2016
DOI: 10.1016/j.watres.2016.06.029
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Identification and characterization of phenylacetonitrile as a nitrogenous disinfection byproduct derived from chlorination of phenylalanine in drinking water

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Cited by 42 publications
(7 citation statements)
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“…The proposed formation pathways of HPAcAms during chlorination of phenylalanine could be proved reasonable from different aspects. First, among all of the five intermediates, I, III, and IV were already detected in previous studies, , and V was positively identified in the present study (Supporting Information Section S8 and Figure S7), which supported the proposed formation pathways. Second, the frontier electron densities (FEDs) of the highest occupied molecular orbital (HOMO) for phenylalanine were calculated using Gaussian 09 software at the B3LYP/3-21G* level (Supporting Information Figure S8), and the N atom in phenylalanine showed an overwhelmingly large 2FED 2 HOMO value (1.2321).…”
Section: Resultssupporting
confidence: 88%
“…The proposed formation pathways of HPAcAms during chlorination of phenylalanine could be proved reasonable from different aspects. First, among all of the five intermediates, I, III, and IV were already detected in previous studies, , and V was positively identified in the present study (Supporting Information Section S8 and Figure S7), which supported the proposed formation pathways. Second, the frontier electron densities (FEDs) of the highest occupied molecular orbital (HOMO) for phenylalanine were calculated using Gaussian 09 software at the B3LYP/3-21G* level (Supporting Information Figure S8), and the N atom in phenylalanine showed an overwhelmingly large 2FED 2 HOMO value (1.2321).…”
Section: Resultssupporting
confidence: 88%
“…In chlorination, the formation of DCAN from PAN is negligible, as PAN is inert to chlorination (Figure S12). PAN has been previously reported to be very stable in chlorination, with a half lifetime of 792 h at 19 °C . However, PAN is readily degraded by UV/chlorine with first-order rate constants of 4.0 × 10 –4 to 9.2 × 10 –4 s –1 (Figure S13).…”
Section: Resultsmentioning
confidence: 99%
“…PAN has been previously reported to be very stable in chlorination, with a half lifetime of 792 h at 19 °C. 52 However, PAN is readily degraded by UV/chlorine with firstorder rate constants of 4.0 × 10 −4 to 9.2 × 10 −4 s −1 (Figure S13). The consumed PAN is partially converted to DCAN in UV/chlorine, with conversion rates of 14.2−25.6%.…”
Section: ■ Materials and Methodsmentioning
confidence: 99%
“…Comparisons of the mass spectra and the GC retention times of these peaks with the corresponding data for commercially available chemical standards confirmed these assignments (data not shown). PAA (Hrudey et al 1988, Bruchet et al 1992, Froese et al 1999, Freuze et al 2005, Ma et al 2016, PAN , Freuze et al 2005, Ma et al 2016, and BC (Ma et al 2016) are reportedly produced during chlorination of phenylalanine. In contrast, CB, BA, and BN have not been reported to be TPs of phenylalanine, possibly because these compounds are produced in only very small amounts.…”
Section: Identification Of Tps In the Chlorinated Phenylalanine-contamentioning
confidence: 99%