Degradation of Acetonitrile by Pseudomonas putida

A bacterium capable of utilizing high concentrations of acetonitrile as the sole source of carbon and nitrogen was isolated from soil and identified as Pseudomonas putida. This bacterium could also utilize butyronitrile, glutaronitrile, isobutyronitrile, methacrylonitrile, propionitrile, succinonitrile, valeronitrile, and some of their corresponding amides, such as acetamide, butyramide, isobutyramide, methacrylamide, propionamide, and succinamide as growth substrates. Acetonitrile-grown cells oxidized acetonitrile with a K_m of 40.61 mM. Mass balance studies with [¹⁴C]acetonitrile indicated that nearly 66% of carbon of acetonitrile was released as ¹⁴CO₂ and 14% was associated with the biomass. Metabolites of acetonitrile in the culture medium were acetic acid and ammonia. The acetate formed in the early stages of growth completely disappeared in the later stages. Cell extracts of acetonitrile-grown cells contained activities corresponding to nitrile hydratase and amidase, which mediate the breakdown of actonitrile into acetic acid and ammonia. Both enzymes were intracellular and inducible and hydrolyzed a wide range of substrates. The specific activity of amidase was at least 150-fold higher than the activity of the enzyme nitrile hydratase.     

Degradation of dibenzothiophene by Pseudomonas putida

The microbial degradation of dibenzothiophene (DBT) and other organosulphur compounds such as thiophene-2-carboxylate (T2C) is of interest for the potential desulphurization of coal. The feasibility of degradation of DBT and T2C by Pseudomonas putida and other bacteria was analysed. Pseudomonas putida oxidized sulphur from DBT in the presence of yeast extract, but it did not when DBT was the sole source of carbon.     

Degradation of aromatic compounds by Pseudomonas putida

The influence of different process kinetics on the course of phenol degradation has been studied as well as the influence of axial dispersion in the liquid phase on the reactor height with relatively large biofilm thickness in a conventional fluidized bed and air-lift bioreactor. The object of this was to achieve a high conversion of substrate in a device of real size in real process time. For calculating the mathematical model, the method of orthogonal collocation with the STIFF integration routine has been used.     

Degradation of methoxylated aromatic acids by Pseudomonas putida

J.E. TURNER AND N. ALLISON. 1995. A newly-isolated strain of Pseudomonas putida (HVA-1) utilized homovanillic acid as sole carbon and energy source. Homovanillate-grown bacteria oxidized homovanillate and homoprotocatechuate but monohydroxylated and other methoxylated phenylacetic acids were oxidized poorly; methoxy-substituted benzoates were not oxidized. Extracts of homovanillate-grown cells contained homoprotocatechuate 2,3-dioxygenase but the primary homovanillate-degrading enzyme could not be detected. No other methoxylated phenylacetic acid supported growth of the organism but vanillate was utilized as a carbon and energy source. When homovanillate-grown cells were used to inoculate media containing vanillate a 26 h lag period occurred before growth commenced. Vanillate-grown bacteria oxidized vanillate and protocatechuate but no significant oxygen uptake was obtained with homovanillate and other phenylacetic acid derivatives. Analysis of pathway intermediates revealed that homovanillate-grown bacteria produced homoprotocatechuate, formaldehyde and the ring-cleavage product 5-carboxymethyl 2-hydroxymuconic semialdehyde (CHMS) when incubated with homovanillate but monohydroxylated or monomethoxylated phenylacetic acids were not detected. These results suggest that homovanillate is degraded directly to the ring-cleavage substrate homoprotocatechuate by an unstable but highly specific demethylase and then undergoes extradiol cleavage to CHMS. It would also appear that the uptake/degradatory pathways for homovanillate and vanillate in this organism are entirely separate and independently controlled. If stabilization of the homovanillate demethylase can be achieved, there is potential for exploiting the substrate specificity of this enzyme in both medical diagnosis and in the paper industry.     

