High prevalence and genomic characteristics of carbapenem-resistant Enterobacteriaceae and colistin-resistant Enterobacteriaceae from large-scale rivers in China

肠杆菌科 质粒 肺炎克雷伯菌 生物 复制子 MCR-1型 微生物学 耐碳青霉烯类肠杆菌科 大肠杆菌 粘菌素 流动遗传元素 抗生素耐药性 多重耐药 碳青霉烯 抗生素 基因 遗传学
作者
Cai‐Hong Guo,Yuqing Liu,Yan Li,Xiaoxiao Duan,Tingyu Yang,Fangyu Li,Ming Zou,Bao‐Tao Liu
出处
期刊:Environmental Pollution [Elsevier BV]
卷期号:331 (Pt 2): 121869-121869 被引量:20
标识
DOI:10.1016/j.envpol.2023.121869
摘要

The widespread presence of carbapenem-resistant Enterobacteriaceae (CRE) and mcr-positive Escherichia coli (MCREC) poses a huge threat to both animal and human health. River water environments are vital reservoirs of antibiotic resistance genes, however, the prevalence and characteristics of CRE and MCREC from large-scale rivers in China have not been reported. In the current study, we sampled 86 rivers from four cities in Shandong Province, China in 2021 and analyzed the prevalence of CRE and MCREC. The blaNDM/blaKPC-2/mcr-positive isolates were characterized with methods including PCR, antimicrobial susceptibility testing, conjugation, replicon typing, whole-genome sequencing and phylogenetic analysis. We found that the prevalence of CRE and MCREC in 86 rivers was 16.3% (14/86) and 27.9% (24/86), respectively and eight rivers carried both mcr-1 and blaNDM/blaKPC-2. A total of 48 Enterobacteriaceae isolates (10 ST11 Klebsiella pneumoniae with blaKPC-2, 12 blaNDM-positive E. coli and 26 MCREC carrying only mcr-1) were obtained in this study and 47 displayed multidrug resistance (MDR). Notably, 10 of the 12 blaNDM-positive E. coli isolates also harbored the mcr-1 gene. The blaKPC-2 gene was located within mobile element ISKpn27-blaKPC-2-ISKpn6 on novel F33:A-:B- non-conjugative MDR plasmids in ST11 K. pneumoniae. The dissemination of blaNDM was mediated by transferable MDR IncB/O plasmids or IncX3 plasmids while mcr-1 was primarily disseminated by highly similar IncI2 plasmids. Notably, these waterborne IncB/O, IncX3 and IncI2 plasmids were all highly similar to previously identified plasmids from animal and human isolates. A phylogenomic analysis revealed that the CRE and MCREC isolates from water environments might be derived from animals and trigger infections in humans. The high prevalence of CRE and MCREC in large-scale environmental rivers is alarming and needs sustained surveillance due to the potential risk for transmission to humans via the food chain (irrigation) or direct contact.
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