Search PubMed⌕ Search

SEARCH · Search PubMed

Results for “Styrenes”

Search indexed PubMed citations on genomics, clinical trials, systematic reviews and public health. Explore titles, authors and supplied subject terms, then open the PubMed record.

Quote a phrase for an exact phrase match. Source license links do not imply unrestricted reuse.

At least 199 records · Page 11Linked to original sources

Stereochemical aspects of styrene biotransformation.

Urine of rats dosed with styrene (240 mg/kg), R-, S- and racemic styrene oxide (150 mg/kg) was analysed for mandelic acid enantiomers and for regioisomers and diastereomers of mercapturic acids by NMR spectrometry. Enantiomers of mandelic acid were converted to diastereomeric Mosher's derivatives prior to analysis. R- and S-styrene oxide yielded predominantly R- and S-mandelic acid, respectively, racemic styrene oxide gave predominantly the R-enantiomer whereas styrene yielded almost racemic mandelate. The regioselectivity of mercapturic acid formation was very similar for styrene, R- and S-styrene oxide. These three species yielded a 2:1 mixture of N-acetyl-S-(1-phenyl-2-hydroxyethyl)cysteine (MA1) and N-acetyl-S-(2-phenyl-2-hydroxyethyl)cysteine (MA2). R-Styrene oxide gave higher conversion to mercapturic acids (28%) than the S-isomer (19% of the dose). However, R-styrene oxide yielded stereospecifically S,R-MA1 and R,R-MA2 whereas S-styrene oxide gave R,R-MA1 and S,R-MA2. Styrene yielded a mixture of diastereomeric mercapturic acids. The ratios of R,R-/S,R-isomers were 80:20 and 15:85 for MA1 and MA2, respectively. These data suggest that styrene is metabolised stereoselectively to S-styrene oxide as a major enantiomer in rat in vivo. This enantiomer has been reported to be less mutagenic than R-styrene oxide in vitro.

Acetylcysteine↗

CYP2C11 and CYP2B1 are major cytochrome P450 forms involved in styrene oxidation in liver and lung microsomes from untreated rats, respectively.

The contribution of cytochrome P450s (P450s) to the formation of styrene glycol from styrene in rat liver microsomes was investigated using monoclonal antibodies to P450s. Anti-CYP2E1 inhibited the formation to a similar extent in ethanol-treated microsomes and in control microsomes in terms of percentage inhibition, whereas to a greater extent in the former than the latter in terms of net inhibition, and only at low substrate concentration. Anti-CYP2C11/6 also inhibited the formation in control and in ethanol-treated microsomes at both low and high concentrations of styrene, and the net degree of inhibition was greater than that obtained with anti-CYP2E1, even in ethanol-treated microsomes where CYP2E1 was induced. Anti-CYP2B1/2 and anti-CYP1A1/2 inhibited the formation only in phenobarbital (PB)- and 3-methylcholanthrene (MC)-induced microsomes, respectively. These results suggest that (1) at least four P450s, CYP2C11/6, CYP2E1, CYP2B1/2 and CYP1A1/2, contribute to the metabolism of styrene, (2) CYP2C11/6, which probably corresponds to CYP2C11, is the major form of P450 responsible for the metabolism in untreated rat liver microsomes, and also in those treated with ethanol. Anti-CYP2E1 inhibited styrene oxidation more prominently in microsomes from styrene-treated rats than in those from control rats at a low substrate concentration. Although styrene treatment did not influence the total metabolism of styrene in liver microsomes at a high substrate concentration, inhibition of the metabolism by anti-CYP2C11/6 decreased with increasing styrene dose, whereas that by anti-CYP2B1/2 increased, suggesting that styrene treatment increases CYP2B1/2 but decreases CYP2C11/6 in rat liver, and the major form of P450 which mediates styrene oxidation is CYP2B1/2 after the treatment. Only anti-CYP2B1/2, which probably corresponds to CYP2B1, inhibited styrene oxidation in lung microsomes from untreated and even styrene-treated rats. Thus, the major form of P450 responsible for the metabolism of styrene is different in each tissue.

Animals↗

Company-level, semi-quantitative assessment of occupational styrene exposure when individual data are not available.

