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. 2022 Aug 6;9:480. doi: 10.1038/s41597-022-01586-x

Metagenome sequencing and 768 microbial genomes from cold seep in South China Sea

Huan Zhang 1,2,#, Minxiao Wang 1,2,#, Hao Wang 1,2, Hao Chen 1,2, Lei Cao 1,2, Zhaoshan Zhong 1,2, Chao Lian 1,2, Li Zhou 1,2, Chaolun Li 1,2,3,✉
PMCID: PMC9357000  PMID: 35933411

Abstract

Cold seep microbial communities are fascinating ecosystems on Earth which provide unique models for understanding the living strategies in deep-sea distinct environments. In this study, 23 metagenomes were generated from samples collected in the Site-F cold seep field in South China Sea, including the sea water closely above the invertebrate communities, the cold seep fluids, the fluids under the invertebrate communities and the sediment column around the seep vent. By binning tools, we retrieved a total of 768 metagenome assembled genome (MAGs) that were estimated to be >60% complete. Of the MAGs, 61 were estimated to be >90% complete, while an additional 105 were >80% complete. Phylogenomic analysis revealed 597 bacterial and 171 archaeal MAGs, of which nearly all were distantly related to known cultivated isolates. In the 768 MAGs, the abundant Bacteria in phylum level included Proteobacteria, Desulfobacterota, Bacteroidota, Patescibacteria and Chloroflexota, while the abundant Archaea included Asgardarchaeota, Thermoplasmatota, and Thermoproteota. These results provide a dataset available for further interrogation of deep-sea microbial ecology.

Subject terms: Marine biology, Environmental microbiology


Measurement(s) metagenome assembled genomes
Technology Type(s) metagenome sequencing and genome binning
Sample Characteristic - Organism microorganism
Sample Characteristic - Environment marine cold seep biome
Sample Characteristic - Location South China Sea

Background & Summary

Cold seeps are seafloor manifestations of methane-rich fluid migration from the sedimentary subsurface and support unique communities via chemosynthetic interactions fuelled1. The microorganisms inhabiting cold seeps transform the chemical energy in methane to products that sustain rich benthic communities around the gas leaks2. The use of next-generation sequencing methods has tremendously improved the insights into seep microbiomes and will advance microbial ecology from the diversity microbial distribution pattern to the adaptive survival strategy in deep-sea environments.

The cold seep in Site F (also known as Formosa Ridge) is one of the active cold seeps on the north-eastern slope of the South China Sea (SCS)3, where the natural gas hydrate exposed on the seafloor and was covered by chemosynthetic communities mainly comprising deep-sea mussels and galatheid crabs4. The geochemical characters have been illustrated by the in-situ detection using the developed Raman insertion Probe (RiP) system and integrated sensors5–7. The horizontal and vertical variations in methane concentrations showed contrasting trends in fields from the center of flourishing communities to the margin of sediments6. No CH4 or H2S Raman peaks were detected in the cold seep fluids, while dissolved CH4 were identified in the fluids under the lush chemosynthetic communities, and the sediment pore water profiles collected near the cold seep were characterized by the loss of SO42− and increased CH4, H2S and HS− peaks5,7. As the microbial communities in deep-sea cold seeps are often shaped by geochemical components in seepage solutions, we collected samples from the Site-F cold seep field in 2017, including the sea water closely above the invertebrate communities, the cold seep fluids, the fluids under the invertebrate communities and the sediment column around the seep vent (Fig. 1 and Table 1). The metagenomes were sequenced with Illumina HiSeq X Ten platform, with each metagenome yielding approximately 52.7 Gbps to 80.6 Gbps of clean bases (Table 2). We further obtained 768 metagenome-assembled genomes (MAGs) of environmental Bacteria and Archaea estimated to be >60% complete and <20% contamination (Supplementary Table 1). Of the MAGs, 61 were estimated to be >90% complete, while an additional 105 were >80% complete. There were 59 high-quality MAGs (completeness > 90% and contamination < 5%), accounting for 7.68% of the total. The anaerobic methanotrophic archaea (ANME), aerobic methanotrophic bacteria Methylococcales, sulfate-reducing Desulfobacterales, as well as sulfide-oxidizing Campylobacterales and Thiotrichales (Supplementary Table 2), well match the most favourable microbial metabolisms at methane seeps in terms of substrate supply. Meanwhile, the phylogenomic analysis suggests that this set of draft genomes includes highly sought-after genomes that lack cultured representatives, such as archaea Bathyarchaeota (30), Aenigmarchaeota (29), Heimdallarchaeota (20) and Pacearchaeota (10), and bacteria Patescibacteria (44), WOR-3 (23), Zixibacteria (13), Marinisomatota (12) and Eisenbacteria (6) et al. (Fig. 2). In addition, there are also some potential new phylum including NPL-UPA2 (7), UBP15 (4), FCPU426 (2) and SM23–31 (2) et al. All the non-redundant draft metagenome-assembled genomes described here were deposited into the National Center for Biotechnology Information (NCBI). These data will hopefully provide a resource for downstream analysis acting as references for largescale comparative genomics within globally vital phylogenetic groups, as well as allowing for the exploration of novel microbial metabolisms.

