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Effect of the net surface charge density of heptakis-6-bromo-6-deoxy-beta-cyclodextrin bonded silica gels on the retention behaviors of neutral cresol isomers in HPLC.

The effect of the surface charge density of heptakis-6-bromo-6-deoxy-beta-cyclodextrin (beta-CD-BR) bonded silica gels, which was used as the stationary phase of a packed capillary column for HPLC, was investigated concerning the retention behaviors of neutral cresol isomers. On the whole, the retention factors of the cresol isomers increased with an increase in the pH values of the mobile phase, although they were slightly smaller at pH 6.1 than at pH 4.7. An investigation on the retention variation using a van't Hoff plot revealed that the increase in the retention factor (k) at a higher pH region could be mainly attributed to the increase in DeltaS, while a partial decrease in k around pH 5 - 6 was caused by a decrease in the -DeltaH/T value. On the other hand, a measurement of the electroosmotic flow velocity under various pH of the mobile phase solutions revealed that the retention variations of the neutral cresol isomers were strongly correlated with the surface charge on the packing materials. The positive charge of secondary ammonium functional groups to bind beta-CD-BR inhibit the insertion of the cresol isomers into the cavity of beta-CD-BR while reducing the retention factor, whereas the negative charge of silanol group enhanced it through a local change in the mobile phase composition.

Chromatography, High Pressure Liquid↗

Hepatocellular injury with hyperaminotransferasemia after cresol ingestion.

A 42-year-old man attempted suicide by ingesting about 150 mL of a saponated cresol solution containing about 50% cresol. His serum aminotransferase concentrations were elevated, and a coagulopathy was present at the time of admission, 15 hours after ingestion. The hyperaminotransferasemia and coagulopathy worsened on the second day, but resolved thereafter with supportive therapy. Histologic examination of a biopsy specimen obtained on the 14th day demonstrated focal dropout of hepatocytes (which were replaced by reticulin and collagen fibers), ballooning or hydropic degeneration of hepatocytes, and rapid regeneration with small hepatocytes in the periportal zones as well as in the centrilobular zones. A rapid onset of illness with periportal hepatocellular injury is inconsistent with damage due to a hepatotoxic metabolite of p-cresol produced by cytochrome P450, which has been suggested by studies in vitro. A direct transient noxious effect mediated via the portal or arterial circulation may be involved in hepatic injury after cresol ingestion.

Adult↗

A fatal case of saponated cresol ingestion.

We describe here a case of suicidal poisoning by saponated cresol ingestion. A 41 year-old male was found unconsciousness in a park in the early morning, and an empty bottle of saponated cresol was found beside him. His death was confirmed approximately 2 hours later, despite attempts at resuscitation and intensive care. The autopsy revealed severe morphological damage of the upper gastrointestinal tract and congestion of the lung. We also observed by histopathological examination severe lung edema and severe erosion of the esophagus and stomach. Toxicological analysis also identified a high concentration of cresol isomer in the blood and gastric contents. The cause of death was given as cresol poisoning, based on the results of the autopsy and toxicological examination.

Adult↗

[Estimating the biological effect of detrimental substances on E. coli with flow microcalorimetry. III. Studies using m-cresol in glucose phosphate buffer].

Investigations are carried out to characterize the influence of the phenolic compound m-cresol on the heat production of glucose-respiring E. coli cells suspended in glucose phosphate buffer in a flow microcalorimeter according to the method of Perry et al. (5) The results are usually obtained within one hour. When testing m-cresol by this method thermic irritations occurred. A modified test procedure which largely avoids these troubles is described. The height (Q = heat flow) of the power-time-curves is evaluated 30 min and 60 min after the addition of the test substance. These values are compared to the values obtained from control-curves without any test substance. The 60 min-values seem less variable than the 30 min-values. The minimum effective m-cresol concentrations come to 7.50 mmol/l after 30 min and to 9.37 mmol/l after 60 min. The coefficients of variation are distinctly lower than +/- 10% at concentrations of less than 11.25 mmol/l. The coefficients of variation from 3 to 5 tests can extend +/- 20% both for the 30 min-values and the 60 min-values at higher concentrations (e.g. 15 mmol/l). Under the influence of increasing m-cresol concentrations the germ content in the solution and the heat flow decrease in a similar way. The results indicate that the used flow microcalorimetric technique is suitable to check the effect of a test substance on a test culture within only one hour's time. Possibly, the method can be helpful for pretesting disinfectants. The gathering of further experience with this system seems advisable.

