The degradation of cholic acid by Pseudomonas sp. N.C.I.B. 10590.

The microbial degradation of cholic acid by Pseudomonas sp. N.C.I.B. 10590 was studied, and two major products were isolated and identified as 7 alpha, 12 beta-dihydroxyandrosta-1,4-diene-3,17-dione and 7 alpha, 12 alpha-dihydroxy-3-oxopregna-1,4-diene-20-carboxylic acid. Four minor products were isolated and evidence is given for the following structures: 7 alpha, 12 alpha-dihydroxyandrosta-1,4-diene-3,17-dione, 12 beta-hydroxyandrosta-1,4,6-triene-3,17-dione, 7 alpha, 12 beta, 17 beta-trihydroxyandrosta-1,4-dien-3-one and 7 alpha, 12 alpha-dihydroxy-3-oxopregn-4-ene-20-carboxylic acid. The significance of the production of the steroid products is discussed, along with the possible enzymic mechanisms responsible for their production.     

The biotransformation of hyodeoxycholic acid by Pseudomonas sp. NCIB 10590 under anaerobic conditions

The bacterial degradation of hyodeoxycholic acid under anaerobic conditions was studied. The major acidic product has been identified as 6 alpha-hydroxy-3-oxochol-4-ene-24-oic acid whilst the major neutral product has been identified as 6 alpha-hydroxyandrosta-1,4-diene-3,17-dione. The minor acidic products were 3,6-dioxochola-1,4-diene-24-oic acid, 3-oxochol-5-ene-24-oic acid, 3-oxochol-4-ene-24-oic acid, 3-oxochola-1,4-diene-24-oic acid and 6 alpha-hydroxy-3-oxochola-1,4-diene-24-oic acid and the minor neutral products were androst-4-ene-3,17-dione, androst-4-ene-3,6,17-trione, androsta-1,4-diene-3,6,17-trione, androsta-1,4-diene-3,17-dione, 17 beta-hydroxyandrosta-1,4-diene-3-one and 6 alpha-hydroxyandrost-4-ene-3,17-dione. Evidence is presented which suggests that under aerobic conditions, one pathway of hyodeoxycholic acid metabolism exists whilst under anaerobic conditions an extra biotransformation pathway becomes operative involving the induction of a 6 alpha-dehydroxylase enzyme. A biochemical pathway of hyodeoxycholic acid metabolism by bacteria under anaerobic conditions is discussed incorporating a scheme involving such an enzyme.     

The degradation of beta-sitosterol by Pseudomonas sp. NCIB 10590 under aerobic conditions

The bacterial degradation of beta-sitosterol by Pseudomonas sp NCIB 10590 has been studied. Major biotransformation products included 24-ethylcholest-4-en-3-one, androsta-1,4-diene-3,17-dione, 3-oxochol-4-en-3-one-24-oic acid and 3-oxopregn-4-en-3-one-20-carboxylic acid. Minor products identified were 26-hydroxy-24-ethylcholest-4-en-3-one, androst-4-ene-3,17-dione, 3-oxo-24-ethylcholest-4-en-26-oic acid, 3-oxochola-1,4-dien-3-one-24-oic acid, 3-oxopregna-1,4-dien-3-one-20 carboxylic acid and 9 alpha-hydroxyandrosta-1,4-diene-3,17-dione. Studies with selected inhibitors have enabled the elucidation of a comprehensive pathway of beta-sitosterol degradation by bacteria.     

Nitrate-dependent salicylate degradation by Pseudomonas butanovora under anaerobic conditions

Nitrate-dependent salicylate degradation by the denitrifying Pseudomonas butanovora was investigated and the molar ratio of the cometabolism under anaerobic circumstances was determined. The bacterium was able to utilize salicylate as an electron donor for the reduction of nitrate. Salicylate was eliminated via catechol, which is degraded by means of catechol 2,3-oxygenases (meta-cleavage), forming 2-hydroxymuconic semialdehyde. The molar ratios of NO(3)(-)-N:salicylate existing during the experiment accorded well with the assumed 1:1 molar ratio. The tolerances of the growth, the salicylate degradation and the denitrification of P. butanovora to various heavy metal ions were also studied. Although the strain was tolerant to Pb(2+) and Cu(2+) up to 1 mM in complete medium, salicylate utilization took place only up to a concentration of 0.1 mM for both heavy metal ions. Of the heavy metal ions investigated, Cd(2+) (at a concentration of 0.05 mM) displayed the highest inhibitory effect on salicylate degradation by P. butanovora.     

