International tempo-spatial study of antibiotic resistance genes across the Rhine river using newly developed multiplex qPCR assays

• Published in: The Science of the total environment 2020-03, Vol.706, p.135733-135733, Article 135733
• Main Authors: Paulus, Gabriela K., Hornstra, Luc M., Medema, Gertjan
• Format: Article
• Language: English
• Subjects: Anti-Bacterial Agents; Drug Resistance, Microbial; Genes, Bacterial; Germany; Netherlands; Rivers; RNA, Ribosomal, 16S; Switzerland
• ISSN: 0048-9697; 1879-1026
• DOI: 10.1016/j.scitotenv.2019.135733

The aim of this study was to capture and explain changes in antibiotic resistance gene (ARG) presence and concentration internationally across the Rhine river. Intl1 concentrations and national antibiotic usage were investigated as proxies to predict anthropogenic ARG pollution. Newly-developed multiplex qPCR assays were employed to investigate ARG profiles across 8 locations (L1-L8) in three countries (Switzerland, Germany, the Netherlands) and to detect potential regional causes for variation. Two of these locations were further monitored, over the duration of one month. A total of 13 ARGs, Intl1 and 16S rRNA were quantified. ARG presence and concentrations initially increased from L1(Diepoldsau) to L3(Darmstadt). A continuous increase could not be observed at subsequent locations, with the large river volume likely being a major contributing factor for stability. ARG presence and concentrations fluctuated widely across different locations. L2(Basel) and L3 were the two most polluted locations, coinciding with these locations being well-developed pharmaceutical production locations. We draw attention to the characteristic, clearly distinct ARG profiles, with gene presence being consistent and gene concentrations varying significantly less over time than across different locations. Five genes were Rhine-typical (ermB, ermF, Intl1, sul1 and tetM). Intl1 and sul1 were the genes with highest and second-highest concentration, respectively. Aph(III)a and blaOXA were permanently introduced downstream of L1, indicating no source of these genes prior to L1. We highlight that correlations between Intl1 and ARG concentrations (R2 = 0.72) were driven by correlations to sul1 and disappeared when excluding sul1 from the analysis (R2 = 0.05). Intl1 therefore seems to be a good proxy for sul1 concentrations but not necessarily for overall (anthropogenic) ARG pollution. Aminoglycoside usage per country correlated with concentrations of aph(III)a and several unrelated antibiotic resistance genes (blaOXA,ermB, ermF and tetM). This correlation can be explained by co-resistance caused by mobile genetic elements (MGEs), such as Tn1545. [Display omitted] •Five multiplex qPCR assays were developed for monitoring ARGs in environmental samples.•Rhine river locations have distinct, characteristic antibiotic resistance genes (ARG) profiles.•ARG concentration do not continuously increase at more downstream locations.•Intl1 correlates with overall ARG concentrations only due to corre