Degradation of lawsone by Pseudomonas putida L2

From humus obtained from Stuttgart, a bacterium was isolated with lawsone (2-hydroxy-1,4-naphthoquinone) as selective source of carbon. This bacterium is capable of utilizing lawsone as sole source of carbon and energy. Morphological and physiological characteristics of the bacterium were examined and it was identified as a strain of Pseudomonas putida. The organism is referred to as Pseudomonas putida L2. The degradation of lawsone by Pseudomonas putida L2 was investigated. Salicylic acid and catechol were isolated and identified as metabolites. In lawsone-induced cells of Pseudomonas putida L2, salicylic acid is converted to catechol by salicylate 1-monooxygenase. Catechol 1,2-dioxygenase catalyses ortho-fission of catechol which is then metabolized via the beta-ketoadipate pathway. Formation of cis,cis-muconate and beta-ketoadipate was demonstrated by enzyme assays. Salicylate 1-monooxygenase and catechol 1,2-dioxygenase are induced sequentially. The enzymes of the beta-ketoadipate pathway are also inducible. Naphthoquinone hydroxylase, however, was demonstrated in induced and non-induced cells. This constitutive enzyme enables Pseudomonas putida L2 to degrade various 1,4-naphthoquinones in experiments with resting cells.     

Degradation of Phenanthrene by Mutant Naphthalene-Degrading Pseudomonas putida Strains

Five naphthalene- and salicylate-utilizing Pseudomonas putida strains cultivated for a long time on phenanthrene produced mutants capable of growing on this substrate and 1-hydroxy-2-naphthoate as the sole sources of carbon and energy. The mutants catabolize phenanthrene with the formation of 1-hydroxy-2-naphthoate, 2-hydroxy-1-naphthoate, salicylate, and catechol. The latter products are further metabolized by the meta- and ortho-cleavage pathways. In all five mutants, naphthalene and phenanthrene are utilized with the involvement of plasmid-born genes. The acquired ability of naphthalene-degrading strains to grow on phenanthrene is explained by the fact that the inducible character of the synthesis of naphthalene dioxygenase, the key enzyme of naphthalene and phenanthrene degradation, becomes constitutive.     

Degradation of Ethylbenzene by Pseudomonas putida Harboring OCT Plasmid

We have investigated the utilization of a variety of alkylbenzenes by P. putida strains and found that a strain harboring the OCT plasmid assimilated ethylbenzene. The linkage between the determinant for the degradation of ethylbenzene (Etb⁺ phenotype) and the OCT plasmid was inferred from conjugation experiments. The growth characteristics of the strains carrying mutations in the alk genes of the OCT plasmid which determine the assimilation of /t-alkanes indicated that alkB, alkA, and alkR should be responsible for the degradation of ethylbenzene. The exposure of ethylbenzene to the P. putida strain harboring the CAM-OCT plasmid resulted in the accumulation of β-phenylethyl alcohol. A possible degradation pathway for ethylbenzene including the terminal oxidation of the alkyl side chain was proposed.     

Degradation of 1,4-dichlorobenzene by a Pseudomonas sp

A Pseudomonas species able to degrade p-dichlorobenzene as the sole source of carbon and energy was isolated by selective enrichment from activated sludge. The organism also grew well on chlorobenzene and benzene. Washed cells released chloride in stoichiometric amounts from o-, m-, and p-dichlorobenzene, 2,5-dichlorophenol, 4-chlorophenol, 3-chlorocatechol, 4-chlorocatechol, and 3,6-dichlorocatechol. Initial steps in the pathway for p-dichlorobenzene degradation were determined by isolation of metabolites, simultaneous adaptation studies, and assay of enzymes in cell extracts. Results indicate that p-dichlorobenzene was initially converted by a dioxygenase to 3,6-dichloro-cis-1,2-dihydroxycyclohexa-3,5-diene, which was converted to 3,6-dichlorocatechol by an NAD+-dependent dehydrogenase. Ring cleavage of 3,6-dichlorocatechol was by a 1,2-oxygenase to form 2,5-dichloro-cis, cis-muconate. Enzymes for degradation of haloaromatic compounds were induced in cells grown on chlorobenzene or p-dichlorobenzene, but not in cells grown on benzene, succinate, or yeast extract. Enzymes of the ortho pathway induced in cells grown on benzene did not attack chlorobenzenes or chlorocatechols.     

