Skip to main content
NCBI home page
Genome Announcements logoLink to Genome Announcements
. 2014 Jan 16;2(1):e01073-13. doi: 10.1128/genomeA.01073-13

Draft Genome Sequences of Type Strain Sediminibacterium salmoneum NJ-44 and Sediminibacterium sp. Strain C3, a Novel Strain Isolated from Activated Sludge

Joaquín M Ayarza a, Eva L M Figuerola a, Leonardo Erijman a,b,✉
PMCID: PMC3894271  PMID: 24435857

Abstract

The genus Sediminibacterium comprises species present in diverse natural and engineered environments. Here, we report for the first time the genome sequences of the type strain Sediminibacterium salmoneum NJ-44 (NBRC 103935) and Sediminibacterium sp. strain C3 (BNM541), isolated from activated sludge, a valuable model for the study of substrate-dependent autoaggregation.

GENOME ANNOUNCEMENT

The genus Sediminibacterium is phylogenetically related to Terrimonas and Niabella, within the phylum Bacteroidetes. It was first described in 2008 by Qu and Yuan (1), who isolated the type strain Sediminibacterium salmoneum NJ-44 from a eutrophic reservoir in Beijing, China. Culture-independent methods allowed the detection of members of this genus in a variety of natural and engineered habitats (2–7).

Sediminibacterium sp. strain C3 was isolated from activated sludge treating wastewater from a petroleum refinery and deposited in the National Bank of Microorganisms (WDCM938) of the Facultad de Agronomia, Universidad de Buenos Aires, Argentina. Planktonic outgrowth of Sediminibacterium sp. C3 occurred after activated sludge deflocculated in response to chemical and thermal shocks. Remarkably, the isolate also showed substrate-dependent autoaggregation in pure culture (J. M. Ayarza, M. A. Mazzella, and L. Erijman, submitted for publication).

The 1,484-nucleotide-long amplicon of the 16S rRNA gene from isolate C3 has 99% similarity to the sequence of S. salmoneum. This, and the fact that the C3 strain appears to share many phenotypic traits with S. salmoneum NJ-44T, prompted us to sequence the genomes of both strains. S. salmoneum NJ-44T was obtained from the Biological Resource Center (NBRC) of the National Institute of Technology and Evaluation, Japan (NITE).

Genomic DNA was isolated using the Wizard Genomic DNA purification kit (Promega) and sequenced using the 454 GS FLX Titanium system (Roche Diagnostics, Branford, CT) with 8-kb paired-end libraries at the Instituto de Agrobiotecnología Rosario (INDEAR), Argentina. Whole-genome sequencing of Sediminibacterium sp. C3 produced a total of 162,749 reads with an average read length of 355.61 bp. De novo assembly was done using Celera Assembler version 6.1, yielding a total consensus of 3,219,312 bp (39.20% G+C content) distributed in one main scaffold of 3,216,888 bp and three minor scaffolds of 1,479, 489, and 456 bp in length. S. salmoneum NJ-44T sequencing generated a total of 277,742 reads with an average read length of 407.22 bp, which were assembled using 454 Newbler version 2.8, resulting in one scaffold of 3,246,830 bp (38.58% G+C content).

The genome sequences were annotated automatically using the Department of Energy Joint Genome Institute (DOE-JGI) Microbial Annotation Pipeline (8) through assembled sequence data submissions in the Integrated Microbial Genomes Expert Review system (IMG-ER). In S. salmoneum NJ-44T, 3,018 genes were predicted, with 2,969 protein-encoding genes and 49 RNA genes. Of the 3,011 genes predicted in Sediminibacterium sp. C3, 2,958 were protein-encoding genes and 53 were RNA genes. A total of 2,615 protein-encoding genes were conserved in both strains.

Sediminibacterium sp. C3 shows an average nucleotide identity (ANI) (9) with the S. salmoneum type strain of only 90.04%. In silico DNA-DNA hybridization (DDH) estimated using the Genome-to-Genome Distance Calculator (GGDC 2.0) Web server (10) was 37.20% ± 2.48%, which has an associated probability of 0.97% that two strains belong to the same species. Therefore, both analyses suggest that C3 represents a novel species of the genus Sediminibacterium.

