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At least 19 recordsLinked to original sources
PubMed1996

Simultaneous spectrophotometric determination of o-cresol and m-cresol in urine by use of the kinetic wavelength-pair method.

The kinetic wavelength-pair method was applied to the simultaneous determination of o-cresol and m-cresol, based on their oxidative coupling with aniline in the presence of hypochlorite as oxidant and nitroprusside as catalyst. The benzoquinoneanils produced exhibited severe spectral overlap. Resolution of this isomer mixture by using discrete wavelengths was subject to a high degree of error for the determination of m-cresol since the ratios vo-cresol/vm-cresol (where v denotes initial rate for the oxidative coupling reaction) and epsilon o-cresol/epsilon m-cresol (where epsilon is the absorptivity of reaction products) were greater than unity at any given wavelength. Selectivity in the resolution was achieved by measuring the initial rate difference at the wavelength pair 666-566 nm where the contribution of o-cresol was removed, o-Cresol and m-cresol were simultaneously determined at mass ratios between 5:1 and 1:5 at concentrations from 1 to 5 micrograms ml-1, with relative standard deviations of less than 3%. The proposed method was applied to the determination of o-cresol and m-cresol in urine samples, with analytical recoveries ranging between 95 and 105%.

Aniline Compounds↗
PubMed1990

Gas chromatographic determination of cresols in the biological fluids of a non-fatal case of cresol intoxication.

A simple and rapid method for analysis of free and conjugated cresols in biological fluids was developed. Prior to and following freeing of the conjugated cresols by acid hydrolysis in a sealed ampoule, free cresols were extracted by Extrelut column extraction, determined by gas chromatography, and confirmed by gas chromatography-mass spectrometry. In a non-fatal case of cresol intoxication a 46-year-old male had ingested about 100 ml of a saponated cresol soap solution. The concentrations of xylenol (2,4- and/or 2,5-dimethylphenol) and p- and m-cresol in the serum sample collected on admission were 15.8 micrograms/g, 43.3 micrograms/g and 73.8 micrograms/g, respectively. The total cresol concentration of 117 micrograms/g in the serum is within the range of fatal concentrations, and it is suspected therefore that the patient's recovery was due to adequate therapy alone.

Chromatography, Gas↗
PubMed1975

Pathways for the degradation of m-cresol and p-cresol by Pseudomonas putida.

A comparison of the oxidation rates of various compounds by whole cells of Pseudomonas putida 3, 5 indicated that m-cresol is metabolized by oxidation to 3-hydroxybenzoate followed by hydroxylation to gentisate, the ring-fission substrate, when grown with 3, 5-xylenol. However, when m-cresol was the growth substrate, similar experiments suggested a different pathway involving a methyl-substituted catechol, and ring-fission by meta cleavage. Assays of ring-fission enzymes in cell-free extracts confirmed that different pathways are induced by the two growth substrates. 3, 5-Xylenol-grown cells contained high levels of gentisate oxygenase and only very small amounts of catechol oxygenase, whereas gentisate ocygenase could not be detected in m-cresol-grown cells, but levels of catechol oxygenase were greatly increased. Extracts of m-cresol-grown cells also contained 2-hydroxymuconic semialdehyde dehydrogenase and hydrolase, whose specificities enable them to metabolize the ring-fission products from catechol, 3-methylcatechol, and 4-methylcatechol. This catechol pathway is also used by m-cresol-grown cells for p-cresol metabolism. In contrast, the results for cells grown with p-cresol point to an alternative pathway involving oxidation to 4-hydroxybenzoate and hydrosylation to protocatechuate as ring-fission substrate. Extracts of these cells contained high levels of protocatechuate oxygenase and only small amounts of catechol oxygenase.

Adipates↗
PubMed1991

p-cresol methylhydroxylase from a denitrifying bacterium involved in anaerobic degradation of p-cresol.

