School of Ecology and Environmental Science & Yunnan Key Laboratory for Plateau Mountain Ecology and Restoration of Degraded Environments, Yunnan University, Kunming, 650091, People's Republic of China.
Institute of International Rivers and Eco-security, Yunnan University, Kunming, 650091, People's Republic of China.
Environ Sci Pollut Res Int. 2019 Sep;26(27):28135-28145. doi: 10.1007/s11356-019-06017-w. Epub 2019 Jul 30.
Microbial methods are promising and environmentally friendly methods for remediating heavy metal contamination. In this study, a Cr(VI)-resistant bacterial strain, DC-B3, which was identified as Pseudomonas sp. by 16S rDNA gene sequencing, was isolated from heavy metal-contaminated mine soil, and its performance in Cr(VI) removal from wastewater in terms of Cr(VI) reduction and total Cr adsorption was assessed. This strain exhibited a high capability to reduce Cr(VI) to less toxic Cr(III) without the addition of an external electron donor at low pH (2.0). The Cr(VI) reduction capacity and rate both increased linearly with increasing Cr(VI) concentration, with a reduction capacity of 32.0 mg Cr(VI)·g achieved at an initial concentration of 135.0 mg L over 75 h. In addition, 41.0% of the total Cr was removed from the solution by biosorption, and equilibrium was reached within approximately 5 h. The total Cr sorption process was well described by the pseudo-second-order kinetic and Langmuir isotherm models. Desorption assays indicated that NaOH was the most efficient agent for total Cr desorption, and Cr(VI) and generated Cr(III) were both loaded on the DC-B3 biomass. The bacterial cells after Cr treatment were characterized by scanning electron microscopy-energy dispersive X-ray spectrometer and Fourier transform infrared spectroscopy analyses. Strain DC-B3 showed high potential for possible application in the remediation of Cr(VI) contamination in mine areas.
微生物方法是一种有前途且环保的修复重金属污染的方法。本研究从重金属污染的矿区土壤中分离出一株耐铬细菌 DC-B3,通过 16S rDNA 基因测序鉴定为假单胞菌属,并评估了其在废水处理中去除 Cr(VI)的性能,包括 Cr(VI)还原和总 Cr 吸附。该菌株在低 pH(2.0)条件下无需外加电子供体即可将 Cr(VI)还原为毒性较低的 Cr(III),表现出很高的还原能力。Cr(VI)还原能力和还原速率均随 Cr(VI)浓度的增加呈线性增加,在初始浓度为 135.0 mg L 的条件下,经过 75 h 的培养,还原能力达到 32.0 mg Cr(VI)·g。此外,通过生物吸附可去除溶液中 41.0%的总 Cr,约 5 h 即可达到平衡。总 Cr 吸附过程较好地符合拟二级动力学和 Langmuir 等温线模型。解吸实验表明,NaOH 是总 Cr 解吸最有效的试剂,Cr(VI)和生成的 Cr(III)均负载在 DC-B3 生物质上。Cr 处理后的细菌细胞通过扫描电子显微镜-能谱仪和傅里叶变换红外光谱分析进行了表征。菌株 DC-B3 显示出在矿区 Cr(VI)污染修复中应用的巨大潜力。