Phenanthrene degradation by bacteria of the genera <Emphasis Type="Italic">Pseudomonas</Emphasis> and <Emphasis Type="Italic">Burkholderia</Emphasis> in model soil systems

Degradation of phenanthrene by strains Pseudomona, Moscow, KMK, 2004simova, I.A. and Chernov, I.s putida BS3701 (pBS1141, pBS1142), Pseudomonas putida BS3745 (pBS216), and Burkholderia sp. BS3702 (pBS1143) were studied in model soil systems. The differences in accumulation and uptake rate of phenanthrene intermediates between the strains under study have been shown. Accumulation of 1-hydroxy-2-naphthoic acid in soil in the course of phenanthrene degradation by strain BS3702 (pBS1143) in a model system has been revealed. The efficiency of phenanthrene biodegradation was assessed using the mathematical model proposed previously for assessment of naphthalene degradation efficiency. The efficiency of degradation of both phenanthrene and the intermediate products of its degradation in phenanthrene-contaminated soil is expected to increase with the joint use of strains P. Putida BS3701 (pBS1141, pBS1142) and Burkholderia sp. BS3702 (pBS1143).     

Growth and survival of Pseudomonas putida strains degrading naphthalene in soil model systems with different moisture levels

The effect of different moisture levels (from 20 to 70%) on the growth and survival of Pseudomonas putida strains G7 and BS3701 degrading naphthalene was studied in soil model systems. P. putida G7 contains plasmid NAH7 and P. putida BS3701 harbours plasmids pBS1141 and pBS1142. A mathematical model is proposed to describe the observed dynamics of the number of viable bacterial cells. Naphthalene and soil organic matter were considered as substrates available to bacteria. Data fitting allowed the estimation of model parameters characterizing microbial growth rate, utilization rate of substrates, specific maintenance rate and yield coefficient. Both the maximum bacterial concentration and the highest yield coefficient were observed at a soil moisture level of 40%. This optimal moisture level is close to but less than the water capacity (48%) of the soil used.     

Phenanthrene biodegradation and the interaction of <Emphasis Type="Italic">Pseudomonas putida</Emphasis> BS3701 and <Emphasis Type="Italic">Burkholderia</Emphasis> sp. BS3702 in plant rhizosphere

The interaction between the strains degrading polycyclic aromatic hydrocarbons, Pseudomonas putida BS3701 and Burkholderia sp. BS3702, was studied in the course of phenanthrene degradation in plant rhizosphere. Strain BS3702 was shown to accumulate 1-hydroxy-2-naphthoic acid (which is toxic for plants); it was then utilized by strain BS3701, which thereby increased the resistance of plants to the pollutant and to the toxic intermediate. With this type of interaction (cooperation), the efficiency of phenanthrene degradation was noted to decrease.     

Phylogenetic analysis of the genes for naphthalene and phenanthrene degradation in Burkholderia sp. strains

The genetic systems responsible for naphthalene and phenanthrene catabolism have been analyzed in the five strains of Burkholderia sp. isolated from soil samples (West Siberia) contaminated by heavy residual fuel and in the laboratory collection strain Burkholderia sp. BS3702 isolated from soil samples of the coke gas plant (Vidnoe, Moscow oblast). The results of this work demonstrate that naphthalene and phenanthrene degradation in the above strains is encoded by the sequences not homologous to the classical nah genes of pseudomonades. In the Burkholderia sp. BS3702 strain, the initial stages of phenanthrene degradation and the subsequent stages of salicylate degradation are controlled by the sequences of different evolutionary descent (phn and nag genes).     

Catabolism of biphenyl by Pseudomonas putida BS 893 strain containing the biodegradation plasmid pBS241

The isolation and identification of biphenyl catabolism products in Pseudomonas putida BS 893 (pBS241) showed the presence of benzoic, m-hydroxybenzoic and cinnamic acids. The two latter compounds were not found in biphenyl degradation by other bacterial strains. P. putida BS 893 (pBS241) differed from other biphenyl-positive Pseudomonas strains in the enzyme activity. These differences may stem from peculiarities in the pathway of biphenyl catabolism controlled by plasmid pBS241.     

