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Isolation and characterization of a novel toluene-degrading, sulfate-reducing bacterium.

A novel sulfate-reducing bacterium isolated from fuel-contaminated subsurface soil, strain PRTOL1, mineralizes toluene as the sole electron donor and carbon source under strictly anaerobic conditions. The mineralization of 80% of toluene carbon to CO2 was demonstrated in experiments with [ring-U-14C]toluene; 15% of toluene carbon was converted to biomass and nonvolatile metabolic by-products, primarily the former. The observed stoichiometric ratio of moles of sulfate consumed per mole of toluene consumed was consistent with the theoretical ratio for mineralization of toluene coupled with the reduction of sulfate to hydrogen sulfide. Strain PRTOL1 also transforms o- and p-xylene to metabolic products when grown with toluene. However, xylene transformation by PRTOL1 is slow relative to toluene degradation and cannot be sustained over time. Stable isotope-labeled substrates were used in conjunction with gas chromatography-mass spectrometry to investigate the by-products of toluene and xylene metabolism. The predominant by-products from toluene, o-xylene, and p-xylene were benzylsuccinic acid, (2-methylbenzyl)succinic acid, and 4-methylbenzoic acid (or p-toluic acid), respectively. Metabolic by-products accounted for nearly all of the o-xylene consumed. Enzyme assays indicated that acetyl coenzyme A oxidation proceeded via the carbon monoxide dehydrogenase pathway. Compared with the only other reported toluene-degrading, sulfate-reducing bacterium, strain PRTOL1 is distinct in that it has a novel 16S rRNA gene sequence and was derived from a freshwater rather than marine environment.

Acetyl Coenzyme A↗

Anaerobic activation of toluene and o-xylene by addition to fumarate in denitrifying strain T.

Anaerobic assays conducted with strain T, a denitrifying bacterium capable of mineralizing toluene to carbon dioxide, demonstrated that toluene-grown, permeabilized cells catalyzed the addition of toluene to fumarate to form benzylsuccinate. This reaction was not dependent on the presence of coenzyme A (CoA) or ATP. In the presence of CoA, formation of E-phenylitaconate from benzylsuccinate was also observed. Kinetic studies demonstrated that the specific rate of benzylsuccinate formation from toluene and fumarate in assays with permeabilized cells was >30% of the specific rate of toluene consumption in whole-cell suspensions with nitrate; this observation suggests that benzylsuccinate formation may be the first reaction in anaerobic toluene degradation by strain T. Use of deuterium-labeled toluene and gas chromatography-mass spectrometry indicated that the H atom abstracted from the toluene methyl group during addition to fumarate was retained in the succinyl moiety of benzylsuccinate. In this study, no evidence was found to support previously proposed reactions of toluene with acetyl-CoA or succinyl-CoA. Toluene-grown, permeabilized cells of strain T also catalyzed the addition of o-xylene to fumarate to form (2-methylbenzyl)succinate. o-Xylene is not a growth substrate for strain T, and its transformation was probably cometabolic. With the exception of specific reaction rates, the observed characteristics of the toluene-fumarate addition reaction (i.e., retention of a methyl H atom and independence from CoA and ATP) also apply to the o-xylene-fumarate addition reaction. Thus, addition to fumarate may be a biochemical strategy to anaerobically activate a range of methylbenzenes.

Anaerobiosis↗

Effects of ethanol and phenobarbital treatments on the pharmacokinetics of toluene in rats.

Rats were exposed to toluene at a wide range of concentrations from 50 to 4000 ppm for six hours, and the effects of ethanol and phenobarbital (PB) treatments on the pharmacokinetics of toluene metabolism were investigated. Ethanol treatment influenced toluene metabolism mainly at low exposure concentrations. Thus ethanol accelerated the clearance of toluene from blood only when the blood concentration of toluene was not high (less than 360 microM), and ethanol increased hippuric acid (HA) excretion in urine more significantly at low (less than 250 ppm) than at high atmospheric toluene concentrations. Ethanol also expressed a similar effect on p-cresol excretion as on HA, but had little effect on o-cresol. Phenobarbital treatment promoted the urinary excretion of all of the metabolites of toluene, especially after exposure to high toluene concentration. As well as HA, benzoylglucuronide (BG) and free benzoic acid were found in urine. These are the products of the side chain metabolism of toluene. Amounts of BG could be detected when the urinary excretion of free benzoic acid exceeded 5 mumol/kg/6 h, indicating that a great deal of benzoic acid is required for the formation of BG. The Michaelis constant (Km) and the maximum rate of metabolic excretion in urine during six hours exposure (Vmax) of isozymes involved in the excretion of toluene metabolites were calculated, and correlated with the subtypes of cytochrome P-450. The significance of the result was suggested in the biological monitoring of exposure to toluene.

