Antibiotic resistance genes and mobile genetic elements in different rivers: The link with antibiotics, microbial communities, and human activities

被引:5
|
作者
Zhang, Lulu [1 ]
Chen, Haoda [1 ]
Gao, Sai [1 ]
Song, Yuanmeng [1 ]
Zhao, Yu [2 ]
Tang, Wenzhong [2 ]
Cui, Jiansheng [1 ]
机构
[1] Hebei Univ Sci & Technol, Coll Environm Sci & Engn, Shijiazhuang 050000, Hebei Prov, Peoples R China
[2] Chinese Acad Sci, Res Ctr Ecoenvironm Sci, State Key Lab Environm Aquat Chem, Beijing 100085, Peoples R China
关键词
Antibiotic resistance genes; Mobile genetic elements; Microbial community; Socio-economic elements; Antibiotics; Different rivers; BACTERIA; DISSEMINATION; ENVIRONMENT; IMPACT; LAKE;
D O I
10.1016/j.scitotenv.2024.170788
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Rivers as a critical sink for antibiotic resistance genes (ARGs), and the distribution and spread of ARGs are related to environmental factors, human activities, and biotic factors (e.g. mobile genetic elements (MGEs)). However, the potential link among ARGs, microbial community, and MGEs in rivers under different antibiotic concentration and human activities remains unclear. In this study, 2 urban rivers (URs), 1 rural-urban river (RUR), and 2 rural rivers (RRs) were investigated to identify the spatial -temporal variation and driving force of ARGs. The total concentration of quinolones (QNs) was 160.1-2151 ng & sdot;g  1 in URs, 23.34-1188 ng & sdot;g  1 in RUR, and 16.39-85.98 ng & sdot;g  1 in RRs. Total population (TP), gross domestic production (GDP), sewage, industrial enterprise (IE), and IEGDP appeared significantly spatial difference in URs, RUR, and RRs. In terms of ARGs, 145-161 subtypes were detected in URs, 59-61 subtypes in RURs, and 46-79 subtypes in RRs. For MGEs, 55-60 MGEs subtypes were detected in URs, 29-30 subtypes in RUR, and 29-35 subtypes in RRs. Significantly positive correlation between MGEs and ARGs were found in these rivers. More ARGs subtypes were related to MGEs in URs than those in RUR and RRs. Overall, MGEs and QNs showed significantly direct positive impact on the abundance of ARGs in all rivers, while microbial community was significantly positive impact on the ARGs abundance in URs and RUR. The ARGs abundance in URs/RUR were directly positive influenced by microbial community/MGEs/socioeconomic elements (SEs)/QNs, while those in RRs were directly positive influenced by QNs/MGEs and indirectly positive impacted by SEs. Most QNs resistance risk showed significantly positive correlation with the abundance of ARGs types. Therefore, not only need to consider the concentration of antibiotics, but also should pay more attention to SEs and MGEs in antibiotics risk management and control.
引用
收藏
页数:14
相关论文
共 50 条
  • [21] Antibiotic resistance genes and mobile genetic elements in a rural river in Southeast China: Occurrence, seasonal variation and association with the antibiotics
    Jiang, Xinshu
    Liu, Liquan
    Chen, Jianfei
    Fan, Xueqi
    Xie, Shuguang
    Huang, Jun
    Yu, Gang
    SCIENCE OF THE TOTAL ENVIRONMENT, 2021, 778
  • [22] Experimental approaches to tracking mobile genetic elements in microbial communities
    Saak, Christina C.
    Dinh, Cong B.
    Dutton, Rachel J.
    FEMS MICROBIOLOGY REVIEWS, 2020, 44 (05) : 606 - 630
  • [23] Investigating the antibiotic resistance genes and mobile genetic elements in water systems impacted with anthropogenic pollutants
    Sharma, Poonam
    Pal, Namrata
    Kumawat, Manoj
    Singh, Samradhi
    Das, Deepanker
    Tilwari, Anita
    Prakash, Anil
    Tiwari, Rajnarayan R.
    Kumar, Manoj
    ENVIRONMENTAL RESEARCH, 2025, 269
  • [24] Mobile genetic elements encoding antibiotic resistance genes and virulence genes in Klebsiella pneumoniae: important pathways for the acquisition of virulence and resistance
    Han, Bin
    Feng, Chunlin
    Jiang, Yuan
    Ye, Caihong
    Wei, Yueshuai
    Liu, Jinbo
    Zeng, Zhangrui
    FRONTIERS IN MICROBIOLOGY, 2025, 16
  • [25] A review focusing on mechanisms and ecological risks of enrichment and propagation of antibiotic resistance genes and mobile genetic elements by microplastic biofilms
    Zhou, Ranran
    Huang, Xirong
    Xie, Zhongtang
    Ding, Zhuhong
    Wei, Hengchen
    Jin, Qijie
    ENVIRONMENTAL RESEARCH, 2024, 251
  • [26] Improved reduction of antibiotic resistance genes and mobile genetic elements from biowastes in dry anaerobic co-digestion
    Wang, Shun
    Hu, Yuansheng
    Hu, Zhenhu
    Wu, Weixiang
    Wang, Zhongzhong
    Jiang, Yan
    Zhan, Xinmin
    WASTE MANAGEMENT, 2021, 126 : 152 - 162
  • [27] Mobile genetic elements are the Major driver of High antibiotic resistance genes abundance in the Upper reaches of huaihe River Basin
    Zhang, Kai
    Xin, Rui
    Zhao, Ze
    Li, Wenpeng
    Wang, Yanan
    Wang, Qian
    Niu, Zhiguang
    Zhang, Ying
    JOURNAL OF HAZARDOUS MATERIALS, 2021, 401
  • [28] Shotgun metagenomics reveals a wide array of antibiotic resistance genes and mobile elements in a polluted lake in India
    Bengtsson-Palme, Johan
    Boulund, Fredrik
    Fick, Jerker
    Kristiansson, Erik
    Larsson, D. G. Joakim
    FRONTIERS IN MICROBIOLOGY, 2014, 5
  • [29] Removal of Antibiotics and Antibiotic Resistance Genes from Urban Rivers Using Artificial Ecosystems
    Zhou H.-D.
    Huang L.-P.
    Chen X.-M.
    Li D.-Y.
    Li X.
    Cui J.-Y.
    Huanjing Kexue/Environmental Science, 2021, 42 (02): : 850 - 859
  • [30] Distribution of Antibiotic Resistance Genes in Microbial Communities: The Impact of Anthropogenic Pollution
    Sazykin, I. S.
    Sazykina, M. A.
    Litsevich, A. R.
    MOLECULAR BIOLOGY, 2024, 58 (06) : 1049 - 1062