2019
DOI: 10.1016/j.chemosphere.2018.12.069
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Simultaneous analysis of haloacetonitriles, haloacetamides and halonitromethanes in chlorinated waters by gas chromatography-mass spectrometry

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Cited by 28 publications
(14 citation statements)
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“…It was found that ascorbic acid reduced BDCNM, DBCNM, TBNM, and TBAN to undetectable concentrations within hours of contact in quenched chlorinated and chloraminated waters. This is consistent with previous studies showing similar results on a smaller subset of compounds. ,,, Further DBP formation was within ±30% of initial concentration between 24 and 48 h for both chlorine quenched with ammonium chloride and chloramine samples not quenched. Several compounds degraded, including iodoacetamide (IAM), which degraded by 30% in 24 h and by 36% in 48 h in chlorinated water quenched with ammonium chloride.…”
Section: Resultssupporting
confidence: 92%
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“…It was found that ascorbic acid reduced BDCNM, DBCNM, TBNM, and TBAN to undetectable concentrations within hours of contact in quenched chlorinated and chloraminated waters. This is consistent with previous studies showing similar results on a smaller subset of compounds. ,,, Further DBP formation was within ±30% of initial concentration between 24 and 48 h for both chlorine quenched with ammonium chloride and chloramine samples not quenched. Several compounds degraded, including iodoacetamide (IAM), which degraded by 30% in 24 h and by 36% in 48 h in chlorinated water quenched with ammonium chloride.…”
Section: Resultssupporting
confidence: 92%
“…This is consistent with previous studies showing similar results on a smaller subset of compounds. 12,15,26,37 Further DBP formation was within ±30% of initial concentration between 24 and 48 h for both chlorine quenched with ammonium chloride and chloramine samples not quenched. Several compounds degraded, including iodoacetamide (IAM), which degraded by 30% in 24 h and by 36% in 48 h in chlorinated water 1 and 2.…”
Section: ■ Results and Discussionmentioning
confidence: 90%
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“…The conventional method for HANs and HNMs determination is the US EPA Method 551, which is based on LLE and GC-ECD (Munch and Hautman, 1995;Liew et al, 2012;Huang et al, 2013) and, most recently LLE and GC-MS with a programmable temperature injector for the analysis of 25 N-DBPs (HAAs, HNMs, and HANs) in drinking water (Carter et al, 2019). Another method widely used for the determination of these compounds is extraction by SPME and the analysis by GC-ECD and/or GC-MS (Montesinos and Gallego, 2012a;Luo et al, 2014;Kermani et al, 2013), as well as single-drop microextraction (SDME) in the static headspace mode followed by GC-MS for the determination of HNMs (Montesinos et al, 2011).…”
Section: Introductionmentioning
confidence: 99%