Fig. 1.

Fig. 1

Sample collection and data analysis process. (a) Location and the sampling area in the cold seep field in the northern South China Sea. (b) Schematic overview of sampling and metagenomic analysis performed in this study. Each rectangle symbolizes processes containing descriptions (in bold), methods or tools used in the corresponding analysis.

Table 1.

Information for all samples utilized in this study.

Sample ID Latitude Longitude Depth (m) Sample Environment characteristics Sample collection date
SW_1 22.36 119.32 1119 seawater water closely above the invertebrate communities 09/25/2017
SW_2 22.36 119.32 1121 seawater water closely above the invertebrate communities 09/25/2017
SW_3 22.16 119.29 1127 seawater cold seep fluids at gas plume 09/25/2017
SW_4 22.16 119.29 1120 seawater fluid under the invertebrate communities 09/26/2017
RS_1 22.01 119.28 1153 sediment (0-2 cmbsf) reductive sediments area 09/21/2017
RS_2 22.01 119.28 1153 sediment (2–4 cmbsf) reductive sediments area 09/21/2017
RS_3 22.01 119.28 1153 sediment (4–6 cmbsf) reductive sediments area 09/21/2017
RS_4 22.01 119.28 1153 sediment (6–8 cmbsf) reductive sediments area 09/21/2017
RS_5 22.01 119.28 1153 sediment (8–10 cmbsf) reductive sediments area 09/21/2017
RS_6 22.01 119.28 1153 sediment (10–12 cmbsf) reductive sediments area 09/21/2017
RS_7 22.01 119.28 1153 sediment (12–14 cmbsf) reductive sediments area 09/21/2017
RS_8 22.01 119.28 1153 sediment (14–16 cmbsf) reductive sediments area 09/21/2017
RS_9 22.01 119.28 1153 sediment (16–18 cmbsf) reductive sediments area 09/21/2017
RS_10 22.01 119.28 1153 sediment (18–20 cmbsf) reductive sediments area 09/21/2017
RS_11 22.17 119.28 1121 sediment (0–20 cmbsf) reductive sediments area 09/25/2017
RS_12 22.17 119.28 1121 sediment (20–55 cmbsf) reductive sediments area 09/25/2017
RS_13 22.17 119.28 1121 sediment (55–90 cmbsf) reductive sediments area 09/25/2017
RS_14 22.17 119.28 1121 sediment (90–125 cmbsf) reductive sediments area 09/25/2017
RS_15 22.17 119.28 1121 sediment (125–160 cmbsf) reductive sediments area 09/25/2017
RS_16 22.17 119.28 1121 sediment (160–195 cmbsf) reductive sediments area 09/25/2017
RS_17 22.17 119.28 1121 sediment (195–230 cmbsf) reductive sediments area 09/25/2017
RS_18 22.17 119.28 1121 sediment (230–265 cmbsf) reductive sediments area 09/25/2017
RS_19 22.17 119.28 1121 sediment (265–300 cmbsf) reductive sediments area 09/25/2017

Table 2.

Metagenome sequencing statistics of each sample.

