Helmholtz Zentrum München-German Research Center for Environmental Health (GmbH), Molecular EXposomics (MEX), Ingolstädter Landstraße 1, 85764, Neuherberg, Germany.
Department für Biowissenschaftliche Grundlagen, Technische Universität München, Weihenstephaner Steig 23, 85350, Freising, Germany.
Environ Sci Pollut Res Int. 2017 Dec;24(35):27525-27538. doi: 10.1007/s11356-017-0055-6. Epub 2017 Oct 5.
Bromocarbazoles and chlorocarbazoles are emerging environmental contaminants that have been reported to be persistent and possessing dioxin-like toxicity; however, their photodegradative fate in water is unknown. The photodegradation of 3-bromocarbazole, 3-chlorocarbazole, and 3,6-dichlorocarbazole was determined in ultrapure water. They proceeded by direct photolysis and followed first-order kinetics. The rate constants (k) were 0.4838, 0.3454, and 0.4422 h corresponding to half-lives (t ) 1.81, 2.01, and 1.62, while the quantum yields (Ф) were 0.232, 0.180, and 0.295 respectively. The maximum wavelengths of absorption (λ ) were in the near ultraviolet region (295, 296, 299, and 301 nm) implying these compounds are likely to degrade slowly under sunlight in natural aquatic environment. The molar extinction coefficients (ε) determined in acetonitrile were 18,573, 17,028, 13,385, and 14,010 L mol cm, respectively, the latter being 3,6-dibromocarbazole. A bathochromic shift was observed with halogen addition on their respective mono-substituted congeners. Bromocarbazoles were observed to degrade faster in water than chlorocarbazoles. In addition, photodegradation was estimated to proceed faster in summer than in winter, in natural water system at 50° N latitude. In the absence of light, hydrolytic degradation occurred but proceeded very slowly. Hexahydroxybenzene and trihydroxycarbazole were positively identified as the likely photoproducts with the former being a known toxic compound. Dehalogenation, oxidative cleavage, hydroxylation, and hydrolysis are suggested as the major photodegradation mechanisms in water, yielding phototoxic products that may be of enhanced toxicity than the parent compounds.
溴代咔唑和氯代咔唑是新兴的环境污染物,据报道它们具有持久性和类二恶英毒性;然而,它们在水中的光降解命运尚不清楚。在超纯水中测定了 3-溴代咔唑、3-氯代咔唑和 3,6-二氯代咔唑的光降解。它们通过直接光解进行,并遵循一级动力学。速率常数(k)分别为 0.4838、0.3454 和 0.4422 h,相应的半衰期(t)分别为 1.81、2.01 和 1.62,而量子产率(Ф)分别为 0.232、0.180 和 0.295。最大吸收波长(λ)在近紫外区域(295、296、299 和 301 nm),这意味着这些化合物在自然水生环境中的阳光照射下可能缓慢降解。在乙腈中测定的摩尔消光系数(ε)分别为 18573、17028、13385 和 14010 L mol cm,后者为 3,6-二溴代咔唑。在各自的单取代同系物上添加卤素观察到红移。溴代咔唑在水中的降解速度快于氯代咔唑。此外,在北纬 50°的自然水系统中,估计光降解在夏季比冬季更快。在没有光的情况下,水解降解发生,但非常缓慢。六羟基苯和三羟基咔唑被确认为可能的光产物,其中前者是一种已知的有毒化合物。在水中,脱卤、氧化裂解、羟化和水解被认为是主要的光降解机制,生成的光毒性产物可能比母体化合物毒性更强。