| Literature DB >> 30211213 |
Luana de Fátima Alves1, Cauã Antunes Westmann2, Gabriel Lencioni Lovate1, Guilherme Marcelino Viana de Siqueira1, Tiago Cabral Borelli3, María-Eugenia Guazzaroni3.
Abstract
Over the past thirty years, since the dawn of metagenomic studies, a completely new (micro) universe was revealed, with the potential to have profound impacts on many aspects of the society. Remarkably, the study of human microbiome provided a new perspective on a myriad of human traits previously regarded as solely (epi-) genetically encoded, such as disease susceptibility, immunological response, and social and nutritional behaviors. In this context, metagenomics has established a powerful framework for understanding the intricate connections between human societies and microbial communities, ultimately allowing for the optimization of both human health and productivity. Thus, we have shifted from the old concept of microbes as harmful organisms to a broader panorama, in which the signal of the relationship between humans and microbes is flexible and directly dependent on our own decisions and practices. In parallel, metagenomics has also been playing a major role in the prospection of "hidden" genetic features and the development of biotechnological applications, through the discovery of novel genes, enzymes, pathways, and bioactive molecules with completely new or improved biochemical functions. Therefore, this review highlights the major milestones over the last three decades of metagenomics, providing insights into both its potentialities and current challenges.Entities:
Year: 2018 PMID: 30211213 PMCID: PMC6126073 DOI: 10.1155/2018/2312987
Source DB: PubMed Journal: Int J Genomics ISSN: 2314-436X Impact factor: 2.326
Figure 1Timeline of the major advancements in metagenomics. Timeline highlighting important developments in the field over the last 40 years, since Sanger sequencing (M1), and over the last 30 years, since the first published metagenomic experiment (M2). The main metagenomic milestones are shown as M1–M11 (all of them are highlighted in the text where they were mentioned).
Figure 2The metagenomics framework and its two main approaches. Both structural and functional metagenomic approaches are the main strategies for exploring key ecological and biotechnological features in environmental samples, respectively. Additionally, 16S rRNA gene surveys can work in synergy with metagenomics for further understanding of microbial ecology.
Genes discovered through metagenomic approaches with high biotechnological potential.
| Function/gene target | DNA source | Library size | Screening method∗ | Number of hits found | Biotechnological relevance | Reference |
|---|---|---|---|---|---|---|
|
| ||||||
| Esterases, endo- | Cow rumen | 1.1 Gb | Function based | 22 | Eight enzymes (36%) were entirely new | [ |
| Laccase | Water from South China Sea | 1.4 Gb | Sequencing based | 1 | High chloride resistance and ability to decolorize industrial dyes | [ |
| Naphthalene dioxygenase | Oil-contaminated soil | 294 Mb | Function based | 2 | Applicable in oil-contaminated soil/water | [ |
| Oxygenases | Artificially polluted soil | 5.2 Gb | Function based | 29 | Applicable in oil-contaminated soil/water | [ |
| Cutinases | Leaf-branch compost | 735 Mb | Function based | 19 | Potential application in polyethylene terephthalate (PET) degradation | [ |
| Phenol hydroxylases and catechol 2,3-dioxygenases | Wastewater treatment plant | 495 Mb | Function based | 413 | Potential use in aromatic compound degradation | [ |
| Carboxylesterase | Marine water | ~1.3 Gb | Function based | 95 | Cold-active and salt-resistant enzyme | [ |
| Cellulase/esterase | Water lakes | 1.86 Gb | Function based | 3 | New cellulase | [ |
| Cellulase | Soil | Not found | Function based | 1 | Halo- and thermotolerant enzyme | [ |
|
| Hydrothermal spring water | Not found | Function based | 1 | Thermotolerant and heath-active enzyme | [ |
| Lipase/protease/hemolysins/biosurfactants | Slaughterhouse drain | ~884 Mb | Function based | 22 | Antimicrobial activity | [ |
|
| ||||||
|
| ||||||
| Acid resistance genes | Plankton and rhizosphere from Tinto River | ~2.3 Gb | Function based | 15 | Genes involved in acid resistance | [ |
| Nickel resistance genes | Rhizosphere of E. andevalensis from Tinto River | 2.15 Gb | Function based | 13 | Genes related to nickel resistance | [ |
| Salt resistance genes | Brine and rhizosphere from Es Trenc saltern | 2.15 Gb | function-based | 11 | Genes conferring salt resistance | [ |
| Arsenic resistance genes | Headwater from Tinto River | 151 Mb | Function based | 18 | Genes involved in arsenic resistance | [ |
|
| ||||||
|
| ||||||
| Constitutive promoters | Soil from secondary Atlantic Forest | ~500 Mb | Function based | 33 | Use as “biobricks” | [ |
|
| ||||||
|
| ||||||
| Naphthalene-degrading system | Naphthalene-contaminated groundwater | ~283 Mb | Sequencing based | 3 | Pollutant-degrading enzyme systems | [ |
| Dioxygenase-degrading cluster | Forest soil | 260–815 bp | Sequencing based | 11 | Degrading phenoxyalkanoic acid (PAA) herbicides avoiding groundwater contamination | [ |
| NRPS biosynthetic pathway | Tunicate consortium in Florida Keys | ~280 Mb | Sequencing based | 1 | ET-743 biosynthetic pathway; anticancer molecule | [ |
|
| ||||||
|
| ||||||
| Pigmentation producing and antibacterial activity | Soil | Not found | Function based | 45 | Potential new molecules to be used as antibiotics | [ |
| Turbomycin A and B | Soil | ~1 Gb | Function based | 3 | Antibiotic activity | [ |
| Antimicrobial small molecules | Soil | ~720 Mb | Function based | 4 | Antibiotic activity | [ |
∗All genes discovered through sequencing-based methodologies were experimentally tested for their related functions.