Abstract
An actinobacterial strain, designated SO9-6, was isolated from a copper iron sulfide mineral. The organism is Gram-positive, facultatively anaerobic, and coccoid. Chemotaxonomic and phylogenetic properties were consistent with its classification in the genus Kocuria. Here, we report the first draft genome sequence of Kocuria marina SO9-6 under accession JROM00000000 (http://www.ncbi.nlm.nih.gov/nuccore/725823918), which provides insights for heavy metal bioremediation and production of compounds of biotechnological interest.
Keywords: Kocuria marina SO9-6, Genome, Copper mine, Aromatic compound degradation, Heavy metal tolerance
Specifications | |
---|---|
Organism | Kocuria marina |
Strain | SO9-6 |
Sequencer or array type | Illumina HiSeq 2500 |
Data format | Processed |
Experimental factors | Laboratory cultured strain |
Experimental features | Very brief experimental description |
Consent | High-quality draft genome of the actinobacterium Kocuria marina SO9-6 |
Sample source location | Brazilian Collection of Environmental and Industrial Microorganisms (CBMAI), accession number 1703 |
1. Direct link to deposited data
The draft genome sequence of Kocuria marina S09-6 has been deposited at DDBJ/EMBL/GenBank under the accession JROM00000000 (http://www.ncbi.nlm.nih.gov/nuccore/725823918), and this paper describes its first version.
2. Experimental design, materials and methods
The genus Kocuria, which belongs to the Micrococcaceae family, was first proposed by Stackebrandt et al. [1]. These bacteria were formerly classified in the genus Micrococcus, but were subsequently separated from it based on phylogenetic and chemotaxonomic analyses. The members of this genus are coccoid, Gram-positive, non-encapsulated, and aerobic, but Kocuria kristinae and Kocuria marina are exceptions, since the first is facultatively anaerobic and the second can grow in 5% CO2 [1], [2]. Members of the Kocuria genus have been isolated from different environments including marine sediment [2], saline desert soil [3] and fermented food [4]. Our strain was isolated from a sulfite ore containing partially oxidized chalcopyrite, obtained from the Sossego mine (6°25′45″S, 50°3′58″W) in Canaã dos Carajás, Brazil. To date, there is only one complete published genome of Kocuria rhizophila DC2201 (GenBank/EMBL/DDBJ accession number AP009152) [5] and four draft published genomes of K. rhizophila P7-4 (GenBank accession number AFID00000000) [6], Kocuria atrinae C3-8 (GenBank/EMBL/DDBJ accession number AJXN00000000) [7], Kocuria sp. strain UCD-OTCP (GenBank/EMBL/DDBJ accession number AOSQ00000000) [8], and Kocuria palustris (GenBank/EMBL/DDBJ accession number ANHZ00000000)[9]. Here, we report the draft genome of K. marina SO9-6, which is the first genome from this species to be sequenced.
Sequencing of the K. marina SO9-6 genome was performed at the Life Sciences Core Facility (LaCTAD) of the State University of Campinas (UNICAMP). A paired-end library (400 bp long) was sequenced using the HiSeq2500 system and yielded 154,561,434 paired-end reads of 100 bp. Reads were preprocessed with NGS QC Toolkit v.2.2.9 [10], with a quality cutoff of 20, minimum length of 70 bp, and removal of ambiguous bases. The genome size was estimated to be 3.24 Mbp based on k-mer count [11], [12] and coverage of 4272 ×. The reads were subsampled to a genome coverage of approximately 250 × and assembled with SPAdes [13]. IMAGE v.2.4 [14] was used to close the gaps, resulting in sequences with a total length of 3,066,141 bp in 62 contigs, N50 of 183,121 bp, and GC content of 68.82%. Open reading frames (ORFs) were predicted with GLIMMER-3 [15], and the Rapid Annotations using Subsystems Technology (RAST) server v.4.0 [16] was used for genome annotation. The K. marina SO9-6 genome sequence comprised 2818 coding sequences (CDSs), 48 tRNAs, and 9 rRNA genes (four 5S rRNA, three 23S rRNA, and two 16S rRNA). A total of 1260 (41.32%) protein-coding genes were classified in 373 subsystems, and a predicted function was assigned to 1208 of them (Table 1).
Table 1.
Attributes | Value |
---|---|
Genome size (bp) | 3,066,141 |
Total contigs | 62 |
GC content (%) | 68.82 |
Protein-coding genes | 2818 |
tRNA genes | 48 |
rRNA genes | 9 |
Genes assigned to subsystems | 1260 |
According to RAST, K. rhizophila DC2201 is the closest neighbor of our strain, encoding a type III polyketide synthase (T3pks) and a nonribosomal peptide synthetase, and is probably capable of degrading the aromatic compounds phenylacetate, protocatechuate, and homoprotocatechuate [5]. The functional annotation of K. marina SO9-6 revealed genes related to the degradation of aromatic compounds including the industrial water contaminant phenylacetic acid [17], benzoate (by means of hydroxylation), and phenylacetate. The antiSMASH v.2.0 [18] analysis revealed five known secondary metabolite clusters, one siderophore, two bacteriocins, one terpene, and one T3pks synthesis, in contigs KM0016, KM0022, KM0028, KM0045, and KM0055, respectively. A nearly complete route for butanol production from glycerol degradation was also identified, as well as genes involved in antibiotic resistance, tolerance to heavy metals (mercury, arsenic, zinc, and especially copper), and siderophore biosynthesis (implying the capacity to acquire iron), which could explain the organism's survival in the high metal content environment. The genes for aromatic compound degradation and heavy metal tolerance suggest that K. marina SO9-6 could be used to improve bioremediation processes in contaminated areas. Comparative genomic analyses of SO9-6 are in progress and will be published separately. This first genome of K. marina helps to provide insights into its survival in extreme environments and raises the possibility of genetic features that could be targeted in future bioremediation studies.
Acknowledgments
DBAC, LBP, MVMS, CC, GVLJ, MBPN, and TMS received fellowships from the São Paulo Research Foundation (FAPESP). BPS and EEGL received fellowships from the National Council for Technological and Scientific Development (CNPq). BRZP, SSZ, and VDR received fellowships from Coordination for the Improvement of Higher Education Personnel (CAPES). DRBB and MBG received fellowships from Petrobrás. The authors are grateful to Vale S.A. for the environmental mine sample.
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