Buffers↗

Rapid analysis of pesticide components, xylene, o-dichlorbenzene, cresol and dichlorvos, in blood and urine by pulse heating-gas chromatography-mass spectrometry.

Analysis of the pesticide components, xylene, o-dichlorbenzene (DCB), cresol and dichlorvos (DDVP, an organophosphate), was attempted using 3 microl of biological samples by pulse heating (Py)-gas chromatography-mass spectrometry (GC-MS) without pretreatment. Xylene, DCB, cresol and DDVP were separately detected by Py-GC-MS. The regression lines for these four substances in the blood were shown to be linear between the peak height and their concentrations, 0.1/0.2-20 microg/ml. Recoveries of DDVP, cresol, DCB and xylene at the concentration of 1.0 microg/ml by Py-GC-MS ranged from 78.8 to 89.0% in blood, and from 84.2 to 91.2% in urine. For within-run precision, the coefficient of variation values at the concentration of 1.0 microg/ml ranged from 7.9 to 10.6% in blood, and from 5.8 to 9.4% in urine. The lower detection limits of xylene, DCB, cresol and DDVP in blood were 50, 50, 50 and 150 ng/ml, respectively. In comparison with the measured value in blood that was added to these four substances, Py-GC-MS showed good accuracy similar to GC-MS after the extraction method. DDVP and xylene could be successfully determined by Py-GC-MS in blood and urine in emergency medical and autopsy cases. From these results, Py-GC-MS can be performed in a short analytical time (15 min) and is a useful method to determine pesticide components in forensic medicine and emergency medical practice.

Journal Article↗

Subunit interactions change the heme active-site geometry in p-cresol methylhydroxylase.

The enzyme p-cresol methylhydroxylase [4-cresol: (acceptor) oxidoreductase (methyl-hydroxylating), EC 1.17.99.1] contains two subunits: a cytochrome c (electron transfer) subunit (cytochrome cpc) and a flavin (catalytic) subunit. When these subunits are separated by isoelectric focusing, a stable cytochrome subunit is obtained. Significant differences are observed between the one-dimensional NMR spectra of oxidized cytochrome cpc and of oxidized p-cresol methylhydroxylase. Analysis of the two-dimensional nuclear Overhauser enhancement and exchange spectroscopy (NOESY) spectrum of reduced cytochrome cpc suggests that the axial ligand, Met-50, of the stable subunit reorients by a rotation about the C gamma-S delta bond when cytochrome cpc binds to the flavin subunit. This reorientation must result in a change in bonding at the heme, which is reflected both in the para-magnetically shifted resonances and in the redox potential. p-Cresol methylhydroxylase thereby provides an interesting example of the coupling of subunit interactions to active-site structure and reactivity.

Allosteric Regulation↗

Anaerobic Oxidation of Toluene, Phenol, and p-Cresol by the Dissimilatory Iron-Reducing Organism, GS-15.

The dissimilatory Fe(III) reducer, GS-15, is the first microorganism known to couple the oxidation of aromatic compounds to the reduction of Fe(III) and the first example of a pure culture of any kind known to anaerobically oxidize an aromatic hydrocarbon, toluene. In this study, the metabolism of toluene, phenol, and p-cresol by GS-15 was investigated in more detail. GS-15 grew in an anaerobic medium with toluene as the sole electron donor and Fe(III) oxide as the electron acceptor. Growth coincided with Fe(III) reduction. [ring-C]toluene was oxidized to CO(2), and the stoichiometry of CO(2) production and Fe(III) reduction indicated that GS-15 completely oxidized toluene to carbon dioxide with Fe(III) as the electron acceptor. Magnetite was the primary iron end product during toluene oxidation. Phenol and p-cresol were also completely oxidized to carbon dioxide with Fe(III) as the sole electron acceptor, and GS-15 could obtain energy to support growth by oxidizing either of these compounds as the sole electron donor. p-Hydroxybenzoate was a transitory extracellular intermediate of phenol and p-cresol metabolism but not of toluene metabolism. GS-15 oxidized potential aromatic intermediates in the oxidation of toluene (benzylalcohol and benzaldehyde) and p-cresol (p-hydroxybenzylalcohol and p-hydroxybenzaldehyde). The metabolism described here provides a model for how aromatic hydrocarbons and phenols may be oxidized with the reduction of Fe(III) in contaminated aquifers and petroleum-containing sediments.

