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Nitrate-N dynamics following improved fallows and maize root development in a Zimbabwean sandy clay loam

机译:津巴布韦沙质壤土中休耕和玉米根系发育改善后的硝态氮动态

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Improved or planted fallows using fast-growing leguminous trees are capable of accumulating large amounts of N through biological N2-fixation and subsoil N capture. During the fallow phase, the cycling of nutrients is largely efficient. However, there are few estimates of the fate of added N during the cropping phase, after the 'safety net' of fallow-tree roots is removed. Nitrate-N at the end of the fallow phase, which is pre-season to the subsequent crop, was monitored in seven land use systems in successive 20-cm soil layers to 120 cm depth at Domboshawa, Zimbabwe in October 2000. Thereafter, nitrate-N dynamics was monitored during cropping phase until April 2001 at 2-week intervals in plots that had previously 2-year planted fallows of Acacia angustissima and Sesbania sesban, and in a continuous maize control. Pre-season nitrate concentrations below 60 cm soil depth were <3 kg N ha−1 layer−1 for S. sesban, A. angustissima, Cajanus cajan and natural woodland compared with the maize (Zea mays L.) control, which had >10 kg N ha−1 layer−1. There was a flush of nitrate in the S. sesbania and A. angustissima plots with the first rains. Topsoil nitrate had increased to >29 kg N ha−1 by the time of establishing the maize crop. This increase in nitrate in the topsoil was not sustained as concentrations decreased rapidly due to leaching. Nitrate then accumulated below 40 cm, early in the season when maize root length density was still low (<0.1 cm cm−3) and inadequate to effectively intercept the nitrate. It is concluded that under light soil and high rainfall conditions, there is an inherent problem in managing nitrate originating from mineralization of organic materials as it accumulates at the beginning of the season, well ahead of peak demand by crops, and is susceptible to leaching before the crop root system develops.
机译:使用快速生长的豆科树木改良或种植休耕地能够通过生物固氮和吸收地下土壤中的氮来积累大量的氮。在休耕阶段,养分循环非常有效。但是,在移除休耕树根的“安全网”之后,几乎没有关于在种植阶段添加N的命运的估计。在2000年10月,在津巴布韦的Domboshawa,在七个土地利用系统中,对连续20厘米土壤层至120厘米深度的休耕期结束前的硝酸盐氮进行了监测。在播种阶段直至2001年4月,以2周为间隔监测-N动态,该田块之前曾种植2年相思树和Sesbania sesban的休耕地,并持续进行了玉米控制。与玉米相比,S。ssban,A。angustissima,Cajanus cajan和天然林地的土壤深度低于60 cm的季前硝酸盐浓度为<3 kg N ha-1 layer-1 L.)对照,其> 10 kg N ha-1 层-1 。第一次降雨时,S。sesbania和A. angustissima地块中硝酸盐含量较高。建立玉米作物时,硝酸表土的硝酸盐氮含量已增加至> 29 kg N ha-1 。由于浸出导致浓度迅速降低,因此表层土壤中硝酸盐的这种增加无法持续。然后,在玉米根长密度仍然很低(<0.1 cm cm-3 )并且不足以有效截留硝酸盐的季节初,硝酸盐在40 cm以下积累。可以得出结论,在轻土壤和高降雨条件下,在管理有机氮矿化产生的硝酸盐时会遇到一个固有问题,因为硝酸盐在季节开始时会积累,远远超过农作物的峰值需求,并且在浸出之前很容易浸出作物根系发达。

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