The metabolism of cyclopentanol by Pseudomonas N.C.I.B. 9872

1. Pseudomonas N.C.I.B. 9872 grown on cyclopentanol as carbon source oxidized it at a rate of 228mul of O(2)/h per mg dry wt. and the overall consumption of 5.9mumol of O(2)/mumol of substrate. Cyclopentanone was oxidized at a similar rate with the overall consumption of 5.2mumol of O(2)mumol of substrate. Cells grown with sodium acetate as sole source of carbon were incapable of significant immediate oxidation of these two substrates. 2. Disrupted cells catalysed the oxidation of cyclopentanol to cyclopentanone by the action of an NAD(+)-linked dehydrogenase with an alkaline pH optimum. 3. A cyclopentanolinduced cyclopentanone oxygenase (specific activity 0.11mumol of NADPH oxidized/min per mg of protein) catalysed the consumption of 1mumol of NADPH and 0.9mumol of O(2) in the presence of 1mumol of cyclopentanone. NADPH oxidation did not occur under anaerobic conditions. The only detectable reaction product with 100000g supernatant was 5-hydroxyvalerate. 4. Extracts of cyclopentanol-grown cells contained a lactone hydrolase (specific activity 7.0mumol hydrolysed/min per mg of protein) that converted 5-valerolactone into 5-hydroxyvalerate. 5. Cyclopentanone oxygenase fractions obtained from a DEAE-cellulose column were almost devoid of 5-valerolactone hydrolase and catalysed the formation of 5-valerolactone in high yield from cyclopentanone in the presence of NADPH. 6. Incubation of 5-hydroxyvalerate with the 100000g supernatant, NAD(+) and NADP(+) under aerobic conditions resulted in the consumption of O(2) and the conversion of 5-hydroxyvalerate into glutarate. 7. The high activity of isocitrate lyase in cyclopentanol-grown cells suggests that the further oxidation of glutarate proceeds through as yet uncharacterized reactions to acetyl-CoA. 8. The reaction sequence for the oxidation of cyclopentanol by Pseudomonas N.C.I.B. 9872 is: cyclopentanol --> cyclopentanone --> 5-valerolactone --> 5-hydroxyvalerate --> glutarate --> --> acetyl-CoA.     

Bioconversion of Lithocholic Acid Under Anaerobic Conditions by Pseudomonas sp. Strain NCIB 10590

The biotransformation of lithocholic acid by Pseudomonas sp. strain NCIB 10590 under anaerobic conditions was studied. The major products were identified as androsta-1,4-diene-3,17-dione and 3-oxochol-4-ene-24-oic acid. The minor products included 17β-hydroxyandrost-4-ene-3-one, 17β-hydroxyandrosta-1,4-diene-3-one, 3-oxo-5β-cholan-24-oic acid, 3-oxochola-1,4-diene-24-oic acid, 3-oxopregn-4-ene-20-carboxylic acid, and 3-oxopregna-1,4-diene-20-carboxylic acid. Anaerobiosis increases the number of metabolites produced by Pseudomonas sp. NCIB 10590 from lithocholic acid.     

Promotion of polylactide degradation by ammonia under hyperthermophilic anaerobic conditions

The objective of this study was to evaluate the promotion effect of ammonia on the biodegradation of polylactide (PLA) under hyperthermophilic (80 °C) and thermophilic (55 °C) anaerobic condition. The results showed that PLA was transformed to lactic acid under hyperthermophilic conditions, but that the transformation ratio was negligible under thermophilic conditions. The hydrolysis process can be markedly increased with ammonia addition and microorganism activity. The maximum transformation ratios of the two kinds of PLA used in this study were 65.2% and 51.8%, respectively, with ammonia addition of 4 g N/L over 3 days treatment of anaerobic sludge. After the hyperthermophilic pretreatment, the hydrolysis products were converted to methane by methanogens under the thermophilic and anaerobic conditions. The final methane conversion ratios of the two kinds of PLA after 22 days treatment were 81.8% and 77.0%, respectively.     