In epidemiological research, self-reported information about determinants and levels of occupational exposures is difficult to obtain, especially if the disease under study has a high mortality rate or follow-up has exceeded several years. In this paper, we present a semi-quantitative exposure assessment strategy for nested case-control studies of styrene exposure among workers of the Danish reinforced plastics industry when no information on job title, task or other indicators of individual exposure were readily available from cases and controls. The strategy takes advantage of the variability in styrene exposure level and styrene exposure probability across companies. The study comprised 1522 cases of selected malignancies and neurodegenerative diseases and controls employed in 230 reinforced plastics companies and other related industries. Between 1960 and 1996, 3057 measurements of styrene exposure level obtained from 191 companies, were identified. Mixed effects models were used to estimate expected styrene exposure levels by production characteristics for all companies. Styrene exposure probability within each company was estimated for all but three cases and controls from the fraction of laminators, which was reported by a sample of 945 living colleagues of the cases and controls and by employers and dealers of plastic raw materials. The estimates were validated from a subset of 427 living cases and controls that reported their own work as laminators in the industry. We computed styrene exposure scores that integrated estimated styrene exposure level and styrene exposure probability. Product (boats), process (hand and spray lamination) and calendar year period were the major determinants of styrene exposure level. Within-company styrene exposure variability increased by calendar year and was accounted for when computing the styrene exposure scores. Exposure probability estimates based on colleagues' reports showed the highest predictive values in the validation test, which also indicated that up to 67% of the workers were correctly classified into a styrene-exposed job. Styrene exposure scores declined about 10-fold from the 1960s-1990s. This exposure assessment approach may be justified in other industries, and especially in industries dominated by small companies with simple exposure conditions.

Case-Control Studies↗

Stable-isotope-based labeling of styrene-degrading microorganisms in biofilters.

Deuterated styrene ([(2)H(8)]styrene) was used as a tracer in combination with phospholipid fatty acid (PLFA) analysis for characterization of styrene-degrading microbial populations of biofilters used for treatment of waste gases. Deuterated fatty acids were detected and quantified by gas chromatography-mass spectrometry. The method was evaluated with pure cultures of styrene-degrading bacteria and defined mixed cultures of styrene degraders and non-styrene-degrading organisms. Incubation of styrene degraders for 3 days with [(2)H(8)]styrene led to fatty acids consisting of up to 90% deuterated molecules. Mixed-culture experiments showed that specific labeling of styrene-degrading strains and only weak labeling of fatty acids of non-styrene-degrading organisms occurred after incubation with [(2)H(8)]styrene for up to 7 days. Analysis of actively degrading filter material from an experimental biofilter and a full-scale biofilter by this method showed that there were differences in the patterns of labeled fatty acids. For the experimental biofilter the fatty acids with largest amounts of labeled molecules were palmitic acid (16:0), 9,10-methylenehexadecanoic acid (17:0 cyclo9-10), and vaccenic acid (18:1 cis11). These lipid markers indicated that styrene was degraded by organisms with a Pseudomonas-like fatty acid profile. In contrast, the most intensively labeled fatty acids of the full-scale biofilter sample were palmitic acid and cis-11-hexadecenoic acid (16:1 cis11), indicating that an unknown styrene-degrading taxon was present. Iso-, anteiso-, and 10-methyl-branched fatty acids showed no or weak labeling. Therefore, we found no indication that styrene was degraded by organisms with methyl-branched fatty fatty acids, such as Xanthomonas, Bacillus, Streptomyces, or Gordonia spp.

Actinomycetales↗

Metabolism of inhaled styrene in acetone-, phenobarbital- and 3-methylcholanthrene-pretreated rats: stimulation and stereochemical effects by induction of cytochromes P450IIE1, P450IIB and P450IA.

