2015
DOI: 10.1016/j.scitotenv.2014.08.108
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Screening triclocarban and its transformation products in river sediment using liquid chromatography and high resolution mass spectrometry

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Cited by 26 publications
(12 citation statements)
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“…DCC and 3′Cl-TCC are known to be present as impurities (∼0.2%, w/w) in technical-grade TCC (Figures S12 and S13). Consequently, the estimated concentrations of DCC and 3′Cl-TCC spiked into the hydroponic media during the initial exposure (0–7 days) and second exposure (7–28 days) were 0.35 and 0.97 μg/L, respectively. Therefore, these two products were present in the media throughout the experiments primarily as byproducts of TCC.…”
Section: Results and Discussionmentioning
confidence: 99%
“…DCC and 3′Cl-TCC are known to be present as impurities (∼0.2%, w/w) in technical-grade TCC (Figures S12 and S13). Consequently, the estimated concentrations of DCC and 3′Cl-TCC spiked into the hydroponic media during the initial exposure (0–7 days) and second exposure (7–28 days) were 0.35 and 0.97 μg/L, respectively. Therefore, these two products were present in the media throughout the experiments primarily as byproducts of TCC.…”
Section: Results and Discussionmentioning
confidence: 99%
“…On the other hand, reductive dechlorination is also known to be a ubiquitous and essential dissimilation route that takes place during the transformation of TCC and its higher chlorinated congeners (such as 3,3',4,4'-tetrachlorocarbanilide (4-Cl-TCC)) into their lesser chlorinated congeners under anaerobic and anoxic conditions by the activity of microorganisms [56,119,[192][193][194]. Through sequential detoxification reactions, TCC can be converted to its core carbanilide structure as follows: Tri-chlorinated TCC is first transformed into DCC, then into MCC and, finally, into non-chlorinated NCC ( Figure 6) [56,188,192].…”
Section: Transformation/degradation Products and Metabolites Of Triclmentioning
confidence: 99%
“…Concerning dechlorination products of TCC, DCC and 4-Cl-TCC are known as manufacturing byproducts in technical-grade TCC (at an estimated level of 0.2% by weight) [213]; thus, TCC-containing personal care products can be considered as another source of the release of these compounds into the environment [177]. The higher-and lower-chlorinated congeners of TCC have been reported to be present in sediments and surface waters impacted by WWTP effluent as well as in sediment-dwelling organisms, such as the freshwater oligochaete Lumbriculus variegatus (worm) [162,192,193,213,230,247]. A previous study conducted by Miller et al [192] reported that the TCC dechlorination process was observed exclusively in strictly anaerobic environments (such as dated estuarine sediments) by strict anaerobic dechlorinating microorganisms.…”
Section: Fate and Impacts Of Triclocarban And Triclocarban-related Comentioning
confidence: 99%
“…More recently, the EDA approach has been used in combination with full-scan screening analysis (FSA) to detect unknown and potentially toxic substances in environmental samples, such as sediment and water . FSA is a powerful tool that is used to identify unknown toxicants in environmental samples based on accurate molecular mass by use of high-resolution mass spectrometry (HRMS), such as time-of-flight mass spectrometry (TOFMS). A previous study using FSA successfully identified 2,3- and 2,8-phenazinediamine from river water, which was subsequently confirmed by use of authentic standards and shown to be a potent mutagenicity in the Ames test . Through combining EDA with FSA, 4-methyl-7-diethylaminocoumarin was confirmed as a potent androgenic receptor agonist in the surface water of rivers with the relative potency (ReP) value of the reference material flutamide exceeding 5.2 .…”
Section: Introductionmentioning
confidence: 98%