Journal Article↗

Metabolism of p-Cresol by the Fungus Aspergillus fumigatus.

The fungus Aspergillus fumigatus ATCC 28282 was shown to grow on p-cresol as its sole source of carbon and energy. A pathway for metabolism of this compound was proposed. This has protocatechuate as the ring-fission substrate with cleavage and metabolism by an ortho-fission pathway. The protocatechuate was formed by two alternative routes, either by initial attack on the methyl group, which is oxidized to carboxyl, followed by ring-hydroxylation, or by ring-hydroxylation as the first step with subsequent oxidation of 4-methylcatechol to the acid. The pathway was elucidated from several pieces of evidence. A number of compounds, including 4-hydroxybenzyl alcohol, 4-hydroxybenzaldehyde, 4-hydroxybenzoic acid, protocatechuic acid, protocatechualdehyde, and 4-methylcatechol, appeared transiently in the medium during growth on p-cresol. These compounds were oxidized without lag by p-cresol-grown cells but not by succinate-grown cells. Enzyme activities for most of the proposed steps were demonstrated in cell extracts after growth on p-cresol, and the products of these activities were identified. None of the activities were found in succinate-grown cells.

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of 4,4'-Thiobis(6- t -butyl- m -cresol) (CAS No. 96-69-5) in F344/N Rats and B6C3F1 Mice (Feed Studies).