1. The effect of various cytochrome P-450 inducers, namely acetone, phenobarbital (PB) and 3-methylcholanthrene (MC), on the pharmacokinetics of styrene metabolism was studied. 2. Styrene metabolism in vivo was studied measuring phenylglyoxylic acid (PGA), the enantiomers of mandelic acid (MA), and total thioethers excreted in the urine during a 24 h period of airborne exposure to styrene at 500 cm3/m3 (2100 mg/m3). In acetone-pretreated rats, PGA and MA and thioether formation were elevated 30-50%. The R/S ratio of MA enantiomers was about two in all styrene-exposed groups except PB-pretreated rats, which showed a ratio of four. 3. Styrene metabolism in liver microsomes measured in vitro was increased by styrene 140%, acetone plus styrene by 190%, methylcholanthrene plus styrene by 180% and phenobarbital plus styrene by 250%. 4. N-Nitrosodimethylamine demethylation (NDMAD) and 7-pentoxyresorufin dealkylation (PROD) in liver microsomes were enhanced 100-150% by styrene inhalation. The metabolism of 7-ethoxyresorufin was not significantly enhanced. 5. Monoclonal antibodies to P-450 IA1, IA2, IIB1 and IIE1 were utilized to identify cytochrome P-450s by Western blot analysis. These studies showed clearly that styrene inhalation induced principally cytochrome P450IE1, whereas styrene given by gavage at a high narcotic dosage induced both P450IIE1 (NDMAD, 60%) and P450IIB (PROD, 3000%). 6. Our conclusions are that styrene metabolism in vivo in both autoinduced and induced by other foreign compounds, that cytochrome P450IIE1 induction has a major impact on styrene metabolism and that P450IIB1 induction yields an altered MA metabolite enantiomer ratio.

Acetone↗

Dose-dependent genotoxic effects of styrene on human blood lymphocytes and the relationship to its oxidative and metabolic effects.

Although the genotoxic potential of styrene is known, very limited information is available regarding its dose-dependent genotoxic response to human blood lymphocytes and how such response correlates with different metabolic events in whole blood lymphocytes. The present study was therefore carried out to study such a relationship using in vitro human blood lymphocytes from healthy volunteers. To study genotoxic response to styrene, sister chromatid exchanges (SCEs), cell cycle, and cell survival were analyzed. Lymphocytes were cultured for 72 hr in the presence of different concentrations of styrene (0-1,000 microM). Twenty-four hr before harvest, BrdU (5 micrograms/ml) was added to assess the increase in SCEs and cell cycle delay. Both the SCE frequency and the cell cycle length were increased linearly with increasing concentrations of styrene up to 200 microM, without addition of any exogenous metabolizing system. Above 200 microM, no further increase in genotoxic response occurred. The range of concentrations (10-200 microM) at which increase of cell cycle length due to styrene was observed did not impair the viability of the cells, suggesting that such cell cycle delay is a genotoxic-related event and not caused by cytotoxicity. In vitro metabolic transformation of styrene in whole-blood lymphocyte cultures without the presence of any exogenous metabolic activation system showed the formation of a reactive intermediate, styrene 7,8-oxide, to be capacity-limited, as verified from a nonlinear increase in the formation of styrene glycol. The value of such metabolic parameter reached a plateau above 200 microM styrene. The same phenomenon of saturation has also been observed with regard to other metabolic effects due to styrene in whole blood lymphocytes in culture, such as dose-dependent increase in lipid peroxidation and depletion of blood lymphocyte glutathione. Based on the relationship between the formation of different metabolic events and the genotoxicity of styrene, it may be possible that the genotoxic properties of styrene in human blood lymphocytes may be mediated initially not only by the formation of the presumably reactive styrene 7,8-oxide, but also by that of a reactive oxygen species as well. However, the present data are not sufficient enough to definitely identify the role of reactive oxygen species in such toxicity and therefore it warrants further study.

Biotransformation↗

Blood styrene concentrations in a "normal" population and in exposed workers 16 hours after the end of the workshift.