Degradation of phenol and phenolic compounds by Pseudomonas putida EKII

Summary The phenol-degrading strain Pseudomonas putida EKII was isolated from a soil enrichment culture and utilized phenol up to 10.6 mM (1.0 g·1 ^-1) as the sole source of carbon and energy. Furthermore, cresols, chlorophenols, 3,4-dimethylphenol, and 4-chloro-m-cresol were metabolized as sole substrates by phenol-grown resting cells of strain EKII. Under conditions of cell growth, degradation of these xenobiotics was achieved only in co-metabolism with phenol. Phenol hydroxylase activity was detectable in whole cells but not in cell-free extracts. The specificity of the hydroxylating enzyme was found during transformation of cresols and chlorophenols: ortho- and meta-substituted phenols were degraded via 3-substituted catechols, while degradation of para-substituted phenols proceeded via 4-substituted catechols. In cell-free extracts of phenol-grown cells a high level of catechol 2,3-dioxygenase as well as smaller amounts of 2-hydroxymuconic semialdehyde hydrolyase and catechol 1,2-dioxygenase were detected. The ring-cleaving enzymes were characterized after partial purification by DEAE-cellulose chromatography.     

Degradation of 1,4-dichlorobenzene by a Pseudomonas sp.

A Pseudomonas species able to degrade p-dichlorobenzene as the sole source of carbon and energy was isolated by selective enrichment from activated sludge. The organism also grew well on chlorobenzene and benzene. Washed cells released chloride in stoichiometric amounts from o-, m-, and p-dichlorobenzene, 2,5-dichlorophenol, 4-chlorophenol, 3-chlorocatechol, 4-chlorocatechol, and 3,6-dichlorocatechol. Initial steps in the pathway for p-dichlorobenzene degradation were determined by isolation of metabolites, simultaneous adaptation studies, and assay of enzymes in cell extracts. Results indicate that p-dichlorobenzene was initially converted by a dioxygenase to 3,6-dichloro-cis-1,2-dihydroxycyclohexa-3,5-diene, which was converted to 3,6-dichlorocatechol by an NAD+-dependent dehydrogenase. Ring cleavage of 3,6-dichlorocatechol was by a 1,2-oxygenase to form 2,5-dichloro-cis, cis-muconate. Enzymes for degradation of haloaromatic compounds were induced in cells grown on chlorobenzene or p-dichlorobenzene, but not in cells grown on benzene, succinate, or yeast extract. Enzymes of the ortho pathway induced in cells grown on benzene did not attack chlorobenzenes or chlorocatechols.     

Degradation of caffeine by immobilized cells of Pseudomonas putida strain C 3024

Summary A caffeine-resistant strain of Pseudomonas putida was isolated from soil and was grown with caffeine as the sole source of carbon, energy and nitrogen. Cells were immobilized in agar gel particles which were continuously supplied with a caffeine solution (0.52 g · l^–1, D=1.0 h^–1) in a homogeneously mixed aerated reaction vessel. In the presence of the ATPase inhibitor arsenate the caffeine was removed by the immobilized cells at an average rate of 0.25 mg caffeine · h^–1 · (mg cell carbon)^–1 during 6 days. Thereafter a rapid decline of activity was observed. From a similar system without arsenate supplied with a growth medium containing a limiting amount of caffeine (0.13 g · l^–1) the caffeine was almost completely oxidized by the immobilized cells. The concentration of the remaining caffeine was 1.4 mg · l^–1, which is much lower than the substrate constant for caffeine (9.7 mg · l^–1) observed with freshly harvested suspended resting cells.     

Degradation of nitriles and amides by the immobilized cells of Pseudomonas putida

Pseudomonas putida, capable of utilizing acetonitrile as a sole source of C and N, was immobilized in calcium alginate and the rates of degradation of nitriles, including acetonitrile, and their respective amides were studied. All the organic nitriles and amides tested were converted into NH₃ and CO₂.     

