...
首页> 外文期刊>Environmental Science & Technology >Formation of N-Nitrosamines from Eleven Disinfection Treatments of Seven Different Surface Waters
【24h】

Formation of N-Nitrosamines from Eleven Disinfection Treatments of Seven Different Surface Waters

机译:七种不同地表水的十一种消毒处理可形成N-亚硝胺

获取原文
获取原文并翻译 | 示例
           

摘要

Formation of nine N-nitrosamines has been investigated when seven different source waters representing various qualities were each treated with eleven bench-scale disinfection processes, without addition of nitrosamine precursors. These disinfection treatments included chlorine (OCl~-), chloramine (NH_2Cl), chlorine dioxide (ClO_2), ozone (O_3), ultraviolet (UV), advanced oxidation processes (AOP), and combinations. The total organic carbon (TOC) of the seven source waters ranged from 2 to 24 mg·L~(-1). The disinfected water samples and the untreated source waters were analyzed for nine nitrosamines using a solid phase extraction and liquid chromatography-tandem mass spectrometry method. Prior to any treatment, N-nitrosodimethylamine (NDMA) was detected ranging from 0 to 53 ng·L~(-1) in six of the seven source waters, and its concentrations increased in the disinfected water samples (0-118 ng·L~(-1)). N-nitrosodiethylamine (NDEA), N-nitrosomor-pholine (NMor), and N-nitrosodiphenylamine (NDPhA) were also identified in some of the disinfected water samples. NDPhA (0.2-0.6 ng·Lz~(-1)) was formed after disinfection with OCl~-, NH_2Cl, O_3, and MPUV/OCl~-. NMEA was produced with OCl~-and MPUV/OCl~-, and NMor formation was associated with O_3. In addition, UV treatment alone degraded NDMA; however, UV/ OCl~- and AOP/OCl~- treatments produced higher amounts of NDMA compared to UV and AOP alone, respectively. These results suggest that UV degradation or AOP oxidation treatment may provide a source of NDMA precursors. This study demonstrates that environmental concentrations and mixtures of unknown nitrosamine precursors in source waters can form NDMA and other nitrosamines.
机译:在不使用亚硝胺前体的情况下,用11种台式规模的消毒工艺处理了代表不同质量的7种不同来源的水时,研究了9种N-亚硝胺的形成。这些消毒处理包括氯(OCl--),氯胺(NH_2Cl),二氧化氯(ClO_2),臭氧(O_3),紫外线(UV),高级氧化过程(AOP)及其组合。七个水源的总有机碳(TOC)范围为2至24 mg·L〜(-1)。使用固相萃取和液相色谱-串联质谱法对消毒后的水样和未经处理的原水进行九种亚硝胺的分析。在进行任何处理之前,在七个来源水中的六个中检测到N-亚硝基二甲胺(NDMA)的范围为0到53 ng·L〜(-1),并且在消毒水样品中的浓度(0-118 ng·L)增加了〜(-1))。在一些消毒后的水样中还鉴定出了N-亚硝基二乙胺(NDEA),N-亚硝基二氢吡啶(NMor)和N-亚硝基二苯胺(NDPhA)。用OCl〜-,NH_2Cl,O_3和MPUV / OCl〜-消毒后形成NDPhA(0.2-0.6 ng·Lz〜(-1))。 NMEA由OCl〜-和MPUV / OCl〜-产生,NMor的形成与O_3有关。另外,仅紫外线处理会使NDMA降解。然而,与单独的UV和AOP相比,UV / OCl-和AOP / OCl-处理分别产生更高数量的NDMA。这些结果表明,紫外线降解或AOP氧化处理可提供NDMA前体的来源。这项研究表明,环境浓度和来源水中未知亚硝胺前体的混合物会形成NDMA和其他亚硝胺。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号