Blood styrene was measured by a gas chromatography-mass spectrometry method in 81 "normal people" and in 76 workers exposed to styrene. In the normal subjects, styrene was also tested in alveolar and environmental air. Styrene was found in nearly all (95%) blood samples. Average styrene levels in the normal subjects were 221 ng/l in blood (Cb), 3 ng/l in alveolar air (Ca) and 6 ng/l in environmental air (Ci). Styrene levels did not differ significantly between smokers and nonsmokers, 95% of values being below 512 ng/l in Cb, 7 ng/l in Ca and 15 ng/l in Ci. In workers with an average exposure to styrene of 204 micrograms/l, at the end of the workshift, mean blood styrene concentration was 1211 micrograms/l. In blood samples collected at the end of the Thursday shift, styrene levels were significantly higher (1590 micrograms/l) than those found at the end of the Monday shift (1068 micrograms/l). A similar difference was found in samples taken the morning after exposure (60 and 119 micrograms/l, respectively). Significant correlations between blood and environmental styrene were found both at the end of the shift and the morning after exposure (r = 0.61 and 0.41, respectively). In workers occupationally exposed to styrene, 16 h after the end of the workshift, blood styrene (94 micrograms/l) was significantly higher than that found in the normal subjects (0.22 microgram/l). The half-life of blood styrene was 3.9 h.

Adult↗

The effect of nutrient limitation on styrene metabolism in Pseudomonas putida CA-3.

Styrene degradation in Pseudomonas putida CA-3 has previously been shown to be subject to catabolite repression in batch culture. We report here on the catabolite-repressing effects of succinate and glutamate and the effects of a limiting inorganic-nutrient concentration on the styrene degradation pathway of P. putida CA-3 in a chemostat culture at low growth rates (0.05 h-1). Oxidation of styrene and the presence of styrene oxide isomerase and phenylacetaldehyde dehydrogenase activities were used as a measure of the expression of the styrene degradation pathway. Both glutamate and succinate failed to repress the styrene degradation ability under growth conditions of carbon and energy limitation. Lower levels of enzyme activities of the styrene degradation pathway were seen in cells grown on styrene or phenylacetic acid (PAA) under conditions of both ammonia and sulfate limitation than were seen under carbon and energy limitation. Cells grown on PAA under continuous culture oxidize styrene and styrene oxide and possess styrene oxide isomerase and NAD(+)-dependent phenylacetaldehyde dehydrogenase activities. Catabolite repression of styrene metabolism was observed in cells grown on styrene or PAA in the presence of growth-saturating (nonlimiting) concentrations of succinate or glutamate under sulfate limitation.

Aldehyde Oxidoreductases↗

The neuroepidemiology of styrene: a critical review of representative literature.

Because exposure to styrene occurs commonly in some industries and styrene is highly lipid soluble, it is reasonable to be concerned about the possibility that styrene is neurotoxic. Styrene, like many other solvents, volatile anesthetics, and drugs, does, at certain concentrations, produce acute changes in consciousness with consequent alterations of feelings, cognition, and psychomotor functioning. Such acute actions do not imply that styrene also would produce reversible or irreversible damage to the nervous system; the evaluation of long-term exposures to styrene also is necessary to draw conclusions about the full range of neural effects that styrene might produce. To that end, several studies of workers exposed to styrene for up to 30 years have been undertaken in factories in many parts of the world. Epidemiologists have suggested that neuropsychological deficits such as slowing of reaction time, loss of color vision, and vestibulooculomotor dysfunction are reliably induced by styrene at levels near or below current exposure standards, which range from 20 to 50 ppm in most of the world. However, the workers so studied always were described as healthy, and the effects noted were considered to be subclinical. A detailed evaluation of much of the neuroepidemiological literature on styrene (38 papers and related literature), however, indicated that the findings were, almost universally, false positive outcomes due to (1) type I statistical error, (2) the action of some factor other than styrene, and (3) misinterpretation of data. Despite the study of workers exposed for many years, no indications of persisting damage to the nervous system were evident from this review. The conclusions of this review of the neuroepidemiology of styrene are consistent with those based on critical reviews of the solvent literature in general, with specific reference to the probable absence of such an entity as the "painter's syndrome" or "chronic toxic encephalopathy". Because the results on styrene neurotoxicity that provide an inclination to lower the current threshold limit values (TLVs) are false positive findings, there is no scientific basis for a reduction in the current TLV.

Animals↗

Influence of GSTM1 and GSTT1 genotypes on sister chromatid exchange induction by styrene in cultured human lymphocytes.

