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Requirement of a second oxidation equivalent for ferryl oxygen transfer to styrene in the epoxidation catalyzed by myoglobin-H2O2.

Ferric myoglobin (Mb) is oxidized by H2O2 to a ferryl (FeIV = O) species and a protein radical, whereas ferrous Mb is similarly oxidized to the ferryl species without the protein radical. The protein radical is unstable and decays within 5 min, but the ferryl species is stable for more than 1 h. Previous studies have shown that styrene is oxidized to styrene oxide and benzaldehyde by ferric Mb and H2O2. We demonstrate here that the ferryl species produced from ferrous equine Mb and H2O2 does not epoxidize styrene. Furthermore, the EPR signal intensity of the protein radical formed from ferric equine Mb and the ability to oxidize styrene decrease in parallel as a function of the time separating the addition of H2O2 and styrene. The ability to oxidize styrene as a function of time after addition of H2O2 is lost much more rapidly with the H64V/K102Q/Y103F/Y146F/Y151F mutant of sperm whale Mb than with the native protein or the Y146F/Y151F mutant. The results indicate that styrene epoxidation requires a two-electron oxidized species of Mb in which the ferryl (FeIV = O) complex is coupled to a protein or highly transient (undetectable) porphyrin radical. Benzaldehyde formation appears to be catalyzed by the same oxidizing species. Styrene oxidation thus differs from linoleic acid oxygenation, which is catalyzed by the ferryl species alone.

Animals↗

Erythrocyte-dependent metabolic activation of styrene and induction of sister chromatid exchange in cultured human lymphocytes.

Human erythrocytes can oxidize styrene to styrene-7,8-oxide in the absence of the co-factors required for metabolic reactions catalysed by the microsomal cytochrome P-450 system. This probably explains the increased incidence of sister chromatid exchanges (SCEs) that was detected in whole blood lymphocyte cultures from 11 male donors after treatment in vitro (48 h) with styrene (2 mM). Styrene-7,8-oxide (0.15 mM) also induced SCEs in these cultures. Styrene (0.5-4.0 mM) increased the incidence of SCEs only slightly in cultures of isolated lymphocytes (2 X 10(4) erythrocytes/ml), but had a clear dose-dependent effect in whole blood cultures (2-4 X 10(8) erythrocytes/ml). When erythrocytes were added to purified cultures, SCE incidence increased after treatment with styrene (2 mM). Cyclophosphamide elevated the incidence of SCEs almost equally efficiently in whole blood and in isolated lymphocytes. It is suggested that styrene induces SCEs after transformation to styrene-7,8-oxide by oxyhemoglobin in erythrocytes, whereas cyclophosphamide is activated by the lymphocytes themselves.

Biotransformation↗

Platelet monoamine oxidase B activity in workers exposed to styrene.

A cross-sectional study was conducted to evaluate monoamine oxidase type B (MAO-B) activity in platelets as a biomarker of effect of styrene and perchloroethylene exposures. MAO-B is an enzyme system involved in dopamine catabolism, the impairment of which has been postulated as a mechanism of styrene-induced neurotoxicity. We previously observed an inverse association between blood styrene and MAO-B among reinforced plastics manufacturing workers. The present study included 59 male boat plant workers exposed to styrene (exposure range < 1-144 ppm, 8-h TWA). Two comparison groups comprised six male dry cleaning workers exposed to perchloroethylene (PCE; exposure range < 2-37 ppm) and 14 male laundry workers not exposed to either agent. Respiratory protection was not used by any of the styrene- or PCE-exposed workers; thus, air concentrations were regarded as valid exposure indicators. MAO-B activity (pmol/10(8) cells/h) was measured in peripheral blood platelets, using phenylethylamine as substrate. Only small overall mean differences in MAO-B were observed among the three groups; mean values were 4.21, 4.51, and 4.12 for the styrene-exposed, PCE-exposed, and laundry workers, respectively. Despite the absence of gross differences among the groups, styrene exposure was inversely related to MAO-B. Mean values for four increasing exposure group quartiles were: 5.60, 4.13, 3.69, and 3.44. The Spearman rank correlation coefficient for styrene with MAO-B was -0.41. Adjustment for age, medication use, smoking, and alcohol consumption had only a minimal effect on this trend.(ABSTRACT TRUNCATED AT 250 WORDS)

Adolescent↗

Effects on the kidney of occupational exposure to styrene.

