Water Pollution Dept, National Research Center, Dokki, Egypt.
J Adv Res. 2013 Jul;4(4):367-74. doi: 10.1016/j.jare.2012.07.004. Epub 2012 Aug 14.
The present work represents the biosorption of Cd(II) and Pb(II) from aqueous solution onto the biomass of the blue green alga Anabaena sphaerica as a function of pH, biosorbent dosage, contact time, and initial metal ion concentrations. Freundlich, Langmuir, and Dubinin-Radushkevich (D-R) models were applied to describe the biosorption isotherm of both metals by A. sphaerica biomass. The biosorption isotherms studies indicated that the biosorption of Cd(II) and Pb(II) follows the Langmuir and Freundlish models. The maximum biosorption capacities (qmax ) were 111.1 and 121.95 mg/g, respectively, at the optimum conditions for each metal. From the D-R isotherm model, the mean free energy was calculated to be 11.7 and 14.3 kJ/mol indicating that the biosorption mechanism of Cd(II) and Pb(II) by A. sphaerica was chemisorption. The FTIR analysis for surface function group of algal biomass revealed the existence of amino, carboxyl, hydroxyl, and carbonyl groups, which are responsible for the biosorption of Cd(II) and Pb(II). The results suggested that the biomass of A. sphaerica is an extremely efficient biosorbent for the removal of Cd(II) and Pb(II) from aqueous solutions.
本研究考察了 pH 值、生物吸附剂用量、接触时间和初始金属离子浓度等因素对蓝藻鱼腥藻生物质吸附 Cd(II)和 Pb(II)的影响。采用 Freundlich、Langmuir 和 Dubinin-Radushkevich(D-R)模型来描述两种金属在鱼腥藻生物质上的吸附等温线。吸附等温线研究表明,Cd(II)和 Pb(II)的吸附均符合 Langmuir 和 Freundlich 模型。在每种金属的最佳条件下,最大吸附容量(qmax)分别为 111.1 和 121.95 mg/g。从 D-R 等温线模型计算得到的平均自由能为 11.7 和 14.3 kJ/mol,表明鱼腥藻对 Cd(II)和 Pb(II)的吸附机制为化学吸附。通过对藻生物质表面官能团的傅里叶变换红外(FTIR)分析,发现了氨基、羧基、羟基和羰基等基团的存在,这些基团是吸附 Cd(II)和 Pb(II)的原因。研究结果表明,鱼腥藻生物质是一种从水溶液中去除 Cd(II)和 Pb(II)的高效生物吸附剂。