Glutathione S-transferases M1 (GSTM1) and T1 (GSTT1) are polymorphically expressed in humans; about 47% and 13% of Finns lack the GSTM1 and GSTT1 activity due to homozygous deletion of the respective genes (null genotypes). We previously observed that GSTT1 null genotype was associated with increased induction of sister chromatid exchanges (SCEs) by a metabolite of styrene, styrene-7,8-oxide, in human lymphocyte cultures, while GSTM1 genotype had no effect. In the present study, we examined the potential effect of these genotypes on SCE induction by the parent compound styrene. Seventy-two hour whole-blood lymphocyte cultures from 24 healthy human donors, representing all different combinations of these genotypes, were examined. In agreement with our earlier findings, styrene was an efficient inducer of SCEs in cultures of all donors. In two separate experiments, the mean number of SCEs/cell induced by 1.5 mM styrene was 1.55 times (P = 0.011) or 1.34 times (P = 0.015) higher in subjects lacking both GSTM1 and GSTT1 than in subjects having both genes. Donors null for only one of the genes showed intermediate SCE induction by styrene. At 0.5 mM styrene, no clear differences in SCE rates among the genotypes were seen. Our results suggest that the concurrent lack of the GSTM1 and GSTT1 genes increases the genotoxic effects of styrene in human cells. The discrepant findings obtained for the importance of GSTM1 genotype in modulating the genotoxic effects induced by styrene-7,8-oxide and styrene may reflect a difference between a direct treatment with styrene-7,8-oxide and its formation from styrene in the cells. Although glutathione conjugation is a minor route in styrene detoxification in human liver in vivo, individual sensitivity associated with GSTM1 and GSTT1 null genotypes may be important locally in blood circulation and in blood-forming organs.

Cells, Cultured↗

Pharmacokinetics of inhaled styrene in rats and humans.

The pharmacokinetic profile of inhaled styrene was examined in rats exposed to levels of 80, 200, 600 or 1,200 ppm for periods of up to 24 h. At levels up to 200 ppm for 6 h, styrene was cleared from the blood according to a two-compartment linear pharmacokinetic model, but at levels of 600 ppm and above the clearance was saturated. In going from 80 to 1,200 ppm (a 15-fold increase), the area under the blood concentration/time curves (AUC) increased by a factor or 112. Fat tissue was shown to comprise the second compartment of the two-compartment pharmacokinetic model. It is suggested that saturation of styrene clearance is due mostly to saturation of the metabolic capacity for styrene. In humans exposed to 80 ppm of styrene for 6 h, styrene was cleared from the blood according to a two-compartment linear pharmacokinetic model similar to that for rats. A maximum blood concentration of 0.9 microgram/ml was reached at the end of the exposure. Most of the inhaled styrene was excreted in the urine as phenylglyoxylic and mandelic acids, and only a small amount as styrene in the expired air. Simulation of the pharmacokinetic model showed that no continued accumulation of styrene would occur during repeated, daily 8-h exposures to 80 ppm. These data reveal that the rat is a reasonable pharmacokinetic model for styrene in humans. At levels of exposure up to 200 ppm, styrene is cleared from the body very efficiently and will not continue to accumulate upon repeated exposure. But at levels of styrene sufficiently high to saturate the metabolic clearance capacity, the integrated dose (measured by the AUC) will be much greater than expected based on exposure levels alone. Therefore, the extrapolation of toxicity observed at high levels of styrene exposure to that expected at low levels may not be justified.

Adipose Tissue↗

Urinary mercapturic acid diastereoisomers in rats subchronically exposed to styrene and ethanol.

