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聚乙烯醇-海藻酸钠-活性炭固定化菌球处理二氯甲烷的研究
引用本文:戴云飞,杨泽玉,陈颖,叶杰旭,陈建孟,陈东之.聚乙烯醇-海藻酸钠-活性炭固定化菌球处理二氯甲烷的研究[J].环境科学学报,2021,41(2):430-439.
作者姓名:戴云飞  杨泽玉  陈颖  叶杰旭  陈建孟  陈东之
作者单位:浙江工业大学环境学院,杭州310014;宁波华研节能环保安全设计研究有限公司,宁波315800;浙江工业大学环境学院,杭州310014;浙江海洋大学石油化工与环境学院,舟山316022
基金项目:国家重点研发计划子课题(No.2018YFC0214103-02);国家自然科学基金(No.21477116,51778581)
摘    要:本研究以聚乙烯醇-海藻酸钠-活性炭为复合载体、自行筛选的高效降解菌Methylobacterium rhodesianum H13为目标菌制备固定化小球,用于去除二氯甲烷,同时优化了固定化小球的制备条件.结果表明,当聚乙烯醇浓度为8%,海藻酸钠浓度为5%,CaCl2浓度为2%,活性炭浓度为1%,包菌量为0.6 g,钙化时间为8 h时,复合固定化细胞对DCM的降解速率达到最高为18.2 mg·L-1·h-1,同时活性炭的添加对小球的机械强度也有显著提升.与游离细胞相比,固定化细胞具有更好的热稳定性与pH稳定性,并且固定化细胞的重复利用性较好,连续处理9批底物后,DCM降解速率仍保持在13.4 mg·L-1·h-1以上.吸附动力学与等温线拟合结果显示,在固定化载体中加入1%活性炭后,小球对DCM的吸附量明显提高,而且吸附能在更短的时间内达到平衡.吸附动力学符合准二级反应动力学方程,复合载体对DCM的吸附遵循Langmuir吸附模型(R2>0.99).

关 键 词:二氯甲烷  固定化技术  PVA-SA  活性炭  生物降解
收稿时间:2020/4/24 0:00:00
修稿时间:2020/6/24 0:00:00

Removel of DCM by microorganism cells immobilized into polyvinyl alcohol-alginate-activated carbon beads
DAI Yunfei,YANG Zeyu,CHEN Ying,YE Jiexu,CHEN Jianmeng,CHEN Dongzhi.Removel of DCM by microorganism cells immobilized into polyvinyl alcohol-alginate-activated carbon beads[J].Acta Scientiae Circumstantiae,2021,41(2):430-439.
Authors:DAI Yunfei  YANG Zeyu  CHEN Ying  YE Jiexu  CHEN Jianmeng  CHEN Dongzhi
Institution:College of Environment, Zhejiang University of Technology, Hangzhou 310014;Ningbo Huayan Energy Efficiency Environmental Protection Safety Design and Research Co., Ltd, Ningbo 315800;1. College of Environment, Zhejiang University of Technology, Hangzhou 310014;2. College of Petrochemical and Environment, Zhejiang Ocean University, Zhoushan 316022
Abstract:In this study, Methylobacterium rhodesianum H13 for dichloromethane (DCM) removal was immobilized into synthetic polyvinyl alcohol-alginate-activated carbon (PVA-SA-AC) beads. The optimal conditions for preparation were 8% PVA, 5% SA, 2% CaCl2, 1% AC, 0.6 g bacterial biomass and 8 h crosslinking time. The average removal rate of DCM maximized at 18.2 mg·L-1·h-1. The mechanical strength of immobilized beads was improved by the addition of 1% AC. Compared with the free suspended cells, the immobilized cells showed a higher tolerance to temperature and pH. In the repeated batch experiment, the removal rate of DCM was still higher than 13.4 mg·L-1·h-1 after 9 cycles. Furthermore, the addition of 1% AC into PVA-SA immobilized beads improved adsorptive capacity and shorten adsorption time achieving the equilibrium. The adsorption process of DCM by PVA-SA-AC beads could be well fitted by the pseudo-second-order kinetic and Langmuir isotherm models (R2>0.99).
Keywords:dichloromethane  immobilization  PVA-SA  activated carbon  biodegradation
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