4,4'-Thiobis(6- t -butyl- m -cresol) (TBBC) is used in the rubber and plastics industries as an antioxidant. TBBC is also used as a stabilizer in polyethylene and polyolefin packaging materials for foodstuffs. Toxicology and carcinogenesis studies were conducted by administering TBBC (99% pure) in feed to groups of male and female F344/N rats and B6C3F1 mice for 15 days, 13 weeks, and 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and cultured Chinese hamster ovary cells. 15-DAY STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were fed diets containing 0, 1,000, 2,500, 5,000, 10,000 or 25,000 ppm TBBC for 15 days. Rats given to 1,000, 2,500, 5,000, or 10,000 ppm received approximate doses of 95, 235, 335, or 365 mg TBBC per kilogram body weight per day (males) or 85, 220, 325, or 270 mg/kg per day (females). Approximate doses for rats receiving 25,000 ppm could not be calculated due to early deaths. All 25,000 ppm rats and three male and four female 10,000 ppm rats died. Surviving rats in the 10,000 ppm groups had a significant weight loss and the final mean body weights of 5,000 and 10,000 ppm male and female rats were significantly lower than those of the controls. Male and female rats exposed to 5,000, 10,000, or 25,000 ppm TBBC consumed markedly less feed than the controls. Diarrhea occurred in 5,000, 10,000, and 25,000 ppm males and females. The principal lesions attributed to the administration of TBBC were renal papillary and tubule necroses which occurred in 10,000 ppm rats. Focal necrosis or erosions of the glandular stomach also occurred in some 10,000 ppm rats. Changes observed in the thymus and spleen were attributed to debilitation or stress; bone marrow depletion was attributed to nutrient deficiency accompanying weight loss. 15-DAY STUDY IN MICE: Groups of 10 male and 10 female B6C3F1, mice were fed diets containing 0, 1,000, 2,500, 5,000, 10,000, or 25,000 ppm TBBC for 15 days. Mice given 1,000, 2,500, or 5,000 ppm received approximate doses of 285, 585, or 475 mg TBBC per kilogram body weight per day (males) or 360, 950, or 1,030 mg/kg per day (females). Approximate doses for mice given 10,000 or 25,000 ppm could not be calculated due to early deaths. All 10,000 and 25,000 ppm mice died, as did eight males and eight females given 5,000 ppm. A significant weight loss occurred in surviving 5,000 ppm males and females and the final mean body weights of 2,500 ppm females and 5,000 ppm males and females were significantly lower than those of the controls. Feed consumption by mice given 5,000, 10,000, or 25,000 ppm was markedly reduced. Diarrhea occurred in all 25,000 ppm mice and in most male and female mice given 5,000 or 10,000 ppm. Renal tubule necrosis occurred in eight males and three females in the 5,000 ppm groups. Lymphocytic depletion of Iymphoid tissues in many 5,000 ppm males and females was attributed to debilitation and stress or to nutrient deficiency accompanying weight loss. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were fed diets containing 0, 250, 500, 1,000, 2,500, or 5,000 ppm TBBC for 13 weeks. These exposure levels delivered approximate doses of 15, 30, 60, 165, or 315 mg TBBC per kilogram body weight per day (males) or 15, 35, 70, 170, or 325 mg/kg per day (females). All rats survived to the end of the study. The final mean body weight of 5,000 ppm males was 40% lower than that of the controls; the final mean body weight of 5,000 ppm females was 27% lower than that of the controls. Feed consumption by male and female rats exposed to 5,000 ppm TBBC was markedly lower than that by the controls throughout the study. The absolute and relative liver weights of 5,000 ppm females were significantly greater than those of the controls. Serum alkaline phosphatase (ALP) levels were significantly higher in 2,500 and 5,000 ppm males and slightly higher in 5,000 ppm females. Serum alanine aminotransferase levels were significantly higher in 2,500 and 5,000 ppm males and females. Hematocrit and hemoglobin concentrations and mean erythroions and mean erythrocyte volume (MCV) values were significantly lower in 1,000, 2,500, and 5,000 ppm males than in controls; MCV values were also significantly lower in 5,000 ppm females. A dose-related significant increase in forelimb and hindlimb grip strength was observed in exposed male and female rats. Histopathologic findings in the liver of 2,500 and 5,000 ppm males and females included hypertrophy of Kupffer cells, bile duct hyperplasia, and individual cell necrosis of hepatocytes; centrilobular hepatocyte hypertrophy also occurred in males and females exposed to 5,000 ppm TBBC. Macrophages were increased in size and number in the mesenteric Iymph nodes of males and females exposed to 5,000 ppm, and to a lesser extent in 2,500 ppm male and female rats. Pigmentation and degeneration of the renal cortical tubule epithelial cells was also present in males and females in the 2,500 and 5,000 ppm groups; cortical tubule necrosis occurred in 5,000 ppm males and females. 