Styrene is stereoselectively oxidized by cytochrome P450 to its reactive metabolite, styrene oxide. The (R)- and (S)-enantiomers of styrene oxide can be conjugated with glutathione (GSH) to both (R)- and (S)-diastereoisomers of the specific mercapturic acids, N-acetyl-S-(1-phenyl-2-hydroxyethyl)-L-cysteine (M1) and N-acetyl-S-(2-phenyl-2-hydroxyethyl)-L-cysteine (M2). Several investigations have indicated different toxic potential of the (R)- and (S)-configurations of styrene oxide and its GSH- and N-acetyl-conjugates. In this study the mercapturic acid diastereoisomers were measured in the urine of rats exposed to styrene in combination with ethanol, a good inducer of styrene metabolism. Male Sprague-Dawley rats were given an isocaloric liquid diet containing ethanol (5% w/v) for 3 weeks. Starting from the 2nd week, the animals were also exposed to styrene vapours (300 ppm, 6 h/day, 5 days/week) in a dynamic exposure chamber. Both the (R)- and (S)-diastereoisomers of the M1 and M2 as well as the conventional biomarkers, mandelic acid (MA) and phenylglyoxylic acid (PGA) were measured in urinary samples. Approximately 30 and 25% reduction of the levels of brain non-protein sulfhydryls (NPS) was observed in the animals given styrene and ethanol, respectively, while the combined ethanol and styrene treatment resulted in a 60% decrease. Ethanol consumption also resulted in higher urinary levels of the M1-R, M1-S and M2 metabolites associated with increased M1-R/S ratio and higher urinary MA excretion compared to animals treated with styrene. These results suggest that the urinary mercapturic acid diastereoisomers may be used as a noninvasive tool to examine stereoselective patterns of styrene metabolism in vivo, as well as their alterations caused by ethanol. These compound-specific mercapturic acids may also be valuable indicators of styrene-induced disorders of GSH homeostasis in nonaccessible organs.

Acetylcysteine↗

A physiologically based description of the inhalation pharmacokinetics of styrene in rats and humans.

A physiologically based pharmacokinetic model which describes the behavior of inhaled styrene in rats accurately predicts the behavior of inhaled styrene in humans. The model consists of a series of mass-balance differential equations which quantify the time course of styrene concentration within four tissue groups representing (1) highly perfused organs, (2) moderately perfused tissues such as muscle, (3) slowly perfused fat tissue, and (4) organs with high capacity to metabolize styrene (principally liver). The pulmonary compartment of the model incorporates uptake of styrene controlled by ventilation and perfusion rates and the blood:air partition coefficient. The metabolizing tissue group incorporates saturable Michaelis-Menten metabolism controlled by the biochemical constants Vmax and Km. With a single set of physiological and biochemical constants, the model adequately simulates styrene concentrations in blood and fat of rats exposed to 80, 200, 600, or 1200 ppm styrene (data from previously published studies). The simulated behavior of styrene is particularly sensitive to changes in the constants describing the fat tissue group, and to the maximum metabolic rate described by Vmax. The constants used to simulate the fate of styrene in rats were scaled up to represent humans. Simulated styrene concentrations in blood and exhaled air of humans are in good agreement with previously published data. Model simulations show that styrene metabolism is saturated at inhaled concentrations above approximately 200 ppm in mice, rats, and humans. At inhaled concentrations below 200 ppm, the ratio of styrene concentration in blood to inhaled air is controlled by perfusion limited metabolism. At inhaled concentrations above 200 ppm, this ratio is controlled by the blood:air partition coefficient and is not linearly related to the ratio attained at lower (nonsaturating) exposure concentrations. These results show that physiologically based pharmacokinetic models provide a rational basis with which (1) to explain the relationship between blood concentration and air concentration of an inhaled chemical, and (2) to extrapolate this relationship from experimental animals to humans.

Administration, Oral↗

Styrene-induced hepatotoxicity in mice depleted of glutathione.

In mice depleted of glutathione (GSH) by pretreatment with an inhibitor of GSH synthesis, buthionine sulfoximine (BSO; 1 hr before styrene, 2 mmol/kg or higher doses, ip), styrene (0.96-5.76 mmol/kg, po) produced hepatotoxicity characterized by an increase in serum alanine transaminase activity and cetrilobular necrosis of hepatocytes. Treatment with inhibitors of hepatic cytochrome P-450-dependent monooxygenases such as carbon disulfide, methoxsalen, piperonyl butoxide, and SKF-525A prevented or tended to reduce the hepatotoxic effect of styrene given in combination with BSO. Styrene 7,8-oxide (3.84 mmol/kg, po), a known metabolite of styrene, in combination with BSO caused an earlier and larger increase in SALT than that caused by an equimolar dose of styrene in combination with BSO. These results suggest that metabolism of styrene, possibly to styrene 7,8-oxide, is a necessary step in styrene-induced hepatotoxicity in GSH-depleted mice. Before the onset of hepatotoxicity, styrene in combination with BSO produced a larger and more prolonged depletion of hepatic GSH than that seen after the sole treatment with BSO or prolonged depletion of hepatic GSH than that seen after the sole treatment with BSO or styrene, but no depletion of hepatic protein sulfhydryls was induced by styrene in combination with BSO.

