Abstract

Although extensive efforts have been made to investigate the dynamics of the occurrence and abundance of antibiotic resistance genes (ARGs) in wastewater treatment plants (WWTPs), understanding the acquisition of antibiotic resistance based on the WWTP scale and the potential effects on WWTPs is of relatively less interest. In this study, metagenomic analysis was carried out to investigate whether the WWTP scale could be affected by the prevalence and persistence of ARGs and mobile genetic elements (MGEs). As a result, 152 ARG subtypes were identified in small-scale WWTP samples, while 234 ARG subtypes were identified in large-scale WWTP samples. Among the detectable ARGs, multidrug, MLS (macrolide–lincosamide–streptogramin), sulfonamide, and tetracycline resistance genes had the highest abundance, and large and small WWTPs had similar composition characteristics of ARGs. In MGE analysis, plasmids and integrons were 1.5–2.0-fold more abundant in large-scale WWTPs than in small-scale WWTPs. The profile of bacteria at the phylum level showed that Proteobacteria and Actinobacteria were the most dominant bacteria, representing approximately 70% across large- and small-scale WWTPs. Overall, the results of this study elucidate the different abundances and dissemination of ARGs between large- and small-scale WWTPs, which facilitates the development of next-generation engineered wastewater treatment systems.

Highlights

  • The WHO has announced that the rapid development of the spread of antibiotic resistance is one of the top 10 global public health threats facing humanity [1]

  • Aquatic environments are regarded as a major source for the aggregation and dissemination of antibiotic resistance genes (ARGs) because they are influenced by human activities [4,5]

  • Metagenomics analysis revealed that 152 ARG subtypes belonging to 18 ARG types were identified in the small-scale wastewater treatment plants (WWTPs) samples, while 234 ARG subtypes belonging to 21 ARG types were identified in the large-scale WWTP samples

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Summary

Introduction

The WHO has announced that the rapid development of the spread of antibiotic resistance is one of the top 10 global public health threats facing humanity [1]. Aquatic environments are regarded as a major source for the aggregation and dissemination of antibiotic resistance genes (ARGs) because they are influenced by human activities [4,5]. The emergence of ARGs could significantly increase the spread of antibiotic resistance, especially via mobile genetic elements (MGEs) including plasmids, integrons and insertion sequences [4,5,6]. There is growing evidence that wastewater treatment plants (WWTPs) have received special attention in playing a major role in the proliferation of antibiotic resistance into other environmental systems, such as rivers, sediment, and oceans [6]. WWTPs can be a reservoir and vehicle for the transmission of biological contaminants such as pathogenic bacteria and antibiotic resistance mechanisms to other environmental media [7]

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