Animals↗

Changes in membrane fluidity and fatty acid composition of Pseudomonas putida CN-T19 in response to toluene.

A bacterial isolate, Pseudomonas putida CN-T19, could grow in a two-phase medium with toluene up to 50% (v/v). Changes in fatty acid composition and membrane fluidity of the isolate were investigated to understand how this microorganism responds toluene. The changes in the ratios of unsaturated to saturated fatty acids were insignificant between cells grown with and without toluene. The changes in the ratio of cis- to trans-fatty acids of C16:1 and C18:1 was, however, significantly lower in cells grown with toluene than cells grown without toluene, giving approximately 1.3 and 9.7, respectively. Toluene had a fluidizing effect on the membrane of cells grown without toluene, resulting in decrease in membrane polarization ratio. Less fluidizing effect of toluene on the membrane of cells grown with toluene was observed, giving 11% of polarization percentage, which was significantly lower than 53% in cells grown without toluene. These results suggest that cis/trans isomeration of C16:1 and C18:1 makes cell membranes more rigid to respond toluene, and is an adaptive strategy allowing P. putida CN-T19 to grow in the presence of organic solvent.

Cell Membrane↗

Phototrophic utilization of toluene under anoxic conditions by a new strain of blastochloris sulfoviridis

The capacity of anoxygenic phototrophic bacteria to utilize aromatic hydrocarbons was investigated in enrichment cultures with toluene. When mineral medium with toluene (provided in an inert carrier phase) was inoculated with activated sludge and incubated under infrared illumination (> 750 nm), a red-to-brownish culture developed. Agar dilution series indicated the dominance of two types of phototrophic bacteria. One type formed red colonies, had rod-shaped cells with budding division, and grew on benzoate but not on toluene. The other type formed yellow-to-brown colonies, had oval cells, and utilized toluene and benzoate. One strain of the latter type, ToP1, was studied in detail. Sequence analysis of the 16S rRNA gene and DNA-DNA hybridization indicated an affiliation of strain ToP1 with the species Blastochloris sulfoviridis, a member of the alpha-subclass of Proteobacteria. However, the type strain (DSM 729) of Blc. sulfoviridis grew neither on toluene nor on benzoate. Light-dependent consumption of toluene in the presence of carbon dioxide and formation of cell mass by strain ToP1 were demonstrated in quantitative growth experiments. Strain ToP1 is the first phototrophic bacterium shown to utilize an aromatic hydrocarbon. In the supernatant of toluene-grown cultures and in cell-free extracts incubated with toluene and fumarate, the formation of benzylsuccinate was detected. These findings indicate that the phototrophic bacterium activates toluene anaerobically by the same mechanism that has been reported for denitrifying and sulfate-reducing bacteria. The natural abundance of phototrophic bacteria with the capacity for toluene utilization was examined in freshwater habitats. Counting series revealed that up to around 1% (1.8 x 10(5) cells per gram dry mass of sample) of the photoheterotrophic population cultivable with acetate grew on toluene.

Journal Article↗

Rats exposed to Toluene and Noise may develop Loss of Auditory Sensitivity due to Synergistic Interaction.

Hearing loss in workers exposed to organic solvents has been shown to be the effect of interaction between the exposure to solvents and noise. Synergistic interaction has been demonstrated in rats following simultaneous exposure to toluene and noise, but only at high-level toluene exposure. The present study was initiated to investigate the potential interaction of exposure to noise and toluene on the auditory system of the rat, covering a dose-range of toluene exposure (0, 500, 1000, 1500, and 2000 ppm, 6 h/d, 10 d). Exposed to toluene only, the rats exposed at the 1500 and 2000 ppm level developed a mid-frequency ABR threshold shift, whereas rats exposed to 0, 500, and 1000 ppm did not exhibit signs of auditory impairment. Rats exposed to 500 ppm toluene and noise (96 dB SPL, 2h following the daily toluene exposure, 10 d) developed a small, but statistically significant threshold shift, equal to the hearing loss in rats exposed to noise only (0 ppm). Synergistic interaction was evident at the 1000, 1500, and 2000 ppm toluene exposure levels. There was no further hearing loss at the 2000 ppm than at the 1500 ppm level, indicating that a saturation of the auditory impairment had been reached. When acute noise exposure (105 dB SPL, 4 h) followed the toluene exposure by 30 days, interaction was noted at the 1500 ppm toluene exposure level, but not at the 1000 ppm level. However, the latter type of interaction is of indirect nature and should be distinguished from the direct interaction, taking place when toluene is physically present in the cochlea during exposure to noise. Further investigations in animal models should preferentially be carried out as long-term, low-level exposure studies, showing the possible interaction at low exposure levels, where exposure to each factor alone is without any effect.

