The naphthalene-degrading activity of a Pseudomonas sp. strain isolated from a creosote-contaminated soil was shown to be encoded by the IncP9 plasmid pNF142 by transfer to Pseudomonas putida KT2442. The effects of the inoculant strain KT2442 (pNF142) and of naphthalene contamination on the soil bacterial community were studied in microcosms with the following treatments: (I) soil, (II) soil with naphthalene, (III) soil with naphthalene and inoculated with KT2442 (pNF142). The inoculant became the dominant bacterial population in treatment (III) as evidenced by cultivation and denaturing gradient gel electrophoresis (DGGE) analysis. The bacterial DGGE profiles revealed drastically reduced complexity due to the numerical dominance of the inoculant. However, group-specific fingerprints (beta-proteobacteria, actinobacteria) that excluded KT2442 (pNF142) showed less severe changes in the bacterial community patterns. A major effect of naphthalene on the soil bacterial community was observed in treatment (II) after 21 days. Two dominant bands appeared whose sequences showed the highest similarity to those of Burkholderia sp. RP007 and Nocardia vinaceae based on 16S rRNA gene sequencing. These bands were less intense in treatment (III). The increased abundance of RP007-like populations due to naphthalene contamination was also confirmed by PCR amplification of the phnAc gene. The nahAc and nahH genes were detected in DNA and cDNA only in treatment III. Although the inoculant strain KT2442 (pNF142) showed good survival and expression of genes involved in naphthalene degradation, this study suggests that KT2442 (pNF142) suppressed the enrichment of indigenous naphthalene degraders.

No 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 ∼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-9β 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.

No abstract

No abstract

No abstract

IncP-9 plasmids are best known as the vehicles for spreading biodegradation functions among Pseudomonas species but can also carry resistance determinants. New PCR primer systems targeting different replicon-specific regions were designed to allow detection of IncP-9 plasmids. Their specificity was checked against a range of IncP-9 plasmids as well as representatives of incompatibility groups IncFI, IncFII, IncN, IncQ, IncP-1alpha, IncP-1beta, IncP-2, IncP-7, IncP-13, IncW, IncU, IncX and IncZ. Products obtained for plasmids assigned to IncP-9 group by traditional incompatibility testing varied in size and restriction pattern suggesting diversity in the 'core' sequence among related replicons. Specific primer pairs were applied to community DNA extracted from a range of environments including those subject to strong selective pressure, caused by antibiotics, metals and organic pollutants. Abundant products were observed in manure and sewage, independently of the presence of antibiotics and metals, but could also be detected in coastal water and streptomycin-treated soil. Community DNA from faeces of piglets treated and non-treated with Zn gave particularly strong PCR product with IncP-9 rep primers. Therefore, an attempt was made to isolate bacteria carrying the IncP-9-like plasmids, but this was not successful. The results of application of these newly designed primer pairs to plasmid isolates as well as community DNA indicate that the IncP-9-related plasmids are a diverse family prevalent in various environments and widely distributed geographically.

1-Hydroxy-2-naphthoate is formed as an intermediate in the bacterial degradation of phenanthrene. A monooxygenase which catalyzed the oxidation of 1-hydroxy-2-naphthoate to 1,2-dihydroxynaphthalene was purified from the phenanthrene- and naphthalene-degrading Pseudomonas putida strain BS202-P1. The purified protein had a molecular weight of 45 kDa and required NAD(P)H and FAD as cofactors. The purified enzyme also catalysed the oxidation of salicylate and various substituted salicylates. The comparison of the Km and Vmax values for 1-hydroxy-2-naphthoate and salicylate demonstrated a higher catalytic efficiency of the enzyme for salicylate as a substrate. A significant substrate-inhibition was detected with higher concentrations of 1-hydroxy-2-naphthoate. The aminoterminal amino acid sequence of the purified enzyme showed significant homologies to salicylate 1-monooxygenases from other Gram negative bacteria. It was therefore concluded that during the degradation of phenanthrene the conversion of 1-hydroxy-2-naphthoate to 1,2-dihydroxynaphthalene is catalysed by a salicylate 1-monooxygenase. Together with previous studies, this suggested that the enzymes of the naphthalene pathway are sufficient to catalyse also the mineralization of phenanthrene.