2010
DOI: 10.1016/j.chroma.2010.04.022
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Pressurized solvent extraction followed by gas chromatography tandem mass spectrometry for the determination of benzotriazole light stabilizers in indoor dust

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Cited by 60 publications
(42 citation statements)
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“…19 Carpinteiro and co-workers investigated wastewater and indoor dust samples in human living environments such as private houses and car cabins in Spain and also reported that UV-326, UV-P, UV-328, and UV-327 were all major BZT contaminants. 18,37 Furthermore, it was found that UV-328 and UV-326 were dominant in river sediment in northern China and U.S. waters. 20 UV-328 and UV-234 were found to be the dominant analogues in the sediments of Japanese rivers and lakes, while contributions from other BZTs were almost negligible.…”
Section: 15mentioning
confidence: 99%
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“…19 Carpinteiro and co-workers investigated wastewater and indoor dust samples in human living environments such as private houses and car cabins in Spain and also reported that UV-326, UV-P, UV-328, and UV-327 were all major BZT contaminants. 18,37 Furthermore, it was found that UV-328 and UV-326 were dominant in river sediment in northern China and U.S. waters. 20 UV-328 and UV-234 were found to be the dominant analogues in the sediments of Japanese rivers and lakes, while contributions from other BZTs were almost negligible.…”
Section: 15mentioning
confidence: 99%
“…16,17 In this study, we focused the attention on benzotriazole UV stabilizers (herein abbreviated as BZTs, shown in Figure 1), also normally referred to as Tinuvins, which constitute one of the most important families of UV adsorbents. 18 These (2-hydroxyphenyl)benzotriazole derivatives are produced in large volumes and usually incorporated in various building materials, automobile polymeric components, waxes, films, and varnishes to prevent yellowing and degradation reactions by ultraviolet radiation from sunlight in the 320−400 nm (UV-A) and 280− 320 nm (UV-B) bands. 19,20 A few investigations indicated that certain benzotriazole derivatives, such as 2-(2-hydroxy-5-methylphenyl)benzotriazole (UV-P, Figure 1), 2-(3-tert-butyl-2-hydroxy-5-methylphenyl)-5-chlorobenzotriazole (UV-326), 5-chloro-2-(3,5-di-tert-butyl-2-hydroxyphenyl)benzotriazole (UV-327), and 2-(3,5-di-tert-amyl-2-hydroxyphenyl)-benzotriazole (UV-328), are present in indoor dust, 18 sewage sludge, 20 and marine sediment at urban estuaries.…”
Section: 15mentioning
confidence: 99%
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“…Substancje te łatwo adsorbują się na cząstkach stałych, w USA w osadach dennych rzeki Pawtuxet związki z grupy BTR wykryto w granicach 4300-5200 mg/kg [15], w Chinach w rzece Songhau od 0,31 do 7,12 μg/kg [14]. Natomiast w Hiszpanii w kurzu domowym zawartość tych związków wahała się w przedziale 22 -657 μg/kg [3]. W glebie zazwyczaj BTR bada się w okolicach dróg, stref przemysłowych, na terenach miejskichw Sztokholmie wartość ta wyniosła 3,7 μg/g dla UV 360 nm [2,9].…”
Section: Występowanie Benzotriazoli W śRodowiskuunclassified
“…[2][3][4] In contrast to polar benzotriazole species, their phenolic derivatives show a medium to extremely high hydrophobic character, and thus potential to be accumulated in solid environmental matrices and even to be magnied through the food chain. 5 Recent studies have demonstrated the accumulation and persistence of several BUVSs such as UV-326, UV-327, UV-328, UV-329 and UV-P in sediments 6,7 and sh.…”
Section: Introductionmentioning
confidence: 99%