Skip to main content
Journal of Bacteriology logoLink to Journal of Bacteriology
. 2012 Oct;194(20):5701–5702. doi: 10.1128/JB.01296-12

Genome Sequences of Pseudomonas luteola XLDN4-9 and Pseudomonas stutzeri XLDN-R, Two Efficient Carbazole-Degrading Strains

Xiaorui Liu 1, Zhonghui Gai 1, Fei Tao 1, Hao Yu 1, Hongzhi Tang 1, Ping Xu 1,
PMCID: PMC3458655  PMID: 23012282

Abstract

Pseudomonas luteola XLDN4-9 and Pseudomonas stutzeri XLDN-R are two efficient carbazole-degrading pseudomonad strains. Here we present 4.63- and 4.70-Mb assemblies of their genomes. Their annotated key genes for carbazole catabolism are similar, which may provide further insights into the molecular mechanism of carbazole degradation in Pseudomonas.

GENOME ANNOUNCEMENT

Carbazole and its derivatives in N-heterocyclic compounds have a dioxin-like structure, and some of them are toxic and mutagenic (5). They are most common in creosote, crude oil, and shale oil and are environmental pollutants and recalcitrant molecules, as well as raw materials for dyes, reagents, explosives, insecticides, lubricants, etc. (11). Microbial degradation is an effective way to remove such pollutants from the environment (1, 13). The genus Pseudomonas is a diverse group and has the ability to degrade various aromatic compounds, including carbazole (2, 12). Moreover, some strains of this genus have drawn much attention because of their denitrification and nitrogen fixation abilities (6).

We have previously isolated Pseudomonas luteola XLDN4-9 (CCTCC M 205094) and Pseudomonas stutzeri XLDN-R (CCTCC AB 2012149) from soil samples on the basis of their abilities to utilize carbazole as their sole source of carbon and nitrogen. They can degrade 99 and 97% of the carbazole present (500 mg/liter) in 16 and 13 h, respectively. It was reported that the carbazole degradation ability of strain XLDN4-9 could be enhanced in the presence of a nonaqueous-phase liquid (8). The derivatives of carbazole were also biodegradable by this strain (7).

The genomes of strains XLDN4-9 and XLDN-R were sequenced using the Illumina HiSeq 2000 system. The reads were assembled into 232 and 167 contigs, respectively, using Velvet 1.2.03. The largest contigs of strains XLDN4-9 and XLDN-R are 265,571 and 235,018 bp. The draft genome sequence of strain XLDN4-9 consists of 4,627,073 bases with a G+C content of 54.2%, while the draft genome sequence of strain XLDN-R contains 4,695,416 bases with a G+C content of 63.9%, which is in accordance with other P. stutzeri strains (6, 14, 15). There were 45 and 58 predicted tRNAs, 4,454 and 4,247 coding sequences, and 444 and 496 subsystems in strains XLDN4-9 and XLDN-R, respectively.

As expected, the genomes of strains XLDN4-9 and XLDN-R encode a diverse array of related proteins with predicted roles in the metabolism of aromatic compounds, such as biphenyl, benzoate, and chloroaromatic compounds. With respect to carbazole degradation, the car genes in strains XLDN4-9 and XLDN-R were found to be clustered in an arrangement similar to that of the car cluster in Pseudomonas sp. strain CA10 (10), which is different from that of Sphingobium yanoikuyae XLDN2-5 (3, 4).

The genomes of strains XLDN4-9 and XLDN-R contain 59 and 69 contigs involved in the degradation of aromatic compounds and multiple predicted pathways of protection against environmental stress. In our previous study, we found that carotenoids produced by strain XLDN2-5 might play a positive role in the degradation of heterocycles (9); however, the carotenoid biosynthetic pathway genes have not been found in these two strains. The above information may be helpful in elucidating the evolution and horizontal transfer of genes for carbazole degradation in Pseudomonas.

Nucleotide sequence accession numbers.

These whole-genome shotgun projects have been deposited at DDBJ/EMBL/GenBank under accession numbers ALAT00000000 and AKYE00000000 for strains XLDN4-9 and XLDN-R, respectively. The versions described in this paper are the first versions, ALAT01000000 and AKYE01000000.

