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首页> 外文期刊>Plant and Soil >Nitric oxide flux from soil during the growing season of wheat by continuous measurements of the NO soil-atmosphere concentration gradient: a process study
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Nitric oxide flux from soil during the growing season of wheat by continuous measurements of the NO soil-atmosphere concentration gradient: a process study

机译:通过连续测量NO土壤-大气浓度梯度从小麦生长季土壤中的一氧化氮通量:一个过程研究

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摘要

The surface flux of nitric oxide from a wheat field was investigated from 23 March to 29 May 1997 in the Kerzersmoos, Switzerland. A plot fertilized with 19 kg Nthinha-1 in cattle slurry and 40 kg Nthinha-1 in mineral NH4NO3 fertilizer and a plot receiving no nitrogen containing fertilizer were compared. The flux was calculated based on hourly measurements of the NO soil-atmosphere concentration gradient using the one-dimensional soil diffusion model of Galbally and Johansson. The soil bulk diffusion coefficient was determined from measurements of the 222Rn surface flux and the activity gradient between 10 cm depth and the surface. It ranged between 79% and 0.3% of the NO diffusion coefficient in air and was parameterised by air filled soil pore space. The indirectly determined NO flux agreed well with standard flux measurements using dynamic chambers. The largest NO emission was found following fertilizer application and irrigation. The emission occurred in pulses, which lasted for 4 days up to3 weeks coinciding with elevated soil ammonium concentrations. Nitric oxide emission in 5 days following application of cattle slurry were 31 g NO-Nthinha-1 and 5 g NO-Nthinha-1 from the non-fertilized plot, respectively. Nitric oxide emission in 15 daysfollowing application of NH4NO3 was 95 g NO-Nthinha-1 and 10 g NO-Nthinha-1 from the non-fertilised plot, respectively. NO emission in 4 days following irrigation on 21 April were 36 g Nthinha-1 from the fertilised and 39 g Nthinha-1 from the non-fertilized plot. The daily NO emission before and after fertilizer and irrigation pulses was between 0.3 and 0.7 g NO-Nthinha-1thind-1. NO production and NO uptake of the soil was measured regularly. No systematic influence of management or climate on NO uptake was found. NO production was strongly stimulated by fertilizer input and soil moisture content. The simulation of NO production could be reproduced using a nitrification algorithm driven by soil temperature, moisture and ammonium concentration. A NO production rate constant of 1.1X10-3thinh-1 at 15oC was derived from a linear regression between nitrification and NO production. Introducing the parameterization of NO production into the model of Galbally and Johansson the duration and the strength of the NO emission pulses could be reproduced and the total NO emission during the experiment was approximated within a factor of two.
机译:1997年3月23日至5月29日在瑞士的Kerzersmoos考察了麦田中一氧化氮的表面通量。比较了一个以19千克牛粪Nthinha-1和40千克矿物NH4NO3肥料的Nthinha-1施肥的田地和一个没有含氮肥料的田地。通量是根据每小时土壤NO浓度梯度的测量结果,使用Galbally和Johansson的一维土壤扩散模型计算得出的。通过测量222Rn表面通量和10 cm深度与表面之间的活度梯度确定土壤体积扩散系数。其范围为空气中NO扩散系数的79%至0.3%,并由充满空气的土壤孔隙空间进行参数化。间接确定的NO通量与使用动态室进行的标准通量测量非常吻合。施肥和灌溉后NO排放量最大。发射以脉冲形式发生,持续了4天,长达3周,这与土壤铵浓度升高相吻合。在未施肥的牛粪中,施用牛粪后5天的一氧化氮排放量分别为31 g NO-Nthinha-1和5 g NO-Nthinha-1。从未施肥区开始,施用NH4NO3后15天的一氧化氮排放量分别为95 g NO-Nthinha-1和10 g NO-Nthinha-1。在4月21日灌溉后的4天内,未施肥田的NO排放为36 g Nthinha-1,非施肥田为39 g Nthinha-1。施肥和灌溉脉冲前后的每日NO排放量在0.3到0.7 g NO-Nthinha-1thind-1之间。定期测量土壤的NO产生和NO吸收。没有发现管理或气候对NO吸收的系统影响。肥料输入和土壤水分强烈刺激了NO的产生。利用土壤温度,水分和铵离子浓度驱动的硝化算法可以模拟NO的产生。从硝化作用与NO生成之间的线性回归可以得出在15℃时NO生成速率常数为1.1X10-3thinh-1。将NO产生的参数化引入到Galbally和Johansson模型中,可以再现NO发射脉冲的持续时间和强度,并且实验期间的总NO发射可以在大约2倍的范围内估算。

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