Degradation of 2-chloroethanol by free and immobilized Pseudomonas putida US 2

The degradation of 2-chloroethanol by Pseudomonas putida US 2 was investigated in shaking flasks, air-bubble columns and packed-bed fermenters by free cells, calcium-alginate-entrapped cells and on cells on granular clay adsorbed. Entrapped cells tolerated increasing concentrations of 2-chloroethanol better than free cells. Their maximum degradative activity could be observed at 34°C and pH 7.0. The degradation of 2-chloroethanol leads to a decrease of pH and to a stagnation of mineralization, particularly with free or entrapped cells. Following the stabilization of pH, supplementation with succinate resulted in a complete degradation of higher 2-chloroethanol concentrations. Less 2-chloroethanol was degraded in air-bubble columns and larger amounts in packed-bed fermenters. 2-Chloroethanol was mineralized faster by free or entrapped P. putida US 2 than by adsorbed cells, which, on the other hand, were able to remove higher concentrations of the compound. The results with P. putida US 2 are a good indication that this microorganism could be used in waste-water treatment and soil-decontamination systems.     

Degradation of L-djenkolate catalyzed by S-alkylcysteine alpha,beta-lyase from Pseudomonas putida

S-Alkylcysteine alpha, beta-lyase [EC 4.4.1.6] of Pseudomonas putida catalyzes alpha,beta-elimination of L-djenkolate [3,3'-methylenedithiobis(2-aminopropionic acid)] to produce pyruvate, ammonia, and S-(mercaptomethyl)cysteine initially. Secondly, S-(mercaptomethyl)-cysteine, which was identified in the form of S-(mercaptomethyl)cysteine thiolactone and S-(2-thia-3-carboxypropyl)cysteine in the absence and presence of iodoacetic acid, respectively, is decomposed enzymatically to pyruvate, ammonia, and bis(mercapto)methane, or spontaneously to cysteine, formaldehyde, and hydrogen sulfide. Balance studies showed that 1.3 mol each of pyruvate and ammonia and 0.2 mol each of formaldehyde and cysteine were produced with consumption of 1 mol of L-djenkolate. 1,2,4,5-Tetrathiane, 1,2,4-trithiolane, 1,2,4,6-tetrathiepane, and 1,2,3,5,6-pentathiepane, which are derivatives of bis(mercapto)methane, were also produced during the alpha,beta-elimination of L-djenkolate. In addition, a polymer with the general formula of -(CH2S)n- was produced as a white precipitate. When the alpha,beta-elimination of L-djenkolate was carried out in the presence of 20 mM iodoacetic acid, neither formaldehyde, cysteine, hydrogen sulfide, or the polymer were formed. Instead, the S-carboxymethyl derivatives of bis(mercapto)methane and S-(mercaptomethyl)cysteine were produced in addition to pyruvate and ammonia.     

Degradation of chloronitrobenzenes by a coculture of Pseudomonas putida and a Rhodococcus sp

A single microorganism able to mineralize chloronitrobenzenes (CNBs) has not been reported, and degradation of CNBs by coculture of two microbial strains was attempted. Pseudomonas putida HS12 was first isolated by analogue enrichment culture using nitrobenzene (NB) as the substrate, and this strain was observed to possess a partial reductive pathway for the degradation of NB. From high-performance liquid chromatography-mass spectrometry and 1H nuclear magnetic resonance analyses, NB-grown cells of P. putida HS12 were found to convert 3- and 4-CNBs to the corresponding 5- and 4-chloro-2-hydroxyacetanilides, respectively, by partial reduction and subsequent acetylation. For the degradation of CNBs, Rhodococcus sp. strain HS51, which degrades 4- and 5-chloro-2-hydroxyacetanilides, was isolated and combined with P. putida HS12 to give a coculture. This coculture was confirmed to mineralize 3- and 4-CNBs in the presence of an additional carbon source. A degradation pathway for 3- and 4-CNBs by the two isolated strains was also proposed.     

Degradation of 3-nitrophenol by Pseudomonas putida B2 occurs via 1,2,4-benzenetriol