Structural and functional variability of genetic systems for catabolizing polycyclic aromatic hydrocarbons in Pseudomonas putida strains

The genetic control of naphthalene, phenanthrene, and anthracene biodegradation was studied in three Pseudomonas putida strains isolated from coal tar- and oil-contaminated soils. These strains isolated from different geographical locations contained similar catabolic plasmids controlling the first steps of naphthalene conversion to salicylate (the nah1 operon), functionally inoperative salicylate hydroxylase genes, and genes of the metha-pathway of catechol degradation (the nah2 operon). Salicylate oxidation in these strains is determined by genes located in trans-position relative to the nah1 operon: in strains BS202 and BS3701, they are located on the chromosome, and in the strain BS3790, on the second plasmid.     

Resistance of certain strains of Pseudomonas bacteria to toxic effect of heavy metal ions]

The effect of heavy metal cations (cobalt, nickel, and copper) and the anion detergent sodium dodecyl sulfate (SDS) on the barrier properties of the plasma membrane (PM) of the Co-sensitive stain Pseudomonas putida BS394 and the Co-resistant strains Pseudomonas sp. BS501 (wild-type strain) and Pseudomonas putida BS394 (pBS501) (transformed strain) was studied by high-frequency electro-orientational spectroscopy. The cations were found to rank, in order of decreasing damage inflicted on the PM, as copper > cobalt > nickel. The strains studied were found to rank, in order of increasing resistance of the PM to damage inflicted by copper and cobalt cations, as P. putida BS394 < P. putida BS394 (pBS501) < Pseudomonas sp. BS501. In order of increasing resistance to SDS, the strains ranked inversely. The strains did not differ in sensitivity to nickel cations. Investigation of the surface of intact and trypsin-treated cells by microelectrophoresis showed that the surface layers of the cell wall of wild-type and transformed cells contained increased amounts of proteins. The surface proteins of Co-resistant cells had molecular masses of 49, 40, and 32 kDa. Exposure of Co-resistant cells to trypsin considerably reduced their resistance to cobalt cations. It is assumed that the resistance of the PM of the wild-type and transformed pseudomonads to heavy metal cations is determined by plasmid pBS501 and is related to the synthesis of protective surface proteins of the cell wall.     

The use of the [13C]/[12C] ratio for the assay of the microbial oxidation of hydrocarbons

The study deals with a comparative analysis of the relative abundances of the carbon isotopes 12C and 13C in the metabolites and biomass of the Burkholderia sp. BS3702 and Pseudomonas putida BS202-p strains capable of utilizing aliphatic (n-hexadecane) and aromatic (naphthalene) hydrocarbons as sources of carbon and energy. The isotope composition of the carbon dioxide, biomass, and exometabolites produced during the growth of Burkholderia sp. BS3702 on n-hexadecane (delta 13C = -44.6 +/- 0.2@1000) were characterized by the isotope effects delta 13CCO2 = -50.2 +/- 0.4@1000, delta 13Cbiom = -46.6 +/- 0.4@1000 and delta 13Cexo = -41.5 +/- 0.4@1000, respectively. The isotope composition of the carbon dioxide, biomass, and exometabolites produced during the growth of the same bacterial strain on naphthalene (delta 13C = -21 +/- 0.4@1000) were characterized by the isotope effects delta 13CCO2 = -24.1 +/- 0.4@1000, delta 13Cbiom = -19.2 +/- 0.4@1000 and delta 13Cexo = -19.1 +/- 0.4@1000, respectively. The possibility of using the isotope composition of metabolic carbon dioxide for the rapid monitoring of the microbial degradation of petroleum hydrocarbons in the enviroment is discussed.     