Sample ID DNA Conc (ng/uL) Volume (ul) DNA Content (ug) Total number of spots Total number of bases Q20 (Gbp) Q20 (%) Q30 (Gbp) Q30 (%) GC content (%) Assembled contigs N50 (bp) Max contig length (kb) Contigs ≥ 10-kb BioProject accession No. BioSample accession No. SRA accession No.
SW_1 38.00 40.00 1.52 268,780,986 80,634,295,800 73.29 96.39 69.65 91.60 36.04 1,534,405 1,413 144.236 3,757 PRJNA707313 SAMN18200485 SRR13892607
SW_2 9.60 226.00 2.17 211,498,327 63,449,498,100 55.74 95.63 52.57 90.17 47.57 2,949,723 841 751.279 2,490 PRJNA707313 SAMN18200486 SRR13892606
SW_3 8.04 257.00 2.07 209,581,242 62,874,372,600 58.72 96.85 55.84 92.58 40.84 4,431,492 825 1533 4,192 PRJNA707313 SAMN18200487 SRR13892595
SW_4 14.96 254.00 3.80 213,078,219 63,923,465,700 59.35 96.40 56.37 91.57 42.30 4,784,748 875 755.276 11,638 PRJNA707313 SAMN18200488 SRR13892591
RS_1 6.30 80.00 0.50 210,376,373 63,112,911,900 59.24 96.49 56.22 91.57 45.43 5,827,198 718 452.39 5,238 PRJNA707313 SAMN18200489 SRR13892590
RS_2 9.90 92.00 0.91 210,044,424 63,013,327,200 59.52 96.63 56.58 91.87 45.19 5,772,932 698 427.971 3,591 PRJNA707313 SAMN18200490 SRR13892589
RS_3 5.94 135.00 0.80 197,222,088 59,166,626,400 57.00 96.09 53.80 90.69 47.52 6,485,322 686 274.684 4,051 PRJNA707313 SAMN18200491 SRR13892588
RS_4 3.54 135.00 0.48 175,717,792 52,715,337,600 55.41 96.60 52.62 91.73 47.43 6,321,787 684 341.334 4,586 PRJNA707313 SAMN18200492 SRR13892587
RS_5 5.18 87.00 0.45 210,273,664 63,082,099,200 59.68 97.12 57.00 92.76 45.76 6,627,379 693 387.906 6,193 PRJNA707313 SAMN18200493 SRR13892586
RS_6 6.66 84.00 0.56 210,496,319 63,148,895,700 59.64 96.67 56.73 91.95 44.75 6,083,188 645 336.042 4,020 PRJNA707313 SAMN18200494 SRR13892585
RS_7 5.48 90.00 0.49 210,215,804 63,064,741,200 59.48 96.59 56.50 91.75 45.59 6,621,563 714 542.774 7,236 PRJNA707313 SAMN18200495 SRR13892605
RS_8 6.44 88.00 0.57 221,216,994 66,365,098,200 62.28 96.48 59.09 91.53 44.89 6,417,883 706 236.738 7,174 PRJNA707313 SAMN18200496 SRR13892604
RS_9 4.59 90.00 0.41 217,513,891 66,365,098,200 61.87 97.17 59.13 92.87 45.50 6,677,947 720 408.486 8,524 PRJNA707313 SAMN18200497 SRR13892603
RS_10 4.01 139.00 0.56 205,597,241 61,679,172,300 58.32 97.12 55.71 92.76 46.23 6,469,960 695 434.319 6,316 PRJNA707313 SAMN18200498 SRR13892602
RS_11 4.48 140.00 0.63 225,785,488 67,735,646,400 65.71 98.12 63.58 94.95 43.50 5,201,517 758 415.221 6,919 PRJNA707313 SAMN18200499 SRR13892601
RS_12 5.44 71.00 0.39 232,763,725 69,829,117,500 67.64 98.08 65.40 94.85 43.42 3,094,173 796 635.758 5,801 PRJNA707313 SAMN18200500 SRR13892600
RS_13 4.88 131.00 0.64 225,203,094 67,560,928,200 65.44 98.14 63.39 95.07 42.51 3,500,917 817 383.492 5,980 PRJNA707313 SAMN18200501 SRR13892599
RS_14 5.16 135.00 0.70 241,881,543 72,564,462,900 70.34 98.21 68.19 95.21 42.45 1,869,638 683 305.012 1,746 PRJNA707313 SAMN18200502 SRR13892598
RS_15 5.70 135.00 0.77 225,763,481 67,729,044,300 65.60 98.17 63.53 95.07 42.59 1,863,140 671 305.23 1,759 PRJNA707313 SAMN18200503 SRR13892597
RS_16 5.66 135.00 0.76 236,000,139 70,800,041,700 68.61 98.12 66.40 94.97 42.71 1,738,136 837 239.392 4,010 PRJNA707313 SAMN18200504 SRR13892596
RS_17 5.12 135.00 0.69 259,045,539 77,713,661,700 74.83 97.86 72.04 94.20 42.40 2,671,409 805 268.822 4,707 PRJNA707313 SAMN18200505 SRR13892594
RS_18 9.10 71.00 0.65 245,684,586 73,705,375,800 71.51 98.29 69.37 95.35 42.72 2,997,732 793 322.724 4,926 PRJNA707313 SAMN18200506 SRR13892593
RS_19 7.88 68.00 0.54 219,631,776 65,889,532,800 63.85 98.29 61.94 95.34 42.01 2,343,571 779 213.639 3,431 PRJNA707313 SAMN18200507 SRR13892592

