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2022
DOI: 10.1021/acs.est.1c07932
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Distribution and Fate of Ultraviolet Absorbents and Industrial Antioxidants in the St. Lawrence River, Quebec, Canada

Abstract: Ultraviolet absorbents (UVAs) and industrial antioxidants (IAs) are contaminants of emerging concern. In this study, we investigated the distribution and partitioning of these contaminants in surface water, suspended particulate matter (SPM), sediment, and various tissues of lake sturgeon ( Acipenser fulvescens ) and northern pike ( Esox lucius ) from the St. Lawrence River (SLR), Quebec, Canada. Results indicated that 2,6-di- tert -butyl-1,4… Show more

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Cited by 39 publications
(29 citation statements)
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“…A more recent study provided new evidence of multiple PPD-derived quinones in environmental media . These selected PPDs and their derived quinones have also been verified to be toxic and pervasive in the environment. In contrast to PPDs, NPAs and DPAs have rarely been investigated, and most have not yet entered the radar of toxicity or environmental studies. Generally, environmental PPDs, NPAs, and DPAs are considered to be linked to tire rubber. ,,, Comprehensive identifications of AAs, including PPDs, NPAs, and DPAs, as well as their significant sources other than tire rubber, are urgently needed to assess the overall risk.…”
Section: Introductionmentioning
confidence: 99%
“…A more recent study provided new evidence of multiple PPD-derived quinones in environmental media . These selected PPDs and their derived quinones have also been verified to be toxic and pervasive in the environment. In contrast to PPDs, NPAs and DPAs have rarely been investigated, and most have not yet entered the radar of toxicity or environmental studies. Generally, environmental PPDs, NPAs, and DPAs are considered to be linked to tire rubber. ,,, Comprehensive identifications of AAs, including PPDs, NPAs, and DPAs, as well as their significant sources other than tire rubber, are urgently needed to assess the overall risk.…”
Section: Introductionmentioning
confidence: 99%
“…Among them, some BTR- and BP-type UVFs are listed as high production volume chemicals by the U.S. EPA and/or European Chemical Agency (ECHA) and have become the most commonly used UVFs over the past decades . Owing to their large-scale applications, BTR- and BP-UVFs have been found to be globally distributed in multiple environmental matrices (e.g., air, water, sediment, sludge, and dust), , biota, , and human specimens. The environmental ubiquity of these two classes of traditional UVFs has gained increasing attention from not only scientific communities but also the public, and thus current concerns on UV filters are mainly focused on BTR- and BP-UVFs.…”
Section: Introductionmentioning
confidence: 99%
“…Previous scientific interests were primarily focused on the environmental behaviors of UV-320, 2-(2-hydroxy-3- tert -butyl-5-methylphenyl)-5-chloro benzotriazole (UV-326), UV-327, UV-328, and 2-(2-hydroxy-5-methylphenyl) benzotriazole (UV-P) in field investigations. ,,,, The occurrence of UV-234, UV-329, and UV-350 was also reported in sewage sludge in China . Recently, through laboratory exposure experiments, , biotransformation products (bio-TPs) of phase I reactions (e.g., hydroxylated and carbonyl-substituted metabolites) have been found in zebrafish (Danio rerio) and human liver microsomes.…”
Section: Introductionmentioning
confidence: 99%