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of Toluene (CAS No.108-88-3) in F344/N Rats and B6C3F1 Mice (Inhalation Studies).

Toluene is used to back-blend gasoline, as a chemical intermediate, and as a solvent; 920 million gallons were produced in the United States in 1988. Toxicology studies were conducted by administering toluene (greater than 99% pure) in corn oil by gavage to groups of F344/N rats and B6C3F1 mice of each sex for 13 weeks or by whole-body inhalation exposure for 14 or 15 weeks. NTP Toxicology and Carcinogenesis studies were conducted by whole-body inhalation exposure of F344/N rats and B6C3F1 mice of each sex for 15 months or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, mouse L5178Y lymphoma cells, and Chinese hamster ovary cells. Thirteen-Week Gavage Studies: All rats that received the top dose of 5,000 mg/kg died during the first week, and 8/10 male rats that received 2,500 mg/kg died early. The final mean body weight of male rats that received 2,500 mg/kg was 19% lower than that of vehicle controls. Relative liver, kidney, and heart (female only) weights for rats that received the higher doses were greater than those for vehicle controls. Necrosis of the brain and hemorrhage of the urinary bladder were seen at increased incidences in dosed rats. All mice that received the top dose of 5,000 mg/kg died during the first week, and 40% of those that received 2,500 mg/kg died before the end of the 13-week gavage studies. The final mean body weight of males at 2,500 mg/kg was 16% lower than that of vehicle controls. At the higher doses, relative liver weights were increased for mice. Fifteen-Week and Fourteen-Week Inhalation Studies: Eight of 10 male rats exposed at the top exposure concentration of 3,000 ppm died during week 2. Final mean body weights of rats exposed at concentrations of 2,500 or 3,000 ppm were 14%-25% lower than that of controls. As in the gavage studies, the relative liver, kidney, and heart weights for rats exposed at the top two concentrations were increased compared with those for controls. No compound-related effects were seen on sperm; no adverse effects on the estrous cycle were observed. Five of 10 male mice and all female mice exposed at 3,000 ppm and 70% of female mice at 2,500 ppm died during the first 2 weeks. Final mean body weights of all exposed groups were 7%-13% lower than those of controls. Relative liver weights for mice exposed at 625 ppm or higher, relative lung weights for mice exposed at 1,250 ppm or higher, and relative kidney weights for female mice exposed at 1,250 ppm or higher were greater than those for controls. Centrilobular hypertrophy of the liver was observed in all male mice exposed at 2,500 ppm and 70% of male mice exposed at 3,000 ppm. No effects on sperm or the estrous cycle were observed. Fifteen-Month and Two-Year Inhalation Studies: Long-term studies were conducted by exposing groups of 60 rats of each sex to 0, 600, or 1,200 ppm toluene by inhalation, 6.5 hours per day, 5 days per week. Groups of 60 mice of each sex were exposed at 0, 120, 600, or 1,200 ppm on the same schedule. Ten animals per group (except male mice) were removed for toxicologic evaluation after being exposed for 15 months. All other animals were exposed to toluene for 103 weeks. In the 15-month inhalation studies, the incidences and severity of nonneoplastic lesions of the nasal cavity (degeneration of olfactory and respiratory epithelium and goblet cell hyperplasia) were increased in exposed rats. Minimal hyperplasia of the bronchial epithelium was seen in 4/10 female mice at 1,200 ppm. The severity of nephropathy was slightly increased in exposed female rats. No chemical-induced neoplasms were observed. Body Weight and Survival in the Two-Year Studies: Mean body weights of rats and mice were generally similar (yearly averages within 5%) among groups throughout the 2-year studies. No significant differences in survival were observed among rats or mice of either sex, although survival in all groups of male mice was lower than usual (male rats: control, 30/50; 600 ppm, 28/50; 1,200 ppm, 22/50; female rats: 33/50; 35/50; 30/50; male mice: control, 17/60; 120 ppm, 22/50; female rats: 33/50; 35/50; 30/50; male mice: control, 17/60; 120 ppm, 22/60; 600 ppm, 16/60; 1,200 ppm, 19/60; female mice: 30/50; 33/50; 24/50; 32/50). Scrotal, preputial, and penile lesions observed in male mice were associated with many of the early deaths and with animals killed in a moribund condition. Nonneoplastic and Neoplastic Effects in the Two-Year Studies: Nephropathy was seen in almost all rats, and the severity was somewhat increased in exposed rats. A rare renal tubular cell carcinoma in a female rat and an equally uncommon sarcoma of the kidney in another female rat were seen in the 1,200-ppm exposure group. Erosion of the olfactory epithelium and degeneration of the respiratory epithelium were increased in exposed rats. Inflammation of the nasal mucosa and metaplasia of the olfactory epithelium were increased in exposed female rats. A rare squamous cell carcinoma of the nasal mucosa was seen in one female rat at 1,200 ppm. A squamous cell papilloma of the forestomach was observed in one female rat at 1,200 ppm, and a squamous cell carcinoma was observed in a second female rat at 1,200 ppm. No chemically related neoplasms were found in male rats, and the one nasal, two kidney, and two forestomach neoplasms observed in female rats were considered not to be associated with inhalation exposed to toluene. For mice, no biologically important increases were observed for any nonneoplastic or neoplastic lesions. Genetic Toxicology: Toluene did not induce gene mutations in S. typhimurium strain TA98, TA100, TA1535, or TA1537 with or without exogenous metabolic activation. In the mouse lymphoma assay, toluene gave an equivocal response with and without exogenous metabolic activation. Toluene did not induce sister chromatid exchanges or chromosomal aberrations in Chinese hamster ovary cells in the presence or absence of exogenous metabolic activation. Conclusions: Under the conditions of these 2-year inhalation studies, there was no evidence of carcinogenic activity for male or female F344/N rats exposed to toluene at concentrations of 600 or 1,200 ppm. There was no evidence of carcinogenic activity for male or female B6C3F1 mice exposed by inhalation to toluene at concentrations of 120, 600, or 1,200 ppm for 2 years. Synonyms: monomethylbenzene; methylbenzene; toluol; phenylmethane; tolueen (Dutch); toluen (Czech), tolueno (Spanish); toluolo (Italian) Trade Name: Methacide

