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含铁黏土矿物与电子传递体强化生物还原固定地下水中Cr(Ⅵ)的过程和机理分析 被引量:1
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作者 马晓旭 孟颖 +6 位作者 张鉴达 赵子旺 姚国庆 王亚华 刘文彬 袁庆科 栾富波 《环境工程学报》 CAS CSCD 北大核心 2020年第9期2527-2536,共10页
为了提高微生物还原固定Cr(Ⅵ)的速率,实现地下水Cr(Ⅵ)污染物的快速有效去除,采用添加黏土矿物与电子传递体的方法,考察了含铁黏土矿物NAu-2和电子传递体AQDS单独/共存条件下对希瓦氏菌Shewanella oneidensis MR-1还原固定地下水中不... 为了提高微生物还原固定Cr(Ⅵ)的速率,实现地下水Cr(Ⅵ)污染物的快速有效去除,采用添加黏土矿物与电子传递体的方法,考察了含铁黏土矿物NAu-2和电子传递体AQDS单独/共存条件下对希瓦氏菌Shewanella oneidensis MR-1还原固定地下水中不同浓度Cr(Ⅵ)(0.1~2.0 mmol·L^−1)的影响。结果表明:单独添加NAu-2对不同浓度Cr(Ⅵ)生物还原过程均无促进作用;单独添加AQDS对不同浓度Cr(Ⅵ)(0.2~2.0 mmol·L^−1)生物还原过程均产生强化作用,强化系数达到1.33~3.90;同时添加NAu-2和AQDS时,不同浓度Cr(Ⅵ)(0.2~2.0 mmol·L^−1)生物还原时的强化作用均得到明显提升,强化系数达到2.02~10.49。此外,对比NAu-2和AQDS共存时对MR-1还原不同浓度Cr(Ⅵ)的协同促进作用,发现在低浓度Cr(Ⅵ)(0.1~0.5 mmol·L^−1)体系中未产生协同作用(协同系数<1.0),中、高浓度Cr(Ⅵ)(0.8~2.0 mmol·L^−1)体系中产生了明显的协同作用(SF>1.0),且在Cr(Ⅵ)浓度为1.2 mmol·L^−1时,协同效果最为明显(协同系数为2.98),说明NAu-2和AQDS对中、高浓度Cr(Ⅵ)(0.8~2.0 mmol·L^−1)还原过程的协同促进作用差异较大。通过对不同Cr(Ⅵ)浓度条件下NAu-2、AQDS与MR-1共存的复杂体系中Cr(Ⅵ)迁移转化过程和机理进行研究,可为实际Cr(Ⅵ)污染场地修复提供新的修复思路及参考数据。 展开更多
关键词 Cr(Ⅵ) 生物还原 Shewanella oneidensis MR-1 绿脱石(nau-2) 蒽醌-2 6-二磺酸(AQDS)
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Anaerobic oxidation of arsenite by bioreduced nontronite 被引量:1
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作者 Ziwang Zhao Ying Meng +3 位作者 Yahua Wang Leiming Lin Fuyu Xie Fubo Luan 《Journal of Environmental Sciences》 SCIE EI CAS CSCD 2021年第12期21-27,共7页
The redox state of arsenic controls its toxicity and mobility in the subsurface environment. Understanding the redox reactions of arsenic is particularly important for addressing its environmental behavior. Clay miner... The redox state of arsenic controls its toxicity and mobility in the subsurface environment. Understanding the redox reactions of arsenic is particularly important for addressing its environmental behavior. Clay minerals are commonly found in soils and sediments, which are an important host for arsenic. However, limited information is known about the redox reactions between arsenic and structural Fe in clay minerals. In this study, the redox reactions between As(Ⅲ)/As(Ⅴ) and structural Fe in nontronite NAu-2 were investigated in anaerobic batch experiments. No oxidation of As(Ⅲ) was observed by the native Fe(Ⅲ)-NAu-2. Interestingly, anaerobic oxidation of As(Ⅲ) to As(Ⅴ) occurred after Fe(Ⅲ)-NAu-2 was bioreduced. Furthermore, anaerobic oxidization of As(Ⅲ) by bioreduced NAu-2 was significantly promoted by increasing Fe(Ⅲ)-NAu-2 reduction extent and initial As(Ⅲ) concentrations. Bioreduction of Fe(Ⅲ)-NAu-2 generated reactive Fe(Ⅲ)-O-Fe(Ⅱ) moieties at clay mineral edge sites. Anaerobic oxidation of As(Ⅲ) was attributed to the strong oxidation activity of the structural Fe(Ⅲ) within the Fe(Ⅲ)-O-Fe(Ⅱ) moieties. Our results provide a potential explanation for the presence of As(Ⅴ) in the anaerobic subsurface environment. Our findings also highlight that clay minerals can play an important role in controlling the redox state of arsenic in the natural environment. 展开更多
关键词 BIOREDUCTION Nontronite nau-2 ARSENIC Redox reactions Clay mineral
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