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Chlorite and bromate alter the conjugative transfer of antibiotic resistance genes: Co-regulation of oxidative stress and energy supply

溴酸盐 绿泥石 化学 生产过剩 抗生素耐药性 活性氧 抗生素 微生物学 环境化学 生物 基因 生物化学 无机化学 古生物学 石英 溴化物
作者
Jinrui Cao,Bin Xue,Shuran Yang,Xiaobo Yang,Xi Zhang,Zhigang Qiu,Zhiqiang Shen,Jingfeng Wang
出处
期刊:Journal of Hazardous Materials [Elsevier BV]
卷期号:471: 134257-134257 被引量:7
标识
DOI:10.1016/j.jhazmat.2024.134257
摘要

The widespread use of disinfectants during the global response to the 2019 coronavirus pandemic has increased the co-occurrence of disinfection byproducts (DBPs) and antibiotic resistance genes (ARGs). Although DBPs pose major threats to public health globally, there is limited knowledge regarding their biological effects on ARGs. This study aimed to investigate the effects of two inorganic DBPs (chlorite and bromate) on the conjugative transfer of RP4 plasmid among Escherichia coli strains at environmentally relevant concentrations. Interestingly, the frequency of conjugative transfer was initially inhibited when the exposure time to chlorite or bromate was less than 24 h. However, this inhibition transformed into promotion when the exposure time was extended to 36 h. Short exposures to chlorite or bromate were shown to impede the electron transport chain, resulting in an ATP shortage and subsequently inhibiting conjugative transfer. Consequently, this stimulates the overproduction of reactive oxygen species (ROS) and activation of the SOS response. Upon prolonged exposure, the resurgent energy supply promoted conjugative transfer. These findings offer novel and valuable insights into the effects of environmentally relevant concentrations of inorganic DBPs on the conjugative transfer of ARGs, thereby providing a theoretical basis for the management of DBPs. Disinfection by-products (DBPs) and antibiotic resistance genes (ARGs) are harmful contaminants with widespread distribution in water environments. Our study demonstrated that the conjugative transfer of ARGs is initially suppressed and subsequently enhanced by environmental concentrations of chlorite and bromate exposure. Our results highlighted the potential risks of low-concentration inorganic DBPs on the spread of antibiotic resistance. Further, our findings contributed to advancing our understanding of the effective management and control of DBPs in water environments, especially considering the selection of chlorine dioxide and ozone to mitigate the formation of chorine-derived DBPs.
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