Abstract

Nuclear production and industrial activities led to widespread contamination of the Department of Energy (DOE) managed Savannah River Site (SRS), located in South Carolina, United States. The H-02 wetland system was constructed in 2007 for the treatment of industrial and storm water runoff from the SRS Tritium Facility. Albeit at low levels, mercury (Hg) has been detected in the soils of the H-02 wetland ecosystem. In anoxic sediments, Hg is typically methylated by anaerobic microbiota, forming the highly neurotoxic methylmercury (MeHg), which biomagnifies across food webs. However, in surficial oxic wetland soils, microbially mediated demethylation and/or volatilization processes can transform Hg2+ into the less toxic Hg0 form which is released into the atmosphere, thus circumventing MeHg formation. To obtain a deeper understanding on bacterial Hg volatilization, a robust Hg-resistant (HgR) bacteria, called as strain H-02-3 was isolated from the H-02 soils. A draft genome sequence of this strain was obtained at a coverage of 700×, which assembled in 44 contigs with an N50 of 171,569 bp. The genomic size of the strain H-02-3 was 4,708,612 bp with a total number of 4,240 genes; phylogenomic analysis revealed the strain as an Arthrobacter species. Comparative genomics revealed the presence of 1100 unique genes in strain H-02-3, representing 26.7% of the total genome; many identified previously as metal resistance genes (MRGs). Specific to Hg-cycling, the presence of mercuric ion reductase (merA), the organomercurial lyase (merB), and the mercuric resistance operon regulatory protein, were identified. By inference, it can be proposed that the organomercurial lyase facilitates the demethylation of MeHg into Hg2+ which is then reduced to Hg0 by MerA in strain H-02-3. Furthermore, gene prediction using resistome analysis of strain H-02-3 revealed the presence of several antibiotic resistance genes (ARGs), that statistically correlated with the presence of metal resistant genes (MRGs), suggesting co-occurrence patterns of MRGs and ARGs in the strain. Overall, this study delineates environmentally beneficial traits that likely facilitates survival of Arthrobacter sp. H-02-3 within the H-02 wetland soil. Finally, this study also highlights the largely ignored public health risk associated with the co-development of ARGs and MRGs in bacteria native to historically contaminated soils.

Highlights

  • Savannah River Site (SRS) managed by the United States Department of Energy (DoE), located in South Carolina (SC), United States, is a former nuclear legacy site

  • Studies conducted on the operation of the H-02 constructed wetlands have demonstrated sequestration of heavy metals, which are removed by adsorption to organic matter and clay particles, followed by sulfate reducing bacteria facilitating the precipitation of metal ions in the anaerobic soils (Nelson et al, 2006; Mills et al, 2011)

  • As part of an ongoing study on heavy metal-microbe interactions, we have demonstrated that long-term exposure of co-contaminants present in the impacted SRS ecosystems to naturally occurring environmental microbiota has enabled acquisition of an arsenal of metal resistant genes (MRGs), that can be referred to asas the metal pollutome (Spînu et al, 2017), conferring tolerance and/or resistance against heavy metals such as uranium (U) and Hg (Benyehuda et al, 2003)

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Summary

Introduction

Another Arthrobacter strain isolated in our lab from the SRS soils, SRS-W-1-2016, was found to contain a plethora of gene determinants including several gene homologs such as efflux pumps and MFS transporters, known to provide resistance against heavy metal/radionuclides, P-type ATPase translocators and heavy metal-responsive transcriptional regulators (Chauhan et al, 2018). We collected Hg contaminated soil samples from the H-02 wetland area and isolated bacterial strains resistant to high concentrations of Hg, including Arthrobacter sp.

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