National Engineering Laboratory for Advanced Municipal Wastewater Treatment and Reuse Technology, Faculty of Environment and Life, Beijing University of Technology, Beijing, 100124, China.
National Engineering Laboratory for Advanced Municipal Wastewater Treatment and Reuse Technology, Faculty of Environment and Life, Beijing University of Technology, Beijing, 100124, China.
Environ Res. 2022 Sep;212(Pt C):113356. doi: 10.1016/j.envres.2022.113356. Epub 2022 Apr 27.
Metagenomic approach was applied to simultaneously reveal the antibiotic resistance genes (ARGs) and antibacterial biocide & metal resistance genes (BMRGs), and the corresponding microbial hosts with high mobility during aerobic granular sludge (AGS) formation process. The results showed that the relative abundance of BMRGs was 88-123 times that of ARGs. AGS process was easier to enrich BMRGs, leading to a greater risk of drug resistance caused by BMRGs than that by ARGs. The enrichments of ARGs and BMRGs in AGS were closely related to several enhanced microbial metabolisms (i.e., cell motility, transposase and ATP-binding cassette transporters) and their corresponding regulatory genes. Several enhanced KEGG Orthologs (KO) functions, such as K01995, K01996, K01997 and K02002, might cause a positive impact on the spread of ARGs and BMRGs, and the main contributors were the largely enriched glycogens accumulating organisms. The first dominant ARGs (adeF) was carried by lots of microbial hosts, which might be enriched and propagated mainly through horizontal gene transfer. Candidatus Competibacter denitrificans simultaneously harbored ARG (cmx) and Cu related RGs (corR). Many enriched bacteria contained simultaneously multiple BMRGs (copR and corR) and mobile genetic elements (integrons and plasmids), granting them high mobility capabilities and contributing to the spread of BMRGs. This study might provide deeper understandings of the proliferation and mobility of ARGs and BMRGs, importantly, highlighted the status of BMRGs, which laid the foundation for the controlling widespread of resistance genes in AGS.
采用宏基因组学方法同时揭示了好氧颗粒污泥(AGS)形成过程中抗生素抗性基因(ARGs)和抗菌杀生物剂/金属抗性基因(BMRGs)及其具有高迁移能力的相应微生物宿主。结果表明,BMRGs 的相对丰度是 ARGs 的 88-123 倍。AGS 过程更容易富集 BMRGs,导致 BMRGs 引起的耐药性风险大于 ARGs。AGS 中 ARGs 和 BMRGs 的富集与几种增强的微生物代谢(即细胞运动性、转座酶和 ATP 结合盒转运蛋白)及其相应的调节基因密切相关。几种增强的 KEGG 直系同源物(KO)功能,如 K01995、K01996、K01997 和 K02002,可能对 ARGs 和 BMRGs 的传播产生积极影响,主要贡献者是大量富集的糖原积累生物体。第一个主要的 ARG(adeF)由许多微生物宿主携带,可能主要通过水平基因转移进行富集和传播。Candidatus Competibacter denitrificans 同时携带 ARG(cmx)和 Cu 相关 RGs(corR)。许多富集的细菌同时含有多种 BMRGs(copR 和 corR)和移动遗传元件(整合子和质粒),赋予它们高迁移能力,并有助于 BMRGs 的传播。本研究可能为深入了解 ARGs 和 BMRGs 的增殖和迁移提供了依据,重要的是,突出了 BMRGs 的地位,为控制 AGS 中抗性基因的广泛传播奠定了基础。