Role of wastewater treatment plants on environmental abundance of Antimicrobial Resistance Genes in Chilean rivers.


Journal

International journal of hygiene and environmental health
ISSN: 1618-131X
Titre abrégé: Int J Hyg Environ Health
Pays: Germany
ID NLM: 100898843

Informations de publication

Date de publication:
01 2020
Historique:
received: 08 08 2019
revised: 04 10 2019
accepted: 12 10 2019
pubmed: 15 11 2019
medline: 9 4 2020
entrez: 15 11 2019
Statut: ppublish

Résumé

Point sources such as wastewater treatment plants (WWTPs) commonly discharge their effluent into rivers. Their waste may include antibiotic residues, disinfectants, antibiotic resistant bacteria (ARB), and Antimicrobial Resistance Genes (ARG). There is evidence that ARG can be found in the natural environment, but attribution to specific point sources is lacking. The goal of this study was to assess the release and dissemination of ARG from three WWTPs in southern Chile via two pathways: through the river systems, and through wild birds. A longitudinal study was conducted, collecting river sediment samples at different distances both upstream and downstream from each WWTP. Wild birds were sampled from around one of the WWTPs once a month for 13 months. A microfluidic q-PCR approach was used to quantify 48 genes covering different molecular mechanisms of resistance, and data was analyzed using ordination methods and linear mixed regression models. There was a statistically significant increase downstream from the WWTPs (p < 0.05) for 17 ARG, but the downstream dissemination through the rivers was not clear. Beta-lactamase genes bla While results from this study indicate an influence of WWTPs on ARG abundance in the rivers, the biological significance of this increase and the extent of the WWTPs influence are unclear. In addition, wild birds were found to play a role in disseminating ARG, although association to the specific WWTP could not be ascertained.

Sections du résumé

BACKGROUND
Point sources such as wastewater treatment plants (WWTPs) commonly discharge their effluent into rivers. Their waste may include antibiotic residues, disinfectants, antibiotic resistant bacteria (ARB), and Antimicrobial Resistance Genes (ARG). There is evidence that ARG can be found in the natural environment, but attribution to specific point sources is lacking.
OBJECTIVES
The goal of this study was to assess the release and dissemination of ARG from three WWTPs in southern Chile via two pathways: through the river systems, and through wild birds.
METHODS
A longitudinal study was conducted, collecting river sediment samples at different distances both upstream and downstream from each WWTP. Wild birds were sampled from around one of the WWTPs once a month for 13 months. A microfluidic q-PCR approach was used to quantify 48 genes covering different molecular mechanisms of resistance, and data was analyzed using ordination methods and linear mixed regression models.
RESULTS
There was a statistically significant increase downstream from the WWTPs (p < 0.05) for 17 ARG, but the downstream dissemination through the rivers was not clear. Beta-lactamase genes bla
CONCLUSIONS
While results from this study indicate an influence of WWTPs on ARG abundance in the rivers, the biological significance of this increase and the extent of the WWTPs influence are unclear. In addition, wild birds were found to play a role in disseminating ARG, although association to the specific WWTP could not be ascertained.

Identifiants

pubmed: 31722832
pii: S1438-4639(19)30702-3
doi: 10.1016/j.ijheh.2019.10.006
pii:
doi:

Substances chimiques

Waste Water 0

Types de publication

Journal Article Research Support, Non-U.S. Gov't

Langues

eng

Sous-ensembles de citation

IM

Pagination

56-64

Informations de copyright

Copyright © 2019 Elsevier GmbH. All rights reserved.

Auteurs

Irene Bueno (I)

Department of Veterinary and Biomedical Sciences, University of Minnesota, St. Paul, MN, USA.

Claudio Verdugo (C)

Laboratorio de Ecología y Evolución de Enfermedades Infecciosas (E3 Lab), Instituto de Patología Animal, Facultad de Ciencias Veterinarias, Universidad Austral de Chile, Valdivia, Chile.

Omar Jimenez-Lopez (O)

Laboratorio de Ecología y Evolución de Enfermedades Infecciosas (E3 Lab), Instituto de Patología Animal, Facultad de Ciencias Veterinarias, Universidad Austral de Chile, Valdivia, Chile.

Pedro Pablo Alvarez (PP)

Laboratorio de Ecología y Evolución de Enfermedades Infecciosas (E3 Lab), Instituto de Patología Animal, Facultad de Ciencias Veterinarias, Universidad Austral de Chile, Valdivia, Chile.

Gerardo Gonzalez-Rocha (G)

Laboratorio de Investigación en Agentes Antibacterianos (LIAA), Facultad de Ciencias Biológicas, Universidad de Concepción. Departamento de Microbiología, Concepción, Chile; Millennium Nucleus on Interdisciplinary Approach to Antimicrobial Resistance, Santiago, Chile.

Celia A Lima (CA)

Laboratorio de Investigación en Agentes Antibacterianos (LIAA), Facultad de Ciencias Biológicas, Universidad de Concepción. Departamento de Microbiología, Concepción, Chile; Departamento de Medicina Interna, Facultad de Medicina, Universidad de Concepción, Concepción, Chile.

Dominic A Travis (DA)

Department of Veterinary Population Medicine, University of Minnesota, St. Paul, MN, USA.

Britta Wass (B)

Department of Veterinary and Biomedical Sciences, University of Minnesota, St. Paul, MN, USA.

Qian Zhang (Q)

BioTechnology Institute, University of Minnesota. 140 Gortner Laboratory of BioChemistry, St. Paul, MN, USA.

Satoshi Ishii (S)

BioTechnology Institute, University of Minnesota. 140 Gortner Laboratory of BioChemistry, St. Paul, MN, USA; Department of Soil, Water, and Climate, University of Minnesota, St. Paul, MN, USA.

Randall S Singer (RS)

Department of Veterinary and Biomedical Sciences, University of Minnesota, St. Paul, MN, USA; Millennium Nucleus on Interdisciplinary Approach to Antimicrobial Resistance, Santiago, Chile. Electronic address: rsinger@umn.edu.

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