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Fe2+与Fe0活化过二硫酸盐降解活性艳蓝KN-R
引用本文:于 辉,金春姬,王鹏远,刘 明,贾红丽. Fe2+与Fe0活化过二硫酸盐降解活性艳蓝KN-R[J]. 环境科学研究, 2015, 28(1): 88-95
作者姓名:于 辉  金春姬  王鹏远  刘 明  贾红丽
作者单位:1.中国海洋大学环境科学与工程学院, 山东 青岛 266100
基金项目:山东省自然科学基金项目(ZR2011BM014)
摘    要:为了解Fe2+与Fe0在活化PDS(过二硫酸盐)降解活性艳蓝KN-R时的差异,通过序批试验,考察了Fe2+/PDS和Fe0/PDS体系中c(Fe2+)、ρ(Fe0)、c(PDS)和初始pH对KN-R降解的影响. 结果表明:在Fe2+/PDS体系中,最佳反应条件〔初始pH为3.0,c(Fe2+)为1.0 mmol/L,c(PDS)为2.0 mmol/L〕下,180 min后KN-R的去除率达到96.55%;过高的pH和c(Fe2+)对KN-R的降解均有明显的抑制作用. 在Fe0/PDS体系中,当pH和ρ(Fe0)过高时,KN-R的去除率仍维持在较高水平,当pH为9.0时,180 min后KN-R的去除率为90.53%;当ρ(Fe0)为448 mg/L时,50 min后KN-R的去除率就能达到94.35%. 在2个体系中,c(PDS)的升高均能显著提高KN-R的去除率,当c(PDS)由0.5 mmol/L增至8.0 mmol/L时,KN-R的去除率由47.25%(Fe2+/PDS体系)和57.00%(Fe0/PDS体系)增至100%. 动力学分析显示,KN-R的降解均遵循一级反应动力学;最佳反应条件下2个体系中的活性自由基均以硫酸根自由基(SO4-·)为主. 因此,在降解KN-R过程中,Fe0/PDS体系的性能明显优于Fe2+/PDS体系. 

关 键 词:活性艳蓝KN-R   Fe2+   Fe0   过二硫酸盐   降解动力学
收稿时间:2014-02-25
修稿时间:2014-08-15

Degradation of Reactive Brilliant Blue KN-R by Persulfate Activated with Fe2+ and Fe0
YU Hui,JIN Chunji,WANG Pengyuan,LIU Ming and JIA Hongli. Degradation of Reactive Brilliant Blue KN-R by Persulfate Activated with Fe2+ and Fe0[J]. Research of Environmental Sciences, 2015, 28(1): 88-95
Authors:YU Hui  JIN Chunji  WANG Pengyuan  LIU Ming  JIA Hongli
Affiliation:1.College of Environmental Sciences and Engineering, Ocean University of China, Qingdao 266100, China2.College of Environmental Sciences and Engineering, Ocean University of China, Qingdao 266100, China ;Key Laboratory of Marine Environment and Ecology, Ministry of Education, Ocean University of China, Qingdao 266100, China
Abstract:Batch experiments were conducted to understand the main differences between Fe2+/PDS and Fe0/PDS systems during the degradation process of reactive brilliant blue KN-R. The effects of dosages of Fe2+, Fe0 and PDS, and the initial pH on KN-R degradation were investigated. In the Fe2+/PDS system, when the initial pH was set at 3.0, Fe2+ concentration was 1.0 mmol/L and PDS concentration was 2.0 mmol/L, the maximum degradation ratio was 96.55% after 180 minutes. The faster the pH or Fe2+ concentration increased, the worse the KN-R degradation decreased. However, in the Fe0/PDS system, pH and Fe0 dosage did not restrain the KN-R removal. The degradation ratio of KN-R was 90.53% after 180 minutes at pH=9.0, while it reached 94.35% within 50 min at Fe0 dosage of 448 mg/L. In the Fe2+/PDS and Fe0/PDS systems, PDS could improve the removal rate of KN-R remarkably. When the concentrations of PDS increased from 0.5 mmol/L to 8.0 mmol/L, the removal ratios increased from 47.25% and 57.00% to 100% in the Fe2+/PDS and Fe0/PDS systems, respectively. Kinetic analysis indicated that the degradation of KN-R followed a first order kinetics equation. Radical identification showed that SO4-· were the main radicals in the Fe2+/PDS and Fe0/PDS systems. In conclusion, the Fe0/PDS system was superior to the Fe2+/PDS system during the degradation process of KN-R. 
Keywords:reactive brilliant blue KN-R   ferrous ion   zero-valent iron   persulfate   degradation kinetics
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