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
“…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.…”
Our
previous work demonstrated that massive emissions of hindered
phenol antioxidants and sulfur-containing antioxidants from e-waste
recycling; however, it remains unclear whether e-waste recycling also
results in the emission of substantial quantities of amine antioxidants
(AAs) and organophosphite antioxidants (OPAs), another two major classes
of under-researched antioxidants. In this study, we continued to screen
the previously studied e-waste dusts for a broad range of 21 AAs,
two p-phenylenediamine-derived quinones, and 15 OPAs.
All 21 AAs and 12 out of the 15 OPAs were detected in the samples,
with the total concentrations ranging from 511 to 10,600 ng/g for
AAs and from 155 to 33,200 ng/g for OPAs. Among the detected chemicals,
nine were identified for the first time in the environment. More importantly, N-(1,3-dimethylbutyl)-N′-phenyl-p-phenylenediamine-quinone (6PPD-quinone), the causal toxicant
of acute mortality in coho salmon, was pervasively detected with greater
environmental abundance (median: 375 ng/g) than its parent chemical
6PPD (median: 113 ng/g), demonstrating that e-waste as another source
of ubiquitous 6PPD-quinone in addition to tire rubber. Waste wires,
cables, and electronic plastics were identified as the main sources
for e-waste-derived AAs and OPAs. Our work highlights a large group
of antioxidant chemicals, including their transformation products,
as emerging e-waste pollutants that require more
attention.
“…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.…”
Our
previous work demonstrated that massive emissions of hindered
phenol antioxidants and sulfur-containing antioxidants from e-waste
recycling; however, it remains unclear whether e-waste recycling also
results in the emission of substantial quantities of amine antioxidants
(AAs) and organophosphite antioxidants (OPAs), another two major classes
of under-researched antioxidants. In this study, we continued to screen
the previously studied e-waste dusts for a broad range of 21 AAs,
two p-phenylenediamine-derived quinones, and 15 OPAs.
All 21 AAs and 12 out of the 15 OPAs were detected in the samples,
with the total concentrations ranging from 511 to 10,600 ng/g for
AAs and from 155 to 33,200 ng/g for OPAs. Among the detected chemicals,
nine were identified for the first time in the environment. More importantly, N-(1,3-dimethylbutyl)-N′-phenyl-p-phenylenediamine-quinone (6PPD-quinone), the causal toxicant
of acute mortality in coho salmon, was pervasively detected with greater
environmental abundance (median: 375 ng/g) than its parent chemical
6PPD (median: 113 ng/g), demonstrating that e-waste as another source
of ubiquitous 6PPD-quinone in addition to tire rubber. Waste wires,
cables, and electronic plastics were identified as the main sources
for e-waste-derived AAs and OPAs. Our work highlights a large group
of antioxidant chemicals, including their transformation products,
as emerging e-waste pollutants that require more
attention.
“…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.…”
Our previous work demonstrated triazine
UV filters (TA-UVFs)
as
an emerging class of abundant, ubiquitous pollutants in the indoor
environment; however, information about human exposure to these novel
chemicals remains unknown. In this study, 17 TA-UVFs as well as 9
benzotriazole (BTR)-UVFs and 6 benzophenone (BP)-UVFs were included
in a comprehensive, dedicated screening in breast milk from South
China. In addition to some previously unrecognized BTR- and BP-UVFs,
11 of the 17 TA-UVFs were detected for the first time in breast milk,
with ethylhexyl triazone (EHT) and bis-ethylhexyloxyphenol methoxyphenyl
triazine (BEMT) as the predominant, omnipresent pollutants in humans.
The median total concentration of TA-UVFs reached 1350 pg/mL, which
is nearly half that of BTR-UVFs (3080 pg/mL) or BP-UVFs (3220 pg/mL).
More daily use of personal care products (≥5 types) significantly
elevated breast milk levels for all three classes of UVFs (p < 0.05) in the studied population. The overall daily
intake of UVFs for infants via breast-feeding will substantially increase
by 28% under the median exposure scenario if TA-UVFs are included
in an integrative assessment. The current breast milk levels of TA-UVFs
indicate a demand for additional monitoring and actions to reduce
maternal and infant exposure to these emerging contaminants.
“…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.…”
Benzotriazole UV stabilizers (BZT-UVs), including 2-(3,5-di-tert-amyl-2-hydroxyphenyl)benzotriazole (UV-328) that is currently under consideration for listing under the Stockholm Convention, are applied in many commodities and industrial products. However, limited information is available on the interannual variation of their environmental occurrence. In this study, an all-in-one strategy combining target, suspect, and nontarget screening analysis was established to comprehensively explore the temporal trends of BZT-UVs in mollusks collected from the Chinese Bohai Sea between 2010 and 2018. Significant residue levels of the target analytes were determined with a maximum total concentration of 6.4 × 10 3 ng/g dry weight. 2-(2-Hydroxy-3-tert-butyl-5-methylphenyl)-5-chloro-benzotriazole (UV-326), 5-chloro-2-(3,5-di-tertbutyl-2-hydroxyphenyl)benzotriazole (UV-327), and 2-(2-hydroxy-5-methylphenyl) benzotriazole (UV-P) were the predominant analogues, and UV-328 was the most frequently detected BZT-UV with a detection frequency (DF) of 87%. Whereas five biotransformation products and six impurity-like BZT-UVs were tentatively identified, their low DFs and semi-quantified concentrations suggest that the targeted analytes were the predominant BZT-UVs in the investigated area. A gradual decrease in the total concentrations of BZT-UVs was observed, accompanied by downward trends of the abundant compounds (e.g., UV-326 and UV-P). Consequently, the relative abundance of UV-327 increased because of its consistent environmental presence. These results suggest that continuous monitoring and risk assessment of BZT-UVs other than UV-328 are of importance in China.
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