| Literature DB >> 29020980 |
Fanny Berglund1,2, Nachiket P Marathe2,3, Tobias Österlund1,2, Johan Bengtsson-Palme2,3, Stathis Kotsakis2,3, Carl-Fredrik Flach2,3, D G Joakim Larsson2,3, Erik Kristiansson4,5.
Abstract
BACKGROUND: Metallo-β-lactamases are bacterial enzymes that provide resistance to carbapenems, the most potent class of antibiotics. These enzymes are commonly encoded on mobile genetic elements, which, together with their broad substrate spectrum and lack of clinically useful inhibitors, make them a particularly problematic class of antibiotic resistance determinants. We hypothesized that there is a large and unexplored reservoir of unknown metallo-β-lactamases, some of which may spread to pathogens, thereby threatening public health. The aim of this study was to identify novel metallo-β-lactamases of class B1, the most clinically important subclass of these enzymes.Entities:
Keywords: Carbapenemases; Hidden Markov model; Resistome; Shotgun metagenomics; β-lactam resistance
Mesh:
Substances:
Year: 2017 PMID: 29020980 PMCID: PMC5637372 DOI: 10.1186/s40168-017-0353-8
Source DB: PubMed Journal: Microbiome ISSN: 2049-2618 Impact factor: 14.650
Summary of the analyzed genome datasets and predicted B1BL genes
| Data set | Size (nt) | Sequences | Predicted B1BL genes | Familiesa | Description | |
|---|---|---|---|---|---|---|
| Known | New | |||||
| Bacteria | 9.23 × 109 | 5.24 × 103 | 92 | 7 | 35 | NCBI RefSeq bacteria [ |
| Plasmid | 5.22 × 108 | 9.23 × 103 | 148 | 7 | 1 | NCBI RefSeq plasmid [ |
| NT | 5.22 × 1010 | 2.07 × 107 | 944 | 21 | 36 | NCBI NT [ |
| EnvNT | 9.55 × 109 | 2.07 × 107 | 15 | 1 | 13 | NCBI environmental NT [ |
| Total | 7.19 × 1010 | 4.15 × 107 | 266b | 21b | 50b | |
aBased on a sequence similarity cut-off of 70%
bNon-redundant genes
Summary of the analyzed metagenomes and predicted B1BL genes
| Data set | Size (nt) | Reads | Predicted B1BL genes | Familiesa | Description | |
|---|---|---|---|---|---|---|
| Known | New | |||||
| Isakavagu river | 3.89 × 1010 | 3.85 × 108 | 0 | 0 | 0 | Polluted river sediment [ |
| Kazipally lake | 6.75 × 109 | 6.68 × 107 | 0 | 0 | 0 | Polluted lake [ |
| Patancheru soil | 4.73 × 1010 | 4.68 × 108 | 0 | 0 | 0 | Soil [ |
| Patancheru well | 7.32 × 1010 | 7.25 × 108 | 3 | 0 | 3 | Well water [ |
| WWTP | 4.82 × 1011 | 5.18 × 109 | 8 | 2 | 6 | Sewage treatment plants [ |
| Oil spill | 2.75 × 1011 | 2.72 × 109 | 1 | 0 | 1 | Oil spill [ |
| Pune river | 3.91 × 1011 | 3.11 × 109 | 4 | 1 | 3 | River water [ |
| Human gut 1 | 3.71 × 1011 | 5.22 × 109 | 0 | 0 | 0 | Human gut [ |
| Human gut 2 | 2.74 × 1011 | 3.41 × 109 | 0 | 0 | 0 | Human gut [ |
| HMP | 4.69 × 1012 | 4.41 × 1010 | 0 | 0 | 0 | Human microbiome [ |
| Total | 5.65 × 1012 | 6.54 × 1010 | 16 | 3 | 13 | |
aBased on a sequence similarity cut-off of 70%
Fig. 1The relative abundance of B1BL gene fragments in the analyzed metagenomic data. The relative abundance of B1BL gene fragments varied between 13.8 and 79.0 per million metagenomic fragments. There was a significant difference in abundance between the environmental metagenomes (left) and the human microbiome (right) (p = 0.0167, Wilcoxon rank sum test). The highest levels were observed in the river sediments sampled close to the effluent of a hospital in Pune, India (“Pune river”)
Summary of the 22 experimentally verified B1BL genes
| Source data set | Gene ID | Predicted family | Group | Proposed name | Protein length (aa) | Positive Carba NP test |
|---|---|---|---|---|---|---|
| RefSeq plasmid | G04 | 4 | B1–3 | MYO-1 | 266 | Yes |
| RefSeq bacteria | G06 | 6 | B1–2 | SHD-1 | 265 | Yes |
| RefSeq bacteria | G09 | 9 | B1–5 | SPS-1 | 263 | Yes |
| RefSeq bacteria | G12 | 11 | B1–1 | MYX-1 | 262 | Yes |
| RefSeq bacteria | G13 | 12 | B1–1 | STA-1 | 262 | Yes |
| RefSeq bacteria | G24 | 17 | B1–3 | 259 | No | |
| RefSeq bacteria | G27 | 20 | B1–1 | ANA-1 | 258 | Yes |
| RefSeq bacteria | G28 | 21 | B1–3 | ECV-1 | 258 | Yes |
| RefSeq bacteria | G29 | 22 | B1–3 | ORR-1 | 256 | Yes |
| RefSeq bacteria | G31 | 24 | B1–4 | FIA-1 | 254 | Yes |
| WWTP | G33 | 25 | B1–3 | 252 | Yes | |
| WWTP | G37 | 29 | B1–4 | 251 | Yes | |
| RefSeq bacteria | G52 | 36 | B1–3 | ZOG-1 | 247 | Yes |
| Patancheru well | G58 | 41 | B1–4 | 245 | Yes | |
| RefSeq bacteria | G63 | 46 | B1–2 | TTU-1 | 244 | Yes |
| Pune river | G65 | 48 | B1–3 | 242 | No | |
| RefSeq bacteria | G67 | 50 | B1–2 | PST-1 | 243 | Yesa |
| RefSeq bacteria | G69 | 52 | B1–3 | 242 | No | |
| Patancheru well | G70 | 53 | B1–2 | 242 | Yes | |
| Oil spill | G71 | 54 | B1–2 | 240 | Yes | |
| RefSeq bacteria | G74 | 57 | B1–2 | SHN-1 | 238 | Yes |
| RefSeq bacteria | G77 | ALI | B1–2 | ALI-2 | 246 | Yes |
aStrain tested
Fig. 2A phylogenetic tree describing the evolutionary relationship between the B1 metallo-β-lactamases predicted in this study. The tree was created from representative sequences for the gene families generated by clustering of predicted and previously characterized B1BL at a 70% amino sequence identity cutoff (see “Methods” section). Previously characterized B1BL genes are annotated with the gene name. Novel gene families that were predicted in this study are annotated with the corresponding family number and the sources (metagenome or species name of the host). The numbers in parenthesis indicate how many unique genes there are in each family. The tree was divided into 5 groups (B1–1 to B1–5) as referred to in the text. Complete information on the predicted genes and families are available in Additional file 2: Table S1