Journal Article↗

Quantitative assessment of color vision impairment in workers exposed to toluene.

Color vision was examined by the Lanthony-D-15 desaturated test in two groups of workers occupationally exposed to toluene and in a control group. Biological parameters of toluene exposure were analyzed: toluene in air and in venous blood, orthocresol, and hippuric acid in urine after workshift. The first exposed group, Group E1, comprised 41 workers (toluene exposure ranged from 11.30 to 49.30 ppm), and the second exposed group, Group E2, comprised 32 workers (toluene exposure ranged from 66.00 to 250.00 ppm). The nonexposed group, Group NE, comprised 83 subjects. Each group was divided into two subgroups; alcohol consumers and nonconsumers. Color vision loss was expressed as a color confusion index (CCI) and as age and alcohol intake-adjusted color confusion index (AACCI). Significantly higher values of CCI and AACCI (both P < 0.0001) in Group E2 in comparison to Group NE, and significantly higher CCI (P < 0.0001) and AACCI (P < 0.05) values in Group E2 in comparison to Group E1 were established. The significant difference in CCI value between alcohol consumers and nonconsumers was established only in Group NE (P < 0.05). In Group NE significant correlation was found between CCI value as a dependent and age and alcohol intake as independent cofactors (R2 = 0.45; P = 0.0000). In Group E2 significant correlation was established between CCI as a dependent factor and age, toluene in air, and alcohol intake (R2 = 0.72; P = 0.0001), or between CCI as dependent and age, toluene in blood and alcohol intake as independent cofactors (R2 = 0.68; P = 0.0002). In Group E1 significant correlation was established only between CCI and age (P <0.005). In Group E2, AACCI value significantly correlated with toluene in air (P < 0.0001), toluene in blood (r < 0.0005), orthocresol (P < 0.005) and hippuric acid (P < 0.005) in urine after workshift. There were no differences between smokers and nonsmokers in CCI values in the examined groups. Results of this study indicate that toluene in exposed workers can impair color vision. The role of alcohol intake and age influence on color vision loss cannot be ignored in such workers.