Fig. 2.

Fig. 2

Phylogenetic diversity of 768 metagenome assembled genomes (MAGs) from cold seep in South China Sea (Supplementary Table 2) and reference genomes of Bacteria and Archaea available in RefSeq (Supplementary Table 3). The scale bar corresponds to 3.00 substitutions per amino acid position. The number of draft genomes in each node are provided. The branches with red dots have no cultured representatives.

Methods

Sampling

Samples were retrieved from a cold seep field in the northern SCS by the KEXUE research vessel during the cruise in Sep 2017 (Fig. 1 a and Table 1). The water closely above the invertebrate communities was collected by an in-situ water sampling cylinder equipped on FAXIAN Remotely Operated Vehicle (ROV) during the dive 164 and 165 (sample ID: SW_1 and SW_2, respectively). The cold seep fluid was collected at the gas plumes during the dive 166 (sample ID: SW_3), and the fluid under the invertebrate communities was collected during the dive 167 (sample ID: SW_4). About 15 L water of each sample was filtered through a 0.22μm polycarbonate membrane (Millipore, Bedford, MA, USA). The membranes were stored at −80 °C and used for DNA extraction. A sediment core was collected by ROV at reductive sediments area nearby the invertebrate communities during dive 157. A thin outer layer ( < 1 cm) of the push core was discarded to avoid contamination. The black reduced sediment core, 20 cm in length, was sliced into layers by every two centimetres with a pushcore equipment (sample ID: RS_1 ~ RS_10). Another sediment core was collected at the same site by a deep-sea light weighted monitorable and controllable long-coring system8, and the sample layers of 0~300 cm below the seafloor (cmbsf) was collected from the sediment core and sliced into 35-cm subsamples (sample ID: RS_11 ~ RS_19). All subsamples were stored at −80 °C until DNA extraction. Environmental data (CH4, H2S and SO42−) were detected in situ by a deep-sea laser Raman spectrometer mounted with the ROV in the previous report5,9.

DNA extraction

A schematic overview of workflow in this study was shown in Fig. 1b. The genomic DNA from 2.5 g of each sediment subsamples was extracted using the PowerSoil DNA Isolation Kit (QIAGEN). The genomic DNA from the 0.22μm filters was extracted using the PowerWater DNA Isolation Kit (QIAGEN). The DNA were examined by gel electrophoresis, and the concentration of DNA was measured using Qubit® dsDNA Assay Kit in Qubit® 2.0 Flurometer (Life Technologies, CA, USA). OD value is between 1.8~2.0, DNA contents above 0.4 μg are used to construct library (Table 2).

Metagenome sequencing

Metagenomic sequencing were performed at the Novogene (Tianjin, China) using the Illumina 2 × 150 PE protocols on an Illumina HiSeq X Ten platform. Preprocessing the Raw Data obtained from the sequencing platform using Readfq v8 (https://github.com/cjfields/readfq) was conducted to acquire the Clean Data for subsequent analysis. Clean Data of all 23 samples are available at NCBI Genbank (SRA) under the accession numbers SRR13892585~SRR13892607 (Table 2), and within the BioProject accession number PRJNA707313.