Molecular classification of IncP-9 naphthalene degradation plasmids

A large collection of naphthalene-degrading fluorescent Pseudomonas strains isolated from sites contaminated with coal tar and crude oil was screened for the presence of IncP-9 plasmids. Seventeen strains were found to carry naphthalene catabolic plasmids ranging in size from 83 to 120 kb and were selected for further study. Results of molecular genotyping revealed that 15 strains were closely related to P. putida, one to P. fluorescens, and one to P. aeruginosa. All catabolic plasmids found in these strains, with the exception of pBS216, pSN11, and p8909N-1, turned out to belong to IncP-9 beta-subgroup. Plasmids pBS216, pSN11, and p8909N-1 were identified as members of IncP-9 delta-subgroup. One plasmid, pBS2, contains fused replicons of IncP-9beta and IncP-7 groups. RFLP analyses of the naphthalene catabolic plasmids revealed that organisation of the replicon correlates well with the overall plasmid structure. Comparative PCR studies with conserved oligonucleotide primers indicated that genes for key enzymes of naphthalene catabolism are highly conserved among all studied plasmids. Three bacterial strains, P. putida BS202, P. putida BS3701, and P. putida BS3790, were found to have two different salicylate hydroxylase genes one of which has no similarity to the "classic" enzyme encoded by nahG gene. Discovery of a large group of plasmid with unique nahR suggested that the regulatory loop may also represent a variable part of the pathway for catabolism of naphthalene in fluorescent Pseudomonas spp.     

Effect of arsenite on the physiological and cytological properties of Pseudomonas putida strains capable of degrading polycyclic aromatic hydrocarbons]

Some physiological and cytological properties of Pseudomonas putida strains resistant to arsenite and capable of degrading polycyclic aromatic hydrocarbons were studied. The resistance of P. putida BS202 (NPL-1) to arsenite proved to be determined by chromosomal genes, while the arsenite resistance of P. putida BS238 (pBS2; pBS3031) was by plasmid-borne genes. Arsenite affected the pattern and rate of growth of strain BS202 (NPL-1) in media with naphthalene or salicylate as carbon sources; particularly, it lengthened the lag phase. Electron-microscope analysis of the strains studied did not reveal any arsenite-induced destructive changes in the cell envelope. At the same time, arsenite in the growth medium induced some alterations in the structure of the outer membrane of strain BS202 (NPL-1) and the cytoplasmic membrane of strain BS238 (pBS2; pBS3031) and, in both strains, led to an increase in the density of intramembrane particles on the EF face of the freeze-fractured cytoplasmic membrane. Arsenite resistance probably evidently protects cells of both strains from greater damage. Physiological and cytological data suggest that the mechanisms of arsenite resistance in the strains studied are different.     

Growth and plasmid-encoded naphthalene catabolism of Pseudomonas putida in batch culture

Abstract The growth characteristics of Pseudomonas putida plasmid-harbouring strains which catabolize naphthalene via various pathways in batch culture with naphthalene as the sole source of carbon and energy have been investigated. The strains under study were constructed using the host strain P. putida BS394 which contained various naphthalene degradation plasmids. The highest specific growth rate was ensured by the plasmids that control naphthalene catabolism through the meta-pathway of catechol oxidation. The strains metabolizing catechol via the ortho -pathway grew at a lower rate. The lowest growth rate was observed with strain BS291 harbouring plasmid pBS4 which controls naphthalene catabolism via the gentisic acid pathway. Various pathways of naphthalene catabolism appear to allow these strains to grow at various rates which should be taken into account when constructing efficient degraders of polycyclic aromatic compounds.     

A new pathway for bacterial catabolism of 3-hydroxybenzoic acid

Abstract This paper is the first to describe the transformation of 3-hydroxybenzoate (3-HBA) by Pseudomonas putida BS893 by a new pathway via 2,3-dihydroxybenzoate (2,3-DBA) and catechol. We have compared the intermediates and appropriate enzyme activities in P. putida BS893 (pBS241) and in a cured derivative BS662 (Bph⁻) thereof, for the ascertainment of plasmid or chromosomal genetic control over 3-HBA-catabolism. The results presented show that catabolism of 3-HBA in P. putida BS893 (pBS241) is controlled by chromosomal genes.     

Reversed-phase high performance liquid chromatography of the products of microbiological degradation of toluene

Conditions have been selected for a reversed-phase high-performance liquid chromatographic assay of intermediate products formed in the course of utilization of toluene by Pseudomonas putida. The composition of products indicates that degradation of toluene by strain BS590-P proceeds primarily through the formation of benzoate and catechol. This is followed by degradation of catechol via ortho-cleavage. In strain BS3701-P, toluene oxidation involves both the side chain and the aromatic ring.     

