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. 2023 May 15:13:1184081.
doi: 10.3389/fcimb.2023.1184081. eCollection 2023.

Hospital and community wastewater as a source of multidrug-resistant ESBL-producing Escherichia coli

Affiliations

Hospital and community wastewater as a source of multidrug-resistant ESBL-producing Escherichia coli

Lenka Davidova-Gerzova et al. Front Cell Infect Microbiol. .

Abstract

Introduction: Hospitals and wastewater are recognized hot spots for the selection and dissemination of antibiotic-resistant bacteria to the environment, but the total participation of hospitals in the spread of nosocomial pathogens to municipal wastewater treatment plants (WWTPs) and adjacent rivers had not previously been revealed.

Methods: We used a combination of culturing and whole-genome sequencing to explore the transmission routes of Escherichia coli from hospitalized patients suffering from urinary tract infections (UTI) via wastewater to the environment. Samples were collected in two periods in three locations (A, B, and C) and cultured on selective antibiotic-enhanced plates.

Results: In total, 408 E. coli isolates were obtained from patients with UTI (n=81), raw hospital sewage (n=73), WWTPs inflow (n=96)/outflow (n=106), and river upstream (n=21)/downstream (n=31) of WWTPs. The majority of the isolates produced extended-spectrum beta-lactamase (ESBL), mainly CTX-M-15, and showed multidrug resistance (MDR) profiles. Seven carbapenemase-producing isolates with GES-5 or OXA-244 were obtained in two locations from wastewater and river samples. Isolates were assigned to 74 different sequence types (ST), with the predominance of ST131 (n=80) found in all sources including rivers. Extraintestinal pathogenic lineages frequently found in hospital sewage (ST10, ST38, and ST69) were also found in river water. Despite generally high genetic diversity, phylogenetic analysis of ST10, ST295, and ST744 showed highly related isolates (SNP 0-18) from different sources, providing the evidence for the transmission of resistant strains through WWTPs to surface waters.

Discussion: Results of this study suggest that 1) UTI share a minor participation in hospitals wastewaters; 2) a high diversity of STs and phylogenetic groups in municipal wastewaters derive from the urban influence rather than hospitals; and 3) pathogenic lineages and bacteria with emerging resistance genotypes associated with hospitals spread into surface waters. Our study highlights the contribution of hospital and municipal wastewater to the transmission of ESBL- and carbapenemase-producing E. coli with MDR profiles to the environment.

Keywords: Escherichia coli; antibiotic resistance; beta-lactamases; wastewater; whole-genome sequencing.

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Conflict of interest statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Figures

Figure 1
Figure 1
Numbers of antibiotic-resistant (E) coli isolates across locations, sources, and sampling periods. Panel (A): Percentage resistances of E. coli isolates against 24 antibiotics across three locations A, B, and C Bar chart, see legend for different antibiotics prevalence. Panel (B): Prevalence of antibiotic resistance based on location without consideration of different sources or particular antibiotics (location A n=216, location B n=160, location C n=32), source (HU n=81, SH n=73, SI n=96, SO n=106, RU n=21, RD n=31), and sampling period (sampling period 1 n=217, sampling period n=191). Box and whiskers plots show median and quartiles in antibiotic resistance based on different characteristics. Sources HU – UTI isolates, RD – downstream river water, RU – upstream river water, SH – hospital wastewater, SI -WWTP inflow, SO – WWTP outflow. Number of isolates in Location A: UTI (n=42), SH (n=30), SI (n=55), SO (n=56), RU (n=12), RD (n=21). Location B: UTI (n=30), SH (n=20), SI (n=41), SO (n=50), RU (n=9), RD (n=10). Location C: UTI (n=9), SH (n=23). Antibiotic AMK, amikacin; AMP, ampicillin; AMS, ampicillin + sulbactam; AZT, aztreonam; CAZ, ceftazidime; CEP, cefepime; CFZ, cefazolin; CIP, ciprofloxacin; CMP, chloramphenicol; COL, colistin; CPS, cefoperazone + sulbactam; CPZ, cefoperazone; CTX, cefotaxime; CXM, cefuroxime; ERT, ertapenem; GEN, gentamicin; MER, meropenem; NET, netilmicin; PIP, piperacillin; PIT, piperacillin + tazobactam; T/S, co-trimoxazole; TET, tetracycline; TGC, tigecycline; TOB, tobramycin.
Figure 2
Figure 2
The percentage of E. coli isolates (n=408) with beta-lactamase encoding genes based on the source. Bar chart presents the prevalence of ESBL, AmpC, and carbapenemase-encoding genes. Source HU, UTI isolates; RD, downstream river water; RU, upstream river water; SH, hospital wastewater; SI, WWTP inflow; SO, WWTP outflow.
Figure 3
Figure 3
Phylogenetic tree of E. coli isolates based on SNP analysis. See legend for phylogenetic group, location, source, variant of CTX-M beta-lactamase (Others covers: bla TEM-106, bla CTX-M-8, bla CTX-M-65, bla CTX-M-32, bla CTX-M-134), presence of genes encoding resistance to carbapenems, STs, four most prevalent STs of F type plasmids (FAB formulas), and presence of ColV plasmids (purple stars). Colored STs were repeatedly mentioned in the manuscript. Read coding as: sampling period (1, 2), HU, UTI isolates; RD, downstream river water; RU, upstream river water; SH, hospital wastewater; SI, WWTP inflow; SO - WWTP outflow, location (A–C), number of isolates, cultivation on plate with antibiotics (c – cefotaxime/m – meropenem), variant of isolate (optionally, if from one plate two morphologically different colonies were taken).

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