OBJECTIVES: To elucidate the extent of nephrotoxicity of long-term occupational exposure to styrene. METHODS: In all 10 styrene-exposed workers (employed, mean age 12.6 years) and 15 nonexposed workers were studied. Each participant collected multiple overnight and end-of-shift urine samples. The sum of the urinary concentrations of mandelic acid and phenylglyoxylic acid (MAP) was determined to assess the absorbed dose of styrene. The urinary parameters alanine aminopeptidase (AAP), beta-galactosidase (beta GAL), N-acetyl-beta-D-glucosaminidase (NAG), retinol-binding protein (RBP), and albumin (ALB) were determined to assess the effects on renal function and integrity. RESULTS: The median concentration of MAP in urine was 175 mg/g urinary creatinine (CREAT-U; range 72-496 mg/g). The 8-h time-weighted average (8-h TWA) exposure to styrene was estimated from the urinary concentration of MAP and ranged from 21 to 405 mg/m3. RBP showed a borderline correlation with the dose of styrene. ALB in end-of-shift urine samples showed a borderline correlation with the absorbed dose of styrene. CONCLUSIONS: From the borderline correlation of RBP with the dose of styrene it was concluded that there might be a slight effect on the tubuli. The borderline correlation of ALB with the dose of styrene, together with the observation that five values were above the reference limit of the laboratory, suggests an effect on this parameter.

Acute Kidney Injury↗

Inhalation pharmacokinetics: evaluating systemic extraction, total in vivo metabolism, and the time course of enzyme induction for inhaled styrene in rats based on arterial blood:inhaled air concentration ratios.

A method is described for evaluating systemic extraction of soluble vapors during inhalation exposures. The physiological basis of the method is the inability to achieve complete equilibrium of vapor between arterial blood and inhaled air whenever there is substantial extraction of the soluble vapor during a single pass through the systemic circulation. The technique was applied to estimate styrene extraction ratios at the end of 6-hr exposures in male rats exposed to various concentrations of inhaled styrene. From extraction ratios and several physiological constants, metabolic constants were evaluated for styrene metabolism in vivo. In naive rats, the maximum velocity of metabolism was 10.0 mg/kg/hr, and Km was of the order of 0.2 mg/liter. Pretreatment with pyrazole (320 mg/kg, 1/2 hr before exposure) essentially abolished in vivo styrene metabolism, while pretreatment with phenobarbital (80 mg/kg/day for the 4 days before styrene exposure) increased Vmax about sixfold. Prior exposure to styrene (1000 ppm for 6 hr/day on each of 4 days before experimentation) increased Vmax by a factor of 2. Significant induction of styrene metabolism in vivo was observed in 24-hr continuous exposure to 400, 600, or 1200 ppm. A curve fitting routine was employed with a physiological model of styrene inhalation kinetics to estimate the dynamics of the induction process in the 24-hr exposures. At 400 ppm, induction began after a lag of 15.5 hr, had a half-life of 3.5 hr, and reached 2.7 times the Vmax in naive rats. At 600 ppm, it began after 10.6 hr, proceeded with a half-life of 2.2 hr, and increased Vmax by 3.4 times. At 1200 ppm, induction began earlier, 4.6 hr, and reached a greater value, 4.4 times Vmax, but had a half-life similar to that at 600 ppm. No induction occurred in 48-hr exposure to 200 ppm. Induction complicates kinetic modeling of continuous inhalation with soluble, well-metabolized vapors because it is time and concentration dependent. These methods should prove useful for studying the in vivo metabolism of other soluble, well-metabolized vapors and for examining the time course of induction of the metabolizing enzymes for these chemicals.

Air↗

The role of metallothionein induction and altered zinc status in maternally mediated developmental toxicity: comparison of the effects of urethane and styrene in rats.

