期刊文献+

饮用水中绿麦隆的氯胺化降解探究 被引量:1

Degradation of Chlortoluron during Chloramination of Drinking Water
原文传递
导出
摘要 系统研究了广泛应用的脲类除草剂绿麦隆在饮用水氯胺化消毒过程中的降解特性,考察了不同的氯胺投加量、pH值、溴离子浓度、水源等条件下绿麦隆的氯胺化降解规律。结果表明,绿麦隆的氯胺化降解速率较慢,由于氯胺自降解反应的存在,其反应机理也较为复杂。随着氯胺初始投加量逐渐增大,绿麦隆降解速率明显加快;不同pH值下绿麦隆的氯胺化降解速率变化明显,当pH值为6-7.5时降解速率较快,尤其在pH值为6时降解最快,在pH值为4.5时降解最慢;不同的溴离子背景浓度下,绿麦隆的氯胺化降解速率没有明显差异;在不同水质背景条件下,当pH值为6时,绿麦隆的氯胺化降解速率具有明显的差异性,而当pH值为7时绿麦隆的氯胺化降解速率变化不显著。 The degradation of chlortoluron as herbicide and precursor of NDMA under different ex- perimental conditions during chloramination of drinking water chlortoluron during chloramination was relatively low and the due to the chloramine self-decomposition. The higher initial was investigated. The degradation rate of reaction mechanism became more complex dosage of chloramine was applied, the faster degradation rate of chlortoluron was found. The degradation of chlortoluron during chloramination was highly dependent on solution pH values. The peak degradation rates were found when pH values ranged from 6 to 7.5, especially at pH of 6. The lowest degradation rate was found at pH of 4.5. No significant difference in degradation rate of chlortoluron during chloramination was found with the addition of bromide ion. The degradation rate of chlortoluron during chloramination was highly impacted by background of wa-ter conditions at pH of 6. However, no significant difference was found at pH of 7 indeed.
出处 《中国给水排水》 CAS CSCD 北大核心 2014年第15期61-65,共5页 China Water & Wastewater
基金 国家水体污染控制与治理科技重大专项(2012ZX07404-004 2012ZX07408-001) 国家自然科学基金资助项目(51278352)
关键词 饮用水 绿麦隆 氯胺化 drinking water chlortoluron chloramination
  • 相关文献

参考文献7

  • 1Acero J L,Real F J,Benitez F J,et al.Kinetics of reac-tions between chlorine or bromine and the herbicides di-uron and isoproturon [ J ].J Chem Technol Biotechnol,2007,82(2):214-222.
  • 2Xu B,Tian F X,Hu C Y,et al.Chlorination of chlortolu-ron:Kinetics,pathways and chloroform formation [J].Chemosphere,2011,83(7):909-916.
  • 3Xu B,Qin C,Hu C Y,et al.Degradation kinetics and N-Nitrosodimethylamine formation during monochloramination of chlortoluron [ J ].Sci Total Environ,2012,417/418:241-247.
  • 4Grasner S W,Weinberg H S,Richardson S D,et al.Oc-currence of a new generation of disinfection byproducts [J].Environ Sci Technol,2006,40(23):7175-7185.
  • 5焦中志,陈忠林,陈杰,刘丽君,卢伟强,李圭白.氯胺消毒对消毒副产物的控制研究[J].哈尔滨工业大学学报,2005,37(11):1486-1488. 被引量:31
  • 6许葆玖.给水处理理论[M].北京:中国建筑工业出版社,2000..
  • 7高乃云,汪雪姣,周超,楚文海.氯胺消毒对不同有机物生成消毒副产物的影响[J].同济大学学报(自然科学版),2009,37(12):1633-1637. 被引量:5

二级参考文献18

  • 1王永华,袁伟,舒宏新.饮水中的挥发性卤代烃研究[J].环境科学学报,1994,14(2):244-250. 被引量:19
  • 2孙青萍.分别测定含氯水样中的各种氯胺[J].中国给水排水,2005,21(11):98-100. 被引量:3
  • 3YANG Xin, SHANG Chi. Chlorination byproduct formation in the presence of humic acid, model nitrogenous organic compounds, ammonia, and bromide[ J ]. Environ Sci Technol, 2004, 38 (19) :4995.
  • 4Amench L. Fractionation of NOM from surface water using macroporous resins[J]. Water Research, 1997,31(9):2987.
  • 5Amy G L, Sierka R A, Bedessem J. Molecular size distribution of dissolved organic matter [ J ]. Journal of AWWA, 1992, 84 (6):67.
  • 6BunyaritP, Taha F M. Vorapot K. Characterization of precursors to trihalomethanes formation in Bangkok source water[J]. Journal of Hazardous Materials, 2005, 120 (1/2/ 3):229.
  • 7Barber L B, Leenheer J A, Noyes T I, et al. Nature and transformation of dissolved organic matter in treatment wetlands[J]. Environ Sci Technol, 2001,35 (24) : 4805.
  • 8Singer P C. Formation and control of disinfection byproducts in drinking water [M]. Denver: American Water Works Association, 1999.
  • 9HUA Guanghui, Reckhow D A. Characterization of disinfection byproduct precursors based on hydrophobicity and molecular size[J]. Environ Sci Technol, 2007,41(9) : 3309.
  • 10ROOK J J. Formation of haloforms during chlorination of natural waters[J]. J Water Treat Exam, 1974,23(2):234 - 243.

共引文献40

同被引文献8

引证文献1

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部