Abstract

Microplastics (MPs) might accumulate and transport antibiotic-resistant bacteria (ARB) in aquatic systems. We determined the abundance and diversity of culturable ciprofloxacin- and cefotaxime-resistant bacteria in biofilms covering MPs placed in river water, and characterized priority pathogens from these biofilms. Our results showed that the abundance of ARB colonizing MPs tends to be higher compared to sand particles. Also, higher numbers were cultivated from a mixture of polypropylene (PP), polyethylene (PE) and polyethylene terephthalate (PET), compared to PP and PET alone. Aeromonas and Pseudomonas isolates were the most frequently retrieved from MPs placed before a WWTP discharge while Enterobacteriaceae dominated the culturable plastisphere 200 m after the WWTP discharge. Ciprofloxacin- and/or cefotaxime-resistant Enterobacteriaceae (n = 54 unique isolates) were identified as Escherichia coli (n = 37), Klebsiella pneumoniae (n = 3), Citrobacter spp. (n = 9), Enterobacter spp. (n = 4) and Shigella sp. (n = 1). All isolates presented at least one of the virulence features tested (i.e. biofilm formation, haemolytic activity and production of siderophores), 70% carried the intI1 gene and 85% exhibited a multi-drug resistance phenotype. Plasmid-mediated quinolone resistance genes were detected in ciprofloxacin-resistant Enterobacteriaceae [aacA4-cr (40% of the isolates), qnrS (30%), qnrB (25%), and qnrVC (8%)], along with mutations in gyrA (70%) and parC (72%). Cefotaxime-resistant strains (n = 23) harbored blaCTX-M (70%), blaTEM (61%) and blaSHV (39%). Among CTX-M producers, high-risk clones of E. coli (e.g. ST10 or ST131) and K. pneumoniae (ST17) were identified, most of which carrying blaCTX-M-15. Ten out of 16 CTX-M producers were able to transfer blaCTX-M to a recipient strain. Our results demonstrated the occurrence of multidrug resistant Enterobacteriaceae in the riverine plastisphere, harboring ARGs of clinical concern and exhibiting virulence traits, suggesting a contribution of MPs to the dissemination of antibiotic-resistant priority pathogens. The type of MPs and especially water contamination (e.g. by WWTPs discharges) seem to determine the resistome of the riverine plastisphere.

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