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An insight into the removal of fluoroquinolones in activated sludge process: Sorption and biodegradation characteristics

机译:对活性污泥工艺中除去氟喹诺酮类的洞察:吸附和生物降解特性

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The detailed sorption steps and biodegradation characteristics of fluoroquinolones (FQs) including ciprofloxacin, enrofloxacin, lomefloxacin, norfloxacin, and ofloxacin were investigated through batch experiments. The results indicate that FQs at a total concentration of 500 mu g/L caused little inhibition of sludge bioactivity. Sorption was the primary removal pathway of FQs in the activated sludge process, followed by biodegradation, while hydrolysis and volatilization were negligible. FQ sorption on activated sludge was a reversible process governed by surface reaction. Henry and Freundlich models could describe the FQ sorption isotherms well in the concentration range of 100-300 mu g/L. Thermodynamic parameters revealed that FQ sorption on activated sludge is spontaneous, exothermic, and enthalpy-driven. Hydrophobicity-independent mechanisms determined the FQ sorption affinity with activated sludge. The zwitterion of FQs had the strongest sorption affinity, followed by cation and anion, and aerobic condition facilitated FQ sorption. FQs were slowly biodegradable, with long half-lives (>100 hr). FQ biodegradation was enhanced with increasing temperature and under aerobic condition, and thus was possibly achieved through co-metabolism during nitrification. This study provides an insight into the removal kinetics and mechanism of FQs in the activated sludge process, but also helps assess the environmental risks of FQs resulting from sludge disposal. (C) 2016 The Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences. Published by Elsevier B.V.
机译:通过分批实验研究了包括环丙沙星,瑞西红柿,洛美氟苯胺,诺氟沙星和氧氟沙星的详细吸附步骤和生物降解特性。结果表明,总浓度为500μg/ l的FQs导致污泥生物活性的抑制作用。吸附是活性污泥过程中FQS的初级去除途径,然后进行生物降解,而水解和挥发可忽略不计。活性污泥的FQ吸附是由表面反应治理的可逆过程。亨利和Freundlich模型可以将FQ吸附等温机器描述在100-300 mu g / l的浓度范围内。热力学参数显示活性污泥上的FQ吸附是自发的,放热和焓驱动的。疏水性无关的机制确定了与活性污泥的FQ吸附亲和力。 FQS的两性期具有最强的吸附亲和力,其次是阳离子和阴离子,并且有氧病症促进了FQ吸附。 FQS缓慢生物降解,长半衰期(> 100小时)。随着温度的增加和在有氧病症下,增强了FQ生物降解,因此可能通过在硝化过程中通过共代谢来实现。本研究介绍了对活性污泥过程中的去除动力学和机制的洞察力,而且还有助于评估由污泥处理产生的FQS的环境风险。 (c)2016中国科学院生态环境科学研究中心。 elsevier b.v出版。

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