrogen transformations in organic manure-amended soil.
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Modelling diffusion and reaction in soils: V. Nitrogen transformations in organic manure-amended soil.

机译:模拟土壤中的扩散和反应:V.有机肥料改良土壤中的氮转化。

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Centimetre-scale measurements of nitrogen transport and transformations were carried out in a soil-manure model system corresponding to direct injection of liquid manure into soil. Influence of manure type (cattle or pig manure), initial soil-water,and soil-nitrate content were investigated. The manure type was the dominating factor with respect to both the initial redistribution of water and solutes and the subsequent nitrogen transformation processes. The liquid transport from the pig manure into the soil was rapid and extensive compared with the cattle manure. In both systems, the initial water transport created a low-nitrate zone at the manure-soil interface, possibly limiting denitrification that was insignificant. Nitrification was inhibited initially in the cattle manure systems with high NH4+ and dissolved organic C concentrations. A small N immobilization during the first 2 days of incubation, followed by net mineralization, was seen in all experiments. An Inverse Diffusion-Reaction Model (IDRM) was used to calculate spatial and temporal variations in net nitrate production rates after the initial water transport had ceased. Good agreement was found between IDRM-calculated net nitrate production rates and measured nitrification rates.The net nitrate production rates were higher in the pig manure than in the cattle manure systems in the first 8 to 10 days, but they then decreased rapidly as a result of NH4+ limitation in the pig manure system. Unlike the frequently used mass balance considerations, the IDRM includes the effects of diffusion and, therefore, seems promising for high resolution analyses of solute transformation processes.
机译:在对应于将液态肥料直接注入土壤中的土壤肥料模型系统中,进行了厘米尺度的氮转运和转化的测量。研究了粪肥类型(牛粪或猪粪),初始土壤水和土壤硝酸盐含量的影响。对于水和溶质的初始再分布以及随后的氮转化过程,肥料类型是主要因素。与牛粪相比,从猪粪到土壤的液体运输迅速而广泛。在这两个系统中,最初的水输送在粪肥-土壤界面处形成了一个低硝酸盐区,这可能会限制微不足道的反硝化作用。 NH4 +和溶解的有机碳浓度较高时,牛粪肥料系统中的硝化作用最初受到抑制。在所有实验中,在培养的前两天都固定了少量N,随后出现了净矿化作用。在初始水输送停止后,使用逆扩散反应模型(IDRM)计算净硝酸盐生产率的时空变化。在IDRM计算的净硝酸盐产生速率与测得的硝化速率之间发现了很好的一致性。在头8至10天中,猪粪中的硝酸盐净产生率高于牛粪系统,但随后迅速下降猪粪便系统中NH4 +的限制。与常用的质量平衡考虑因素不同,IDRM包括扩散的影响,因此,对于溶质转化过程的高分辨率分析似乎很有希望。

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