Growth of Pseudomonas putida B2 in chemostat cultures on a mixture of 3-nitrophenol and glucose induced 3-nitrophenol and 1,2,4-benzenetriol-dependent oxygen uptake activities. Anaerobic incubations of cell suspensions with 3-nitrophenol resulted in complete conversion of the substrate to ammonia and 1,2,4-benzenetriol. This indicates that P. putida B2 degrades 3-nitrophenol via 1,2,4-benzenetriol, via a pathway involving a hydroxylaminolyase. Involvement of this pathway in nitroaromatic metabolism has previously only been found for degradation of 4-nitrobenzoate.Reduction of 3 nitrophenol by cell-free extracts was strictly NADPH-dependent. Attempts to purify the enzymes responsible for 3-nitrophenol metabolism were unsuccessful, because their activities were extremely unstable. 3-Nitrophenol reductase was therefore characterized in cell-free extracts. The enzyme had a sharp pH optimum at pH 7 and a temperature optimum at 25°C. At 30°C, reductase activity was completely destroyed within one hour, while at 0°C, the activity in cell-free extracts was over 100-fold more stable. The K_m values for NADPH and 3-nitrophenol were estimated at 0.17 mM and below 2 M, respectively. The substrate specificity of the reductase activity was very broad: all 17 nitroaromatics tested were reduced by cell-free extracts. However, neither intact cells nor cell-free extracts could convert a set of synthesized hydroxylaminoaromatic compounds to the corresponding catechols and ammonia. Apparently, the hydroxylaminolyase of P. putida B2 has a very narrow substrate specificity, indicating that this organism is not a suitable biocatalyst for the industrial production of catechols from nitroaromatics.     

Degradation of trichloroethylene by toluene dioxygenase in whole-cell studies with Pseudomonas putida F1

Toluene-induced cells of Pseudomonas putida F1 removed trichloroethylene from growth media at a significantly greater initial rate than the methanotroph Methylosinus trichosporium OB3b. With toluene-induced P. putida F1, the initial degradation rate varied linearly with trichloroethylene concentration over the range of 8 to 80 microM (1.05 to 10.5 ppm). At 80 microM (10.5 ppm) trichloroethylene and 30 degrees C, the initial rate was 1.8 nmol/min per mg of total cell protein, but the rate decreased rapidly with time. A series of mutant strains derived from P. putida F1 that are defective in the todC gene, which encodes the oxygenase component of toluene dioxygenase, failed to degrade trichloroethylene and to oxidize indole to indigo. A spontaneous revertant selected from a todC culture regained simultaneously the abilities to oxidize toluene, to form indigo, and to degrade trichloroethylene. The three isomeric dichloroethylenes were degraded by P. putida F1, but tetrachloroethylene, vinyl chloride, and ethylene were not removed from incubation mixtures.     

Degradation of 2-chloroethanol by wild type and mutants of Pseudomonas putida US2

A strain of Pseudomonas putida was isolated that was able to degrade 2-chloroethanol. The degradation proceeded via 2-chloroacetaldehyde and chloroacetate to glycolate. In crude extracts the enzymes for this degradation pathway could be detected. All enzymes proved to be inducible. The dehalogenase that catalyzed the dehalogenation of chloroacetate to glycolate was further characterized. It consisted of a single polypeptide chain with a molecular mass of 28 kDa. After induction the dehalogenase was expressed at a high level. In a mutant resistant to high concentrations of 2-chloroethanol the dehalogenase was no longer expressed. The mechanism of resistance seemed to be due to the inability to convert chloroacetate and export of this compound out of the cell.Non-standard abbreviations CEO 2-chloroethanol - DCPIP 2,6-dichlorophenolindophenol - FPLC fast protein liquid chromatography - PAGE polyacrylamide gelelectrophoresis - PES phenazine ethosulfate - PMS phenazine methosulfate - PQQ pyrroloquinoline quinone     

Molybdenum Involvement in Aerobic Degradation of 2-Furoic Acid by Pseudomonas putida Fu1

An organism identified as Pseudomonas putida was isolated from an enrichment culture with 2-furoic acid as its sole source of carbon and energy. The organism contained a 2-furoyl-coenzyme A (CoA) synthetase to form 2-furoyl-CoA and a 2-furoyl-CoA dehydrogenase to form 5-hydroxy-2-furoyl-CoA as the first two enzymes involved in the degradation. Tungstate, the specific antagonist of molybdate, decreased growth rate and consumption of 2-furoic acid but had no influence on growth with succinate. Correspondingly, the 2-furoyl-CoA dehydrogenase activity decreased when the organism was grown on 2-furoic acid in the presence of increasing amounts of tungstate. The addition of molybdate reversed the negative effect on 2-furoyl-CoA dehydrogenase activity, which points to the involvement of a molybdoenzyme in this reaction. Both enzymes studied were inducible. No plasmid was detected in this organism.