期刊文献+

Capability of cation exchange technology to remove proven N-nitrosodimethylamine precursors

Capability of cation exchange technology to remove proven N-nitrosodimethylamine precursors
原文传递
导出
摘要 N-nitrosodimethylamine(NDMA) precursors consist of a positively charged dimethylamine group and a non-polar moiety, which inspired us to develop a targeted cation exchange technology to remove NDMA precursors. In this study, we tested the removal of two representative NDMA precursors, dimethylamine(DMA) and ranitidine(RNTD), by strong acidic cation exchange resin. The results showed that pH greatly affected the exchange efficiency, with high removal(DMA 〉 78% and RNTD 〉 94%) observed at pH 〈 pk_a-1 when the molar ratio of exchange capacity to precursor was 4. The exchange order was obtained as follows: Ca^(2+)〉 Mg^(2+)〉 RNTD~+〉 K~+〉 DMA~+〉 NH_4~+〉 Na~+. The partition coefficient of DMA~+to Na~+was 1.41 ± 0.26, while that of RNTD~+to Na~+was 12.1 ± 1.9. The pseudo second-order equation fitted the cation exchange kinetics well. Bivalent inorganic cations such as Ca^(2+)were found to have a notable effect on NA precursor removal in softening column test. Besides DMA and RNTD, cation exchange process also worked well for removing other 7 model NDMA precursors. Overall, NDMA precursor removal can be an added benefit of making use of cation exchange water softening processes. N-nitrosodimethylamine(NDMA) precursors consist of a positively charged dimethylamine group and a non-polar moiety, which inspired us to develop a targeted cation exchange technology to remove NDMA precursors. In this study, we tested the removal of two representative NDMA precursors, dimethylamine(DMA) and ranitidine(RNTD), by strong acidic cation exchange resin. The results showed that pH greatly affected the exchange efficiency, with high removal(DMA 〉 78% and RNTD 〉 94%) observed at pH 〈 pk_a-1 when the molar ratio of exchange capacity to precursor was 4. The exchange order was obtained as follows: Ca^(2+)〉 Mg^(2+)〉 RNTD~+〉 K~+〉 DMA~+〉 NH_4~+〉 Na~+. The partition coefficient of DMA~+to Na~+was 1.41 ± 0.26, while that of RNTD~+to Na~+was 12.1 ± 1.9. The pseudo second-order equation fitted the cation exchange kinetics well. Bivalent inorganic cations such as Ca^(2+)were found to have a notable effect on NA precursor removal in softening column test. Besides DMA and RNTD, cation exchange process also worked well for removing other 7 model NDMA precursors. Overall, NDMA precursor removal can be an added benefit of making use of cation exchange water softening processes.
出处 《Journal of Environmental Sciences》 SCIE EI CAS CSCD 2017年第8期331-339,共9页 环境科学学报(英文版)
基金 supported by the National Natural Science Foundation of China (No.21477059) the National Water Major Project (No.2015ZX07402-002) the Fundamental Research Funds for the Central Universities (No.15CX02016A) the Tsinghua University Initiative Scientific Research Program (No.20131089247) the open project of State Key Joint Laboratory of environmental simulation and pollution control (Tsinghua University)
关键词 Ion exchange Cation exchange resin N-nitrosamine precursors Dimethylamine Ranitidine Ion exchange Cation exchange resin N-nitrosamine precursors Dimethylamine Ranitidine
  • 相关文献

参考文献4

二级参考文献65

  • 1Beller T A, Lichtenberg J J, Kroner R C. Occurrence of organohalides in chlorinated drinking waters. Journal-American Water Works Association, 1974,66 (12): 703-706.
  • 2Rook J 1. Chlorination reactions of fulvic acids in natural waters. Environmental Science & Technology, 1977, 11(5): 478-482.
  • 3Richardson S D. Disinfection by-products and other emerging contaminants in drinking water. TrAC Trends in Analytical Chemistry, 2003, 22(10): 666-684.
  • 4Zhao Y Y, Boyd J, Hrudey S E, Li X F. Characterization of new nitrosamines in drinking water using liquid chromatography tandem mass spectrometry. Environmental Science & Technology, 2006, 40 (24): 7636-7641.
  • 5US Environmental Protection Agency. The Occurrence of Disin?fection By-Products CDBPs) of Health Concern in Drinking Water: Results of a Nationwide DBP Occurrence Study. EPAl600fR02/068. Athens, GA: National Exposure Research Laboratory, 2002.
  • 6Plewa M J, Wagner ED, Richardson S D, Thruston A D Jr, Woo Y T, McKague A B. Chemical and biological characterization of newly discovered iodoacid drinking water disinfection byproducts. Environmental Science & Technology, 2004, 38(18): 4713-4722.
  • 7Plewa M J, Wagner ED, Jazwierska P, Richardson S D, Chen P H, McKague A B. Halonitromethane drinking water disinfection byproducts: chemical characterization and mammalian cell cyto?toxicity and genotoxicity. Environmental Science & Technology, 2004, 38(1): 62-68.
  • 8Charrois J W A, Boyd J M, Froese K L, Hrudey S E. Occurrence of N-nitrosamines in Alberta public drinking water distribution systems. Journal of Environmental Engineering and Science, 2007,6(1): 103-114.
  • 9Barrett S, Hwang C, Guo Y, Andrews S A, Valentine R. Occurrence ofNDMA in drinking water: a North American survey, 2001-2002. In: Proceeding of the American Water Works Association's Annual Conference. America Water Works Association, Denver CO, USA, 2003: 19.
  • 10US Environmental Protection Agency. N-nitrosodimethylamine CASRN 62-75-9, Intergrated Risk Information Service (IRIS) Substance File. Washington DC, USA, 1997.

共引文献25

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