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在批处理系统和固定床柱中,应用车桑子锯末作为一种有效的生物吸附剂,用于从水溶液中去除结晶紫。

Application of Cordia trichotoma sawdust as an effective biosorbent for removal of crystal violet from aqueous solution in batch system and fixed-bed column.

机构信息

Chemical Engineering Department, Federal University of Santa Maria-UFSM, Roraima Avenue 1000, Santa Maria, RS, 97105-900, Brazil.

Graduate Program in Civil Engineering, Federal University of Santa Maria, Santa Maria, 97105-900, Brazil.

出版信息

Environ Sci Pollut Res Int. 2021 Feb;28(6):6771-6783. doi: 10.1007/s11356-020-11005-6. Epub 2020 Oct 2.

Abstract

In this work, for the first time, Cordia trichotoma sawdust, a residue derived from noble wood processing, was applied as an alternative biosorbent for the removal of crystal violet by discontinuous and continuous biosorption processes. The optimum conditions for biosorption of crystal violet were 7.5 pH and a biosorbent dosage of 0.8 g L. The biosorption kinetics showed that the equilibrium was reached at 120 min, achieving a maximum biosorption capacity of 107 mg g for initial dye concentration of 200 mg L. The Elovich model was the proper model for representing the biosorption kinetics. The isotherm assays showed that the rise of temperature causes an increase in the biosorption capacity of the crystal violet, with a maximum biosorption capacity of 129.77 mg g at 328 K. The Langmuir model was the most proper model for describing the behavior. The sign of ΔG indicates that the process was spontaneous and favorable, whereas the ΔH indicates an endothermic process. The treatment of the colored simulated effluent composed by dyes and salts resulted in 80% of color removal. The application of biosorbent in the fixed-bed system achieved a breakthrough time of 505 min, resulting in 83.35% of color removal. The Thomas and Yoon-Nelson models were able to describe the fixed-bed biosorption behavior. This collection of experimental evidence shows that the Cordia trichotoma sawdust can be applied for the removal of crystal violet and a mixture of other dyes that contain them.

摘要

在这项工作中,首次将来自珍贵木材加工的剩余物——黄槐木屑用作替代生物吸附剂,通过间歇和连续生物吸附过程来去除结晶紫。结晶紫的最佳生物吸附条件为 pH7.5 和生物吸附剂用量 0.8 g/L。生物吸附动力学表明,120 分钟达到平衡,初始染料浓度为 200mg/L 时,最大生物吸附容量为 107mg/g。Elovich 模型是表示生物吸附动力学的合适模型。等温吸附实验表明,温度升高会导致结晶紫的生物吸附容量增加,在 328K 时最大生物吸附容量为 129.77mg/g。Langmuir 模型是描述行为的最合适模型。ΔG 的符号表明该过程是自发和有利的,而 ΔH 表明是吸热过程。处理由染料和盐组成的有色模拟废水可去除 80%的颜色。将生物吸附剂应用于固定床系统可实现 505 分钟的穿透时间,从而去除 83.35%的颜色。Thomas 和 Yoon-Nelson 模型能够描述固定床生物吸附行为。这一系列实验证据表明,黄槐木屑可用于去除结晶紫和含有它们的其他染料混合物。

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