Genome binning

The initial de novo assembly was carried out using MEGAHIT v1.1.3 with default parameters10. Short genomic assemblies ( < 1,000 bp) that could have biased the subsequent analysis were first excluded. Genomes were then binned based on their tetranucleotide frequency, differential coverage, and GC content, as well as codon usage, using different binning tools, including MetaBAT 2, MaxBin 2.0 and CONCOCT implemented by MetaWRAP v1.2.1 pipeline (default parameters) (Supplementary Table 1)11–13. The binning results were refined using the MetaWRAP package (parameters: -c 60 -x 20)14 and all the produced bin sets were aggregated and dereplicated at 95% average nucleotide identity (ANI) using dRep v2.3.2 (parameters: -comp 60 -con 20 -sa 0.9)15. Taxonomic classification of each bin was determined by CheckM v1.0.3 and GTDB-Tk with default parameters (Supplementary Table 2)16,17. The bin quality assessment (completeness > 60% and contamination < 20%) of different binners was then performed by CheckM v1.0.3 (parameters: lineage_wf)17. Next, the selected bins for each sample were reassembled by using metaSPAdes implemented through the MetaWRAP pipeline14,18. The coding regions of the final MAGs were predicted with the the Prodigal v2.6.3 (metagenome mode -p meta)19. All the predicted genes were searched against the nr database and KEGG prokaryote database using diamond blastp (parameters: -e 1e-5–id 40)20,21. Data of all MAGs are available at NCBI Assembly under the accession numbers JAGLBO000000000~ JAGMFB000000000 (Supplementary Table 1).

Phylogenomic analysis

The 768 draft genomes and the 208 reference genome sequences accessed from NCBI GenBank (Supplementary Table 3) were combined to find orthologs for phylogenetic analysis by Orthofinder (default parameters)22. Each ortholog was aligned using MUSCLE v.3.8.31 (parameters:–maxiters 16)23, trimmed using trimAL v.1.2rev59 (parameters: -automated1)24 and manually assessed. Gene tree of each ortholog was constructed using FastTree v2.1.9 (parameters: -gamma -lg;)25. The final species tree was inferred based on 40,080 gene trees using STAG v1.0.0 (https://github.com/davidemms/STAG) and was viewed and annotated using FigTree v1.4.3 (http://tree.bio.ed.ac.uk/software/figtree/) (Fig. 2).

Data Records

This project has been deposited at DDBJ/ENA/GenBank under the BioProject accession no. PRJNA707313, with the Sequence Read Archive deposited under the accessions SRR13892585~SRR1389260726–48. Other data is available through figshare49, including the fasta files containing the contigs of all 768 MAG, the newick format of the phylogenetic tree.

Technical Validation

Potential contamination of samples was limited by following guidelines for analyses of microbiota communities50,51. Briefly, the samples were pre-treated in a sterile station in the lab of the Research Vessel KEXUE. DNA extractions took place within a dedicated laboratory space under a laminar flow hood using aseptic techniques (such as, surface sterilisation, DNA-OFF, use of sterile plasticware, and use of aerosol barrier pipette tips). Sample processing was completed within 2 days, using the same batch of PowerSoil DNA Isolation Kit for all sediment samples, and PowerWater DNA Isolation Kit for all water-filters samples. The filtered and trimmed Illumina reads were evaluated for their sequencing qualities using fastp v0.20.1 (https://github.com/OpenGene/fastp) with default parameters52. In all samples, the Q score for the reads of each sample was calculated and showed that more than 90% of reads scored Q30 (Table 2), indicating that most of the reads were constructed with low error rates. Metagenome data have been assembled and refined into MAGs using the automated quality control steps and assembly procedures described in the manuscript. To ensure the assembly quality of the contigs, several kmers (21,29,39,59,79,99,119,141) were selected in the assembly procedures of MEGAHIT. As for binning, more strict standards were selected, and the sequence after binning was re-assembled to ensure the best result.

