2017
DOI: 10.1016/j.aca.2017.08.016
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Identification of novel non-ionic, cationic, zwitterionic, and anionic polyfluoroalkyl substances using UPLC–TOF–MSE high-resolution parent ion search

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Cited by 83 publications
(80 citation statements)
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“…Currently available commercial analytical techniques and those being developed for nondrinking water matrices do not have the capability to identify all the potential individual PFAS related treatment by‐products. However, some of the advanced analytical techniques (e.g., AOP, TOP, and PIGE) are capable of approximating the total equivalent organofluorine of these precursors as researchers continue to develop libraries of standards to identify individual precursor compounds (Mejia‐Avendano et al ; Xiao et al ; Xu et al , ).…”
Section: Summary Observationsmentioning
confidence: 99%
“…Currently available commercial analytical techniques and those being developed for nondrinking water matrices do not have the capability to identify all the potential individual PFAS related treatment by‐products. However, some of the advanced analytical techniques (e.g., AOP, TOP, and PIGE) are capable of approximating the total equivalent organofluorine of these precursors as researchers continue to develop libraries of standards to identify individual precursor compounds (Mejia‐Avendano et al ; Xiao et al ; Xu et al , ).…”
Section: Summary Observationsmentioning
confidence: 99%
“…Similarly, the first C−F bond cleaved during the B12catalyzed abiotic defluorination of 2,3,3,3-tetrafluoropropene was also at the sp 2 C−F bond on the unsaturated carbon (33). Additionally, it is worth noting that although the tertiary sp 3 C−F bond in PFMeUPA has the lowest bond dissociation energy (BDE) ( Fig. 3), the formation of TP256 indicates that the sp 2 C−F bonds are more microbially active.…”
mentioning
confidence: 95%
“…2A). The sp 3 C−F bond in the -C3F7 group has the lowest BDE, thus more likely to be cleaved. Furthermore, the behavior of TP195 on the LC-HRMS/MS was different from the authentic standard of the sp 2 C−F cleavage product (3-(trifluoromethyl)-3,4,4,4-tetrafluorobutene-1) (Table S1), indicating a different structure of TP195.…”
mentioning
confidence: 99%
“…The specific compounds perfluorooctanoic acid (PFOA) and perfluorooctanesulfonate (PFOS) have drinking water health advisory levels set by the EPA 1,2 and their major US production ceased in the 2000s 3,4 . To gain a significant understanding for the properties of PFAS materials in the textile and consumer product manufacturing spheres, hundreds, if not thousands, of alternate PFAS chemistries have been developed to fill product niches, including replacements for the deprecated compounds 5,6,7,8 . There is an ongoing need to monitor the environmental levels of straight chain perfluorinated carboxylic acids and sulfonates such PFOS, PFOA, and their related homologous series, but emerging chemical compounds are not covered by established methods such as EPA Method 537 9 and frequently lack analytical standards for traditional targeted analysis.…”
Section: Introductionmentioning
confidence: 99%