Siderophore production by Pseudomonas stutzeri under aerobic and anaerobic conditions

The siderophore production of the facultative anaerobe Pseudomonas stutzeri, strain CCUG 36651, grown under both aerobic and anaerobic conditions, was investigated by liquid chromatography and mass spectrometry. The bacterial strain has been isolated at a 626-m depth at the Äspö Hard Rock Laboratory, where experiments concerning the geological disposal of nuclear waste are performed. In bacterial culture extracts, the iron in the siderophore complexes was replaced by gallium to facilitate siderophore identification by mass spectrometry. P. stutzeri was shown to produce ferrioxamine E (nocardamine) as the main siderophore together with ferrioxamine G and two cyclic ferrioxamines having molecular masses 14 and 28 atomic mass units lower than that of ferrioxamine E, suggested to be ferrioxamine D₂ and ferrioxamine X₁, respectively. In contrast, no siderophores were observed from anaerobically grown P. stutzeri. None of the siderophores produced by aerobically grown P. stutzeri were found in anaerobic natural water samples from the Äspö Hard Rock Laboratory.In order to facilitate iron(III) acquisition, plants and microorganisms, such as fungi and bacteria, produce and excrete strong iron(III) chelators, i.e., siderophores (18, 22, 23, 33, 34). While fungal siderophores bind to iron(III) by hydroxamate ligands, bacterial siderophores are more structurally diverse, and common ligands are catecholates, hydroxamates, and carboxylates (21). The iron(III) stability constants for bacterial siderophores vary in the range of 10²⁰ to 10⁵² (6). In addition to iron(III), other metals can be complexed by siderophores. For the trihydroxamate siderophore desferrioxamine B, sometimes called proferrioxamine B (10), some actinides have been shown to have stability constants in the same range as the ferric stability constant (10^30.6), e.g., 10^26.6 with thorium(IV) and 10^30.8 with plutonium(VI) (32), while the stability constant for uranium(VI) was lower, i.e., 10¹⁸ (2).Concerning bacteria, there are several reports on siderophore production by Pseudomonas spp. (1, 3, 4, 19). More than 50 structurally related siderophores, i.e., pyoverdins, produced by the fluorescent Pseudomonas spp., especially Pseudomonas fluorescens and Pseudomonas aeruginosa, have been characterized (3). All pyoverdins emit yellow fluorescent light due to the presence of a 5-amino-2,3-dihydro-8,9-dihydroxy-1-H-pyrimido-quinoline-carboxylic chromophore, to which a peptide chain and a carboxyl chain are attached (1, 3). Nonfluorescent Pseudomonas has also been shown to produce siderophores, such as ferrioxamine E, also called nocardamine (Fig. ​(Fig.1),1), which was produced by one strain of Pseudomonas stutzeri (19). In addition to ferrioxamines, the P. stutzeri strain KC produced a smaller siderophore, i.e., pyridine-2,6-bis(thiocarboxylic acid) (35). Conversely, a catecholate-type siderophore was shown to be produced by another strain of P. stutzeri, which did not produce any hydroxamate siderophores (4).Open in a separate windowFIG. 1.Structures, molecular masses (mw), and stability constants (K_s) of ferric complexes of the three ferrioxamines: ferrioxamine B (B), ferrioxamine E (E), and ferrioxamine G (G) (5, 18).Most of the studies on bacterial siderophore production have been conducted on microorganisms growing under aerobic conditions. One field-based report, however, indicates the occurrence of putative siderophores in anaerobic environments also (29). In the present study, siderophore production has been studied with both aerobic and anaerobic cultures of P. stutzeri. This