Key Laboratory of Pesticide Environmental Assessment and Pollution Control, Nanjing Institute of Environmental Science, Ministry of Ecology and Environment of the People's Republic of China, Nanjing 210042, China.
College of Energy and Environmental Engineering, Hebei Key Laboratory of Air Pollution Cause and Impact, Hebei Engineering Research Center of Sewage Treatment and Resource Utilization, Hebei University of Engineering, Handan 056038, China.
Water Res. 2024 Nov 15;266:122444. doi: 10.1016/j.watres.2024.122444. Epub 2024 Sep 13.
Pharmaceutical wastewater often contains significant levels of antibiotic residues, which continuously induce and promote antibiotic resistance during the sewage treatment process. However, the specific impact of antibiotics on the emergence of antibiotic resistance genes (ARGs), microbiomes, and mobile genetic elements (MGEs), as well as the dose-response relationship remain unclear. Herein, through metagenomic sequencing and analysis, we investigated the fate, transmission, and associated risk of ARGs over a ten-year period of exposure to a gradient of sulfonamide antibiotics at a pharmaceutical wastewater treatment plant (PWWTP), an associated wastewater treatment plant (WWTP), and the receiving river. Through abundance comparison and principal co-ordinates analysis (PCoA), our results revealed distinct ARG, microbiome, and MGE profiles across different antibiotic concentrations. Notably, there was a decreasing trend in the abundance of ARGs and MGEs as the antibiotic concentrations were attenuated (p < 0.05). Further partial least squares path modeling analysis, Procrustes analysis and network analysis indicated that variation in MGEs and microbiomes were the driving forces behind the distribution of ARGs. Based on these findings, we proposed an antibiotic-microbiome-MGE-ARG dissemination paradigm, in which integrons as key drivers were closely associated with prevalent ARGs such as sul1, sul2, and aadA. With a focus on human pathogenic bacteria and the associated health risks of ARGs, we conducted pathogen source analysis and calculated the antibiotic resistome risk index (ARRI). Our findings highlighted potential risks associated with the transition from PWWTP to WWTP, raising concerns regarding risk amplification due to the mixed treatment of antibiotic-laden industrial wastewater and domestic sewage. Overall, the results of our study provide valuable information for optimizing wastewater treatment practices to better manage antibiotic resistance.
制药废水中常含有大量的抗生素残留,这些残留物质在污水处理过程中不断诱导和促进抗生素耐药性的产生。然而,抗生素对抗生素耐药基因(ARGs)、微生物组和可移动遗传元件(MGEs)的出现的具体影响,以及剂量-反应关系尚不清楚。在此,我们通过宏基因组测序和分析,研究了在一家制药废水处理厂(PWWTP)、一家相关污水处理厂(WWTP)和受纳河流中,经过十年时间暴露于磺胺类抗生素梯度浓度下,ARGs 的命运、传播及其相关风险。通过丰度比较和主坐标分析(PCoA),我们的结果揭示了不同抗生素浓度下 ARG、微生物组和 MGE 图谱的显著差异。值得注意的是,随着抗生素浓度的减弱(p<0.05),ARG 和 MGE 的丰度呈下降趋势。进一步的偏最小二乘路径模型分析、Procrustes 分析和网络分析表明,MGEs 和微生物组的变化是 ARG 分布的驱动力。基于这些发现,我们提出了一个抗生素-微生物组-MGE-ARG 传播范式,其中整合子作为关键驱动因素与普遍存在的 ARGs 密切相关,如 sul1、sul2 和 aadA。我们关注人类致病菌和 ARGs 相关的健康风险,进行了病原体溯源分析并计算了抗生素抗性组风险指数(ARRI)。我们的研究结果强调了从 PWWTP 到 WWTP 转变所带来的潜在风险,对混合处理含抗生素的工业废水和生活污水导致的风险放大表示担忧。总的来说,我们的研究结果为优化废水处理实践提供了有价值的信息,以更好地管理抗生素耐药性。