Nucleotide sequence accession numbers.

The whole-genome shotgun projects for Sediminibacterium sp. C3 and S. salmoneum NJ-44T were deposited at DDBJ/EMBL/GenBank under accession no. AXUM00000000 and AXZP00000000, respectively.

ACKNOWLEDGMENTS

This work was funded by grants from FONCyT (PICT 2008 no. 1950 and PICT 2012 no. 1877) and UBACyT (cod. 20020110100078).

Footnotes

Citation Ayarza JM, Figuerola ELM, Erijman L. 2014. Draft genome sequences of type strain Sediminibacterium salmoneum NJ-44 and Sediminibacterium sp. strain C3, a novel strain isolated from activated sludge. Genome Announc. 2(1):e01073-13. doi:10.1128/genomeA.01073-13.

REFERENCES

  • 1. Qu J-H, Yuan H-L. 2008. Sediminibacterium salmoneum gen. nov., sp. nov., a member of the phylum Bacteroidetes isolated from sediment of a eutrophic reservoir. Int. J. Syst. Evol. Microbiol. 58:2191–2194. 10.1099/ijs.0.65514-0 [DOI] [PubMed] [Google Scholar]
  • 2. Besemer K, Peter H, Logue JB, Langenheder S, Lindström ES, Tranvik LJ, Battin TJ. 2012. Unraveling assembly of stream biofilm communities. ISME J. 6:1459–1468. 10.1038/ismej.2011.205 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3. Kahlisch L, Henne K, Gröbe L, Brettar I, Höfle MG. 2012. Assessing the viability of bacterial species in drinking water by combined cellular and molecular analyses. Microb. Ecol. 63:383–397. 10.1007/s00248-011-9918-4 [DOI] [PubMed] [Google Scholar]
  • 4. Torrentó C, Urmeneta J, Otero N, Soler A, Viñas M, Cama J. 2011. Enhanced denitrification in groundwater and sediments from a nitrate-contaminated aquifer after addition of pyrite. Chem. Geol. 287:90–101. 10.1016/j.chemgeo.2011.06.002 [DOI] [Google Scholar]
  • 5. Khemkhao M, Nuntakumjorn B, Techkarnjanaruk S, Phalakornkule C. 2011. Effect of chitosan on UASB treating POME during a transition from mesophilic to thermophilic conditions. Bioresour. Technol. 102:4674–4681. 10.1016/j.biortech.2011.01.032 [DOI] [PubMed] [Google Scholar]
  • 6. Singleton DR, Richardson SD, Aitken MD. 2011. Pyrosequence analysis of bacterial communities in aerobic bioreactors treating polycyclic aromatic hydrocarbon-contaminated soil. Biodegradation 22:1061–1073. 10.1007/s10532-011-9463-3 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7. Wang H, Hu C, Hu X, Yang M, Qu J. 2012. Effects of disinfectant and biofilm on the corrosion of cast iron pipes in a reclaimed water distribution system. Water Res. 46:1070–1078. 10.1016/j.watres.2011.12.001 [DOI] [PubMed] [Google Scholar]
  • 8. Mavromatis K, Ivanova NN, Chen IA, Szeto E, Victor M, Kyrpides NC. 2009. The DOE-JGI standard operating procedure for the annotations of microbial genomes. Stand. Genomic Sci. 1:63–67. 10.4056/sigs.632 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9. Goris J, Konstantinidis KT, Klappenbach JA, Coenye T, Vandamme P, Tiedje JM. 2007. DNA-DNA hybridization values and their relationship to whole-genome sequence similarities. Int. J. Syst. Evol. Microbiol. 57:81–91. 10.1099/ijs.0.64483-0 [DOI] [PubMed] [Google Scholar]
  • 10. Meier-Kolthoff JP, Auch AF, Klenk H-P, Göker M. 2013. Genome sequence-based species delimitation with confidence intervals and improved distance functions. BMC Bioinformatics 14:60. 10.1186/1471-2105-14-60 [DOI] [PMC free article] [PubMed] [Google Scholar]

Articles from Genome Announcements are provided here courtesy of American Society for Microbiology (ASM)

RESOURCES