species is a facultative aerobe, able to grow with oxygen or nitrate as the electron acceptor, meaning that it can be active under both anaerobic and aerobic conditions. The P. stutzeri strain CCUG 36651, studied here, has been isolated from a depth of 626 m below ground at the Äspö Hard Rock Laboratory (16), where research concerning the geological disposal of nuclear waste is performed. The possibility of mobilizing radionuclides by complexing compounds from bacteria is an important research area in the context of nuclear waste disposal research. It is unknown if such compounds are produced in aquifers under conditions relevant to a disposal site, which would be approximately 500 m underground in granitic rock (27).A study from 2004 shows that P. stutzeri growing aerobically in the presence of uranium-containing shale leached Fe, Mo, V, and Cr from the shale material (17). More recently it was shown that the supernatant of aerobically and anaerobically cultured P. stutzeri was able to increase the partitioning of added Fe, Pm, Am, and Th into the aqueous phase in samples where quartz sand was used as a solid surface (16). Aerobic supernatants maintained 60% or more of the added metals in solution, while anaerobic supernatants were best at maintaining Am in solution, reaching a value of 40% in solution. The increased partitioning to the aqueous phase in the presence of the supernatants was ascribed to the production of organic ligands. Supernatants of both aerobically and anaerobically grown P. stutzeri strain CCUG 36651 yielded a positive response on the universal siderophore assay, the CAS assay (16). This assay is based on ligand competition for iron bound to the colored chrome azurol complex (25, 30).In this study, siderophore production by P. stutzeri strain CCUG 36651 was investigated using mass spectrometry (MS) and liquid chromatography (LC) followed by mass spectrometric detection. Electrospray ionization mass spectrometry (ESI-MS) and electrospray ionization tandem mass spectrometry (ESI-MS/MS) are useful tools in characterizing siderophores such as ferrioxamines (10, 13, 14, 28, 31). In order to detect iron(III)-chelating compounds, the ferric iron can be replaced by gallium(III) through ascorbate-mediated reduction of iron(III) (8, 20). In mass spectra, gallium-bound substances are easily recognized due to the characteristic isotope pattern of gallium, where the intensity of the ⁷¹Ga signal is about 66% of that of the ⁶⁹Ga signal. The use of ESI provides so-called soft ionization; thus, information about the molecular weight is obtained. However, by employing MS/MS, fragmentation is achieved, providing more information about the compound structure.In order to verify the chemical difference between the siderophores found by ESI-MS, chromatographic separation was performed. In this case, one reversed-phase C₁₈ column and one column containing a porous graphitic carbon (PGC) stationary phase were used. The separation mechanism of PGC is a combination of hydrophobic interactions, as in C₁₈, and electrostatic interactions between π-electrons. In order to detect substances at low concentrations, column-switched capillary chromatography with MS detection was used. The detection limits of the combined LC-MS/MS system used in this study are in the range of 1 to 5 nM for hydroxamate siderophores of the ferrichrome and ferrioxamine families (9). In order to facilitate analysis of lower concentrations of ferrioxamines, natural water samples were preconcentrated by solid-phase extraction (SPE), resulting in minimum detectable concentrations in the range of 0.02 to 0.1 nM, depending on the initial sample volume.     