We hypothesize that maternal metallothionein (MT) induction by toxic dosages of chemicals may contribute to or cause developmental toxicity by a chain of events leading to a transient but developmentally adverse decrease in Zn availability to the embryo. This hypothesis was tested by evaluating hepatic MT induction, maternal and embryonic Zn status, and developmental toxicity after exposure to urethane, a developmental toxicant, or styrene, which is not a developmental toxicant. Pregnant Sprague-Dawley rats were given 0 or 1 g/kg urethane ip, or 0 or 300 mg/kg styrene in corn oil po, on Gestation Day 11 (sperm positive = Gestation Day 0). These were maternally toxic dosages. As both treatments decreased food consumption, separate pair-fed control groups were also evaluated for effects on MT and Zn status and development. In addition, Gestation Day 11 rat embryos were exposed to urethane in vitro in order to determine whether urethane has the potential to be directly embryotoxic. Urethane treatment induced hepatic MT 14-fold over control; styrene treatment induced MT 2.5-fold. The MT induction by styrene could be attributed to decreased food intake, as a similar level of induction was observed in a pair-fed untreated control group. However, the level of MT induction by urethane was much greater than that produced by decreased food intake alone. Hepatic Zn concentration, particularly in the cytosol, was increased in the presence of increased hepatic MT concentration. Plasma Zn concentration was significantly decreased (approximately 30%) by urethane treatment, but not by styrene or food restriction (pair-feeding). Distribution of 65Zn to the liver of urethane-treated dams was significantly greater (by 30%), while distribution to embryonic tissues was significantly lower (by at least 50%) than in pair-fed or ad lib.-fed controls. Styrene treatment had no effect on 65Zn distribution. Urethane was developmentally toxic, causing an 18% decrease in fetal weight and a significant delay in skeletal ossification, but was not toxic to rat embryos in vitro. Styrene was not developmentally toxic. The changes observed after urethane treatment, namely substantial hepatic MT induction and altered maternal and embryonic Zn status, along with the lack of direct embryotoxicity of urethane in vitro, support the hypothesis that these maternal effects contribute to developmental toxicity. The lack of similar changes in styrene-intoxicated dams provides one explanation for its low developmental toxicity at maternally toxic dosages.

Abnormalities, Drug-Induced↗

Effects of various pretreatments on the acute nephrotoxic potential of styrene in Fischer-344 rats.

The effects of various inducers and inhibitors of hepatic microsomal mixed-function oxidase (MFO) system and diethylmaleate treatment on styrene-induced acute nephrotoxicity in male Fischer-344 rats were studied. Groups of rats were pretreated with either 3-methylcholanthrene (15 mg/kg, i.p., 3 days), or phenobarbital (80 mg/kg, i.p., 3 days), or SKF525-A (50 mg/kg, i.p., 1 h), or piperonyl butoxide (300 mg/kg, i.p., 2 h), or diethylmaleate (400 mg/kg, i.p., 90 min) prior to an i.p. administration of styrene (0, 0.6 and 0.9 g/kg) in corn oil. The uptake of p-aminohippurate (PAH) by renal cortical slices, the morphology of renal cortices, as well as urinary excretion of N-acetyl-beta-D-glucosaminidase (NAG) and gamma-glutamyl transpeptidase (gamma-GT) of control and pretreated rats were examined 24 h after styrene. The inducers and inhibitors of MFO system failed to modify further the acute nephrotoxicity of styrene. On the other hand, diethylmaleate pretreatment not only reduced further the uptake of PAH, but also produced further significant increase in the urinary excretion of NAG and gamma-GT observed at the higher dose of styrene. Similarly, ultrastructural studies showed a moderate increase in the severity of kidney damage induced at the higher dose of styrene due to pretreatment with diethylmaleate. These data suggest that tissue glutathione concentrations and hence, corresponding conjugating activity might be important determinants of styrene nephrotoxicity. The results further indicate that a metabolic activation system not involving certain cytochrome P-450 might be responsible in styrene-induced nephrotoxicity.

