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EFFECT OF IRRADIANCE SPECTRA ON THE PHOTOINDUCED TOXICITY OF THREE POLYCYCLIC AROMAfIC HYDROCARBONS

机译:辐照光谱对三种多环芳烃的光致毒性的影响

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Photoinduced toxicity of polycyclic aromatic hydrocarbons (PAHs) is dependent on the concentration of compounds present and the dose of light received. Of the light present, only those wavelengths absorbed by the compound have the potential to initiate the photochemical events underlying phototoxicity. This suggests that variation in light spectra present in natural waters, arising from variation in dissolved organic carbon composition, is an important determinant of phototoxicity risk in specific, PAH- contaminated waterbodies. To quantify the effect of environmentally realistic variation in light spectra on toxicity, brine shrimp (Artemia salina) assays were conducted under various light spectra and with three PAHs (pyrene, fluoranthene, and anthracene) of known phototoxicity potential. In these spectral assays, the total ultraviolet light present was equivalent; only the spectral char- acteristics varied. Based on the absorbance spectra of these PAHs, it was predicted that toxicity, quantified using immobilization as the endpoint, would vary significantly among light spectra in pyrene assays, but not in anthracene assays, and that variation in toxicity in fluoranthene assays would be intermediate. The results supported these assumptions. In the pyrene exposures, the glass filter time to 50 population immobilization (IT50) (39.5 min) was ll7 longer than the KCr filter IT50 (l8.2 min). In the fluoranthene exposures, the glass filter IT50 (49.5 min) was 27 Ionger than the KCr filter IT50 (39.l min). In the anthracene exposures, the glass filter IT50 (62.2 min) was not st
机译:多环芳烃(PAHs)的光诱导毒性取决于存在的化合物的浓度和接收到的光的剂量。在存在的光中,只有化合物吸收的那些波长才有可能引发潜在的光毒性光化学事件。这表明,由于溶解的有机碳组成的变化而导致的天然水中存在的光谱变化,是特定的,受PAH污染的水体中光毒性风险的重要决定因素。为了量化光谱中环境现实变化对毒性的影响,在各种光谱下并使用三种具有已知光毒性潜能的多环芳烃(py,荧蒽和蒽)进行了盐水虾(卤虫)检测。在这些光谱测定中,存在的总紫外光是等效的。只有光谱特性有所变化。根据这些多环芳烃的吸收光谱,可以预测,以固定化为终点进行量化的毒性在pyr测定中的光谱之间会发生显着变化,但在蒽测定中则没有变化,并且荧蒽测定中的毒性变化将是中等的。结果支持了这些假设。在the暴露中,玻璃过滤器到50人口固定化的时间(IT50)(39.5分钟)比KCr过滤器IT50(18.2分钟)长11。在荧蒽暴露中,玻璃滤池IT50(49.5分钟)比KCr滤池IT50(39.1分钟)长27%。在蒽暴露中,玻璃过滤器IT50(62.2分钟)不牢固

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