Abstract:Abstract2-(2H-Benzotriazol-2-yl)-4,6-di-tert-pentylphenol (UV 328; CAS: 25973-55-1) is an ultraviolet light (UV) absorber which belongs to the class of hydroxy phenol benzotriazoles. Therefore, UV 328 is added to plastics and other polymers due to its photostability to prevent discoloration and prolong product stability which may result in an exposure of consumers. However, information about the toxic effects on humans and the human metabolism are still lacking. In the present study, human metabolism pathways … Show more
“…The mass fraction of UV-328 in textiles should not be >0.1% according to Oeko-Tex . Previous studies have reported that UV-328, UV-329, UV-9, and UV-326 were seldom detected in textiles − or in plastics in China. , In a kinetics study involving oral exposure to UV-328, the UV-328 excretion rate in urine was quite low and the UV-328 concentration was much higher in serum than urine . UV-328 may have a similarly low excretion rate in human breast milk.…”
Ultraviolet (UV) filters are of great concern due to
their wide
occurrence, bioaccumulation, and toxicity. Little is known about human
exposure to UV filters. A total of 3467 individual human milk samples
from 24 Chinese provinces were collected during 2017–2019.
The concentrations of 12 UV filters in 100 pooled milk samples were
determined. The total UV filter concentration was 78–846 (mean
235 ± 120) ng/g lipid weight. The highest and lowest total mean
concentrations were for samples from Qinghai and Sichuan provinces,
respectively. A significant positive correlation was found between
UV radiation levels and UV concentrations in the samples. The dominant
UV filters were 2-(2-hydroxy-5-methylphenyl) benzotriazole (UV-P)
and ethylhexyl methoxycinnamate (EHMC), which contributed means of
32 and 22%, respectively, to the total concentrations. Plastic products
and sunscreens were probably the sources of UV-P and EHMC in the human
milk from China, respectively. The mean 2-(3,5-di-tert-amyl-2-hydroxyphenyl) benzotriazole (UV-328) concentration was 2.6
± 2.6 ng/g lipid weight. The UV filter profiles were similar
to profiles for samples from Japan, the Philippines, and Switzerland
but not for samples from Korea and Vietnam. The estimated daily UV
filter intake for breastfed infants was below the corresponding reference
dose. This was the first large-scale study of UV filters in human
milk and will help assess the risks posed.
“…The mass fraction of UV-328 in textiles should not be >0.1% according to Oeko-Tex . Previous studies have reported that UV-328, UV-329, UV-9, and UV-326 were seldom detected in textiles − or in plastics in China. , In a kinetics study involving oral exposure to UV-328, the UV-328 excretion rate in urine was quite low and the UV-328 concentration was much higher in serum than urine . UV-328 may have a similarly low excretion rate in human breast milk.…”
Ultraviolet (UV) filters are of great concern due to
their wide
occurrence, bioaccumulation, and toxicity. Little is known about human
exposure to UV filters. A total of 3467 individual human milk samples
from 24 Chinese provinces were collected during 2017–2019.
The concentrations of 12 UV filters in 100 pooled milk samples were
determined. The total UV filter concentration was 78–846 (mean
235 ± 120) ng/g lipid weight. The highest and lowest total mean
concentrations were for samples from Qinghai and Sichuan provinces,
respectively. A significant positive correlation was found between
UV radiation levels and UV concentrations in the samples. The dominant
UV filters were 2-(2-hydroxy-5-methylphenyl) benzotriazole (UV-P)
and ethylhexyl methoxycinnamate (EHMC), which contributed means of
32 and 22%, respectively, to the total concentrations. Plastic products
and sunscreens were probably the sources of UV-P and EHMC in the human
milk from China, respectively. The mean 2-(3,5-di-tert-amyl-2-hydroxyphenyl) benzotriazole (UV-328) concentration was 2.6
± 2.6 ng/g lipid weight. The UV filter profiles were similar
to profiles for samples from Japan, the Philippines, and Switzerland
but not for samples from Korea and Vietnam. The estimated daily UV
filter intake for breastfed infants was below the corresponding reference
dose. This was the first large-scale study of UV filters in human
milk and will help assess the risks posed.
“…The high concentrations found for bisphenol A and nonylphenol therefore do not result from bioaccumulation but from high exposure levels. This is different for substances such as UV-328 that are only slowly metabolized [21,22]. Experimental results show here that leaching into digestive fluids of seabirds is a relevant exposure pathway [17,18].…”
Section: ) View On Leaching Of Plastic Additives Too Narrowmentioning
“…For example, propyl paraben reached maximum serum levels 1.4 ± 1.1 h after oral administration (Shin et al 2019) and the natural product N,N-dimethyltyramine reached plasma peak levels 30-90 min after oral administration (Sommer et al 2020). Nevertheless, the structurally related BUVS 2-(2H-benzotriazol-2-yl)-4,6-di-tert-pentylphenol (UV-328) showed retarded resorption kinetics as well and reached maximum blood levels 8 h after oral administration (Denghel et al 2021). The comparable findings for UV-327 and UV-328 indicate similar resorption processes for these substituted BUVSs.…”
Section: Discussionmentioning
confidence: 99%
“…Most of the substance must, therefore, be excreted via an alternative route. Consistently, biliary excretion was assumed to be the main route of excretion for UV-328, too (Denghel et al 2021).…”
UV-327 (2-(5-chloro-benzotriazol-2-yl)-4,6-di-(tert-butyl)phenol) is used as an ultraviolet (UV) absorber in plastic products and coatings. Due to its ubiquitous distribution in the environment, human exposure is conceivable. In the study presented herein, initial information on the human in vivo metabolism of UV-327 was obtained by single oral administration to three volunteers. Urine and blood samples were collected up to 72 h after exposure. One study participant additionally donated plasma samples. Maximum blood and plasma levels of UV-327 and its two monohydroxylated metabolites UV-327-6-mOH and UV-327-4-mOH were reached 6 h post-exposure. Almost the entire amount found in blood and plasma samples was identified as UV-327, whereas the two metabolites each accounted for only 0.04% of the total amount, indicating that UV-327 is well-absorbed from the intestine, but only partially metabolized. Plasma to blood ratios of UV-327, UV-327-6-mOH, and UV-327-4-mOH ranged from 1.5 to 1.6. Maximum urinary excretion rates of UV-327, UV-327-6-mOH, UV-327-4-mOH, and UV-327-4 + 6-diOH were reached 9–14 h post-exposure. However, only about 0.03% of the orally administered dose of UV-327 was recovered as UV-327 and its metabolites in urine, indicating that biliary excretion may be the major route of elimination of UV-327 and its hydroxylated metabolites. The present study complements the insight in the complex absorption, distribution, metabolism, and elimination (ADME) processes of benzotriazole UV stabilizers (BUVSs).
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