13-WEEK STUDY IN MICE: Groups of up to 10 male and 10 female B6C3F1 mice were fed diets containing 0, 100, 250, 500, 1,000, or 2,500 ppm TBBC for 13 weeks. These exposure levels delivered approximate doses of 15, 30, 65, 145, or 345 mg TBBC per kilogram body weight per day (males) or 10, 35, 60, 165, or 340 mg/kg per day (females). All mice survived to the end of the study. The final mean body weights of 2,500 ppm males and of 500,1,000, or 2,500 ppm females were significantly lower than those of the controls. Feed consumption by 2,500 ppm males averaged 24% lower than that by controls through week 3 and was similar to that by controls for the remainder of the study. Feed consumption by females receiving 2,500 ppm averaged 27% less than that by the controls during most of the study. The absolute and relative liver weights of males and females exposed to 2,500 ppm TBBC were slightly but significantly greater than those of the controls. Males exposed to 500, 1,000, or 2,500 ppm and females exposed to 2,500 ppm had significantly increased absolute and relative spleen weights. No clinical findings in mice were considered chemical related. Hematocrit concentrations and erythrocyte counts of males receiving 1,000 or 2,500 ppm were significantly less than those of the controls; hemoglobin concentration in males receiving 2,500 ppm was significantly less and mean erythrocyte volume was significantly less in males receiving 2,500 ppm. Females in the 1,000 and 2,500 ppm groups had significantly decreased hematocrit concentrations and erythrocyte counts; 2,500 ppm females also had significantly decreased hemoglobin concentrations and mean erythrocyte volumes. Kupffer cell hypertrophy, bile duct hyperplasia, and an increase in size and number of macrophages in mesenteric Iymph nodes were present in 2,500 ppm male and female mice. 2-YEAR STUDY IN RATS: Doses selected for the 2-year study of TBBC were based on the lower body weights and liver and kidney toxicity observed at 5,000 ppm in the 13-week study. Groups of 115 male and 75 female F344/N rats were fed diets containing 0, 500, 1,000, or 2,500 ppm TBBC for 2 years. Based on average daily feed consumption, these exposure levels resulted in a daily ingestion of TBBC of approximately 20, 40, or 100 mg/kg body weight for males and 20, 45, or 120 mg/kg body weight for females. Hematology, clinical chemistry, and urinalysis evaluations were performed on 15 male and 15 female rats from each group at 3, 9, and 15 months. Also at 15 months, an additional 10 male and 10 female rats from each group were evaluated for histopathology, hematology, and clinical chemistry. Forty male rats per group were evaluated for neurotoxic effects. Survival, Body Weights, Feed Consumption, and Clinical Findings: Two-year survival rates and mean body weights of exposed male and female rats were generally similar to those of the controls. The mean body weights of 2,500 ppm male rats were slightly lower than those of the controls throughout the study. At week 65, the mean body weight of 2,500 ppm females was 14% lower than that of the controls, but the final mean body weight of this group was 6% lower than that of the control group. Feed consumption, behavior, and general health and appearance of exposed male and female rats were similar to those of the controls. Hematology and Clinical Chemistry: Results of the hematology evaluation were not uniformly consistent at 3, 9, and 15 months in one set of rats, nor were they consistent between the two sets of rats evaluated at 15 months. Slight but significant decreases in hematocrit levels, hemoglobin concentrations, and erythrocyte counts were observed in the 1,000 and 2,500 ppm groups in one set of males at 15 months. Similar significant decreases in hematocrit level and hemoglobin concentration occurred in 2,500 ppm females at 9 months. Mean erythrocyte hemoglobin and mean erythrocyte hemoglobin concentration of 2,500 ppm females were also significantly lower than those of controls at 9 months and in both sets of female rats evaluated at 15 months. Platelet counts of 2,500 ppm male and female rats were slightly but significantly higher than those of controls at 3 and 9 months. Platelet counts were also slightly but significantly increased in 2,500 ppm males of one set evaluated at 15 months, and in 2,500 ppm females of the second set evaluated at 15 months. Serum activities of alkaline phosphatase, alanine aminotransferase, and sorbitol dehydrogenase in 2,500 ppm males were significantly greater than those in the controls at 3, 9, and 15 months. Alkaline phosphatase activities in both sets of 1,000 ppm males evaluated at 15 months were also significantly greater than those of controls. Serum activities of alanine aminotransferase and sorbitol dehydrogenase in 2,500 ppm females were also significantly greater than those in controls at 3, 9, and 15 months. Neurotoxicity Findings: There were no significant inhibitory effects of TBBC on motor nerve excitability or conduction, neuromuscular transmission, or muscle contractility. There were no microscopic lesions in the sciatic nerve, quadriceps muscle, or teased nerve preparations of sciatic nerve that could be attributed to TBBC administration. Pathology Findings: At the 15-month interim evaluation, the