Li Ding-Chang, Gao Jing-Feng, Zhang Shu-Jun, Gao Yong-Qing, Sun Li-Xin
National Engineering Laboratory for Advanced Municipal Wastewater Treatment and Reuse Technology, Beijing University of Technology, Beijing 100124, China.
National Engineering Laboratory for Advanced Municipal Wastewater Treatment and Reuse Technology, Beijing University of Technology, Beijing 100124, China.
Environ Int. 2020 Apr;137:105540. doi: 10.1016/j.envint.2020.105540. Epub 2020 Feb 5.
The prevalence and accumulation of antibiotic resistance genes (ARGs) were frequently detected in biological wastewater treatment processes, which might cause potential health crisis to human. In present study, the fates of ARGs during two different aerobic granular sludge (AGS) cultivation processes were investigated. The results showed that traditional AGS (T-AGS) cultivation process and enhanced AGS (E-AGS) cultivation process had significant differences (P < 0.005) in ARGs shift patterns. E-AGS process had higher average relative abundance (0.280 ± 0.079) of ARGs than T-AGS process (0.130 ± 0.041), while the intensity of ARGs enrichment during E-AGS (1.52-5.29 fold) was lower than T-AGS (3.79-75.31 fold) process. TnpA and intI1 as two different types of mobile genetic elements (MGEs) carrying ARGs, were observed to contribute significantly to the horizontal gene transfer (HGT) during T-AGS (r = 0.902, P < 0.050) and E-AGS (r = 0.823, P < 0.001) processes, respectively. Higher HGT level took place and more possible potential hosts (25 hosts) harboring ARGs were detected during E-AGS process comparing with T-AGS process (17 hosts). Meanwhile, over large AGS might increase the propagation of several antibiotic deactivation ARGs, so it was not advised. Overall, whether during T-AGS or during E-AGS process which was applied in a pilot-scale sequencing batch reactor treating municipal wastewater, the accumulation and spread of ARGs were inevitable. It should be valued that some suitable pre-treatments of seed sludge should be executed, meanwhile, advanced treatment for removing of ARGs in AGS should be conducted to maintain the relative abundances of ARGs at relatively low level.
在生物废水处理过程中,抗生素抗性基因(ARGs)的流行和积累经常被检测到,这可能会给人类带来潜在的健康危机。在本研究中,调查了两种不同的好氧颗粒污泥(AGS)培养过程中ARGs的去向。结果表明,传统AGS(T-AGS)培养过程和强化AGS(E-AGS)培养过程在ARGs转移模式上存在显著差异(P < 0.005)。E-AGS过程中ARGs的平均相对丰度(0.280±0.079)高于T-AGS过程(0.130±0.041),而E-AGS过程中ARGs的富集强度(1.52 - 5.29倍)低于T-AGS过程(3.79 - 75.31倍)。TnpA和intI1作为携带ARGs的两种不同类型的移动遗传元件(MGEs),分别在T-AGS(r = 0.902,P < 0.050)和E-AGS(r = 0.823,P < 0.001)过程中对水平基因转移(HGT)有显著贡献。与T-AGS过程(17个宿主)相比,E-AGS过程中发生了更高水平的HGT,并且检测到更多携带ARGs的可能潜在宿主(25个宿主)。同时,过大的AGS可能会增加几种抗生素失活ARGs的传播,因此不建议这样做。总体而言,无论是在中试规模的序批式反应器处理城市废水时应用的T-AGS过程还是E-AGS过程中,ARGs的积累和传播都是不可避免的。值得重视的是,应执行一些合适的种子污泥预处理,同时,应进行去除AGS中ARGs的深度处理,以将ARGs的相对丰度维持在相对较低的水平。