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Phosphorus dynamics and movement in soil with long term manure application.

机译:长期施用肥料后土壤中的磷动力学和运动。

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摘要

The objective of this study was to examine the phosphorus (P) dynamics (changes in soil P either in quantity or form) and P movement under field and laboratory conditions as impacted by 33 years of beef cattle manure application at rates equivalent to one, two and three times the normal recommendation rates by Alberta Agriculture (1982), irrigation, and soil depth.;Concentration of sulphate ion (83.8 - 6313.9 mg SO4 2- L-1) and phosphate ions (0 to 7 mg L-1) in the leachate suggest possible anionic exclusion of phosphate ion from soil sorption sites with greater tendencies for the formation of calcium sulphate minerals in the soil and Ca-P-colloidal complexes in soil solution. Movement of these forms of P that is attached to Ca and colloidal particles is a possible mechanism responsible for P leaching observed in the groundwater. Generally, P concentration varies with depths and the greatest volume of soil solution was sampled at 120cm depth. Irrigation events in summer 2006 did not have any significant effect on solution P concentrations.;Sequential extraction of soil P suggests that the largest portion of P is associated with the NaHCO3 and HCl extractable fractions of soil P. The NaOH extractable P fraction remains relatively constant by the rate of manure application, suggesting the limited impact of Fe and Al as P-retaining cations in calcareous system.;Total extractable P (sum of P in the 5 extracts) increased with increasing rate of manure application at depths of 0 to 15 cm and significant impact of increasing rate of manure at 15 to 30 cm depth was only observed at rate of 120 Mg ha-1yr-1. Manure application significantly increased labile P fractions (form of P directly affecting P concentrations in soil solution) at all depth.;Leachate samples collected at depths of 30, 60 and 120 cm from the manured plots using suction cup lysimeters showed a range of concentrations of dissolved phosphorus which can have negative impact on surface and groundwater quality. Total P concentration in unfiltered soil leachate samples ranged between 0 to 7 mg L-1, with a mean concentration of 4 mg L-1. Molybate reactive P concentrations are generally less than 1 mg L-1 resulting in greater concentration of molybdate unreactive P. There is also a high possibility of P forms associated with colloidal particles contributing to the observed high concentration of molybate unreactive P apart from the recalcitrant organic forms of P.;The maximum, minimum and range of P concentrations observed in column leachates from soil samples at 0 to 15 and 15 to 30 cm layer increased with increasing rate of manure application. The inorganic P accounted for about 70 % of the P in the leachates. The maximum P concentrations were generally observed in these soils within the first 5 pore volumes, which is the same for both organic and inorganic forms of P. This confirmed that both organic and inorganic P forms are mobile.;Analysis of the impact of column leaching of the clay loam soil with 20 pore volumes of 0.01M CaCl2 indicate that the HCl fraction was a source of P while the NaHCO3 fraction was a sink for P during the column leaching process. This is confirmed by drastic reduction in HCl extractable P and an increase in NaHCO3 extractable P. This clearly indicates that the HCl fraction which has been classified as non-labile fraction significantly contributed to the P movement in this study.;The water, bicarbonate and HCl fractions are the major extractable P fractions responsible for the leachate P concentration, as positive and significant correlation was observed between these extractable P fractions and leachate P concentration. The highest rate of P movement was also observed at depth of 0 to 15 cm.;These studies confirmed that the rates of manure application over a long period of time should be of concern from environmental point of view as long term manure loading increased soil P content, and rate of release of P into soil solution at favorable hydrologic condition. Excessive loading of P will eventually leads to possible negative impact on soil and water quality.;Manure application in calcareous soil increased P forms associated with Ca. In the event of favorable hydrologic condition, the water, bicarbonate and HCl fractions, which constitute the largest fraction of extractable P, are the main P fractions that contribute to dissolved P in the soil. (Abstract shortened by UMI.)
机译:这项研究的目的是研究33年肉牛粪肥施用量(等于一,二)对磷(P)动力学(土壤磷的数量或形式的变化)和磷在田间和实验室条件下的移动情况是正常农业推荐率(1982年),灌溉和土壤深度的三倍。硫酸根离子(83.8-6313.9 mg SO4 2- L-1)和磷酸根离子(0至7 mg L-1)的浓度渗滤液表明可能从土壤吸附位点排除磷酸根离子,而在土壤中形成硫酸钙矿物和在土壤溶液中形成Ca-P-胶体复合物的趋势更大。这些附着在Ca和胶体颗粒上的P的运动是造成地下水中P浸出的可能机制。通常,磷的浓度随深度而变化,最大土壤溶液体积是在120cm深度处取样的。 2006年夏季的灌溉事件对溶液中P的浓度没有显着影响。;土壤P的顺序提取表明,P的最大部分与土壤P的NaHCO3和HCl提取级分有关。NaOH提取的P级分保持相对恒定。通过施用肥料的速率,表明铁和铝作为钙保持系统中的P保留阳离子的作用有限;随着可施肥速率的增加,在0至15深度处总可提取P(5种提取物中的P的总和)增加仅在120 Mg ha-1yr-1的速率下才能观察到15 cm至30 cm深度的cm cm和粪肥增加速率的显着影响。在所有深度施肥均显着增加了不稳定的P分数(P的形式直接影响土壤溶液中P的浓度);使用吸盘渗漏仪在距施肥区30、60和120 cm的深度处收集的渗滤液样品显示一定浓度范围的溶解的磷可能对地表水和地下水质量产生负面影响。未过滤的土壤渗滤液样品中的总P浓度在0至7 mg L-1之间,平均浓度为4 mg L-1。钼酸盐反应性P的浓度通常小于1 mg L-1,导致钼酸盐非反应性P的浓度更高。除顽固有机物外,与胶体颗粒相关的P形式也有可能导致观察到的高浓度钼酸盐非反应性P P的形式;随着土壤肥料施用量的增加,从土壤样品中0至15厘米和15至30厘米层的渗滤液中观察到的P浓度的最大值,最小值和范围都增加了。无机磷约占渗滤液中磷的70%。通常在这些土壤中的前5个孔体积中观察到最大的P浓度,有机和无机形式的P都相同。这证实了有机和无机P形式都是可移动的。 20孔体积的0.01M CaCl2的粘土壤土的碳酸盐含量表明,在柱浸过程中,HCl组分是P的来源,而NaHCO3组分是P的吸收剂。 HCl可萃取P的急剧减少和NaHCO3可萃取P的增加证实了这一点。这清楚地表明,在本研究中被分类为非不稳定组分的HCl组分显着促进了P的移动。 HCl馏分是造成渗滤液P浓度的主要可提取P馏分,因为在这些可提取P馏分与渗滤液P浓度之间观察到正相关和显着相关。在0至15 cm的深度处也观察到了最高的P运移速度;这些研究证实,从环境角度来看,长期施用肥料的速率应引起关注,因为长期的肥料负荷会增加土壤P水文条件下磷的含量和磷向土壤溶液的释放速率。磷的过量负载最终会对土壤和水质产生不利影响。在钙质土壤中人工施用与钙有关的增加的磷形态。在有利的水文条件下,水,碳酸氢盐和HCl馏分构成可提取P的最大部分,是促使P溶解在土壤中的主要P馏分。 (摘要由UMI缩短。)

著录项

  • 作者单位

    University of Manitoba (Canada).;

  • 授予单位 University of Manitoba (Canada).;
  • 学科 Agriculture Agronomy.;Agriculture Soil Science.;Engineering Environmental.
  • 学位 M.Sc.
  • 年度 2008
  • 页码 175 p.
  • 总页数 175
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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