Adult↗

Inhalation of low concentrations of toluene induces persistent effects on a learning retention task, beam-walk performance, and cerebrocortical size in the rat.

The organic solvent toluene is widely used in industry. The threshold limit value for extended occupational exposure to toluene is presently set to 200 ppm in the United States. We have investigated the effect of an inhalation exposure of 80 ppm for 4 weeks (6 h/day, 5 days/week), followed by a postexposure period of at least 4 weeks, on behavior and brain features in the rat. Toluene exposure appeared to affect spatial memory, since toluene-exposed rats showed a longer time in the correct quadrant in a Morris swim maze. This effect may indicate that the exposed rats used their praxis strategy longer before they started to look for the platform elsewhere. Toluene-exposed rats showed trends for increases in both locomotion and rearing behaviors and a significantly reduced beam-walk performance. The area of the cerebral cortex, especially the parietal cortex, was decreased by 6-10% in toluene-exposed rats, as shown by magnetic resonance imaging of living rats and autoradiograms of frozen brain sections. The K(D) and B(max) values of the dopamine D(3) agonist [(3)H]PD 128907 were not affected by toluene, as measured in caudate-putamen and subcortical limbic area using biochemical receptor binding assays and in caudate-putamen and islands of Calleja using quantitative receptor autoradiography. Hence, previously demonstrated persistent effects by toluene on the binding characteristics of radioligands binding to both D(2) and D(3) receptors seem to indicate a persistent effect of toluene selectively on dopamine D(2) receptors. Taken together, the present results indicate that exposure to low concentrations of toluene leads to persistent effects on cognitive, neurological, and brain-structural properties in the rat.

Administration, Inhalation↗

Biomonitoring of occupational toluene exposure.

Toluene exposure was studied in 20 workers employed in painting and hand-finishing in an art furniture factory. Toluene was determined in the environmental air of places of work and in the alveolar air and blood of the workers. Hippuric acid and cresols were also tested in the workers' urine. Blood and urine tests were carried out before the work shift on Monday and Friday morning and at the end of the work shift on Friday afternoon. The other tests were performed on Friday afternoon only. Alveolar toluene concentrations, which were significantly correlated with environmental toluene concentrations (r = 0.6230; P less than 0.01), corresponded to 19.4% of the toluene concentration in the atmosphere. Blood toluene was also found in painters on Monday morning and was significantly correlated with the other parameters. On Friday afternoon it was three times higher than the environmental toluene concentration. Urinary o-Cresol was highly correlated with toluene in the atmosphere, in blood and with hippuric acid in urine. On the basis of the slope of the regression line the ratio between urinary o-Cresol and blood toluene concentration was 0.99. At the end of the work shift urinary hippuric acid concentration was highly correlated with o-Cresoluria and with toluene in blood and in the atmosphere.

Air Pollutants↗

Evaluation of biological monitoring parameters for occupational exposure to toluene.

A survey was conducted in a rotogravure printing plant with inhalatory and percutaneous exposure to toluene. Workers (n = 9) were followed for 2 consecutive days and the frequency and duration of skin contact with toluene were monitored. In order to assess percutaneous absorption an airstream helmet was worn during one day. Urine and exhaled air samples were collected simultaneously 5 times each day for toluene (urine and breath) and hippuric acid (urine). The mean (personal air sampling) exposure concentration was between 30 mg/m3 and 600 mg/m3. The best biological monitoring parameter of external exposure (without a helmet) was the concentration toluene in exhaled air 8 h after work (r = 0.99). While wearing the airstream helmet the relationship between external exposure (measured in the helmet) and concentrations in exhaled air and urine deviated from the preceding relations. This was likely the result of the high body burden and not of skin contact with toluene. Skin contact with toluene (usually by cleaning of the hands) was limited to 0-30 minutes a day, with an average of about 5 minutes. During experimental exposure (n = 6) in which the hands were washed with toluene for 5 minutes the toluene in exhaled air (max after 1040 min) clearly demonstrated skin absorption of toluene. The next morning 0.1 mg/m3 toluene was still detectable; this was less than the concentration measured the next morning in exhaled air of workers: between 0.5 and 10 mg/m3.

