School of Minerals Processing and Bioengineering, Central South University, Changsha, Hunan, 410083, PR China.
School of Minerals Processing and Bioengineering, Central South University, Changsha, Hunan, 410083, PR China.
Chemosphere. 2022 Sep;303(Pt 2):135095. doi: 10.1016/j.chemosphere.2022.135095. Epub 2022 May 23.
Heavy metal pollution is consistently a critical global issue, and bioremediation is regarded as one of the most promising approaches. In this work, the biosorption characteristics of Cd(II), Pb(II), Cu(II) and Zn(II) from aqueous solutions using three phosphorus-accumulating organisms (PAOs) biomasses, Ochrobactrum cicero (PAB-006), Stenotrophomonas maltophilia (PAB-009), and Pseudomonas putida (PAB-0031), as biosorbents were investigated. Results indicated that the equilibrium biosorption capacities of biosorbents to heavy metal ions were sensitive to the solution pH, and increased with increasing pH values. The experimental data of Cd(II), Pb(II), Cu(II) and Zn(II) biosorption were in good agreement with the Pseudo-second-order, Redlich-Peterson and Temkin models, implying that the biosorption was a hybrid chemical reaction-biosorption process. In addition, the theoretical maximum biosorption capacities of Cd(II), Pb(II), Cu(II) and Zn(II) were calculated to be 67.84, 80.23, 50.56 and 63.07 mg/g for PAB-006, 59.99, 87.71, 39.26 and 64.00 mg/g for PAB-009 and 68.31, 85.43, 38.97 and 62.85 mg/g for PAB-031, respectively (pH = 5.0 ± 0.1, T = 25 °C), according to the parameters of the Langmuir model. Moreover, ionic strength had negligible influences or slight promoting effects, while humic acid exhibited positive effects on the removal of heavy metals. Further, PABs were stable and displayed excellent reusability. Characterization techniques of FTIR and XPS revealed that surface complexation, ion exchange, hydrogen bonding and electrostatic interaction were the main mechanisms involved in the biosorption process. In summary, the biosorbent PABs possessed high biosorption performance with excellent reusability, and which hold the great application prospect in the treatment of heavy metal contaminated water.
重金属污染一直是一个全球性的重大问题,生物修复被认为是最有前途的方法之一。在这项工作中,使用三种聚磷菌(PAOs)生物量 Ochrobactrum cicero(PAB-006)、 Stenotrophomonas maltophilia(PAB-009)和 Pseudomonas putida(PAB-0031)作为生物吸附剂,从水溶液中研究了 Cd(II)、Pb(II)、Cu(II)和 Zn(II)的生物吸附特性。结果表明,吸附剂对重金属离子的平衡生物吸附容量对溶液 pH 敏感,并随 pH 值的增加而增加。Cd(II)、Pb(II)、Cu(II)和 Zn(II)的实验吸附数据与伪二级、Redlich-Peterson 和 Temkin 模型吻合较好,表明吸附是一种混合化学反应-生物吸附过程。此外,根据 Langmuir 模型的参数,计算得到 PAB-006 对 Cd(II)、Pb(II)、Cu(II)和 Zn(II)的理论最大生物吸附容量分别为 67.84、80.23、50.56 和 63.07 mg/g,PAB-009 为 59.99、87.71、39.26 和 64.00 mg/g,PAB-031 为 68.31、85.43、38.97 和 62.85 mg/g(pH = 5.0 ± 0.1,T = 25°C)。此外,离子强度的影响可以忽略不计或略有促进作用,而腐殖酸对重金属的去除则表现出积极的影响。此外,PABs 稳定且具有优异的可重复使用性。FTIR 和 XPS 等表征技术表明,表面络合、离子交换、氢键和静电相互作用是生物吸附过程中的主要机制。综上所述,生物吸附剂 PABs 具有较高的生物吸附性能和优异的可重复使用性,在处理重金属污染水方面具有广阔的应用前景。