Animals↗

Effect of blood on styrene oxidation in perfused rat liver.

The oxidation of styrene to styrene oxide was studied in the isolated perfused rat liver in the presence and absence of blood at styrene concentrations of 2.5 and 50 mM. Erythrocytes contained in whole blood increased the levels of styrene glycol about 5 times after a short perfusion time with both concentrations. This increase was observed up to 1 h with 2.5 mM styrene. At both styrene concentrations styrene oxide was not detectable, either in the presence or absence of blood indicating that the liver was able completely to detoxify the styrene oxide produced by the mixed-function oxidases (MFO) and the oxyhemoglobin in the erythrocytes.

Animals↗

Evaluation of the metabolism and hepatotoxicity of styrene in F344 rats, B6C3F1 mice, and CD-1 mice following single and repeated inhalation exposures.

Styrene is used for the manufacture of plastics and polymers. The metabolism and hepatotoxicity (mice only) of styrene was compared in male B6C3F1 mice, CD-1 mice, and F344 rats to evaluate biochemical mechanisms of toxicity. Rats and mice were exposed to 250 ppm styrene for 6 h/day for 1 to 5 days, and liver (mice only) and blood were collected following each day of exposure. Mortality and increased serum alanine aminotransferase (ALT) activity were observed in mice but not in rats. Hepatotoxicity in B6C3F1 mice was characterized by severe centrilobular congestion after one exposure followed by acute centrilobular necrosis. Hepatotoxicity was delayed by 1 day in CD-1 mice, and the increase in ALT and degree of necrosis was less than observed for B6C3F1 mice. Following exposure to unlabeled styrene for 0, 2, or 4 days, rats and mice were exposed to [7-14C]-styrene (60 microCi/mmol) for 6 h. Urine, feces, and expired air were collected for up to 48 h. Most styrene-derived radioactivity was excreted in urine. The time-course of urinary excretion indicates that rats and CD-1 mice eliminated radioactivity at a faster rate than B6C3F1 mice following a single 250 ppm exposure, consistent with a greater extent of liver injury for B6C3F1 mice. The elimination rate following 3 or 5 days of exposure was similar for rats and both mouse strains. Following three exposures, the total radioactivity eliminated in excreta was elevated over that measured for one exposure for both mouse strains. An increased excretion of metabolites on multiple exposure is consistent with the absence of ongoing acute necrosis following 4 to 5 daily exposures. These data indicate that an induction in styrene metabolism occurs after multiple exposures, resulting in an increased uptake and/or clearance for styrene.

Administration, Inhalation↗

Evaluation of genotoxic potential of styrene in furniture workers using unsaturated polyester resins.

Styrene is a widely used chemical, mostly in making synthetic rubber, resins, polyesters, plastics and insulators. Increasing attention has been focused on this compound since experiments using cytogenetic end-points have implicated styrene as a potential carcinogen and mutagen. In order to perform biological monitoring of genotoxic exposure to styrene monomer, we evaluated the urinary thioether (UT) excretion, and sister chromatid exchanges (SCEs) and micronuclei (MN) in peripheral lymphocytes from 53 furniture workers employed in small workplaces where polyester resin lamination processings were done and from 41 matched control subjects. The mean air concentration of styrene in the breathing zone of workers was 30.3 ppm. As a metabolic marker for styrene exposure, mandelic acid + phenylglyoxylic acid was measured in the urine and the mean value was 207 mg/g creatinine. The mean +/- SD value of UT excretions of workers was 4.43 +/- 3.42 mmol SH-/mol creatinine and also mean UT for controls was found to be a 2.75 +/- 1.78 mmol SH-/mol creatinine. The mean +/- SD/cell values of SCE frequency in peripheral lymphocytes from the workers and controls were 6.20 +/- 1.56 and 5.23 +/- 1.23, respectively. The mean +/- SD frequencies (%o) of MN in the exposed and control groups were 1.98 +/- 0.50 and 2.09 +/- 0.35, respectively. Significant effects of work-related exposure were detected in the UT excretion and SCEs analyzed in peripheral blood lymphocytes (p < 0.05 and p < 0.01, respectively). The MN frequency in lymphocytes from the styrene-exposed group did not differ from that in the controls (p > 0.05). Effect of smoking, age and duration of exposure on the genotoxicity parameters analyzed were also evaluated. In conclusion, although our data do not demonstrate a dose-response relationship, they do suggest that styrene exposure was evident and that this styrene exposure may contribute to the observed genotoxic damage in furniture workers.

