Solid-state 13C nuclear magnetic resonance spectroscopy of simultaneously metabolized acetate and phenol in a soil Pseudomonas sp

A unique global metabolic trait of Pseudomonas bharatica CSV86T: metabolism of aromatics over simple carbon sources and co-metabolism with organic acids

Hierarchical utilization of substrate by microbes (utilization of simple carbon sources prior to complex ones) poses a major limitation to the efficient remediation of aromatic pollutants. Aromatic compounds, being complex and reduced in nature, appear to be a deferred choice as the carbon source in the presence of a plethora of simple organic compounds in the environment. The soil bacterium Pseudomonas bharatica CSV86^T displays a unique carbon source utilization hierarchy. It preferentially utilizes aromatics over glucose and co-metabolizes them with succinate or pyruvate (Basu et al., 2006, Applied and Environmental Microbiology, 72 : 22226-2230). In the present study, the substrate utilization hierarchy for strain CSV86^T was tested for additional simple carbon sources such as glycerol, acetate, and tri-carboxylic acid (TCA) cycle intermediates like α-ketoglutarate and fumarate. When grown on a mixture of aromatics (benzoate or naphthalene) plus glycerol, the strain displayed a diauxic growth profile with significantly high activity of aromatic utilization enzymes (catechol 1,2- or 2,3-dioxygenase, respectively) in the first-log phase. This suggests utilization of aromatics in the first-log phase followed by glycerol in the second-log phase. On a mixture of an aromatic plus organic acid (acetate, α-ketoglutarate or fumarate), the strain displayed a monoauxic growth profile, indicating co-metabolism. Interestingly, the presence of glycerol, acetate, α-ketoglutarate or fumarate does not repress metabolism/utilization of the aromatic. Thus, the substrate utilization hierarchy of strain CSV86^T is aromatics=organic acids>glucose/glycerol, which is unique as compared to other Pseudomonas species, where degradation of aromatics is repressed by glycerol, glucose, acetate or organic acids, including TCA cycle intermediates. This novel substrate utilization hierarchy appears to be a global metabolic phenomenon in strain CSV86^T, thus implying it to be an ideal host for metabolic engineering as well as for its potential application in bioremediation.

Characterization of a Pseudomonas sp. Capable of Aniline Degradation in the Presence of Secondary Carbon Sources

Pseudomonas strain K1 is a gram-negative rod which grows aerobically on minimal media containing aniline with a doubling time of 2 h at 30 degrees C. The half-saturation parameter for aniline metabolism by aniline-grown cells was 3.8 mumol . liter. Concentrations of aniline as low as 50 nM were metabolized. Neither substituted anilines nor other aromatic compounds (other than aromatic amino acids) supported growth. Cells grew as fast on aniline as on nonaromatic substrates such as lactate. The aromatic ring was cleaved via the meta pathway. Catechol 2,3-oxygenase activity was induced by aniline, even in cultures containing alternative carbon sources such as lactate. Cultures grown on a mixture of aniline and lactate mineralized aniline in the presence of the second substrate. Lactate-grown cultures lacked catechol oxygenase activity, and resting cells from these cultures did not respire aniline. Resting cells from aniline-grown cultures exhibited high respiratory activity upon the addition of aniline or catechol, some activity with toluidine, and no activity after addition of a wide variety of other aromatic compounds, including dihydroxybenzylamine, chloroanilines, ethylanilines, aminophenols, aminobenzoates, and dihydroxybenzoates. Although substituted anilines were not metabolized, 3-or 4-chloroaniline did induce the enzymes for aniline oxidation.

Catabolism of 2,4,6-trinitrotoluene by Mycobacterium vaccae

Mycobacterium vaccae strain JOB-5 cometabolized 2,4,6-trinitrotoluene (TNT) in the presence of propane as a carbon and energy source. Two novel oxidized metabolites, as well as several known reduced products, were generated during catabolism of TNT by M. vaccae. During the cometabolic process, there was transient production of a brown chromophore. This compound was identified as 4-amino-2,6-dinitrobenzoic acid. When M. vaccae was incubated with [14C]TNT and propane, 50% of the added radiolabel was incorporated into the cellular lipid fraction. These results suggest that ring cleavage occurred prior to the incorporation of radiolabelled carbon into phosphatidyl-L-serine, phosphatidylethanolamine, cardiolipin, and other polar lipids.

Effects of co-occurring aromatic hydrocarbons on degradation of individual polycyclic aromatic hydrocarbons in marine sediment slurries

Rates of polycyclic aromatic hydrocarbon (PAH) degradation and mineralization were influenced by preexposure to alternate PAHs and a monoaromatic hydrocarbon at relatively high (100 ppm) concentrations in organic-rich aerobic marine sediments. Prior exposure to three PAHs and benzene resulted in enhanced [14C]naphthalene mineralization, while [14C]anthracene mineralization was stimulated only by benzene and anthracene preexposure. Preexposure of sediment slurries to phenanthrene stimulated the initial degradation of anthracene. Prior exposure to naphthalene stimulated the initial degradation of phenanthrene but had no effect on either the initial degradation or mineralization of anthracene. For those compounds which stimulated [14C]anthracene or [14C]naphthalene mineralization, longer preexposures (2 weeks) to alternative aromatic hydrocarbons resulted in an even greater stimulation response. Enrichment with individual PAHs followed by subsequent incubation with one or two PAHs showed no alteration in degradation patterns due to the simultaneous presence of PAHs. The evidence suggests that exposure of marine sediments to a particular PAH or benzene results in the enhanced ability of these sediments to subsequently degrade that PAH as well as certain other PAHs. The enhanced degradation of a particular PAH after sediments have been exposed to it may result from the selection and proliferation of specific microbial populations capable of degrading it. The enhanced degradation of other PAHs after exposure to a single PAH suggests that the populations selected have either broad specificity for PAHs, common pathways of PAH degradation, or both.