A bacterium, strain PC-07, previously isolated as part of a coculture capable of growing on p-cresol under anaerobic conditions with nitrate as the acceptor was identified as an Achromobacter sp. The first enzyme of the pathway, p-cresol methylhydroxylase, which converts its substrate into p-hydroxybenzyl alcohol, was purified. The enzyme had an Mr of 130,000 and the spectrum of a flavocytochrome. It was composed of flavoprotein subunits of Mr 54,000 and cytochrome subunits of Mr 12,500. The midpoint redox potential of the cytochrome was 232 mV. The Km and kcat for p-cresol were 21 microM and 112 s-1 respectively, and the Km for phenazine methosulfate, the artificial acceptor used in the assays, was determined to be 1.7 mM. These properties place the enzyme in the same class as the p-cresol methylhydroxylases from aerobically isolated Pseudomonas spp.

Alcaligenes↗
PubMed1993

Biodegradation of ortho-cresol by a mixed culture of nitrate-reducing bacteria growing on toluene.

A mixed culture of nitrate-reducing bacteria degraded o-cresol in the presence of toulene as a primary growth substrate. No degradation of o-cresol was observed in the absence of toluene or when the culture grew on p-cresol and 2,4-dimethylphenol. In batch cultures, the degradation of o-cresol started after toluene was degraded to below 0.5 to 1.0 mg/liter but continued only for about 3 to 5 days after the depletion of toluene since the culture had a limited capacity for o-cresol degradation once toluene was depleted. The total amount of o-cresol degraded was proportional to the amount of toluene metabolized, with an average yield of 0.47 mg of o-cresol degraded per mg of toluene metabolized. Experiments with [ring-U-14C]o-cresol indicated that about 73% of the carbon from degraded o-cresol was mineralized to CO2 and about 23% was assimilated into biomass after the transient accumulation of unidentified water-soluble intermediates. A mathematical model based on a simplified Monod equation is used to describe the kinetics of o-cresol degradation. In this model, the biomass activity toward o-cresol is assumed to decay according to first-order kinetics once toluene is depleted. On the basis of nonlinear regression of the data, the maximum specific rate of o-cresol degradation was estimated to be 0.4 mg of o-cresol per mg of biomass protein per h, and the first-order decay constant for o-cresol-degrading biomass activity was estimated to be 0.15 h-1.(ABSTRACT TRUNCATED AT 250 WORDS)

Biodegradation, Environmental↗
PubMed1991

Anaerobic degradation of cresols by denitrifying bacteria.

The initial reactions in anaerobic metabolism of methylphenols (cresols) and dimethylphenols were studied with denitrifying bacteria. A newly isolated strain, possibly a Paracoccus sp., was able to grow on o- or p-cresol as sole organic substrate with a generation time of 11 h; o- or p-cresol was completely oxidized to CO2 with nitrate being reduced to N2. A denitrifying Pseudomonas-like strain oxidized m- or -p-cresol as the sole organic growth substrate completely to CO2 with a generation time of 14 h. Demonstration of intermediates and/or in vitro measurement of enzyme activities suggest the following enzymatic steps: (1) p-Cresol was metabolized by both strains via benzoyl-CoA as central intermediate as follows: p-cresol----4-OH-benzaldehyde----4-OH-benzoate----4-OH-benzoyl-CoA----be nzoyl-CoA. Oxidation of the methyl group to 4-OH-benzaldehyde was catalyzed by p-cresol methylhydroxylase. After oxidation of the aldehyde to 4-OH-benzoate, 4-OH-benzoyl-CoA is formed by 4-OH-benzoyl-CoA synthetase; subsequent reductive dehydroxylation of 4-OH-benzoyl-CoA to benzoyl-CoA is catalyzed by 4-OH-benzoyl-CoA reductase (dehydroxylating). (2) o-Cresol was metabolized in the Paracoccus-like strain via 3-CH3-benzoyl-CoA as central intermediate as follows: o-cresol----4-OH-3-CH3-benzoate----4-OH-3-CH3-benzoyl-CoA----3-CH3-benzo yl-CoA. The following enzymes were demonstrated: (a) An enzyme catalyzing an isototope exchange reaction between 14CO2 and the carboxyl of 4-OH-3-CH3-benzoate; this activity is thought to be a partial reaction catalyzed by an o-cresol carboxylase. (b) 4-OH-3-CH3-benzoyl-CoA synthetase (AMP-forming) activating the carboxylation product 4-OH-3-CH3-benzoate to its coenzyme A thioester. (c) 4-OH-3-CH3-benzoyl-CoA reductase (dehydroxylating) catalyzing the reductive dehydroxylation of the 4-hydroxyl group with reduced benzyl viologen as electron donor to yield 3-CH3-benzoyl-CoA. This thioester may also be formed by action of a coenzyme A ligase when 3-CH3-benzoate is metabolized. 2,4-Dimethylphenol was metabolized via 4-OH-3-CH3-benzoate and further to 3-CH3-benzoyl-CoA. (3) The initial reactions of anaerobic metabolism of m-cresol in the Pseudomonas-like strain were not resolved. No indication for the oxidation of the methyl group nor for the carboxylation of m-cresol was found. In contrast, 2,4- and 3,4-dimethylphenol were oxidized to 4-OH-3-CH3- and 4-OH-2-CH3-benzoate, respectively, probably initiated by p-cresol methylhydroxylase; however, these compounds were not metabolized further.