Adult↗

Cooxidation of styrene by horseradish peroxidase and phenols: a biochemical model for protein-mediated cooxidation.

Styrene is oxidized to styrene oxide and benzaldehyde when incubated with horseradish peroxidase, H2O2, and 4-methylphenol. Styrene oxide is not formed in the absence of any of these reaction components or of molecular oxygen. The coupling products 2-(4-methylphenoxy)-1-phenylethane, 2-(4-methylphenoxy)-1-phenylethan-1-ol, and 2-(4-methylphenoxy)-2-phenylethan-1-ol are not formed, but the ortho-linked dimer of 4-methylphenol is a major product. The epoxide oxygen is labeled in the presence of 18O2 but not H218O2. Styrene oxide formation is not inhibited by mannitol or superoxide dismutase. The stereochemistry of trans-[1-2H]styrene is partially scrambled in the epoxide product. EPR signals attributable to the 2,4-dihydroxy-5-methylphenoxy radical, a product of the oxidation of 4-methylcatechol, are observed if Zn2+ is added to stabilize the radical. This radical is only detected in the presence of styrene. The results imply that styrene is epoxidized by the hydroperoxy radical generated by addition of molecular oxygen to the 4-methylphenoxy radical. The epoxidation mimics the chemistry proposed to occur in the protein-mediated cooxidation of styrene by hemoglobin and myoglobin.

Electron Spin Resonance Spectroscopy↗

Comparison of mouse strains for susceptibility to styrene-induced hepatotoxicity and pneumotoxicity.

Styrene is known to cause both hepatotoxicity and pneumotoxicity in mice. Strain differences have been reported by other investigators suggesting that Swiss mice are less susceptible than non-Swiss mice to styrene-induced liver damage. In this study, A/J and C57BL/6 mice were found to be similar to non-Swiss albino (NSA) mice in susceptibility whereas CD-1 (Swiss) mice were more resistant to hepatotoxicity as assessed by serum sorbitol dehydrogenase levels and pneumotoxicity as determined by gamma-glutamyltranspeptidase and lactate dehydrogenase measurements in bronchoalveolar lavage fluid. Styrene was hepatotoxic in CD-1 mice treated with pyridine to induce CYP2E1. CYP2E1 apoprotein levels and p-nitrophenol hydroxylase activities in control and pyridine-induced mice were similar in the two strains. Hepatic and pulmonary microsomal preparations from both strains metabolized styrene to styrene oxide at similar rates. CD-1 mice were as susceptible as the NSA mice to the effects of styrene oxide. The data suggest that there are no differences in the bioactivation of styrene to styrene oxide or innate susceptibility to the active metabolite that would account for the differences between the CD-1 and NSA mice.

Animals↗

Styrene-induced alterations in the respiratory tract of rats treated by inhalation or intraperitoneally.

Although exposure to styrene occurs primarily via inhalation, the action of this agent on the respiratory tract has scarcely been investigated. This article describes morphological and biochemical changes occurring in the respiratory tract of rats after either inhalation of styrene vapors (300 ppm, 6 h/d, 5 d/wk, for 2 wk) or systemic (ip) treatment with 40 or 400 mg/kg styrene for 3 consecutive days. Electron microscopy analysis showed diffuse cell damage involving the tracheal, bronchiolar, and alveolar epithelium. In the tracheal epithelium, several cell types were affected. Ciliated cells presented vacuolation, detachment of cilia, blebbing of the apical cytoplasm, and compound cilia. Most secretory cells showed scant secretory granules and blebbings. Dense bodies and fibrillary inclusions were seen in intermediate and basal cells. Styrene also caused alterations of cytoplasmic components in type II pneumocytes and bronchiolar cells as well as thickness of the alveolar wall. These abnormalities were accompanied by depletion of glutathione (GSH) in the lung tissue. Pneumotoxic effects of systemic administration of styrene were dose dependent and tended to be more severe than those seen in the animals exposed for longer periods to styrene by inhalation. Metabolic activation of styrene and subsequent cell damage induced by the reactive metabolite styrene oxide may be involved in the sequence of events culminating in the toxic insult to the respiratory tract.

