Department of Microbiology, The American College, Madurai 625 002, Tamil Nadu, India E-mail:
Postgraduate & Research Department of Zoology, The American College, Madurai 625 002, Tamil Nadu, India.
Water Sci Technol. 2022 Feb;85(4):970-986. doi: 10.2166/wst.2022.031.
Through this investigation, we establish the mechanism and physical characterization of zinc (II) sequestration by Morganella morganii ACZ05 strain, which was isolated and characterized from soil polluted by effluents from electroplating industries. As far as we know, there is very little literature concerning zinc biosorption using an environmental strain of M. morganii. The SEM analysis shows the dark porous gaps in the aggregated cell-matrix of test bacterial biomass which is inferred as water channels usually seen in biofilms, as compared to metal-unexposed control. M. morganii is not known to produce biofilms unless in the rare nosocomial conditions. Here, SEM analysis shows the production of biofilms after exposure to zinc (II) at 500 ppm, which has not been previously reported. EDX analysis of bacterial biomass also specified the sorption of zinc (II) by the bacterial cells and the presence of new peaks for zinc in contrast to control. Both XRD and FTIR analysis observations strongly implicate the potential of physical adsorption as a mechanism for heavy metal resistance. Analysis of the cell surface by Atomic force microscopy and examination of the topography revealed cell aggregation occurs during biofilm production after zinc biosorption. Unlike other reports, regular models such as Langmuir isotherm and Freundlich isotherm were found insufficient to explain the physisorption of zinc (II) metal ions on complex multicomponent adsorbents such as the exopolymeric surface of the bacterial cells. However, adsorption kinetics of zinc (II) to the bacterial biomass was most effectively elucidated by a pseudo-second-order kinetic model, suggesting a certain kind of chemisorption that requires further study.
通过这项研究,我们确定了 Morganella morganii ACZ05 菌株螯合锌(II)的机制和物理特性,该菌株是从电镀工业废水污染的土壤中分离和鉴定出来的。据我们所知,目前关于使用 Morganella morganii 的环境菌株进行锌生物吸附的文献很少。SEM 分析显示,测试细菌生物量的聚集细胞基质中存在暗多孔间隙,这被推断为生物膜中通常可见的水通道,而与未暴露于金属的对照相比。除非在罕见的医院感染条件下,Morganella morganii 才会产生生物膜。在这里,SEM 分析显示,在暴露于 500ppm 的锌(II)后会产生生物膜,这是以前没有报道过的。细菌生物量的 EDX 分析还指定了细菌细胞对锌(II)的吸附,并且与对照相比存在新的锌峰。XRD 和 FTIR 分析观察结果都强烈暗示了物理吸附作为重金属抗性机制的潜力。原子力显微镜分析细胞表面,观察形貌,发现细胞在锌生物吸附后产生生物膜时发生聚集。与其他报道不同的是,发现像 Langmuir 等温线和 Freundlich 等温线这样的常规模型不足以解释锌(II)金属离子在复杂多组分吸附剂(如细菌细胞的胞外聚合物表面)上的物理吸附。然而,锌(II)向细菌生物量的吸附动力学最有效地通过拟二级动力学模型来解释,这表明某种需要进一步研究的化学吸附。