嗜卤芽孢杆菌 CdRPSD103 菌株在去除水溶液中的镉(II)方面的生物吸附性能和机理研究

IF 4.1 2区 环境科学与生态学 Q2 BIOTECHNOLOGY & APPLIED MICROBIOLOGY
Ranjan Kumar Mohapatra , Manoranjan Nayak , Pankaj Kumar Parhi , Sony Pandey , Hrudayanath Thatoi , Chitta Ranjan Panda , Younggyun Choi
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引用次数: 0

摘要

从海洋沉积物中分离出一种嗜卤多重重金属抗性细菌--CdRPSD103,并确定其为海拔芽孢杆菌(Bacillus altitudinis)菌株 CdRPSD103。该菌株能够耐受高浓度盐分(高达 13% w/v NaCl)并在其中生长。高纬度芽孢杆菌 CdRPSD103 的生物质可在活体和死体条件下用于镉(II)生物吸附。研究并优化了各种操作参数的影响,如 pH 值、温度、盐度、金属浓度、搅拌速度和生物量用量。在最佳条件下,当镉(II)浓度为 100 至 500 毫克/升时,使用活生物质对镉(II)的去除率为 99.45% 至 55.24%,使用死生物质对镉(II)的去除率为 98.81% 至 53.13%。在初始镉(II)浓度为 500 毫克/升时,每 1 克活生物质和死生物质对镉(II)的最大生物吸附量(qmax)分别为 280.2 毫克和 269.6 毫克。伪二阶模型最适合该 Cd(II)批量生物吸附过程,可描述为两步过程(表面吸附和细胞间积累)。吸附等温线符合代表单层吸附机理的 Langmuir 模型。傅立叶变换红外光谱和场发射扫描电子显微镜以及能量色散 X 射线分析证实,在生物吸附过程中,细菌细胞表面配体(如羟基、羰基羧基和胺基)可能通过表面吸附、离子交换和微沉淀等方式与 Cd+2 离子相互作用。透射电子显微镜分析证实了金属可能在活菌生物质内积累。因此,CdRPSD103 是一种能有效去除含盐金属污染废水中镉(II)的细菌菌株。本研究的发现也有助于今后在批处理和连续处理过程中广泛使用细菌生物质去除工业污染水系统中的各种有害金属离子。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Biosorption performance and mechanism insights of live and dead biomass of halophilic Bacillus altitudinis strain CdRPSD103 for removal of Cd(II) from aqueous solution

Biosorption performance and mechanism insights of live and dead biomass of halophilic Bacillus altitudinis strain CdRPSD103 for removal of Cd(II) from aqueous solution

A halophilic multiple heavy metal-resistant bacterium, CdRPSD103, was isolated from the sea sediment and identified as Bacillus altitudinis strain CdRPSD103. This bacterial strain is able to tolerate and grow at high salt concentrations (up to 13% w/v NaCl). Biomass of Bacillus altitudinis CdRPSD103 is used in both live and dead conditions for Cd(II) biosorption. The effects of various operational parameters, such as pH, temperature, salinity, metal concentration, agitation speed, and biomass dosage, have been studied and optimised. Under optimal conditions, the removal of Cd(II) ranged from 99.45% to 55.24% using live biomass and from 98.81% to 53.13% using dead biomass, at Cd(II) concentrations ranging from 100 to 500 mg/L. The maximum biosorption (qmax) of Cd(II) was 280.2 and 269.6 mg per 1 g of live and dead biomass, respectively, at 500 mg/L of the initial Cd(II) concentration. The pseudo-second-order model was best fitted to this Cd(II) batch biosorption process and can be described as a two-step process (surface adsorption and intercellular accumulation). The adsorption isotherm was found in accordance with the Langmuir model, which represents the monolayer adsorption mechanism. Fourier transform infrared spectroscopy and field emission scanning electron microscopy with an energy dispersive X-ray analyses confirmed the possible interactions of bacterial cell surface ligands like hydroxyl, carbonyl carboxyl, and amine groups with Cd+2 ions during the biosorption process by means of surface adsorption, ion exchange, and micro-precipitation. Transmission electron microscopic analysis confirmed the possible intracellular metal accumulation in live bacterial biomass. Therefore, CdRPSD103 is an effective bacterial strain for removing Cd(II) from saline metal-contaminated wastewater. The findings of this study can also be helpful for future widespread use of bacterial biomass, in both batch and continuous processes, to remove different hazardous metal ions from industrially polluted water systems.

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来源期刊
CiteScore
9.60
自引率
10.40%
发文量
107
审稿时长
21 days
期刊介绍: International Biodeterioration and Biodegradation publishes original research papers and reviews on the biological causes of deterioration or degradation.
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