Adult↗

Subclinical effects of groundwater contaminants. III. Effects of repeated oral exposure to combinations of benzene and toluene on immunologic responses in mice.

Toxicity of environmental pollutants may be expressed as combined effects of a chemicals. Benzene, a proven hematotoxic agent, frequently occurs with toluene in cocontaminated groundwater. Groups of CD-1 male mice were exposed continuously for 4 weeks to benzene (166 mg/l), toluene (80 and 325 mg/l), and combinations of benzene (166 mg/l) + toluene (80 mg/l or 325 mg/l) in drinking water. Benzene-induced anemia was alleviated by simultaneous toluene treatment. Leukopenia and lymphopenia were observed in the case of benzene only and benzene + toluene (80 mg/l)-treated mice. The cytopenia, however, was less severe in the benzene + toluene (325 mg/l)-treated group. Immunotoxicity induced by benzene treatment alone was characterized by involution of thymic mass and suppressions of both B- and T-cell mitogeneses, mixed lymphocyte culture response to alloantigens, the tumor lytic ability of cytotoxic T-lymphocytes as determined by 51Cr-release assay, and antibody production response to T-dependent antigen (sheep red blood cells). IL-2 secretion by Con A-stimulated mouse T-cells was decreased in the benzene-treated group. Toluene (325 mg/l) completely inhibited these adverse effects when it was coadministered with benzene, while the low dose of toluene (80 mg/l) did not protect against benzene-induced depressions of immune functions. Toluene administered alone at levels up to 325 mg/l showed no obvious immunotoxic effects. Results of this study demonstrated that toluene, in sufficient amounts, has an antagonistic effect on benzene immunotoxicity.

Administration, Oral↗

Developmental toxicity of toluene in male rats: effects on semen quality, testis morphology, and apoptotic neurodegeneration.

In one study, pregnant Wistar rats were exposed to 1200 ppm toluene by inhalation 6 h a day from gestational day (GD) 7 to postnatal day (PND) 18. Sperm analysis was performed in the adult male offspring at PND 110 by using computer-assisted sperm analysis. Toluene did not affect the semen quality of exposed rats. In another study, pregnant rats were exposed to 1800 ppm from GD 7 to GD 20, and the male offspring were killed at PND 11, 21 or 90. Paired testes weight, histopathology and immunoexpression of vimentin in Sertoli cells were used as markers of testis toxicity. In the brain, the number of apoptotic cells in the hippocampus and cerebellum were counted after visualisation by means of the TUNEL assay. Mean body weight in pups of exposed dams was lower than in pups from control litters. This decrease was still statistically significant at PND 11, but at PND 21 and 90 the body weight of toluene-exposed males tended to approach that of the controls. Absolute and relative testes weights were reduced in all three age groups, although not to a statistically significant degree. Histopathological examinations of the testis and immuno-expression of vimentin did not reveal any differences between toluene-exposed animals and control animals. In the hippocampus, almost no apoptosis was observed in any age group, and there were no differences in apoptotic neurodegeneration between male rats exposed to 1800 ppm and control animals at PND 11, 21 or 90. Generally, a marked increase in number of apoptotic cells was observed in cerebellar granule cells at PND 21 compared with the other age groups. Toluene induced a statistically significant increase in the number of apoptotic cells in the cerebellar granule layer at PND 21. The mean was increased from 37 in the control group to 71 in the toluene-exposed group. Thus, the granular cell layer in cerebellum is a highly relevant tissue with which to study toluene-induced apoptosis, because of the continuous migration of neurons and high frequency of neuronal apoptosis during the weaning period. In summary, it is concluded, that neither pre- and postnatal exposure to 1200 ppm toluene nor prenatal exposure to 1800 ppm induced significant effects on the reproductive parameters investigated. However, prenatal exposure to 1800 ppm toluene did increase neuronal apoptosis in the cerebellum of weaned male rats, possibly by delaying postnatal migration of granule cells to their final destination, or by toluene-induced retardation of generalised fetal growth.

Abnormalities, Drug-Induced↗

Chlorzoxazone: a probe drug whose metabolism can be used to monitor toluene exposure in rats.