Structural and Functional Variation in Genetic Systems for Catabolism of Polycyclic Aromatic Hydrocarbons in Pseudomonas putida Strains

The genetic control of naphthalene, phenanthrene, and anthracene biodegradation was studied in three Pseudomonas putida strains isolated from coal tar- and oil-contaminated soils. These strains isolated from different geographical locations contained similar catabolic plasmids controlling the first steps of naphthalene conversion to salicylate (the nah1operon), functionally inoperative salicylate hydroxylase genes, and genes of the metha-pathway of catechol degradation (the nah2 operon). Salicylate oxidation in these strains is determined by genes located in trans-position relative to the nah1 operon: in strains BS202 and BS3701, they are located on the chromosome, and in the strain BS3790, on the second plasmid.     

Biodegradation of phenanthrene by Pseudomonas bacteria bearing rhizospheric plasmids in model plant-microbial associations

The consumption phenanthrene in soil by model plant-microbial associations including natural and transconjugant plasmid-bearing rhizospheric strains of Pseudomonas fluorescens and P. aureofaciens degrading polycyclic aromatic hydrocarbons was studied. It was shown that phytoremediation of soil polluted with phenanthrene in the rhizosphere of barley (Hordeum sativum L.) was inefficient with the absence of the degrading strains. Inoculation of barley seeds with both natural and transconjugant plasmid-bearing Pseudomonas strains able to degrade polycyclic aromatic hydrocarbons (PAH) protected plants from the phytotoxic action of phenanthrene and favored its degradation in soil. Rape (Brassica napus L.) was shown to be an appropriate sentinel plant, sensitive to phenanthrene, which can be used for testing the efficiency of phenanthrene degradation in soil. The biological test with the use of sensitive rape plants can be applied for estimation of the efficiency of phyto/bioremediation of PAH-polluted soils.     

Comparative study of aromatic ring meta-cleavage enzymes in Pseudomonas strains with plasmid and chromosomal genetic control of the catabolism of biphenyl and m-toluate

It was shown that two different enzymes of aromatic ring oxidative meta-cleavage (2,3-dihydroxybiphenyl-1,2-dioxygenase), DBO and catechol-2,3-dioxygenase, C230) function in Pseudomonas strains with a plasmid and chromosomal genetic control of biphenyl and toluate catabolism. A comparative analysis of DBO's and C230's expressed by the pBS241 biphenyl degradative plasmid in P. putida BS893, pBS311 in P. putida U83, chromosomal genes in P. putida BF and C230 from P. putida PaW160 (pWWO) was carried out. It was found that the DBO's of all strains under study are highly specialized enzymes in respect of 2,3-dihydroxybiphenyl cleavage and are also able to cleave 3-methyl-catechol and catechol (but not 4-methylcatechol) at low rates. In contrast with DBO's, in Pseudomonas strains the substrate specificities of all C230's are variable. The C230's expressed by the D-plasmids pBS241 and pBC311 have a moderate affinity for catechol, 3-methyl- and 4-methylcatechol, but are unable to cleave 2,3-dihydroxybiphenyl. The C230 which is encoded by the chromosomal structure gene from P. putida BF is very similar to C230 which codes for the TOL-plasmid pWWO. These plasmid differ from C230's expressed by biphenyl D-plasmids due to their capability to cleave 2,3-dihydroxybiphenyl in addition to catechol cleavage. All DBO's and C230's under study possess a number of properties that are typical for the enzymes having an oxidative meta-cleaving effect. The different roles of these enzymes in biphenyl and toluate catabolism in Pseudomonas strains are discussed.     

Aerobic biodegradation of N-nitrosodimethylamine (NDMA) by axenic bacterial strains

