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Sorption of cadmium(II) and copper(II) by soil humic acids: temperature effects and sorption heterogeneity

机译:腐殖酸对镉和铜的吸附:温度效应和吸附异质性

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Sorption by humic acids is known to modify the bioavailability and toxicity of metals in soils and aquatic systems. The sorption of cadmium(II) and copper(II) to two soil humic acids was measured at pH 6.0 using ion-selective electrode potentiometric titration at different temperatures. Sorption reactions were studied with all components in aqueous solution, or with the humates in suspension. Adsorption reactions were described using a multiple site-binding model, and a model assuming a continuous log-normal distribution of adsorption constants. Adsorption of Cu2+ was more favourable than adsorption of Cd2+. The log-normal distribution model provided the closest fit to observations and allowed parameterisation of adsorption data using a mean adsorption constant (log K μ). Sorption of Cd2+ to dissolved humic acids increased slightly in extent and sorption affinity with increasing temperature, but the effect was small (log K μ 2.96-3.15). A slightly greater temperature effect occurred for sorption of Cd2+ to solid-phase humic acids (log K μ 1.30-2.08). Sorption of copper(II) to both aqueous- and colloidal-phase humates showed more pronounced temperature dependence, with extent of sorption, and sorption affinity, increasing with increasing temperature (log K μ 3.4-4.9 in solution and 1.4-4.5 in suspension). The weaker adsorption of Cd2+ than Cu2+, and smaller temperature effects for dissolved humates than suspended humates, suggested that the observed temperature effects had a kinetic, rather than thermodynamic, origin. For any metal-to-ligand ratio, free metal ion concentration, and by inference metal bioavailability, decreased with increasing temperature. The consistency of the data with kinetic rather than thermodynamic control of metal bioavailability suggests that equilibrium modelling approaches to estimating bioavailability may be insufficient.
机译:众所周知,腐殖酸的吸附会改变金属在土壤和水生系统中的生物利用度和毒性。使用离子选择电极电位滴定法在不同温度下,在pH 6.0时测量了镉(II)和铜(II)对两种土壤腐殖酸的吸附。研究了所有组分在水溶液中或腐殖酸盐在悬浮液中的吸附反应。使用多位点结合模型和假设吸附常数连续对数正态分布的模型描述了吸附反应。 Cu 2 + 的吸附比Cd 2 + 的吸附更有利。对数正态分布模型提供了最接近的观测值,并允许使用平均吸附常数(log K ¼)对吸附数据进行参数化。 Cd 2 + 对腐殖酸的吸附程度随温度升高而在一定程度上和吸附亲和力略有增加,但是效果很小(log K ¼ 2.96-3.15)。固相腐殖酸的吸附Cd 2 + 发生稍大的温度影响(log K ¼ 1.30-2.08)。铜(II)对水和胶体腐殖质的吸附显示出更明显的温度依赖性,随着程度的吸附和吸附亲和力,随着温度的升高而增加(溶液中的log K 3.4-4.9和1.4-4.5的悬浮液)。 Cd 2 + 的吸附作用比Cu 2 + 弱,并且溶解的腐殖质的温度效应小于悬浮的腐殖质,这表明所观察到的温度效应具有动力学而非热力学性质。 ,来源。对于任何金属与配体的比率,自由金属离子浓度以及推断的金属生物利用度随温度升高而降低。数据与金属生物利用度的动力学控制而不是热力学控制的一致性表明,用于估算生物利用度的平衡建模方法可能不够充分。

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  • 来源
    《Chemistry and Ecology》 |2010年第5期|p.371-383|共13页
  • 作者

    Andrew W. Rate;

  • 作者单位

    School of Earth and Environment, The University of Western Australia, Crawley, Australia;

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  • 正文语种 eng
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