In this study we investigated cytochrome P450 (CYP) 2E1 expression using a probe drug, chlorzoxazone (CZX), whose metabolism can be used to monitor toluene exposure in rats. The animals received an i.p. injection of toluene (0.25, 0.5 and 1 ml/kg) once a day for 3 days. The total CYP and CYP2E1 content and the aniline and CZX hydroxylase activity (Vmax and CL(int)) increased depending on the dose of toluene administered. At the highest concentration (128 mM) of diethyldithiocarbamate, a specific inhibitor of CYP2E1, the production of 6-hydroxychlorzoxazone (HCZX) in microsomes from toluene-treated rats was reduced by about 80%. The IC50 values in microsomes from toluene-treated rats were between 3 and 5 microM. The production of HCZX and the activity of aniline hydroxylase in toluene-treated rats were correlated with the amount of rat CYP2E1 protein (r = 0.88 and r = 0.88, respectively). The elimination of CZX by toluene-treated rats was increased and the HCXZ production in the toluene-treated group was greater than that in the olive oil control group. The correlations between intrinsic clearance (CL(int): Vmax/Km) in vitro and total body clearance (CL(tot)) of CZX hydroxylation and the elimination half-life (t1/2) of CZX in vivo in toluene-treated rats were high (r = 0.784, P < 0.001; r = -0.678, P < 0.001, respectively). In addition, the metabolic plasma HCZX/CZX ratio did not require multiple blood sampling and 2 h after CZX administration in vivo there was also a high correlation with CL(int) (Vmax/Km) in vitro (r = -0.729, P < 0.001). In conclusion, these results demonstrate that CZX is a very good probe for monitoring induction in toluene-treated rats.

Animals↗

A comparative study of the effects of benzene, toluene, and xylenes on their in vitro metabolism and drug-metabolizing enzymes in rat liver.

Male Sprague-Dawley rats were injected ip with benzene, toluene, or a mixture of xylene isomers at 20 mmol hydrocarbon/kg daily for 3 days. The effects of administration of these hydrocarbons upon their own in vitro metabolism, as well as upon cytochrome P-450, NADPH-cytochrome c reductase, aminopyrine N-demethylase, aniline hydroxylase, glutathione, glutathione S-transferase, and UDPglucuronyltransferase in liver were studied. Each hydrocarbon studied increased its own in vitro metabolism. Benzene had no effect on the metabolism of toluene or xylenes. Toluene and xylenes increased the metabolism of benzene, toluene, and xylenes. Cytochrome P-450 was elevated by toluene and xylenes, but was not affected by benzene. NADPH-cytochrome c reductase was induced by all three hydrocarbons. Aminopyrine N-demethylase and aniline hydroxylase were induced by toluene and xylenes and were not affected by benzene. Glutathione was elevated by benzene, decreased by xylenes, and not affected by toluene. Glutathione S-transferase was induced differentially by these hydrocarbons toward various substrates: toward 1-chloro-2,4-dinitrobenzene by benzene and toluene, toward 1,2-dichloro-4-nitrobenzene by benzene and xylenes, and no effect toward 1,2-epoxy-3-(p-nitrophenoxy)propane by any hydrocarbons. UDPglucuronyltransferase was induced by benzene and toluene when o-aminophenol and phenol were used as the substrate. Xylenes had no effect. Benzene was more effective at inducing conjugation enzymes. Xylenes were more effective at inducing cytochrome P-450 dependent enzymes. Toluene was equipotent at inducing both types of enzymes. The results indicate that the addition of methyl groups to the aromatic ring affects the inductive pattern of these monocyclic aromatic hydrocarbons.

Animals↗

Toluene exposure during maturation of intraocular brain tissue transplants: alterations of host and graft cerebellar Purkinje neuron function and sensitivity to norepinephrine.

