| Literature DB >> 32153535 |
Runar Stokke1,2, Eoghan P Reeves2,3, Håkon Dahle1,2, Anita-Elin Fedøy1,2, Thomas Viflot2,3, Solveig Lie Onstad2,3, Francesca Vulcano1,2, Rolf B Pedersen2,3, Vincent G H Eijsink4, Ida H Steen1,2.
Abstract
Deep-sea hydrothermal vents are amongst the most extreme environments on Earth and represent interesting targets for marine bioprospecting and biodiscovery. The microbial communities in hydrothermal vents are often dominated by chemolithoautotrophs utilizing simple chemical compounds, though the full extent of their heterotrophic abilities is still being explored. In the bioprocessing industry, where degradation of complex organic materials often is a major challenge, new microbial solutions are heavily needed. To meet these needs, we have developed novel in situ incubators and tested if deployment of recalcitrant materials from fish farming and wood-pulping industries introduced changes in the microbial community structure in hot marine hydrothermal sediments. The incubation chambers were deployed in sediments at the Bruse vent site located within the Jan Mayen vent field for 1 year, after which the microbial populations in the chambers were profiled by 16S rRNA Ion Torrent amplicon sequencing. A total of 921 operational taxonomic units (OTUs) were assigned into 74 different phyla where differences in community structure were observed depending on the incubated material, chamber depth below the sea floor and/or temperature. A high fraction of putative heterotrophic microbial lineages related to cultivated members within the Thermotogales were observed. However, considerable fractions of previously uncultivated and novel Thermotogales and Bacteroidetes were also identified. Moreover, several novel lineages (e.g., members within the DPANN superphylum, unidentified archaeal lineages, unclassified Thermoplasmatales and Candidatus division BRC-1 bacterium) of as-yet uncultivated thermophilic archaea and bacteria were identified. Overall, our data illustrate that amendment of hydrothermal vent communities by in situ incubation of biomass induces shifts in community structure toward increased fractions of heterotrophic microorganisms. The technologies utilized here could aid in subsequent metagenomics-based enzyme discovery for diverse industries.Entities:
Keywords: biotechnology; deep sea; hydrothermal sediments; in situ enrichment; marine bioprospecting
Year: 2020 PMID: 32153535 PMCID: PMC7046548 DOI: 10.3389/fmicb.2020.00249
Source DB: PubMed Journal: Front Microbiol ISSN: 1664-302X Impact factor: 5.640
FIGURE 1Sampling site and in situ incubation set-up. (A) Bathymetry map of the Bruse hydrothermal vent field with location (enclosed map). (B) In situ incubation set-up using Salmeal, Sulfite-pulped spruce and unamended sediment; cmbsf, centimeters below sea floor. Numbering, 1–3, relates to the different chambers given in Table 1. (C) incubators deployed in hot hydrothermal sediments at the Bruse vent field with white microbial mat on sediment surface and (D), incubators being deployed from the ROV showing the gray incubator holsters mounted in a basket at the front of the ROV.
Sample and sequencing overview for the in situ enrichments.
| CGB12_MID81_IS7_1 | SAMN06885931 | CGB7_1 | Salmeal | ∼4.5–7 cm | ∼30 | 33232 |
| CGB12_MID82_IS7_2 | SAMN06885933 | CGB7_2 | ∼9–11 cm | ∼50 | 20136 | |
| CGB12_MID83_IS7_3 | SAMN09901157 | CGB7_3 | ∼13.5–16 cm | ∼75 | 29967 | |
| CGB11_MID92_IS8_1 | SAMN09901172 | CGB8_1 | Unamended sediment | ∼4.5–7 cm | ∼30 | 44308 |
| CGB11_MID93_IS8_2 | SAMN09901206 | CGB8_2 | ∼9–11 cm | ∼50 | 39474 | |
| CGB11_MID94_IS8_3 | SAMN09901209 | CGB8_3 | ∼13.5–16 cm | ∼75 | 32820 | |
| CGB11_MID89_IS6_1 | SAMN09901170 | CGB6_1 | Sulfite-pulped spruce | ∼4.5–7 cm | ∼30 | 33303 |
| CGB11_MID90_IS6_2 | SAMN09768205 | CGB6_2 | ∼9–11 cm | ∼50 | 26849 | |
| CGB11_MID91_IS6_3 | SAMN09768207 | CGB6_3 | ∼13.5–16 cm | ∼75 | 35463 |
FIGURE 2Relative taxonomic abundances of in situ enrichments at the phylum level. The sample codes are explained in Figure 1 and Table 1.
FIGURE 3Heatmap showing the distribution of the 50 most abundant OTUs > 2% relative abundance within each of the collected in situ chambers. Samples are clustered by complete hierarchical clustering (top) and OTUs are clustered phylogenetically (right) using the neighbor-joining algorithm implemented in FastTree (Price et al., 2010).
Fraction (%) of Thermotogae OTUs in the incubators.
| OTU_11 | 0.02 | 0.01 | 0.02 | 0.17 | 0.09 | 0.00 | 0.04 | 11.98 | 4.85 |
| OTU_17 | 0.00 | 0.00 | 0.00 | 0.41 | 0.00 | 0.00 | 9.14 | 2.06 | 0.00 |
| OTU_24 | 2.97 | 2.82 | 2.06 | 0.01 | 0.14 | 0.17 | 0.00 | 0.00 | 0.18 |
| OTU_3 | 5.99 | 0.01 | 0.07 | 0.00 | 0.06 | 0.10 | 0.00 | 0.35 | 23.55 |