Research Group of Analytical Chemistry and Life Sciences, Department of Analytical Chemistry, University of Granada, Campus of Fuentenueva, E-18071 Granada, Spain.
J Environ Manage. 2013 May 15;120:75-83. doi: 10.1016/j.jenvman.2013.02.007. Epub 2013 Mar 15.
This work describes the removal of 6 quinolone antibiotics from wastewaters under different redox conditions (aerobic, nitrifying and anoxic) through batch experiments in laboratory scale activated sludge reactors using mixed liquor from a membrane bioreactor pilot plant (MBR). The main removal pathways for antibiotics from wastewaters involved in each treatment are described. Mass balances indicated that sorption on sludge played a dominating role in the elimination of antibiotics. Sorption potential depended on the redox conditions, being lower in nitrifying (Kd, 414-876 L kg(-1)) and anoxic (Kd, 471-930 L kg(-1)) sludge in comparison with aerobic sludge (Kd, 534-1137 L kg(-1)). Kd was higher for piperazinylic quinolones. Redox conditions also influenced biodegradation, a secondary pathway, which followed first-order kinetics with degradation rates constants ranging from 1.8·10(-3) to 8.2·10(-3) h(-1). Biodegradation rates under anoxic conditions were negligible. The experimental results have also demonstrated much higher removal efficiency by biodegradation (36.2-60.0%) under nitrifying conditions in comparison with aerobic conditions (14.9-43.8%). The addition of allylthiourea, an ammonia monooxygenase inhibitor, inhibited nitrification completely and reduced significantly the biodegradation of target antibiotics (16.5-29.3%). The residual biodegradation in the presence of allylthiourea may be due to the activity of heterotrophs in the enriched nitrifier culture. The removal of the selected antibiotics under the studied redox conditions depended significantly on the bacteria composition of the sludge. These results suggest that despite the known persistence of this group of antibiotics it is possible to enhance their degradation using nitrifying conditions, which at adequate working conditions as high SRT, typical in MBR, become a promising alternative for improving quinolones removal from environment.
本工作描述了在实验室规模的膜生物反应器(MBR)中使用混合液,在不同氧化还原条件(好氧、硝化和缺氧)下从废水中去除 6 种喹诺酮类抗生素。描述了每种处理方法中抗生素从废水中去除的主要途径。质量平衡表明,污泥吸附在抗生素的消除中起着主导作用。吸附潜力取决于氧化还原条件,硝化(Kd,414-876 L kg(-1)) 和缺氧(Kd,471-930 L kg(-1)) 污泥中的吸附潜力低于好氧污泥(Kd,534-1137 L kg(-1))。哌嗪基喹诺酮的 Kd 值较高。氧化还原条件也影响生物降解,这是一种次要途径,遵循一级动力学,降解速率常数范围为 1.8·10(-3) 至 8.2·10(-3) h(-1)。缺氧条件下的生物降解速率可以忽略不计。实验结果还表明,在硝化条件下(36.2-60.0%)比好氧条件下(14.9-43.8%)通过生物降解去除的效率更高。添加氨单加氧酶抑制剂烯丙基硫脲完全抑制硝化,并显著降低目标抗生素的生物降解(16.5-29.3%)。在存在烯丙基硫脲的情况下残留的生物降解可能是由于富集硝化培养物中异养菌的活性。在所研究的氧化还原条件下,所选抗生素的去除明显取决于污泥中细菌的组成。这些结果表明,尽管已知该组抗生素具有持久性,但可以通过硝化条件来增强其降解,在适当的工作条件下,如 MBR 中的高 SRT,成为改善喹诺酮类抗生素从环境中去除的有前途的替代方法。