Anaerobiosis↗
PubMed1987

Biodegradation of cresol isomers in anoxic aquifers.

The biodegradation of o-, m-, and p-cresol was examined in material obtained from a shallow anaerobic alluvial sand aquifer. The cresol isomers were preferentially metabolized, with p-cresol being the most easily degraded. m-Cresol was more persistent than the para-isomer, and o-cresol persisted for over 90 days. Biodegradation of cresol isomers was favored under sulfate-reducing conditions (SRC) compared with that under methanogenic conditions (MC). Slurries that were acclimated to p-cresol metabolism transformed this substrate at 18 and 330 nmol/h per g (dry weight) for MC and SRC, respectively. Inhibition of electron flow to sulfate reduction with 2.0 mM molybdate reduced p-cresol metabolism in incubations containing sulfate. When methanogenesis was blocked with 5 mM bromoethanesulfonic acid in incubations lacking sulfate, p-cresol catabolism was retarded. Under SRC 3.4 mol of sulfate was consumed per mol of p-cresol metabolized. The addition of sulfate to methanogenic incubations stimulated p-cresol degradation. Simultaneous adaptation studies in combination with spectrophotometric and chromatographic analysis of metabolites indicated that p-cresol was oxidized under SRC to p-hydroxybenzoate via the corresponding alcohol and aldehyde. This series of reactions was inhibited under sulfate-limited or aerobic conditions. Therefore, the primary catabolic event for p-cresol decomposition under SRC appears to involve the hydroxylation of the aryl methyl group.

Anaerobiosis↗
PubMed1994

Cresol isomers: comparison of toxic potency in rat liver slices.

A comparison of the toxicity of cresol isomers (o-, m-, and p-methylphenol) was carried out using precision-cut rat liver slices as a test system. At equimolar concentrations p-cresol was the most toxic isomer. A 5- to 10-fold higher concentration of either the o- or m-isomers was required to observe the same degree of cell killing as p-cresol. The toxicity of p-cresol was inhibited by the thiol precursor N-acetylcysteine and was enhanced by pretreatment of liver slices with diethyl maleate to deplete glutathione. These treatments, however, had little effect on either o- or m-cresol toxicity. p-Cresol rapidly depleted intracellular glutathione levels, while the o- and m-isomers depleted glutathione to a lesser extent. [14C]p-cresol was metabolized to a reactive intermediate which covalently bound to slice protein and was inhibited by N-acetylcysteine. In microsomal incubations covalent binding of [14C]p-cresol metabolites was also observed. This binding was inhibited by glutathione and resulted in the formation of a glutathione conjugate. In the absence of glutathione, p-hydroxybenzyl alcohol was the major microsomal metabolite formed from p-cresol, but this compound was not toxic to liver slices at a concentration of 2 mM. These results demonstrate that p-cresol is the most toxic cresol isomer in rat liver tissue and that its toxicity is dependent on the formation of a reactive intermediate. The results also suggest that the mechanism(s) of toxicity of the o- and m-isomers may differ from that of p-cresol.