absolute and relative liver weights of 2,500 ppm female rats were significantly greater than those of controls; at 15 months and at the end of the study, the incidences of Kupffer cell hypertrophy, hepatocyte cytoplasmic vacuolization, and mixed cell foci were also significantly increased. At the end of the study, the incidence of hepatocellular fatty change was significantly increased in 2,500 ppm females. The incidence of Kupffer cell hypertrophy was significantly increased in 2,500 ppm males at 15 months and at 2 years; the incidence of cytoplasmic vacuolization was significantly increased in all exposed males at 15 months but only moderately increased in 1,000 and 2,500 ppm males at 2 years; the incidence of basophilic foci was significantly increased in 2,500 ppm males at 15 months and the incidence of mixed cell foci was significantly increased in 1,000 and 2,500 ppm male rats at 2 years. The incidences of hepatocellular adenoma or carcinoma (combined) in exposed male rats were not significantly greater than that in the controls (0 ppm, 1/50; 500 ppm, 3/50; 1,000 ppm, 3/50; 2,500 ppm, 5/49), were within the historical control range, and were not considered chemical related. The severity of nephropathy was significantly increased in 2,500 ppm female rats. There was a significant negative trend in the incidence of mammary gland fibroadenoma, adenoma, or carcinoma (combined) in female rats (32/50, 24/50, 11/50, 16/50), and the incidences of fibroadenoma in 1,000 and 2,500 ppm females were significantly less than that of the controls. 2-YEAR STUDY IN MICE: Because of the reduction in body weights, the increase in liver and spleen weights, and the accompanying histopathologic changes in the liver of 2,500 ppm male and female mice in the 13-week study, the doses selected for the 2-year study were 250, 500, and 1,000 ppm. Groups of 80 male and 80 female mice were fed diets containing 0, 250, 500, or 1,000 ppm TBBC for 2 years. Based on average daily feed consumption, these exposure levels resulted in the daily ingestion of approximately 30, 60, or 145 mg TBBC/kg body weight for males and 45, 110, or 255 mg TBBC/kg body weight for females. Nine or 10 animals from each exposure group were evaluated at 3, 9, and 15 months. Survival, Body Weights, Feed Consumption, and Clinical Findings: Two-year survival rates of exposed male and female mice were similar to those of the controls. The final mean body weights of male and female mice exposed to 1,000 ppm were 8% and 18% lower than those of the controls, respectively. The final mean body weights of females exposed to 250 or 500 ppm were 8% to 9% lower than that of the controls. Feed consumption by exposed males was similar to that by controls, and there were no clinical findings attributed to TBBC administration. Hematology and Clinical Chemistry: Hematocrit level, hemoglobin concentration, and erythrocyte count in 1,000 ppm male mice were significantly lower than those in controls at the 15-month interim evaluation. Serum alkaline phosphatase activities in 1,000 ppm males were slightly but significantly greater than those in controls at 3 and 9 months, as was the serum alkaline phosphatase activity in 1,000 ppm females at 9 months. Serum levels of total bilirubin in all exposed groups of males were significantly greater than those in controls at 9 and 15 months. Pathology Findings: In the liver of male mice, negative trends in the incidences of fatty change, clear cell foci, and adenoma or carcinoma combined occurred at the end of the 2-year study. There were no compound-related increased incidences of neoplasms or nonneoplastic lesions in mice receiving TBBC for 2 years. A negative trend in the incidence of fatty change in the liver of male mice also occurred at 15 months. GENETIC TOXICOLOGY: 4,4'-Thiobis(6- t -butyl- m -cresol) was not mutagenic in Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537 with or without exogenous metabolic activation (S9). Sister chromatid exchanges were induced in cultured Chinese hamster ovary cells treated with TBBC, with and without S9, but no increases in chromosomal aberrations were noted in cultured Chinese hamster ovary cells after treatment with TBBC. CONCLUSIONS: Under the conditions of these 2-year feed studies, there was no evidence of carcinogenic activity of 4,4'-thiobis(6- t -butyl- m -cresol) in male or female F344/N rats administered 500, 1,000, or 2,500 ppm or in male or female B6C3F1, mice administered 250, 500, or 1,000 ppm. Nonneoplastic lesions associated with exposure to TBBC included: Kupffer cell hypertrophy, cytoplasmic vacuolization, and mixed cell foci in the liver of male and female rats, fatty change in the liver of female, rats, and an increase in the severity of nephropathy in the kidney of female rats. In addition, decreased incidences of fibroadenoma, adenoma, or carcinoma (combined) were observed in the mammary gland of female rats. Decreases also occurred in the incidences of fatty change, clear cell foci, and adenoma or carcinoma (combined) in the liver of male mice. Synonyms: 4,4'-Thiobis(6- t -butyl-3-cresol); bis(3- t -butyl-4-hydroxy-6-methylphenyl)sulfide

