Literature DB >> 26941158

Draft Genome Sequence of a Chlorinated-Ethene Degrader, Cupriavidus necator Strain PHE3-6 (NBRC 110655).

Kenta Yonezuka1, Jun Shimodaira2, Michiro Tabata1, Shun Nagase1, Daisuke Kasai1, Akira Hosoyama2, Atsushi Yamazoe2, Nobuyuki Fujita2, Masao Fukuda3.   

Abstract

Cupriavidus necator strain PHE3-6 grows on phenol as a sole carbon source and cometabolizes cis- and trans-dichloroethenes and trichloroethene. Here, we report the draft genome sequence of PHE3-6, which provides insights into the degradation system of phenol and chlorinated ethenes.
Copyright © 2016 Yonezuka et al.

Entities:  

Year:  2016        PMID: 26941158      PMCID: PMC4777769          DOI: 10.1128/genomeA.01743-15

Source DB:  PubMed          Journal:  Genome Announc


GENOME ANNOUNCEMENT

Cupriavidus necator strain PHE3-6 (NBRC 110655) was isolated from soil in Niigata, Japan. It utilized phenol as a sole carbon source and cometabolized chlorinated ethenes, such as trichloroethene (TCE), cis-dichloroethene, and trans-dichloroethene (tDCE). Chlorinated ethenes are known as environmental pollutants in soil and groundwater. TCE degradation by phenol degraders has been reported (1–6). However, tDCE degradation by phenol degraders has not been reported. Therefore, the degradation of chlorinated ethenes including tDCE in PHE3-6, is of importance for tDCE degradation is a novel activity among phenol degraders. To obtain insights into the degradation system of phenol and chlorinated ethenes in PHE3-6, the whole-genome shotgun sequence was performed. The genomic DNA of PHE3-6 was sequenced by using paired-end sequencing with an Illumina MiSeq platform (Illumina, San Diego, CA, United States). The 4,892,926 reads obtained were assembled by Newbler version 2.6. The contigs were analyzed using the NCBI Prokaryotic Genome Annotation Pipeline (PGAP) (http://www.ncbi.nlm.nih.gov/genome/annotation_prok) to annotate protein-coding, rRNA, and tRNA genes. The draft genome of PHE3-6 has a total size of 7,267,813 bp with 66.33% G+C content and consists of 118 contigs ranging from 544 to 293,011 bp with an average coverage of 94× and an N50 length of 125,732 bp. The annotation revealed 6,722 protein-coding sequences and 59 RNA genes. The 16S rRNA gene sequence of PHE3-6 has 98.56% and 100% identities with those of type strains Cupriavidus taiwanensis LMG 19424T (CU633749) and C. necator N-1T (CP002878), respectively. The analysis of average nucleotide identity (ANI) of PHE3-6 using the ANI calculator (http://enve-omics.ce.gatech.edu/ani) showed 88.64% and 99.49% ANI values with C. taiwanensis LMG 19424T (CU633749 and CU633750) and C. necator N-1T (AM260479 and AM260480), respectively. Thus, the phylogenetic affiliation of strain PHE3-6 was closely related to C. necator N-1T. The results of genome sequencing indicated that PHE3-6 has a couple of gene clusters for phenol degradation, both of which contain orthologs of the multicomponent phenol hydroxylase subunit genes dmpKLMNOP in Pseudomonas putida CF600 (7). The dmpKLMNOP orthologs, which are located in the different contigs, showed amino acid sequence identities of 50.8% to 68.7% between their individual subunits and 40.7% to 65.6% with the corresponding subunits of CF600. The dmpN gene is known to encode the largest subunit of multicomponent phenol hydroxylase and contain catalytic domain. One of the dmpN orthologs showed an amino acid sequence identity of 99.6% with that of a phenol degrader, C. necator N-1T. The other dmpN ortholog showed an amino acid sequence identity of 87.8% with that of a TCE-degrading phenol degrader, Burkholderia kururiensis KP23T.

Nucleotide sequence accession numbers.

The draft sequence of PHE3-6 has been deposited in the DDBJ/EMBL/GenBank databases under the accession number LMVF00000000. The version used here is the first version, LMVF01000000.
  7 in total

1.  Burkholderia kururiensis sp. nov., a trichloroethylene (TCE)-degrading bacterium isolated from an aquifer polluted with TCE.

Authors:  H Zhang; S Hanada; T Shigematsu; K Shibuya; Y Kamagata; T Kanagawa; R Kurane
Journal:  Int J Syst Evol Microbiol       Date:  2000-03       Impact factor: 2.747

2.  Trichloroethylene degradation by Ralstonia sp. KN1-10A constitutively expressing phenol hydroxylase: transformation products, NADH limitation, and product toxicity.

Authors:  H Ishida; K Nakamura
Journal:  J Biosci Bioeng       Date:  2000       Impact factor: 2.894

3.  Chlorinated aliphatic hydrocarbon-induced degradation of trichloroethylene in Wautersia numadzuensis sp. nov.

Authors:  Chizuko Kageyama; Toshiya Ohta; Kazuyo Hiraoka; Morimasa Suzuki; Tetsuji Okamoto; Kazuo Ohishi
Journal:  Arch Microbiol       Date:  2004-11-27       Impact factor: 2.552

4.  Characterization of phenol and trichloroethene degradation by the rhizobium Ralstonia taiwanensis.

Authors:  Wen-Ming Chen; Jo-Shu Chang; Chih-Hui Wu; Shu-Chen Chang
Journal:  Res Microbiol       Date:  2004-10       Impact factor: 3.992

5.  Trichloroethylene degradation by two independent aromatic-degrading pathways in Alcaligenes eutrophus JMP134.

Authors:  A R Harker; Y Kim
Journal:  Appl Environ Microbiol       Date:  1990-04       Impact factor: 4.792

Review 6.  Genetics and biochemistry of phenol degradation by Pseudomonas sp. CF600.

Authors:  J Powlowski; V Shingler
Journal:  Biodegradation       Date:  1994-12       Impact factor: 3.909

7.  Biodegradation of trichloroethylene and involvement of an aromatic biodegradative pathway.

Authors:  M J Nelson; S O Montgomery; W R Mahaffey; P H Pritchard
Journal:  Appl Environ Microbiol       Date:  1987-05       Impact factor: 4.792

  7 in total

北京卡尤迪生物科技股份有限公司 © 2022-2023.