Department of Civil and Environmental Engineering, University of Nebraska-Lincoln, Lincoln, Nebraska, USA.
Nebraska Center for Biotechnology, University of Nebraska-Lincoln, Lincoln, Nebraska, USA.
Appl Environ Microbiol. 2022 Oct 11;88(19):e0112122. doi: 10.1128/aem.01121-22. Epub 2022 Sep 12.
Bacteria in the effluent of wastewater treatment plants (WWTPs) can transfer antibiotic resistance genes (ARGs) to the bacteria in receiving water through conjugation; however, there is a lack of quantitative assessment of this phenomenon in continuous cultures. Our objective was to determine the effects of background nutrient levels in river water column and growth rates of bacteria on the conjugation frequency of ARGs from effluent bacteria to river bacteria, as well as on the resulting resistance level (i.e., MICs) of the river bacteria. Chemostats were employed to simulate the discharge points of WWTPs into rivers, where effluent bacteria (donor cells) meet river bacteria (recipient cells). Both donor and recipient cells were Escherichia coli cells, and the donor cells were constructed by filter mating with bacteria in the effluent of a local WWTP. Results showed that higher bacterial growth rate (0.45 h versus 0.15 h) led to higher conjugation frequencies (10 versus 10 transconjugant per recipient). The nutrient level also significantly affected the conjugation frequency, albeit to a lesser extent than the growth rate. The MIC against tetracycline increased from 2 mg/L in the recipient to 64 to 128 mg/L in transconjugants. In comparison, the MIC only increased to as high as 8 mg/L in mutants. Whole-genome sequencing showed that the -containing plasmid in both the donor and the transconjugant cells also occur in other fecal bacterial genera. The quantitative information obtained from this study can inform hazard identification related to the proliferation of wastewater-associated ARGs in surface water. WWTPs have been regarded as an important hot spot of ARGs. The discharge point of WWTP effluent, where ARGs may be horizontally transferred from bacteria of treated wastewater to bacteria of receiving water, is an important interface between the human-dominated ecosystem and the natural environment. The use of batch cultures in previous studies cannot adequately simulate the nutrient conditions and growth rates in receiving water. In this study, chemostats were employed to simulate the continuous growth of bacteria in receiving water. Furthermore, the experimental setup allowed for separate investigations on the effects of nutrient levels (i.e., simulating background nutrients in river water) and bacterial growth rates on conjugation frequencies and resulting resistance levels. The study generates statistically sound ecological data that can be used to estimate the risk of wastewater-originated ARGs as part of the One Health framework.
污水处理厂(WWTP)废水中的细菌可以通过接合将抗生素耐药基因(ARGs)转移到受纳水中的细菌中;然而,在连续培养中,这种现象缺乏定量评估。我们的目的是确定河流水柱中背景营养水平和细菌生长速率对来自废水细菌的 ARGs 与河流水细菌的接合频率以及河流水细菌的抗性水平(即 MICs)的影响。恒化器用于模拟 WWTP 排放点进入河流,其中废水细菌(供体细胞)与河流水细菌(受体细胞)相遇。供体和受体细胞均为大肠杆菌细胞,供体细胞通过与当地 WWTP 废水的细菌进行滤膜交配构建。结果表明,较高的细菌生长速率(0.45 h 对 0.15 h)导致较高的接合频率(10 个对 10 个转导子对受体)。营养水平也显著影响接合频率,尽管影响程度小于生长速率。对四环素的 MIC 从受体中的 2 mg/L 增加到转导子中的 64 至 128 mg/L。相比之下,MIC 仅增加到 8 mg/L 左右的突变体。全基因组测序表明,供体和转导子细胞中的 - 质粒也存在于其他粪便细菌属中。本研究获得的定量信息可以为识别与地表水污水相关 ARGs 增殖相关的危害提供信息。WWTP 一直被认为是 ARGs 的一个重要热点。WWTP 废水的排放点是 ARGs 可能从处理废水中的细菌水平转移到受纳水中的细菌的重要界面,是人类主导的生态系统与自然环境之间的重要接口。在以前的研究中使用批量培养不能充分模拟受纳水中的营养条件和生长速率。在这项研究中,恒化器被用来模拟受纳水中细菌的连续生长。此外,实验装置允许分别研究营养水平(即模拟河水中的背景营养物质)和细菌生长速率对接合频率和产生的抗性水平的影响。该研究产生了具有统计学意义的生态数据,可用于根据“同一健康”框架评估源自废水的 ARGs 的风险。