Journal Article↗

Phenol and cresol metabolism in Bacillus pumilus isolated from contaminated groundwater.

From an aquifier contaminated with phenolic compounds seven bacterial strains able to grow on phenol and several mono- and disubstituted alkylphenols as sole source of carbon and energy were isolated. Five isolates belong to the genus Pseudomonas, two to the genus Bacillus. The isolate most active in utilization of the applied xenobiotics was identified as Bacillus pumilus and used for the investigation of the degradation pathways in liquid cultures. Cells of this strain precultured on phenol were able to utilize para-cresol as sole carbon source via the oxidation of the methylsubstituent and intradiol ring cleavage of the resulting protocatechuic acid, whereas an intradiol ring fission of the intermediate 4-methylcatechol led to 4-methylmuconolactone as dead end-product. Cells precultured on meta- and ortho-cresol were able to utilize the respective compounds as sole carbon sources via 3-methylcatechol, which induced the following extradiol ring fission pathway. Cells precultured on phenol were able to cooxidize meta- as well as ortho-cresol to 3-methylcatechol, which was cleaved via an intradiol ring fission, finally leading to the dead end-product 2-methylmuconolactone.

Bacillus↗

Simultaneous biodegradation of p-cresol and phenol by the basidiomycete Phanerochaete chrysosporium.

The fungus Phanerochaete chrysosporium BKM-F-1767 was able to degrade high concentrations of p-cresol (up to 150 mg L-1) provided that glucose was added as a carbon and energy source and conditions favourable to ligninolytic enzyme activities were used, i.e. a nitrogen-limited medium. The fungus also simultaneously degraded p-cresol (50 mg L-1) and phenol (50 mg L-1) in a mixture at similar rates. Kinetics of p-cresol biodegradation were almost identical whether the compound was tested individually or in a mixture with phenol.

Basidiomycota↗

Anaerobic degradation of m-cresol by Desulfobacterium cetonicum is initiated by formation of 3-hydroxybenzylsuccinate.

The anaerobic bacterium Desulfobacterium cetonicum oxidized m-cresol completely with sulfate as electron acceptor. During growth, 3-hydroxybenzylsuccinate (identified by gas chromatography/mass spectroscopy and by comparison of high-performance liquid chromatography retention time and UV spectrum with a chemically synthesized reference compound) accumulated in the medium. This finding indicates that the methyl group of m-cresol is activated by addition to fumarate as in the case of anaerobic toluene metabolism. In cell-free extracts of D. cetonicum, the formation of 3-hydroxybenzylsuccinate from m-cresol and fumarate was detected at an activity of 0.5 nmol min(-1) (mg protein)(-1). This reaction depended strictly on anoxic assay conditions. Treatment with air resulted in a complete loss of activity; however, some activity could be recovered after restoring anoxic conditions. The activity was slightly membrane-associated. 3-Hydroxybenzylsuccinate was degraded via CoA thioesterification and further oxidation to 3-hydroxybenzoyl-CoA as subsequent steps in the degradation pathway.

Anaerobiosis↗

Metabolism and excretion of 2-nitro-p-cresol in rats.

Metabolism of 2-nitro- p-cresol (NPC), an important commercial chemical, was studied in female Sprague-Dawley rats, using (14)C-NPC. It was found that NPC was rapidly absorbed and excreted after an oral dose of 250 mg/kg. Approximately 90% of the administered dose was excreted into urine and less than 10% of the dose into feces for 5 days. Urinary and fecal excretion were found to the same extent after 48 h. Bile excretion amounted to approximately 25% for 2 days. Blood levels of (14)C-NPC reached the maximum concentration (39.4 micro g-equivalents/g) within 1 h, and decreased bi-exponentially. The apparent half-lives of (14)C-NPC were 3.8 h for the rapid phase and 37 h for the slow phase, respectively. From studying the distribution in organs at 1.5, 6, 24, 72 and 120 h, we found that the concentrations of radioactivity in various tissues of rats were relatively high in the stomach, intestine, liver, kidney, blood, ovary and uterus. Most organs showed the maximum concentrations at 1.5 h, except for intestine, kidney, ovary, and uterus at 6 h. There was no specific tissue retention after 72 h. Two main conjugate metabolites, glucuronide and sulfate of NPC, were detected with free NPC and 2-acetylamino- p-cresol (AAPC) in the urine. NPC was rapidly absorbed and excreted mainly into urine as the conjugate metabolites. A part of NPC was reduced to 2-amino- p-cresol, followed by acetylation to give AAPC.

Administration, Oral↗

Simple high-performance liquid chromatographic analysis of phenol and p-cresol in urine and feces.

Previous reports which present methods of analysis of phenol and p-cresol by HPLC are usually designed for the detection of these compounds in urine, can be complicated by the use of uncommon equipment or additional techniques such as steam distillation or derivatisation, or concentrate on the detection of phenol rather than p-cresol. In this paper we report a simple method suitable for the analysis of phenol and p-cresol in both urine and feces, based upon extraction into ether following acid hydrolysis and UV detection.

Chromatography, High Pressure Liquid↗

Similarities of toluene and o-cresol neuroexcitation in rats.