Administration, Inhalation↗

Exposure to styrene and mortality from nervous system diseases and mental disorders.

Chronic low-dose exposure to solvents has been associated in epidemiologic studies with chronic neurotoxicity, but the evidence is not consistent. Styrene causes acute disturbances in the central and peripheral nervous systems. To determine if exposure to styrene may contribute to chronic diseases of the central nervous system, the authors examined mortality from nervous system diseases, mental disorders, and suicide in relation to styrene exposure in an international historical cohort study. The cohort involved 35,443 workers employed during 1945-1991 in the reinforced plastics industry, where high exposures to styrene occur. Indicators of exposure were reconstructed through job histories and environmental and biologic monitoring data. Poisson regression was used for internal comparisons. Mortality from diseases of the central nervous system (27 deaths) increased with time since first exposure, duration of exposure, average level of exposure, and cumulative exposure to styrene. A quadratic model described best the dose-response shape for cumulative exposure and duration of exposure with the highest risks at around 300 ppm-years and 5 years, respectively, and a subsequent decrease in risk in the highest exposure categories. Mortality from epilepsy increased monotonically with all styrene exposure indicators, while associations for degenerative diseases of the central nervous system were generally weaker. Mortality from mental disorders and suicide decreased with increasing duration of exposure and cumulative exposure, while there was no trend with time since first exposure and average exposure to styrene. These findings suggest that, in addition to the known acute effects, exposure to styrene may contribute to chronic diseases of the central nervous system.

Cause of Death↗

Genetic and functional analysis of the styrene catabolic cluster of Pseudomonas sp. strain Y2.

The chromosomal region of Pseudomonas sp. strain Y2 involved in the conversion of styrene to phenylacetate (upper catabolic pathway) has been cloned and sequenced. Four catabolic genes, styABCD, and two regulatory genes, stySR, were identified. This gene cluster when transferred to Escherichia coli W confers to this phenylacetate-degrading host the ability to grow on styrene as the sole carbon and energy source. Genes styABCD are homologous to those encoding the styrene upper catabolic pathway in Pseudomonas fluorescens ST. Northern blot analyses have confirmed that genes styABCD constitute a transcription unit. The transcription start site of the sty operon was mapped 33 nucleotides upstream of the styA translational start codon. The styS and styR genes, which form an independent transcriptional unit, are located upstream of the styABCD operon, and their gene products show high similarity to members of the superfamily of two-component signal transduction systems. The styS gene product is homologous to histidine kinase proteins, whereas the styR gene product exhibits similarity at its N-terminal domain with cluster 1 of receiver modules and at its C terminus with the LuxR/FixJ family 3 of DNA-binding domains. Expression of the catabolic operon decreased significantly in the absence of the stySR genes and was restored when the stySR genes were provided in trans in the presence of styrene, suggesting that the stySR system behaves as a styrene-inducible positive regulator of the styABCD operon. Finally, a gene encoding a phenylacetyl-coenzyme A ligase that catalyzes the first step in the phenylacetate catabolism (styrene lower catabolic pathway) has been identified upstream of the styS gene. This activity was found to be induced in Pseudomonas sp. strain Y2 cells grown on styrene but not present in cells grown on glycerol. These results strongly suggest that the genes responsible for the complete mineralization of styrene are clustered in the chromosome of Pseudomonas sp. strain Y2.

Amino Acid Sequence↗

Uptake, distribution, metabolism, and elimination of styrene in man. A comparison between single exposure and co-exposure with acetone.