The effects of chronic toluene exposure on central neurons were examined using syngeneic grafts into the anterior chamber of the eye. Young adult albino rats with intraocular brain transplants inhaled toluene (1000 ppm) for 9 weeks starting at the time of transplantation, or from Week 8 to 17 after the graft was placed in oculo. Control animals were exposed to room air during the same intervals. Toluene treatment during development did not affect general growth or morphology of any of the brain areas examined. The distribution of neurofilament or glial fibrillary acidic protein immunoreactivity was similar in the experimental group and control group as well. Extracellular recordings of cerebellar Purkinje neurons showed a significantly reduced spontaneous firing rate, of 15-25%, both in intraocular transplants and in cerebellum in situ in toluene exposed animals. Postsynaptic sensitivity of intraocular and in situ Purkinje neurons to norepinephrine (NE) was evaluated. Purkinje neurons in transplants exposed to toluene during development were markedly supersensitive to superfused NE as compared to controls, while neither Purkinje neurons in mature cerebellar grafts nor cerebellum in situ showed any effects of the toluene treatment on NE sensitivity. The tissue content of NE in transplants exposed to toluene during maturation, evaluated with high-performance liquid chromatography coupled with electrochemical detection, was greater than that in the control grafts. Moreover, the content of free (3-methoxy-4-hydroxyphenyl) ethylene glycol (MHPG) was increased in both transplant and host cerebellum after toluene exposure. Taken together, these data indicate that toluene exposure during development of cerebellar grafts in oculo causes changes in postsynaptic noradrenergic sensitivity as well as decreased spontaneous activity of Purkinje neurons. Toluene exposure of adult cerebellum in situ or in oculo appears to decrease the Purkinje neuron discharge rate and increase NE turnover, but has no marked effect on postsynaptic NE sensitivity.

Administration, Inhalation↗

Effects of toluene inhalation on carbon dioxide production and locomotor activity in mice.

Rapid and noninvasive tests of locomotor activity (LA) and carbon dioxide production (minute volume expired CO2, or VECO2) in mice were sensitive to the effects of inhaled toluene. Compared to sham exposures, toluene at 100 ppm had no effect on LA or VECO2; at 1000 and 3000 ppm, LA increased during exposure, while VECO2 was suppressed for 6 to 24 min at the beginning of exposure. In a nominal 10,000-ppm exposure, toluene levels were increased from 1000 to 10,500 ppm in 60 min. At these levels, toluene abolished LA at concentrations above 8000 ppm, and suppressed VECO2 throughout exposure. During recovery from toluene-induced narcosis, both LA and VECO2 were elevated above control. In other studies, groups of mice inhaled toluene daily at 0, 100, 1000, or 3000 ppm, 5 hr/day for 8 or 90 days, and were tested individually 30 to 90 min after termination of exposure. Under these conditions, toluene decreased postexposure VECO2 for 1-2 weeks, altered the weekly pattern of change in VECO2, and did not affect LA. No effects of repeated, daily exposure to toluene were observed on body weight. These results demonstrate the utility of the present method to detect changes in LA and metabolic rate resulting from toluene inhalation, and suggest that different mechanisms are involved in the behavioral and metabolic responses to toluene inhalation.

Animals↗

Neonatal exposure to toluene: effects on the development of liver microsomal cytochrome P-450 and serum hormone levels in the rat.

Lactating Sprague-Dawley rats and their pups were exposed on postnatal days 1-7, 6 h/day, to 80, 500 and 1000 ppm toluene, respectively, by inhalation. Exposure to 80 ppm toluene decreased the liver microsomal AHH activity and the rate of 7 alpha- and 6 beta-hydroxylation of androstenedione in 8-day-old-pups. On the other hand, neonatal exposure to 500 or 1000 ppm toluene resulted in a significant increase in AHH and 7-ethoxyresorufin O-deethylase activities and in the formation of 16-oxygenated metabolites of androstenedione in 8-day-old animals. Exposure to toluene increased the cytochrome P-450 content at all 3 dose levels in male but not in female pups. Twenty-one days after neonatal exposure no such effects were seen in young animals of either sex. In 56-day-old male rats, however, neonatal exposure to 80 ppm toluene resulted in a decreased rate of 6 beta-hydroxylation of androstenedione and a reduced AHH activity. No such effects were seen in female rats of the same age. Neonatal exposure to toluene affected the body and liver weights in 8-day-old pups of both sexes but had no effect on these parameters in 21-day-old animals of either sex. Exposure to 80 ppm toluene during the neonatal period gave a significantly increased body weight of 56-day-old male but not of female rats of the same age although this treatment increased liver weight in both sexes at this age. Serum testosterone levels were decreased in 21-day-old male rats following neonatal exposure to 80 or 500 ppm toluene and in 56-day-old male rats exposed neonatally to 1000 ppm toluene. In conclusion, exposure to toluene during the first week of life caused significant changes in various liver microsomal cytochrome P-450 dependent enzyme activities in 8-day-old pups, whereas the long-term effects on liver metabolism of the adult animal were small.

Androstenedione↗