| Literature DB >> 18832300 |
Yanina R Sevastsyanovich1, Renata Krasowiak1, Lewis E H Bingle1, Anthony S Haines1, Sergey L Sokolov2, Irina A Kosheleva2, Anastassia A Leuchuk3, Marina A Titok3, Kornelia Smalla4, Christopher M Thomas1.
Abstract
IncP-9 plasmids are important vehicles for degradation and resistance genes that contribute to the adaptability of Pseudomonas species in a variety of natural habitats. The three completely sequenced IncP-9 plasmids, pWW0, pDTG1 and NAH7, show extensive homology in replication, partitioning and transfer loci (an approximately 25 kb region) and to a lesser extent in the remaining backbone segments. We used PCR, DNA sequencing, hybridization and phylogenetic analyses to investigate the genetic diversity of 30 IncP-9 plasmids as well as the possibility of recombination between plasmids belonging to this family. Phylogenetic analysis of rep and oriV sequences revealed nine plasmid subgroups with 7-35 % divergence between them. Only one phenotypic character was normally associated with each subgroup, except for the IncP-9beta cluster, which included naphthalene- and toluene-degradation plasmids. The PCR and hybridization analysis using pWW0- and pDTG1-specific primers and probes targeting selected backbone loci showed that members of different IncP-9 subgroups have considerable similarity in their overall organization, supporting the existence of a conserved ancestral IncP-9 sequence. The results suggested that some IncP-9 plasmids are the product of recombination between plasmids of different IncP-9 subgroups but demonstrated clearly that insertion of degradative transposons has occurred on multiple occasions, indicating that association of this phenotype with these plasmids is not simply the result of divergent evolution from a single successful ancestral degradative plasmid.Entities:
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Year: 2008 PMID: 18832300 PMCID: PMC2885752 DOI: 10.1099/mic.0.2008/017939-0
Source DB: PubMed Journal: Microbiology (Reading) ISSN: 1350-0872 Impact factor: 2.777
Strains used in this study
Cb, Gm, Km, Sm, Su, Tc and Hg, resistance to antibiotics carbenicillin, gentamicin, kanamycin, streptomycin, sulphonamide, tetracycline and to mercury ions, respectively; Uv, ultraviolet light protection; Ant, Cap, Nah, Phn, Sal, Tol and Xyl, ability to degrade anthracene, ε-caprolactam, naphthalene, phenanthrene, salicylic acid, toluene and (m- and p-) xylenes, respectively.
| NAH7 | 83 | Nah Sal | Coal-tar-contaminated soil, CA, USA | ||
| NPL-1 | 100 | Nah Sal | Coal-tar-contaminated soil near coal tar mine, Makeevka, Ukraine | ||
| p8C | 110 | Nah Sal Phn | Oil-contaminated soil, Tumen region, Western Siberia, Russia | ||
| p15C | 110 | Nah Sal Phn | Oil-contaminated soil, Tumen region, Western Siberia, Russia | ||
| pBS2 | 130 | Nah Sal | Soil from territory of metallurgical plant, Nizhniy Tagil, Russia | ||
| pBS216 | 83 | Nah Sal Phn | Soil from territory of metallurgical plant, Magnitogorsk, Russia | ||
| pBS240 | 160 | Nah | Coke chemical plant, Kemerovo, Russia | RAS | |
| pBS243 | 160 | Nah | Soil from territory of metallurgical plant, Magnitogorsk, Russia | RAS | |
| pBS265 | 130 | Cap | Chemical plant sewage, Severodonetsk, Ukraine | ||
| pBS267 | 130 | Cap | Chemical plant sewage, Severodonetsk, Ukraine | ||
| pBS268 | 85 | Cap | Chemical plant sewage, Kemerovo, Russia | ||
| pBS1141, pBS1142 | 100, 60 | Nah Sal Phn Ant cryptic | Coke chemical plant, Vidnoe, Moscow region, Russia | ||
| pBS1181 | 120 | Nah Sal Phn | Oil-contaminated soil, Tumen region, Western Siberia, Russia | ||
| pBS1191, pBS1192 | 100, 60 | Nah Sal Phn Ant cryptic | Oil-contaminated soil, Tumen region, Western Siberia, Russia | ||
| pDTG1 | 83 | Nah | Coal-tar-contaminated site, Bangor, Wales, UK | ||
| Unknown† | pFKY1 | 200 | Nah Sal | Oil-contaminated site, Japan | M. Tsuda, unpublished data |
| pM3 | 75 | Sm Tc Uv | Sewage and soil from different industrial and agricultural locations in Belarus and Azerbaijan | ||
| pM77 | 75 | Sm Tc | Soil from the area of sewage treatment plant, Minsk, Belarus | ||
| pM80 | 75 | Sm Tc | Soil from the area of sewage treatment plant, Minsk, Belarus | ||
| pMG18 | 100 | Cb Gm Km Sm Su Hg | Japan | ||
| pNL4 | 75 | Nah Sal | Soil from a distillery area, Minsk, Belarus | ||
| pNL15‡ | 75 | Sm | Soil from a petrol station area, Minsk, Belarus | ||
| pNL22 | 100 | Nah Sal | Soil from a petrol station area, Minsk, Belarus | ||
| pNL25 | 75 | Nah Sal | Soil from a railway station area, Minsk, Belarus | ||
| pNL29 | Nah Sal | Soil from a petrol station area, Minsk, Belarus | |||
| pNL31 | Nah Sal | Soil from the roadside, Minsk, Belarus | |||
| pNL60 | 120 | Nah Sal | Soil from the foundry area, Homel, Belarus | ||
| pOV17 | 85 | Nah | Oat rhizosphere from oil-contaminated soil, Western Siberia, Russia | RAS | |
| pSN11 | 83 | Nah Sal | Salt-contaminated soil from chemical plant, Berezniki, Ural, Russia | ||
| pSVS15 | 90 | Tol Xyl | Piece of rubber from used-car-tyre storage, Minsk, Belarus | ||
| pWW0 | 116.58 | Tol Xyl | USA | ||
| R2 | 73 | Cb Sm Su Uv | Japan |
*RAS and BSU, bacterial strain collections obtained from Russian Academy of Sciences and Belarus State University, respectively.
