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Iron-impregnated activated carbons precursor to rice hulls and areca nut waste in the remediation of Cu(II) and Pb(II) contaminated waters: a physico-chemical studies

机译:稻壳和槟榔废铁在处理Cu(II)和Pb(II)污染的水中时用铁浸渍的活性炭前体:物理化学研究

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The aim of this study is to exploit the abundantly available rice hulls and areca nut waste in obtaining the activated carbons which is further impregnated with a low dose of iron to obtain the iron-impregnated activated carbon (IIAC) samples. The solids are characterized by the IR and XRD analytical tools whereas the surface morphology is discussed with the SEM images of these solids. BET specific surface area which was obtained for these materials showed that the impregnation of iron did not significantly affect the specific surface area of these solids. Further, the materials were employed in the removal of two different heavy metal toxic ions viz. Cu(II) and Pb(II) under the batch and column reactor operations. The batch data were collected for various physico-chemical parametric studies, viz. effect of solution pH, sorptive concentration, contact time, electrolyte concentrations, etc. The mechanism involved at solid/solution interface was discussed with the help of these studies. Moreover, the equilibrium state sorption data and the time dependence data were utilized to conduct the adsorption isotherm and kinetic modeling studies, respectively. The pseudo-second-rate equation was fitted well to the sorption of these two cations; hence, the sorption capacity was estimated to be 1.770 and 1.926 mg/g (for Cu(II)) and 3.507 and 3.439 mg/g (for Pb(II)), respectively for IIAC-R and IIAC-N. The removal of these two cations was also performed under the dynamic experimentations under column studies. The column data were utilized obtaining the breakthrough curves and hence the breakthrough volumes were obtained. Further, the breakthrough data were utilized to simulate it with Thomas equation and, hence, the loading capacity of the columns was estimated to be 2.746 and 3.057 mg/g (for Cu(II)) and 6.957 and 6.505 mg/g (for Pb(II)), respectively for IIAC-R and IIAC-N samples.
机译:这项研究的目的是利用丰富的稻壳和槟榔来获得活性炭,然后用低剂量的铁进一步浸渍以获得活性炭(IIAC)样品。固体通过IR和XRD分析工具表征,而表面形态用这些固体的SEM图像讨论。从这些材料获得的BET比表面积表明,铁的浸渍不会显着影响这些固体的比表面积。此外,该材料用于去除两种不同的重金属毒性离子,即。分批和塔式反应器操作下的Cu(II)和Pb(II)。收集批次数据以进行各种理化参数研究。溶液pH值,吸附剂浓度,接触时间,电解质浓度等的影响。在这些研究的帮助下讨论了固/溶液界面涉及的机理。此外,利用平衡态吸附数据和时间依赖性数据分别进行吸附等温线和动力学建模研究。拟二级速率方程很好地拟合了这两个阳离子的吸附。因此,对IIAC-R和IIAC-N的吸附容量估计分别为1.770和1.926 mg / g(对于Cu(II))和3.507和3.439 mg / g(对于Pb(II))。还在柱研究的动态实验下去除了这两个阳离子。利用柱数据获得穿透曲线,从而获得穿透体积。此外,利用突破数据通过Thomas方程进行模拟,因此,色谱柱的负载量估计为2.746和3.057 mg / g(对于Cu(II))以及6.957和6.505 mg / g(对于Pb) (II)),分别用于IIAC-R和IIAC-N样品。

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