ACKNOWLEDGMENTS

We acknowledge Huajun Zheng and his colleagues for genome sequencing performed at the Chinese National Human Genome Center at Shanghai.

This work was supported in part by the Chinese National Natural Science Foundation (20977061 and 30821005).

REFERENCES

  • 1. Benedik MJ, Gibbs PR, Riddle RR, Willson RC. 1998. Microbial denitrogenation of fossil fuels. Trends Biotechnol. 16:390–395 [DOI] [PubMed] [Google Scholar]
  • 2. Cladera AM, Bennasar A, Barceló M, Lalucat J, García-Valdés E. 2004. Comparative genetic diversity of Pseudomonas stutzeri genomovars, clonal structure, and phylogeny of the species. J. Bacteriol. 186:5239–5248 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3. Gai Z, et al. 2010. The genes coding for the conversion of carbazole to catechol are flanked by IS6100 elements in Sphingomonas sp. strain XLDN2-5. PLoS One 5:e10018 doi:10.1371/journal.pone.0010018 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4. Gai Z, et al. 2011. Genome sequence of Sphingobium yanoikuyae XLDN2-5, an efficient carbazole-degrading strain. J. Bacteriol. 193:6404–6405 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5. Jha AM, Bharti MK. 2002. Mutagenic profiles of carbazole in the male germ cells of Swiss albino mice. Mutat. Res. 500:97–101 [DOI] [PubMed] [Google Scholar]
  • 6. Lalucat J, Bennasar A, Bosch R, García-Valdés E, Palleroni NJ. 2006. Biology of Pseudomonas stutzeri. Microbiol. Mol. Biol. Rev. 70:510–547 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7. Li L, et al. 2006. Degradation of carbazole and its derivatives by a Pseudomonas sp. Appl. Microbiol. Biotechnol. 73:941–948 [DOI] [PubMed] [Google Scholar]
  • 8. Li L, Xu P, Blankespoor HD. 2004. Degradation of carbazole in the presence of non-aqueous phase liquids by Pseudomonas sp. Biotechnol. Lett. 26:581–584 [DOI] [PubMed] [Google Scholar]
  • 9. Liu X, Gai Z, Tao F, Tang H, Xu P. 2012. Carotenoids play a positive role in the degradation of heterocycles by Sphingobium yanoikuyae. PLoS One 7:e39522 doi:10.1371/journal.pone.0039522 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 10. Nojiri H, et al. 2001. Genetic characterization and evolutionary implications of a car gene cluster in the carbazole degrader Pseudomonas sp. strain CA10. J. Bacteriol. 183:3663–3679 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11. Ouchiyama N, Zhang Y, Omori T, Kodama T. 1993. Biodegradation of carbazole by Pseudomonas spp. CA06 and CA10. Biosci. Biotechnol. Biochem. 57:455–460 [Google Scholar]
  • 12. Spiers AJ, Buckling A, Rainey PB. 2000. The causes of Pseudomonas diversity. Microbiology 146:2345–2350 [DOI] [PubMed] [Google Scholar]
  • 13. Xu P, Yu B, Li FL, Cai XF, Ma CQ. 2006. Microbial degradation of sulfur, nitrogen and oxygen heterocycles. Trends Microbiol. 14:398–405 [DOI] [PubMed] [Google Scholar]
  • 14. Yan Y, et al. 2008. Nitrogen fixation island and rhizosphere competence traits in the genome of root-associated Pseudomonas stutzeri A1501. Proc. Natl. Acad. Sci. U. S. A. 105:7564–7569 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15. Yu H, et al. 2011. Complete genome sequence of the nitrogen-fixing and rhizosphere-associated bacterium Pseudomonas stutzeri strain DSM4166. J. Bacteriol. 193:3422–3423 [DOI] [PMC free article] [PubMed] [Google Scholar]

Articles from Journal of Bacteriology are provided here courtesy of American Society for Microbiology (ASM)

RESOURCES