Acetylcysteine↗
PubMed1973

Metabolism of phenol and cresols by mutants of Pseudomonas putida.

Mutant strains of Pseudomonas putida strain U have been obtained which are deficient in enzymes of the degradative pathways of phenol and cresols. Mutant strains deficient in catechol 2, 3-oxygenase accumulated the appropriate catechol derivative from cresols. A mutant strain which would not grow on either phenol or a cresol was shown to be deficient in both 2-hydroxymuconic semialdehyde hydrolase and a nicotinamide adenine dinucleotide, oxidized form, (NAD(+))-dependent aldehyde dehydrogenase. When this strain was grown in the presence of phenol or a cresol, the appropriate product of meta fission of these compounds accumulated in the growth medium. A partial revertant of this mutant strain, which was able to grow on ortho- and meta-cresol but not para-cresol, was shown to have regained only the hydrolase activity. This strain was used to show that the products of meta ring fission of the cresols and phenol are metabolized as follows: (i) ortho- and meta-cresol exclusively by a hydrolase; (ii) para-cresol exclusively by a NAD(+)-dependent aldehyde dehydrogenase; (iii) phenol by both a NAD(+)-dependent dehydrogenase and a hydrolase in the approximate ratio of 5 to 1. This conclusion is supported by the substrate specificity and enzymatic activity of the hydrolase and NAD(+)-dependent aldehyde dehydrogenase enzymes of the wild-type strain. The results are discussed in terms of the physiological significance of the pathway. Properties of some of the mutant strains isolated are discussed.

Adipates↗
PubMed1983

Hippuric acid and o-cresol in the urine of workers exposed to toluene.

Factory workers, 74 males and 56 females exposed predominantly to toluene up to 129 ppm, were examined for the urinary excretion of hippuric acid and o-cresol. The time-weighted averages (TWA) of toluene exposure were measured by personal sampling with carbon felt dosimeters. A preliminary study revealed that the concentrations of hippuric acid and o-cresol in urine increased during work and both reach their peaks at the end of the shift. Correlation coefficients between the TWA of toluene concentration in air and hippuric acid concentration in urine collected at the end of the shift were 0.803 for the 74 males, and 0.830 for the 56 females, while the counterpart correlation coefficients between toluene and o-cresol were 0.607 for the 74 males, and 0.627 for the 56 females, suggesting that hippuric acid is more reliable than o-cresol as an index of toluene exposure. In the urine samples (4 to 8 samples per subject) collected during 8-h worktime from 11 males and 13 females, the urinary levels of o-cresol increased as a function of exposure time in parallel with those of hippuric acid, and the correlation coefficients between o-cresol and hippuric acid were significant (r = 0.834 approximately 0.987; P less than 0.05) when the urine samples from the same subjects were examined. The comparison of the slopes of 24 regression lines between o-cresol and hippuric acid in urine revealed that the maximal slope was almost 8 times as large as the minimal one. From 8 female workers, five urine samples each were collected during 8-h worktime on two consecutive Mondays and analyzed for the two metabolites. The slopes of the regression lines between o-cresol and hippuric acid in the samples from the same subject were identical, regardless of variation in exposure intensity. The findings indicate that an individual difference exists in the pattern of toluene metabolism, and that the ratio between aliphatic and aromatic oxidation is presumably set congenitally. Possible toxicological significance is discussed.

Air Pollutants, Occupational↗