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臭氧氧化乙硫氮的效率、能耗及中间产物生成研究 被引量:1

The Ozonation of Diethyl Dithiocarbamate(SN-9) Collector: Degradation Efficiency, Energy Consumption and Byproducts
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摘要 捕收剂乙硫氮经水解、氧化可生成剧毒消毒副产物NDEA,因此安全、高效去除浮选废水中残留乙硫氮等浮选药剂日益受到重视。本文研究了低臭氧投加率下臭氧氧化乙硫氮的效率、能耗及中间产物生成规律,结果表明,在低O3投加率时,臭氧氧化乙硫氮的能耗(EE/O)远低于可接受能耗水平,降解生成的含硫副产物H2S浓度约为CS2的20倍。固相微萃取/气相色谱-质谱(SPE/GC-MS)分析表明,降解中间产物多为酰胺类有机物,未检测到亚硝胺类有毒产物,延长氧化时间,有机中间产物种类大幅减少,表明臭氧能进一步分解中间产物。 N-nitrosodiethylamine(NDEA)is generated by hydrolysis and oxidation of the collector diethyl dithiocarbamate(SN-9),thus,it has attracted high concern to remove SN-9 from flotation wastewater effectively and safely.In this study,the degradation efficiency,energy consumption and formation of byproducts were investigated in the ozonation of SN-9 with low O3 dosage.The results showed that the energy consumption index of EE/O was much lower than the acceptable level.The concentration of sulfur byproducts H2S was almost 20 folds higher than CS2.The solid phase extraction and gas chromatography-mass spectrometry(SPE/GC-MS)analysis indicated that main byproducts were amide compounds without the detection of N-nitrosamines.The kinds of byproducts were decreased by extending the degradation time,indicating further degradation of formed byproducts.
作者 傅平丰 马艳红 林小凤 李根 Fu Pingfeng;Ma Yanhong;Lin Xiaofeng;Li Gen(School of Civil and Resources Engineering,University of Science and Technology Beijing,Beijing 100083,China)
出处 《中国资源综合利用》 2019年第11期17-22,共6页 China Resources Comprehensive Utilization
基金 国家自然科学基金项目(项目编号:51674017)的阶段性研究成果之一
关键词 浮选废水 乙硫氮 臭氧氧化 能耗 中间产物 flotation wastewater diethyl dithiocarbamate(SN-9) ozonation energy consumption byproducts
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  • 1王庆国,乐晨,卓瑞锋,邓鹏,黄兴刚,韩颖,张珍明.电化学氧化法处理垃圾渗滤液纳滤浓缩液[J].环境工程学报,2015,9(3):1308-1312. 被引量:30
  • 2张萍,孙水裕,徐劲.一株有机浮选药剂——黄原酸盐降解菌的特性研究[J].环境污染治理技术与设备,2006,7(2):53-56. 被引量:26
  • 3朱潜力.黄药废水治理的新工艺研究[J].有色矿冶,1997,13(1):53-54. 被引量:20
  • 4GB16889-2008生活垃圾填埋污染控制标准[S].
  • 5[1]Legube B,Karpel Vel Leitner N.Catalytic ozonation:a promising advanced oxidation technology for water treatment[J].Catalysis Today,1999,53(1):61-72.
  • 6[3]Gouvea Carlos A K,Wypych F,Moraes S G,et al.Semiconductor-assisted photodegradation of llgnin,dye,and kraft effluent by Ag-doped ZnO[J].Chemosphere,2000,40(4):427-432.
  • 7[4]HuangWJ,FangGC,WangCC.Ananometer-ZnOcatalyst to enhance the ozonatlon of2,4,6-trieldorophenol in water[J].Colloids and Surfaces.A:Physicochemical and Engineering Aspects,2005,260(1-3):45-51.
  • 8[5]Jung H Y,Choi H C.Catalytic decomposition of ozone and para-Chlorobenzoic acid(pCBA)in the presence of nanosized ZnO[J].Applied Catalysis B:Environmental,2006,66(3-4):288-294.
  • 9[6]Bader J,Hoigne H.Determination of ozone in water by the indigo method[J].Water Research,1981,15(4):449-456.
  • 10[7]Beltran F J.Ozone reaction kinetics for water and wastewater systems[M].USA:Lewifl Publisher,2004.

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