首页> 外文期刊>Plant and Soil >Effect of lime, dicyandiamide and soil water content on ammonia and nitrous oxide emissions following application of liquid hog manure to a marshland soil.
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Effect of lime, dicyandiamide and soil water content on ammonia and nitrous oxide emissions following application of liquid hog manure to a marshland soil.

机译:在沼泽地土壤上施用猪肥后,石灰,双氰胺和土壤水分对氨和一氧化二氮排放的影响。

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摘要

The loss of nitrogen (N) from field-applied animal manure through ammonia (NH3) volatilisation and nitrous oxide (N2O) emission is of major environmental concern. Both lime and dicyandiamide (DCD) have been suggested as amendments that can mitigate N2O emissions, but simultaneously increase the risk of NH3 volatilisation. This study evaluated the impact of lime and DCD on NH3 and N2O emissions following application of liquid hog manure. Hydrated lime (Ca(OH)2) was added to an acidic soil to achieve three pH levels (4.7, 6.3 and 7.4). Soil samples (100 g) were then placed in 500 ml screw-top Mason-jars and de-ionised water was added to bring the samples to 50, 70 and 90% water-filled pore space (WFPS). Slurry was applied at a rate equivalent to 116,000 l ha-1, while DCD was applied at 30% of the NH4-N rate applied. Jars were sealed and incubated at 21 degrees C for 21 d. Ammonia volatilisation was quantified using boric acid traps, while N2O gas concentration was analysed using gas chromatography. Dicyandiamide had no effect (P&0.05) on either NH3 or N2O emissions. Both NH3 and N2O emissions increased (P&0.05) as WFPS increased, with emissions ranging from 0.9 to 1.4 kg NH3-N ha-1 and 123 to 353 g N2O-N ha-1, respectively. Liming decreased (P&0.01) N2O emissions from 547 to 46 g N2O-N ha-1, but increased (p&0.01) NH3 volatilisation from 0.36 to 1.92 kg NH3-N ha-1. Results suggest that liming to a pH&=6.3 can reduce N2O emissions, however, this reduction will be accompanied by a substantial loss of NH3..
机译:氨气(NH3)的挥发和一氧化二氮(N2O)的排放使田间施用的动物粪便中的氮(N)损失十分严重。已建议使用石灰和双氰胺(DCD)作为可减轻N2O排放但同时增加NH3挥发风险的修正剂。这项研究评估了施用液态猪粪肥后石灰和DCD对NH3和N2O排放的影响。将熟石灰(Ca(OH)2)添加到酸性土壤中以达到三个pH值(4.7、6.3和7.4)。然后将土壤样品(100 g)放入500 ml螺旋盖梅森罐中,并添加去离子水,使样品达到50%,70%和90%的水填充孔隙空间(WFPS)。以等于116,000 l ha-1的速率施用浆料,而以NH4-N施用速率的30%施用DCD。密封广口瓶并在21摄氏度下孵育21天。使用硼酸捕集阱对氨挥发进行定量,同时使用气相色谱仪分析N2O气体浓度。双氰胺对NH 3或N 2 O排放没有影响(P> 0.05)。随着WFPS的增加,NH 3和N 2 O的排放均增加(P <0.05),NH 3 -N ha-1的排放分别为0.9至1.4kg,N 2 O-N ha-1的排放为123至353g。石灰使N2O排放量从547降低(P <0.01)至46 g N2O-N ha-1,但使NH3挥发量从0.36千克增加(p <0.01)至1.92 kg NH3-N ha-1。结果表明,将石灰限制为pH> = 6.3可以减少N 2 O排放,但是,这种减少将伴随大量NH 3的损失。

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