Supplementary information

Supplementary Table 1 (149.9KB, xlsx)
Supplementary Table 2 (48.2KB, xlsx)
Supplementary Table 3 (22.3KB, xlsx)

Acknowledgements

We acknowledge the support of the Research Vessel KEXUE of the National Major Science and Technology Infrastructure from the Chinese Academy of Sciences (CAS), and Canter for Ocean Mega-Science, CAS. We are especially grateful to the pilots and crew of FAXIAN ROV. We also thank all the laboratory members for their technical advice and helpful discussions. This work was funded supported by the Marine S&T Fund of Shandong Province for Pilot National Laboratory for Marine Science and Technology (Qingdao) (2022QNLM030004-3), the National Natural Science Foundation of China (42030407 and 42076091) and the Senior User Project of RV KEXUE (KEXUE2021GH01 and KEXUE2019GZ06).

Author contributions

M.W., H.Z. and C.L. designed the study. M.W., H.Z., H.C., L.C., C.L. and Z.Z. collected the samples. M.W., H.Z., H.C., H.W. and L.Z. performed the analysis. H.Z. and M.W. wrote the paper and prepared the figure and tables. All co-authors commented on the final manuscript.

Code availability

The above methods indicate the programs used for analysis within the relevant sections. The code used to analyse individual data packages is deposited at https://github.com/zhcosa/MAGs-from-cold-seep.

Competing interests

The authors declare no competing interests.

Footnotes

Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

These authors contributed equally: Huan Zhang, Minxiao Wang.

Supplementary information

The online version contains supplementary material available at 10.1038/s41597-022-01586-x.

