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Aggregation of subtropical soil under liming: a study using laser diffraction

机译:雷岭下亚热带土的聚集:激光衍射研究

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Laser diffraction (LD) provides detailed analysis of particle size distribution. Its application to testing the stability of soil aggregates can assist studies on the aggregation of soils with contrasting electrochemical properties. The objectives of the present work were: (a) to propose a protocol for using LD to study soil aggregation, (b) to study the aggregation of an Acrisol under the influence of different doses and forms of lime. Samples were collected in 2005 from a Brazilian Acrisol that in 1994 had received 0.0; 2.0; 8.5 and 17.0 Mg ha-1 of lime, left on the soil surface or incorporated. Aggregates from 4.76 to 8.00 mm diameters were studied using the traditional method proposed by Kemper & Chepil (1965), with wet sieving, while aggregates from 1.00 to 2.00 mm were studied using a CILAS? laser diffractometer that distinguishes particles ranging from 0.04 to 2,500.00 μm. LD readings were made after six consecutive pre-treatments, using agitation times, a chemical dispersion agent and ultrasound. Mean Weighted Diameter (MWD) and the Aggregate Stability Index (ASI) calculated, using the traditional method does not discriminate the treatments. However, LD is able to produce detailed data on soil aggregation, resulting in indexes of stability of aggregates that are linearly related to the doses of lime applied (MWD: R2 = 0.986 and ASI: R2 = 0.876). It may be concluded that electrochemical changes in the Brazilian Acrisol resulting from incorporated lime affect the stability of aggregates, increasing stability with increased doses of lime.
机译:激光衍射(LD)提供了粒度分布的详细分析。其对测试土壤骨料稳定性的应用可以帮助研究与对比电化学性质的土壤聚集。本作本作的目标是:(a)提出使用LD研究土壤聚集的方案,(b)在不同剂量和形式的石灰的影响下研究丙氨酸的聚集。 2005年从1994年收到的巴西酰亚丙基收集了样品。 2.0; 8.5和17.0mg石灰的17.0mg Ha-1,留在土壤表面或掺入。使用kemper&chepil(1965)提出的传统方法研究了4.76至8.00 mm直径的聚集体,湿筛选,而使用CILAS研究了1.00至2.00 mm的聚集体?激光衍射仪,将颗粒与0.04〜2,500μm的颗粒区分开。在连续六种预处理后,使用搅拌时间,化学分散剂和超声波进行LD读数。使用传统方法计算的平均加权直径(MWD)和综合稳定性指数(ASI)不区分处理。然而,LD能够生产关于土壤聚集的详细数据,导致聚集体的稳定性指标与施加的石灰的剂量线性相关(MWD:R2 = 0.986和ASI:R2 = 0.876)。可以得出结论,由掺入的石灰产生的巴西酰基丙基丙氨酸的电化学变化影响了聚集体的稳定性,随着较高剂量的石灰增加了稳定性。

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