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采用未处理和化学处理的生物吸附剂从水介质中吸附 Cd(II)和 Pb(II)离子的动力学研究。

Kinetic studies of Cd (II) and Pb (II) ions biosorption from aqueous media using untreated and chemically treated biosorbents.

机构信息

Department of Sustainable Development, Environmental Science and Engineering, Kungliga Tekniska Högskolan, Brinellvägen 28, SE-100 44 Stockholm, Sweden E-mail:

Water and Sanitation Department, African Development Bank, Tunis, Tunisia.

出版信息

Water Sci Technol. 2014;69(11):2230-6. doi: 10.2166/wst.2014.147.

DOI:10.2166/wst.2014.147
PMID:24901616
Abstract

Untreated and chemically treated Albizia coriaria, Erythrina abyssinica and Musa spp. were studied in batch for uptake of Cd(2+) and Pb(2+) ions at pH 2.0-9.0 and agitation time of 30-390 min. Optimum biosorption conditions were pH 4 for Pb(2+) ions and pH 5 for Cd(2+) ions, contact time was 3.5 hours at 24 ± 1 °C for 10 mg/L biosorbent dosage and initial metal ions concentration of 20 mg/L. Chemical treatment had a 10-17% biosorption efficiency enhancement for Cd(2+) ions and a 1.6-2.3% reduction effect for Pb(2+) ions. The sorption capacities for Cd(2+) and Pb(2+) ions for treated biosorbents were 1.760-1.738 mg g(-1) compared to 1.415-1.539 mg g(-1) for untreated materials. The pseudo second-order model suitably fitted the Cd(2+) and Pb(2+) ions biosorption data with regression coefficients (R(2)) of 0.9784-0.9999. Fitting of the Ho model to the experimental data showed that the biosorption mechanism for both metal ions studied was mainly a chemisorption process. Therefore, treated A. coriaria, E. abyssinica and Musa spp. were potential biosorbents for remediation of Cd(2+) ions and the untreated materials suitable for removing Pb(2+) ions from contaminated aqueous media.

摘要

未经处理和化学处理的 Albizia coriaria、Erythrina abyssinica 和 Musa spp. 在 pH 2.0-9.0 和搅拌时间 30-390 分钟的批处理条件下研究了对 Cd(2+)和 Pb(2+)离子的吸附。最佳吸附条件为 pH 4 对 Pb(2+)离子和 pH 5 对 Cd(2+)离子,接触时间为 24 ± 1 °C 时 3.5 小时,10 mg/L 生物吸附剂剂量和 20 mg/L 初始金属离子浓度。化学处理对 Cd(2+)离子的生物吸附效率提高了 10-17%,对 Pb(2+)离子的降低效果为 1.6-2.3%。处理后的生物吸附剂对 Cd(2+)和 Pb(2+)离子的吸附容量分别为 1.760-1.738 mg/g,而未处理材料的吸附容量分别为 1.415-1.539 mg/g。准二级模型适合拟合 Cd(2+)和 Pb(2+)离子的生物吸附数据,回归系数(R(2))为 0.9784-0.9999。Ho 模型对实验数据的拟合表明,研究的两种金属离子的吸附机制主要是化学吸附过程。因此,经处理的 A. coriaria、E. abyssinica 和 Musa spp. 是修复 Cd(2+)离子的潜在生物吸附剂,未经处理的材料适合从受污染的水介质中去除 Pb(2+)离子。