References

  • 1.Ceramicola, S., Dupré, S., Somoza, L. & Woodside, J. in Submarine Geomorphology (eds Aaron Micallef, Sebastian Krastel, & Alessandra Savini) 367-387 (Springer International Publishing, 2018).
  • 2.Ruff SE, et al. Global dispersion and local diversification of the methane seep microbiome. Proc. Natl. Acad. Sci. USA. 2015;112:4015–4020. doi: 10.1073/pnas.1421865112. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Feng D, et al. Cold seep systems in the South China Sea: An overview. J. Asian Earth Sci. 2018;168:3–16. doi: 10.1016/j.jseaes.2018.09.021. [DOI] [Google Scholar]
  • 4.Zhang X, et al. In situ Raman detection of gas hydrates exposed on the seafloor of the South China Sea. Geochem. Geophy. Geosy. 2017;18:3700–3713. doi: 10.1002/2017GC006987. [DOI] [Google Scholar]
  • 5.Zhang X, et al. Development of a new deep-sea hybrid Raman insertion probe and its application to the geochemistry of hydrothermal vent and cold seep fluids. Deep-Sea Res. Pt. I. 2017;123:1–12. doi: 10.1016/j.dsr.2017.02.005. [DOI] [Google Scholar]
  • 6.Cao L, et al. In situ detection of the fine scale heterogeneity of active cold seep environment of the Formosa Ridge, the South China Sea. Journal of Marine Systems. 2021;218:103530. doi: 10.1016/j.jmarsys.2021.103530. [DOI] [Google Scholar]
  • 7.Du Z, Zhang X, Xue B, Luan Z, Yan J. The applications of the in situ laser spectroscopy to the deep-sea cold seep and hydrothermal vent system. Solid Earth Sciences. 2020;5:153–168. doi: 10.1016/j.sesci.2020.06.001. [DOI] [Google Scholar]
  • 8.Wang B, et al. A novel monitorable and controlable long-coring system with maximum operating depth 6000 m. Marine Sciences. 2018;42:25–31. [Google Scholar]
  • 9.Du Z, et al. In situ Raman quantitative detection of the cold seep vents and fluids in the chemosynthetic communities in the South China Sea. Solid Earth Sciences. 2018;5:153–168. doi: 10.1016/j.sesci.2020.06.001. [DOI] [Google Scholar]
  • 10.Li D, Liu CM, Luo R, Sadakane K, Lam TW. MEGAHIT: an ultra-fast single-node solution for large and complex metagenomics assembly via succinct de Bruijn graph. Bioinformatics. 2015;31:1674–1676. doi: 10.1093/bioinformatics/btv033. [DOI] [PubMed] [Google Scholar]
  • 11.Kang DD, et al. MetaBAT 2: an adaptive binning algorithm for robust and efficient genome reconstruction from metagenome assemblies. PeerJ. 2019;7:e7359. doi: 10.7717/peerj.7359. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 12.Nissen JN, et al. Improved metagenome binning and assembly using deep variational autoencoders. Nat. Biotechnol. 2021;39:555–560. doi: 10.1038/s41587-020-00777-4. [DOI] [PubMed] [Google Scholar]
  • 13.Wu YW, Simmons BA, Singer SW. MaxBin 2.0: an automated binning algorithm to recover genomes from multiple metagenomic datasets. Bioinformatics. 2016;32:605–607. doi: 10.1093/bioinformatics/btv638. [DOI] [PubMed] [Google Scholar]
  • 14.Uritskiy GV, DiRuggiero J, Taylor J. MetaWRAP-a flexible pipeline for genome-resolved metagenomic data analysis. Microbiome. 2018;6:158. doi: 10.1186/s40168-018-0541-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15.Olm MR, Brown CT, Brooks B, Banfield JF. dRep: a tool for fast and accurate genomic comparisons that enables improved genome recovery from metagenomes through de-replication. ISME J. 2017;11:2864–2868. doi: 10.1038/ismej.2017.126. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16.Chaumeil PA, Mussig AJ, Hugenholtz P, Parks DH. GTDB-Tk: a toolkit to classify genomes with the Genome Taxonomy Database. Bioinformatics. 2019;36:1925–1927. doi: 10.1093/bioinformatics/btz848. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Parks DH, Imelfort M, Skennerton CT, Hugenholtz P, Tyson GW. CheckM: assessing the quality of microbial genomes recovered from isolates, single cells, and metagenomes. Genome Res. 2015;25:1043–1055. doi: 10.1101/gr.186072.114. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Nurk S, Meleshko D, Korobeynikov A, Pevzner PA. metaSPAdes: a new versatile metagenomic assembler. Genome Res. 2017;27:824–834. doi: 10.1101/gr.213959.116. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Hyatt D, et al. Prodigal: prokaryotic gene recognition and translation initiation site identification. BMC Bioinformatics. 2010;11:119. doi: 10.1186/1471-2105-11-119. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20.Kanehisa M, Goto S. KEGG: kyoto encyclopedia of genes and genomes. Nucleic Acids Res. 2000;28:27–30. doi: 10.1093/nar/28.1.27. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Buchfink B, Xie C, Huson DH. Fast and sensitive protein alignment using DIAMOND. Nat. Methods. 2015;12:59–60. doi: 10.1038/nmeth.3176. [DOI] [PubMed] [Google Scholar]
  • 22.Emms DM, Kelly S. OrthoFinder: phylogenetic orthology inference for comparative genomics. Genome Biol. 2019;20:238. doi: 10.1186/s13059-019-1832-y. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 23.Edgar RC. MUSCLE: multiple sequence alignment with high accuracy and high throughput. Nucleic Acids Res. 2004;32:1792–1797. doi: 10.1093/nar/gkh340. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 24.Capella-Gutierrez S, Silla-Martinez JM, Gabaldon T. trimAl: a tool for automated alignment trimming in large-scale phylogenetic analyses. Bioinformatics. 2009;25:1972–1973. doi: 10.1093/bioinformatics/btp348. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25.Price MN, Dehal PS, Arkin AP. FastTree 2–approximately maximum-likelihood trees for large alignments. PLoS One. 2010;5:e9490. doi: 10.1371/journal.pone.0009490. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.2022. NCBI Sequence Read Archive. SRR13892585
  • 27.2022. NCBI Sequence Read Archive. SRR13892586
  • 28.2022. NCBI Sequence Read Archive. SRR13892587
  • 29.2021. NCBI Sequence Read Archive. SRR13892588
  • 30.2021. NCBI Sequence Read Archive. SRR13892589
  • 31.2021. NCBI Sequence Read Archive. SRR13892590
  • 32.2021. NCBI Sequence Read Archive. SRR13892591
  • 33.2021. NCBI Sequence Read Archive. SRR13892592
  • 34.2021. NCBI Sequence Read Archive. SRR13892593
  • 35.2021. NCBI Sequence Read Archive. SRR13892594
  • 36.2021. NCBI Sequence Read Archive. SRR13892595
  • 37.2021. NCBI Sequence Read Archive. URL="https://identifiers.org/ncbi/insdc.sra:SRR13892596"https://identifiers.org/ncbi/insdc.sra:SRR13892596
  • 38.2021. NCBI Sequence Read Archive. SRR13892597
  • 39.2021. NCBI Sequence Read Archive. SRR13892598
  • 40.2021. NCBI Sequence Read Archive. SRR13892599
  • 41.2021. NCBI Sequence Read Archive. SRR13892600
  • 42.2021. NCBI Sequence Read Archive. SRR13892601
  • 43.2021. NCBI Sequence Read Archive. SRR13892602
  • 44.2021. NCBI Sequence Read Archive. SRR13892603
  • 45.2021. NCBI Sequence Read Archive. SRR13892604
  • 46.2021. NCBI Sequence Read Archive. SRR13892605
  • 47.2021. NCBI Sequence Read Archive. SRR13892606
  • 48.2021. NCBI Sequence Read Archive. SRR13892607
  • 49.Zhang H, 2022. Metagenome sequencing and 768 microbial genomes from cold seep in South China Sea. figshare. [DOI] [PMC free article] [PubMed]
  • 50.Eisenhofer R, et al. Contamination in Low Microbial Biomass Microbiome Studies: Issues and Recommendations. Trends Microbiol. 2019;27:105–117. doi: 10.1016/j.tim.2018.11.003. [DOI] [PubMed] [Google Scholar]
  • 51.Salter SJ, et al. Reagent and laboratory contamination can critically impact sequence-based microbiome analyses. BMC Biol. 2014;12:87. doi: 10.1186/s12915-014-0087-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 52.Chen S, Zhou Y, Chen Y, Gu J. fastp: an ultra-fast all-in-one FASTQ preprocessor. Bioinformatics. 2018;34:i884–i890. doi: 10.1093/bioinformatics/bty560. [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Citations

