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Fate and effects of triclosan in subtropical river biofilms

机译:三氯烷在亚热带河生物膜中的命运和影响

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摘要

Triclosan (TCS, 5-chloro-2-(2,4-dichlorophenoxy) phenol) is a broad-spectrum antimicrobial compound. Owing to its wide use, TCS has been frequently detected in river systems, especially in the (sub-)tropics. However, little information on its interaction with river biofilm in the (sub)tropics is currently available. In the present study, subtropical river biofilms were chronically exposed to TCS for 14 d at concentrations of 0.1-100 mu g/L in artificial river water, which was followed by a 7 d recovery period. The results show that 100 mu g/L TCS inhibited the growth of river biofilms and the no-observed-effect concentration (NOEC) of TCS on river biofilms was 10 mu g/L. The affected biofilms did not completely recover within the 7 d of recovery period due to the adsorbed TCS which was not removed together with dissolved TCS. Exposure to TCS caused significant changes in prokaryotic species composition of river biofilms but no significant effects on eukaryotic species composition. In particular, the relative abundance of several TCS-tolerant bacterial species (e.g., Pseudoxanthomonas mexicana, Sphingopyxis alaskensis and Sphingomonas wittichii) in river biofilms increased following exposure to 10 and 100 mu g/L TCS. River biofilm efficiently removed TCS from the liquid phase and the pH values of the aquatic system significantly affected the removal efficiency of TCS (from 36% at pH 6.5 to 60% at pH 8.5). No degradation products were detected in the liquid phase after 5 days of exposure, possibly due to strong adsorption of the hydrophobic degradation products to river biofilms and through biodegradation by bacteria utilizing TCS and its degradation products as source of carbon and energy for growth, such as Methyloversalitis universalis and Methylobacterium aquaticum.
机译:三氯烷(TCS,5-氯-2-(2,4-二氯氧基)苯酚)是广谱抗微生物化合物。由于其广泛使用,TCS经常在河流系统中检测到,特别是在(子)热带地区。但是,目前可获得有关其与(Sub)热带地区的河流生物膜相互作用的信息很少。在本研究中,亚热带河生物膜在人工河水中以0.1-100μmg/ L的浓度慢地暴露于14d的TCS,其次是7 d恢复期。结果表明,100μg/ l tcs抑制河流河生物膜的生长,生物膜上的TCS的无观察到效应浓度(NOEC)为10μg/ l。由于吸附的TCS没有与溶解的TC一起除去的吸附TC,受影响的生物膜未完全恢复7D恢复期。暴露于TCS导致河流生物膜的原核物种组成的显着变化,但对真核物种组合物没有显着影响。特别地,在暴露于10和100μglTCS之后,在河生物膜中增加了几种耐受性细菌物种(例如,假毒素,墨西哥州墨西哥州,鞘翅基,鞘氨酰胺,鞘氨基菌菌)。河生物膜从液相有效地除去了TCS,水生系统的pH值显着影响了TCS的去除效率(从pH8.5时从pH值为6.5至60%。在暴露5天后没有在液相中检测到降解产物,可能是由于将疏水性降解产物强烈吸附到河流生物膜中,并通过使用TCS的生物降解及其降解产物作为碳和能量的生长来源,例如甲苯血清腺炎和甲基杆菌属性。

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