Deoxycholic acid degradation by a Pseudomonas sp. Acidic intermediates with A-ring unsaturation.

The microbial catabolism of deoxycholic acid by a Pseudomonas sp. was studied, and six further acidic intermediates were isolated, as their methyl esters. Evidence is presented that the compounds are methyl 12 alpha-hydroxy-3-oxochol-4-en-24-oate, methyl 12 alpha-hydroxy-3-oxo-23,24-dinorchol-4-en-22-oate, methyl 12 alpha-hydroxy-3-oxochola-1,4-dien-24-oate, methyl 12 alpha-hydroxy-3-oxo-23,24-dinorchola-1,4-dien-22-oate, methyl 12 alpha-hydroxy-3-oxochola-1,4,22E-trien-24-oate and methyl 12 alpha-hydroxy-3-oxo-23,24-dinorchola-1,4,17(20)-trien-22-oate. On the basis of these compounds, together with the seven intermediates previously reported, a catabolic pathway is proposed.     

Transformation of carbon tetrachloride by Pseudomonas sp. strain KC under denitrification conditions.

A denitrifying Pseudomonas sp. (strain KC) capable of transforming carbon tetrachloride (CT) was isolated from groundwater aquifer solids. Major products of the transformation of 14C-labeled CT by Pseudomonas strain KC under denitrification conditions were 14CO2 and an unidentified water-soluble fraction. Little or no chloroform was produced. Addition of dissolved trace metals, notably, ferrous iron and cobalt, to the growth medium appeared to enhance growth of Pseudomonas strain KC while inhibiting transformation of CT. It is hypothesized that transformation of CT by this organism is associated with the mechanism of trace-metal scavenging.     

Transformation of carbon tetrachloride by Pseudomonas sp. strain KC under denitrification conditions

A denitrifying Pseudomonas sp. (strain KC) capable of transforming carbon tetrachloride (CT) was isolated from groundwater aquifer solids. Major products of the transformation of 14C-labeled CT by Pseudomonas strain KC under denitrification conditions were 14CO2 and an unidentified water-soluble fraction. Little or no chloroform was produced. Addition of dissolved trace metals, notably, ferrous iron and cobalt, to the growth medium appeared to enhance growth of Pseudomonas strain KC while inhibiting transformation of CT. It is hypothesized that transformation of CT by this organism is associated with the mechanism of trace-metal scavenging.     

Microbial metabolism of amino alcohols. Aminoacetone metabolism via 1-aminopropan-2-ol in Pseudomonas sp. N.C.I.B. 8858

1. Pseudomonas sp. N.C.I.B. 8858 grew well on d- and l-1-aminopropan-2-ol and on aminoacetone. 2. Cell-free extracts possessed high activities of inducibly formed l-1-aminopropan-2-ol-NAD(+) oxidoreductase, amino alcohol-ATP phosphotransferase, dl-1-aminopropan-2-ol O-phosphate phospho-lyase and aldehyde-NAD(+) oxidoreductase, but no 1-aminopropan-2-ol racemase or d-1-aminopropan-2-ol-NAD(+) oxidoreductase. 3. The amino alcohol kinase (activated by ADP) was non-stereospecific towards 1-aminopropan-2-ol and was one-third as active with ethanolamine. The phospho-lyase was active with l- and d-1-aminopropan-2-ol O-phosphate, but ethanolamine O-phosphate was only one-tenth as active as its higher homologues. The purified aldehyde dehydrogenase was active with propionaldehyde, acetaldehyde and also with methylglyoxal. The previously observed 2-oxo aldehyde dehydrogenase activity was considered to be due to the broadly specific aldehyde dehydrogenase. 4. Mutants of Pseudomonas sp. N.C.I.B. 8858 deficient in 1-aminopropan-2-ol kinase, 1-aminopropan-2-ol O-phosphate phospho-lyase, aldehyde dehydrogenase or an enzyme involved in propionate metabolism were incapable of growth on aminoacetone or 1-aminopropan-2-ol as carbon source, although all except the kinase- or phospho-lyasedeficient mutants could use these compounds and ethanolamine as nitrogen sources. The aldehyde dehydrogenase-deficient mutants produced copious amounts of propionaldehyde and acetaldehyde during growth on the corresponding amino alcohols. 5. The path of aminoacetone metabolism in Pseudomonas sp. N.C.I.B. 8858 was concluded to involve l-1-aminopropan-2-ol, the O-phosphate ester of this compound, propionaldehyde and propionate as obligatory intermediates. d-1-Aminopropan-2-ol was metabolized by the same route as the l-isomer, gratuitously inducing formation of the stereospecific l-1-aminopropan-2-ol dehydrogenase. 6. Extracts of the pseudomonad grown with ethanolamine as the nitrogen source were devoid of 1-aminopropan-2-ol dehydrogenase, the kinase and the phospho-lyase, but exhibited cobamide coenzyme-dependent deaminase activity. Mutants deficient in kinase or phospho-lyase (deaminating) grew well on ethanolamine as the nitrogen source. Ethanolamine deaminase was inactive with, but inhibited by, 1-aminopropan-2-ol.