Literature DB >> 18656677

Analysis of nitrosamines in water by automated SPE and isotope dilution GC/HRMS Occurrence in the different steps of a drinking water treatment plant, and in chlorinated samples from a reservoir and a sewage treatment plant effluent.

Carles Planas1, Oscar Palacios, Francesc Ventura, Josep Rivera, Josep Caixach.   

Abstract

A method based on automated solid-phase extraction (SPE) and isotope dilution gas chromatography/high resolution mass spectrometry (GC/HRMS) has been developed for the analysis of nine nitrosamines in water samples. The combination of automated SPE and GC/HRMS for the analysis of nitrosamines has not been reported previously. The method shows as advantages the selectivity and sensitivity of GC/HRMS analysis and the high efficiency of automated SPE with coconut charcoal EPA 521 cartridges. Low method detection limits (MDLs) were achieved, along with a greater facility of the procedure and less dependence on the operator with regard to the methods based on manual SPE. Quality requirements for isotope dilution-based methods were accomplished for most analysed nitrosamines, regarding to trueness (80-120%), method precision (<15%) and MDLs (0.08-1.7 ng/L). Nineteen water samples (16 samples from a drinking water treatment plant {DWTP}, 2 chlorinated samples from a sewage treatment plant {STP} effluent, and 1 chlorinated sample from a reservoir) were analysed. Concentrations of nitrosamines in the STP effluent were 309.4 and 730.2 ng/L, being higher when higher doses of chlorine were applied. N-Nitrosodimethylamine (NDMA) and N-nitrosodiethylamine (NDEA) were the main compounds identified in the STP effluent, and NDEA was detected above 200 ng/L, regulatory level for NDMA in effluents stated in Ontario (Canada). Lower concentrations of nitrosamines were found in the reservoir (20.3 ng/L) and in the DWTP samples (n.d. -28.6 ng/L). NDMA and NDEA were respectively found in the reservoir and in treated and highly chlorinated DWTP samples at concentrations above 10 ng/L (guide value established in different countries). The highest concentrations of nitrosamines were found after chlorination and ozonation processes (ozonated, treated and highly chlorinated water) in DWTP samples.

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Year:  2008        PMID: 18656677     DOI: 10.1016/j.talanta.2008.04.060

Source DB:  PubMed          Journal:  Talanta        ISSN: 0039-9140            Impact factor:   6.057


  6 in total

1.  Variation of levels and distribution of N-nitrosamines in different seasons in drinking waters of East China.

Authors:  Ting Li; Dian Yu; Qiming Xian; Aimin Li; Cheng Sun
Journal:  Environ Sci Pollut Res Int       Date:  2015-04-11       Impact factor: 4.223

2.  Nitrosamine occurrence at Korean surface water using an analytical method based on GC/LRMS.

Authors:  Gyung-A Kim; Hee-Jong Son; Chang-Won Kim; Seung-Hyun Kim
Journal:  Environ Monit Assess       Date:  2012-05-09       Impact factor: 2.513

3.  [Determination of nine N-nitrosamines in animal derived foods by QuEChERS-isotope dilution combined with gas chromatography-tandem mass spectrometry].

Authors:  Xiangyi Kong; Lili Zhuang; Enhua Fang; Peng Lin; Zilong Zheng; Xianghua Zheng; Dunming Xu
Journal:  Se Pu       Date:  2021-01

4.  Detection and occurrence of N-nitrosamines in archived biosolids from the targeted national sewage sludge survey of the U.S. Environmental Protection Agency.

Authors:  Arjun K Venkatesan; Benny F G Pycke; Rolf U Halden
Journal:  Environ Sci Technol       Date:  2014-04-15       Impact factor: 9.028

5.  Factors affecting N-nitrosodimethylamine formation from poly(diallyldimethyl-ammonium chloride) degradation during chloramination.

Authors:  Siying Tan; Shaojie Jiang; Xiaoyu Li; Qiuhong Yuan
Journal:  R Soc Open Sci       Date:  2018-08-08       Impact factor: 2.963

6.  N-Nitrosodimethylamine Contamination in the Metformin Finished Products.

Authors:  Adam Zmysłowski; Iza Książek; Arkadiusz Szterk
Journal:  Molecules       Date:  2020-11-13       Impact factor: 4.411

  6 in total

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