Exposure to high concentrations of toluene vapors, or to intravenous o-cresol (a toluene metabolite) at about 0.9 mg/min, caused excitation of the somatosensory evoked potential (SEP) and EEG of Fischer 344 rats. SEP excitation was characterized by a large increase in a positive waveform at about 20-50 msec. Prolonged exposure to either compound caused numerous oscillations to appear from 20 msec to the end of the recording (150 msec). Both substances induced an increase in EEG beta activity and caused a large increase in activity at 5 Hz. Toluene exposed rats were lightly anesthetized, while o-cresol rats were conscious but hyperreactive. If exposure was continued, both sets of rats had involuntary muscle movements and tremors. Benzoic acid and hippuric acid, also metabolites of toluene, were similarly tested. Neither caused neuroexcitation (about 2.4 mg/min IV, 144 mg total dose). It was concluded, therefore, that metabolically derived cresols are plausible candidates for the neuroexcitatory properties of toluene.

Animals↗

Influence of phenol, p-cresol and indole on growth and survival of intestinal lactic acid bacteria.

Some intestinal bacteria can produce many genotoxic, mutagenic and carcinogenic substances. The major products of the bacterial aromatic amino acids fermentation-phenolic and indolic compounds which are responsible for colon cancer development are accumulated in the colon. The effect of phenol, p-cresol and indole (2, 20 and 100 microg/ml doses) on growth and survival of four strains of intestinal lactic acid bacteria was studied. Growth of bacteria was not affected by any of the concentrations of phenol and p-cresol tested. The growth of 2 strains was slightly inhibited by 100 microg/ml of indole. There was no influence of phenol and p-cresol on survival of lactic bacteria until 120 h and specific reaction to carcinogens depending on strain was observed after that incubation time. Indole concentrations 20 and 100 microg/ml appeared to be toxic for all tested strains but just after 24, 48 or 72 h of incubation depending on the strain. In total, 2 microg/ml of indole had a very little effect.

Carcinogens↗

Degradation of phenol and cresols at low temperatures using a suspended-carrier biofilm process.

Degradation of phenol and o-, m- and p-cresol at a concentration of 150 mg l(-1) of each compound was studied in a suspended-carrier biofilm process consisting of two aerobic stages. The fungus Mortierella sarnyensis Mil'ko dominated the microflora in the first reactor, while bacteria dominated in the second reactor. The process was studied at 4, 7, 11 and 15 degrees C. The results from the experiments showed the process to be relatively efficient even at 4 degrees C. The degradation rate was 33% of that at 15 degrees C for o-cresol. Both phenol and the cresols were degraded in the first reactor and a new peak appeared in the HPLC-chromatograms indicating the formation of one or more intermediate compounds in the first stage. These compounds were however degraded to below the detection limit in the second reactor. Small new peaks appeared in the chromatograms of the outlet from the second reactor at the maximum loading rates.

Biodegradation, Environmental↗

Integrated catalytic wet air oxidation and aerobic biological treatment in a municipal WWTP of a high-strength o-cresol wastewater.

This study examines the feasibility of coupling a Catalytic Wet Air Oxidation (CWAO), with activated carbon (AC) as catalyst, and an aerobic biological treatment to treat a high-strength o-cresol wastewater. Two goals are pursued: (a) To determine the effect of the main AC/CWAO intermediates on the activated sludge of a municipal WasteWater Treatment Plant (WWTP) and (b) To demonstrate the feasibility of coupling the AC/CWAO effluent as a part of the influent of a municipal WWTP. In a previous study, a high-strength o-cresol wastewater was treated by AC/CWAO aiming to establish the distribution of intermediates and the biodegradability enhancement. In this work, the biodegradability, toxicity and inhibition of the most relevant intermediates detected in the AC/CWAO effluent were determined by respirometry. Also, the results of a pilot scale municipal WWTP study for an integrated AC/CWAO-aerobic biological treatment of this effluent are presented. The biodegradation parameters (i.e. maximum oxygen uptake rate and oxygen consumption) of main AC/CWAO intermediates allowed the classification of the intermediates into readily biodegradable, inert or toxic/inhibitory compounds. This detailed study, allowed to understand the biodegradability enhancement exhibited by an AC/CWAO effluent and to achieve a successful strategy for coupling the AC/CWAO step with an aerobic biological treatment for a high-strength o-cresol wastewater. Using 30%, as COD, of AC/CWAO effluent in the inlet to the pilot scale WWTP, the integrated AC/CWAO-biological treatment achieved a 98% of total COD removal and, particularly, a 91% of AC/CWAO effluent COD removal without any undesirable effect on the biomass.

Bacteria, Aerobic↗