†Plasmid obtained by exogenous isolation.
‡Plasmid was labelled with mini-Tn5 (Km) and transferred by conjugation into E. coli C600 (selection for Km Nah− phenotype) from the natural host P. fluorescens 42 (Leuchuk ).
§Not determined.
Fig. 1.Neighbour-joining rooted phylogenies of the IncP-9 plasmid family based on sequence analysis of rep (a) and oriV (b) loci. Plasmid subgroups are bracketed and named with letters of the Greek alphabet from α to ι; grey background shapes define plasmid phenotypes: rectangle, multiple antibiotic resistance; oval, toluene/xylene degradation; circle, caprolactam degradation; no shape (clear background), naphthalene degradation. Bootstrap values (out of 1000 replicates) are shown adjacent to branch nodes. pBBR1 sequences were used to root the trees (pBBR1 branches are shortened for convenience). The lengths of horizontal branches correspond to evolutionary distances and the scale bars show the number of substitutions per site.
Fig. 2.Schematic representation of alignment of pWW0, pDTG1 and NAH7 plasmid sequences generated using Artemis software. Grey areas connect similar orfs. The tra and mpf blocks included traD–C and mpfJ–R genes showing perfect synteny in three plasmids. Not to scale.
PCR- and hybridization-based detection of the selected backbone loci in plasmids representing seven of the nine IncP-9 subgroups using pWW0- and pDTG1-specific tools
a, +, (+) and − correspond to strong, weak and no PCR or hybridization signal, respectively. PW, PCR with pWW0-specific primers; H, hybridization with pWW0-specific probes; PD, PCR with pDTG1-specific primers. An asterisk indicates a PCR product larger than the expected size. nd, Not determined.
b, Pairs of homologous backbone loci from pWW0 and pDTG1 are indicated in this order; if only one orf pair is indicated, it belongs to pWW0.
Fig. 3.Hybridization of selected IncP-9 plasmids with pWW0-derived DIG-labelled probes specific to particular backbone loci. For hybridization, genomic DNA isolated from plasmid-containing bacteria was used; genomic DNA from plasmid-free P. putida BS 394 was used as a negative control (lane ‘BS394’). The DNA was digested with AvaI (orf6–7 and ruvB–ruvA loci) or SalI (others) before loading of the agarose gels, and was hybridized with pWW0-derived probes as described in Methods. In several hybridizations, multiple bands appeared in pWW0 and some test plasmids (orf6–orf7, orf31–orf32, orf39A–orf40). This might result from (i) incomplete digestion of the genomic DNA, (ii) non-specific hybridization or (iii) the presence of another region of homology elsewhere on the plasmid. The last could account for the appearance of multiple bands in the hybridizations of pWW0 and closely related β plasmids with orf31–32 and orf39A–40 probes, since pWW0orf32 and pWW0orf40 show 92.7 and 78.7 % nucleotide sequence identity to pWW0orf15 and pWW0orf171, respectively (Fig. 2).
Fig. 4.Schematic representation of the pWW0 versus pDTG1 plasmid alignment to show the location of the conserved primers specific to determinants flanking the insertions of corresponding catabolic pathways. The conserved primer pairs are shown by black arrows; the genetic determinants used for the primer design are shown by grey arrows; white triangles (tol and nah) indicate insertions of toluene and naphthalene catabolic pathways, respectively. The sizes of the expected PCR products are indicated.
Analysis of possible insertions in two sites of the IncP-9 backbone by PCR and hybridization with plasmids representing the eight best-characterized subgroups
| R | pM3 | + | − | − | + | |
| Tol | pWW0 | + | (−) | − | (+) | |
| Nah | NPL-1, pBS2, pBS1141, p8C, p15C, pBS1181 | + | − | + | − | |
| Nah | pBS1191 | + | − | − | + | |
| Cap | pBS265, pBS267 | + | − | − | + | |
| Nah | pBS216, pSN11 | − | (+) | + | (−) | |
| ε | R | R2 | + | − | − | + |
| R | pMG18 | − | + | − | + | |
| θ | Tol | pSVS15 | + | − | + | − |
| R | pNL15 | + | − | − | + | |
| Nah | pNL60 | + | (−) | + | (−) | |
*Tol, Nah and Cap, degradation of toluene/xylenes, naphthalene and caprolactam, respectively; R, antibiotic resistance.
†+ or − indicates predicted presence or absence of insertions in uncharacterized plasmids. (+) or (−) indicates known presence or absence of insertions in characterized plasmids (pWW0, δ and ζ plasmids).
Fig. 5.PCR and hybridization analyses of selected IncP-9 plasmids with the primers and hybridization probes targeting the sites of accessory DNA insertions in the common plasmid backbone. (a) PCR products obtained from IncP-9 plasmids with the ruvB-F(2)–ruvA-R(2) primers and subsequently hybridized with the pWW0-derived ruvB/ruvB1-ruvA DIG-labelled hybridization probe. (b) PCR products obtained with the 39A/607F–175/613R primers and hybridized with the pBS216-derived hybridization probe orf39A/orf607–orf175/orf613. PCR with genomic DNA from the plasmid-free P. putida BS 394 was used as a negative control (lane ‘BS394’).