The water contaminant N-nitrosodimethylamine (NDMA) is a probable human carcinogen whose appearance in the environment is related to the release of rocket fuel and to chlorine-based disinfection of water and wastewater. Although this compound has been shown to be biodegradable, there is minimal information about the organisms capable of this degradation, and little is understood of the mechanisms or biochemistry involved. This study shows that bacteria expressing monooxygenase enzymes functionally similar to those demonstrated to degrade NDMA in eukaryotes have the capability to degrade NDMA. Specifically, induction of the soluble methane monooxygenase (sMMO) expressed by Methylosinus trichosporium OB3b, the propane monooxygenase (PMO) enzyme of Mycobacterium vaccae JOB-5, and the toluene 4-monooxygenases found in Ralstonia pickettii PKO1 and Pseudomonas mendocina KR1 resulted in NDMA degradation by these strains. In each of these cases, brief exposure to acetylene gas, a suicide substrate for certain monooxygenases, inhibited the degradation of NDMA. Further, Escherichia coli TG1/pBS(Kan) containing recombinant plasmids derived from the toluene monooxygenases found in strains PKO1 and KR1 mimicked the behavior of the parent strains. In contrast, M. trichosporium OB3b expressing the particulate form of MMO, Burkholderia cepacia G4 expressing the toluene 2-monooxygenase, and Pseudomonas putida mt-2 expressing the toluene sidechain monooxygenase were not capable of NDMA degradation. In addition, bacteria expressing aromatic dioxygenases were not capable of NDMA degradation. Finally, Rhodococcus sp. RR1 exhibited the ability to degrade NDMA by an unidentified, constitutively expressed enzyme that, unlike the confirmed monooxygenases, was not inhibited by acetylene exposure.     

Regulation of the expression of plasmid determination responsible for caprolactam degradation by bacteria of the genus Pseudomonas]

On the basis of the study of some Tn5 induced mutants in Pseudomonas putida strain BS836 containing the plasmid pBS268 coding caprolactam degradation, growth on caprolactam and its intermediates, and the data on the induction of oxidative activities in plasmid containing P. putida strain BS831 it was shown that plasmid and chromosome genes regulated the expression of CAP-determinants. The regulation has some elements of the negative control mechanism. Caprolactam is the inducer of the synthesis of key enzymes cleaving it and its intermediates (aminocaproic and adipic acids). At the same time each of its intermediates induced the synthesis of enzymes responsible for its cleavage.     

Rhizosphere bacteria Pseudomonas aureofaciens and Pseudomonas chlororaphis oxidizing naphthalene in the presence of arsenic

Rhizosphere strains of P. aureofaciens BS1393(pBS216, pKS1) and P. chlororaphis PCL1391(pBS216, pKS1), exhibiting the ability to stimulate the growth of plants and protect them from phytopathogens, have been obtained. In these strains, plasmid pBS216 ensures naphthalene degradation and plasmid pKS1 confers resistance to arsenic. In the presence of arsenic and naphthalene, the number of living cells and the growth rate of the arsenic-resistant strains were higher than those of the arsenic-sensitive strains BS1393(pBS216) and PCL1391(pBS216). During the cultivation of the resistant strains, arsenic had no inhibitory effect on the activity of the key enzymes of naphthalene biodegradation, except for catechol-2,3-dioxygenase. In a model system containing plant-microbial associations, strains BS1393(pBS216, pKS1) and PCL1391(pBS216, pKS1) degraded as much as 97% of added naphthalene in the presence of arsenic.     

Plasmid-mediated mineralization of naphthalene, phenanthrene, and anthracene.

The well-characterized plasmid-encoded naphthalene degradation pathway in Pseudomonas putida PpG7(NAH7) was used to investigate the role of the NAH plasmid-encoded pathway in mineralizing phenanthrene and anthracene. Three Pseudomonas strains, designated 5R, DFC49, and DFC50, were recovered from a polynuclear aromatic hydrocarbon-degrading inoculum developed from a manufactured gas plant soil slurry reactor. Plasmids pKA1, pKA2, and pKA3, approximately 100 kb in size, were isolated from these strains and characterized. These plasmids have homologous regions of upper and lower NAH7 plasmid catabolic genes. By conjugation experiments, these plasmids, including NAH7, have been shown to encode the genotype for mineralization of [9-14C]phenanthrene and [U-14C]anthracene, as well as [1-14C]naphthalene. One strain, Pseudomonas fluorescens 5RL, which has the complete lower pathway inactivated by transposon insertion in nahG, accumulated a metabolite from phenanthrene and anthracene degradation. This is the first direct evidence to indicate that the NAH plasmid-encoded catabolic genes are involved in degradation of polynuclear aromatic hydrocarbons other than naphthalene.