State Key Laboratory of Marine Pollution (SKLMP), Research Centre for the Oceans and Human Health, Shenzhen Key Laboratory for the Sustainable Use of Marine Biodiversity, City University of Hong Kong, Hong Kong, China.
State Key Laboratory of Marine Pollution (SKLMP), Research Centre for the Oceans and Human Health, Shenzhen Key Laboratory for the Sustainable Use of Marine Biodiversity, City University of Hong Kong, Hong Kong, China; Department of Chemistry, City University of Hong Kong, Hong Kong, China.
Water Res. 2019 Feb 1;149:607-616. doi: 10.1016/j.watres.2018.11.010. Epub 2018 Nov 9.
Concern about the presence of chiral pharmaceuticals in the environment from wastewater discharge is mounting. In this work, the occurrence and fate of atenolol, metoprolol, venlafaxine, and chloramphenicol, including 10 different stereoisomers, were investigated in sewage and sludge from diverse treatment processes in 4 sewage treatment plants (STPs) in Hong Kong via 4 sampling campaigns over a period of 2 years. The average amounts of individual pharmaceuticals entering the STPs ranged from 4.91 g/d to 6290 g/d, with sludge carrying much lower amounts than the discharged effluent. Mass balance analysis revealed that: larger quantities of these pharmaceuticals were released during the dry seasons, biodegradation was the primary removal mechanism for atenolol and chloramphenicol, and the removal via primary sedimentation and disinfection processes was insignificant (<30%). Selectivity toward R-(+)-atenolol, S-(-)-metoprolol, and R-(-)-venlafaxine was mostly found across secondary-treated effluent samples. Sold as an enantiopure pharmaceutical in R,R-para-form, chloramphenicol was preferentially eliminated after biological process. This is the first study on the occurrence of chloramphenicol enantiomers in the aquatic environment. Ecotoxicological assessment indicated that atenolol and metoprolol could pose risks to marine fish in effluent-receiving waters (i.e., the western waters and Victoria Harbor) of Hong Kong, while R-(+)-atenolol could pose a risk to protozoans five times higher than the S-(-)-enantiomer.
人们越来越关注到环境中手性药物是由污水排放产生的。在这项工作中,通过在两年内进行的 4 次采样活动,研究了香港 4 家污水处理厂(STP)中不同处理工艺的污水和污泥中,包括 10 种不同立体异构体的阿替洛尔、美托洛尔、文拉法辛和氯霉素的存在和命运。进入 STP 的各种药物的平均量从 4.91g/d 到 6290g/d 不等,而污泥中的含量比排放的污水低得多。质量平衡分析表明:这些药物在旱季释放的量较大,生物降解是阿替洛尔和氯霉素的主要去除机制,而初级沉淀和消毒过程的去除率(<30%)并不显著。在经过二级处理的出水样品中,大多发现了对 R-(+)-阿替洛尔、S-(-)-美托洛尔和 R-(-)-文拉法辛的选择性。氯霉素作为一种对映体纯的药物以 R,R-para-form 出售,在经过生物处理后被优先去除。这是首次在水生环境中研究氯霉素对映体的出现。生态毒理学评估表明,阿替洛尔和美托洛尔可能对香港受纳水域(即西部水域和维多利亚港)的海洋鱼类构成风险,而 R-(+)-阿替洛尔对原生动物的风险是 S-(-)-对映体的五倍。