  1. 2022. NCBI Sequence Read Archive. SRR13892585
  2. 2022. NCBI Sequence Read Archive. SRR13892586
  3. 2022. NCBI Sequence Read Archive. SRR13892587
  4. 2021. NCBI Sequence Read Archive. SRR13892588
  5. 2021. NCBI Sequence Read Archive. SRR13892589
  6. 2021. NCBI Sequence Read Archive. SRR13892590
  7. 2021. NCBI Sequence Read Archive. SRR13892591
  8. 2021. NCBI Sequence Read Archive. SRR13892592
  9. 2021. NCBI Sequence Read Archive. SRR13892593
  10. 2021. NCBI Sequence Read Archive. SRR13892594
  11. 2021. NCBI Sequence Read Archive. SRR13892595
  12. 2021. NCBI Sequence Read Archive. URL="https://identifiers.org/ncbi/insdc.sra:SRR13892596"https://identifiers.org/ncbi/insdc.sra:SRR13892596
  13. 2021. NCBI Sequence Read Archive. SRR13892597
  14. 2021. NCBI Sequence Read Archive. SRR13892598
  15. 2021. NCBI Sequence Read Archive. SRR13892599
  16. 2021. NCBI Sequence Read Archive. SRR13892600
  17. 2021. NCBI Sequence Read Archive. SRR13892601
  18. 2021. NCBI Sequence Read Archive. SRR13892602
  19. 2021. NCBI Sequence Read Archive. SRR13892603
  20. 2021. NCBI Sequence Read Archive. SRR13892604
  21. 2021. NCBI Sequence Read Archive. SRR13892605
  22. 2021. NCBI Sequence Read Archive. SRR13892606
  23. 2021. NCBI Sequence Read Archive. SRR13892607
  24. Zhang H, 2022. Metagenome sequencing and 768 microbial genomes from cold seep in South China Sea. figshare. [DOI] [PMC free article] [PubMed]

Supplementary Materials

Supplementary Table 1 (149.9KB, xlsx)
Supplementary Table 2 (48.2KB, xlsx)
Supplementary Table 3 (22.3KB, xlsx)

Data Availability Statement

The above methods indicate the programs used for analysis within the relevant sections. The code used to analyse individual data packages is deposited at https://github.com/zhcosa/MAGs-from-cold-seep.


Articles from Scientific Data are provided here courtesy of Nature Publishing Group

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