Six male subjects were exposed for two hours during light physical exercise to 2.81 mmol/m3 (293 mg/m3) of styrene on one occasion and to a mixture of 2.89 mmol/m3 (301 mg/m3) of styrene and 21.3 mmol/m3 (1240 mg/m3) of acetone on another (combination study). About 68% of the dose (somewhat more than 4 mmol) of styrene was taken up. The arterial blood concentration of styrene reached a relatively stable level after about 75 minutes of exposure of about 18 and 20 mumol/l after the single and combined exposure, respectively. Calculated values of mean blood clearance were 1.9 l/min in the styrene study and 1.6 l/min in the combination study; the half life of styrene in blood was about 40 minutes in both studies. The concentration of non-conjugated styrene glycol increased linearly during exposure and reached about 3 mumol/l at the end of exposure and was eliminated with a half life of about 70 minutes. Styrene-7,8-oxide was detected and quantified in the blood in a complementary study. The half lives for the excretion of mandelic and phenylglyoxylic acid in the urine were about four and nine hours, respectively, in both studies.

Acetone↗

Peripheral markers of neurochemical function among workers exposed to styrene.

A cross sectional study of biological markers of neurochemical function in peripheral blood cells, and self reported nervous system symptoms, was conducted among 60 workers exposed to styrene in three reinforced plastics plants and 18 reference workers not exposed to styrene or other solvents. Concentrations of styrene in the air at the plants ranged from less than 1 to 160 ppm. Biomarkers of neurochemical function measured were: sigma receptor binding in lymphocytes, monoamine oxidase type B (MAO-B) activity in platelets, and serotonin uptake by platelets. Blood styrene concentration was used as the exposure index to take account of the use of protective equipment and dermal uptake. Four blood styrene exposure groups were defined as: non-exposed (reference) and exposed to less than 0.05, 0.05-0.19, and greater than or equal to 0.20 micrograms/ml. The prevalences of headache, dizziness, light headedness, fatigue, irritability, memory loss, and feeling "drunk" at work increased with increasing blood styrene concentration. No effect on sigma receptor binding was seen. A slight positive correlation was found for uptake of serotonin, which has been used as an exposure related effect indicator in previous studies of workers exposed to solvents. The MAO-B activity decreased with increasing blood styrene concentration; the mean (SE) MAO-B values for the four groups were 34.2 (3.0), 28.1 (5.3), 20.1 (4.8), and 16.9 (7.7) pmol/10(7) cells/min. The MAO-B activity also correlated negatively with the number of reported nervous system symptoms, whereas no associations were seen between prevalence of symptoms and either serotonin uptake or sigma receptor binding. The findings for MAO-B activity are consistent with previously reported experimental data, and suggest that MAO-B may be a useful marker of styrene neurotoxicity.

Adult↗

Evidence for a free radical mechanism of styrene-glutathione conjugate formation catalyzed by prostaglandin H synthase and horseradish peroxidase.

We have proposed, using styrene as a model, a new mechanism for the formation of glutathione conjugates that is independent of epoxide formation but dependent on the oxidation of glutathione to a thiyl radical by peroxidases such as prostaglandin H synthase or horseradish peroxidase. The thiyl radical reacts with styrene to yield a carbon-centered radical which subsequently reacts with molecular oxygen to give the styrene-glutathione conjugate. We have used electron spin resonance spin trapping techniques to detect the proposed free radical intermediates. A styrene carbon-centered radical was trapped using the spin traps 5,5-dimethyl-1-pyrroline N-oxide (DMPO) and t-nitrosobutane. The position of the carbon-centered radical was confirmed to be at carbon 7 by the use of specific 2H-labeled styrenes. The addition of the spin trap DMPO inhibited both the utilization of molecular oxygen and the formation of styrene-glutathione conjugates. Under anaerobic conditions additional styrene-glutathione conjugates were formed, one of which was identified by fast atom bombardment mass spectrometry as S-(2-phenyl)ethylglutathione. The glutathione thiyl radical intermediate was observed by spin trapping with DMPO. These results support the proposed free radical-mediated formation of styrene-glutathione conjugates by peroxidase enzymes.

Aminopyrine↗