Alanine Transaminase↗

The toxicity of styrene to the nasal epithelium of mice and rats: studies on the mode of action and relevance to humans.

Inhaled styrene is known to be toxic to the nasal olfactory epithelium of both mice and rats, although mice are markedly more sensitive. In this study, the nasal tissues of mice exposed to 40 and 160 ppm styrene 6 h/day for 3 days had a number of degenerative changes including atrophy of the olfactory mucosa and loss of normal cellular organisation. Pretreatment of mice with 5-phenyl-1-pentyne, an inhibitor of both CYP2F2 and CYP2E1 completely prevented the development of a nasal lesion on exposure to styrene establishing that a metabolite of styrene, probably styrene oxide, is responsible for the observed nasal toxicity. Comparisons of the cytochrome P-450 mediated metabolism of styrene to its oxide, and subsequent metabolism of the oxide by epoxide hydrolases and glutathione S-transferases in nasal tissues in vitro, have provided an explanation for the increased sensitivity of the mouse to styrene. Whereas cytochrome P-450 metabolism of styrene is similar in rats and mice, the rat is able to metabolise styrene oxide at higher rates than the mouse thus rapidly detoxifying this electrophilic metabolite. Metabolism of styrene to its oxide could not be detected in human nasal tissues in vitro, but the same tissues did have epoxide hydrolase and glutathione S-transferase activities, and were able to metabolise styrene oxide efficiently, indicating that styrene is unlikely to be toxic to the human nasal epithelium.

Alkynes↗

Assessment of biotransformation of the arene moiety of styrene in volunteers and occupationally exposed workers.

Styrene is a chemical widely used in the plastic industry. The main pathway of styrene metabolism in humans occurs via the oxidation to styrene-7,8-oxide (7,8-SO). The aim of this study was the investigation of a minor metabolic route, involving the oxidation of the arene moiety of styrene, by means of the characterization of the conjugated urinary metabolites of 4-vinylphenol (4-VP). 4-vinylphenol-glucuronide (4-VP-G) and -sulfate (4-VP-S), were measured by liquid chromatography electrospray tandem mass spectrometry (LC-ESI-MS/MS) from 174 workers belonging to three cohorts recruited in European countries and from 26 volunteers exposed to 50 mg/m(3) (11.8 ppm) of styrene for 8 h. The 4-VP conjugates represented about 0.5-1% of the total excretion of styrene metabolites. Both 4-VP-G and 4-VP-S are eliminated with a monophasic kinetic, the glucuronide being excreted faster (half-time, 2.2 +/- 0.2 h) than the sulfate (half-time 9.7 +/- 1.7 h). The urinary 4-VP was found to be significantly correlated both with airborne styrene (r = 0.607, p < 0.001) and the sum of MA and PGA (r = 0.903, p < 0.001 in "end-of-shift" samples). Apart from 7,8-SO, 4-VP is the only styrene metabolite not shared with ethylbenzene and therefore thought to be a highly specific marker of styrene exposure. However, a measurable background excretion of 4-VP was also found in all urine samples from controls not occupationally exposed to styrene. This background appears to be highly correlated to smoking (p < 0.001) and possibly also to the dietary intake of styrene or 4-VP. Consequently, the use of 4-VP as a biomarker of styrene exposure is recommended for exposures exceeding 1 ppm.

Adult↗

New aspects in genotoxic risk assessment of styrene exposure--a working hypothesis.

Styrene is one of the most important plastic monomers worldwide. Styrene-7,8-oxide (SO), the major in-vivo metabolite of styrene, is classified as probably carcinogenic to humans and carcinogenic in rodents. Biological monitoring of exposure to styrene is usually carried out by determination of mandelic acid and phenylglyoxylic acid, the two main styrene metabolites in urine. SO binds covalently to human plasma protein and haemoglobin. The ability of SO to induce DNA adducts and DNA strand-breaks has been well documented. Recently in-vitro results showed that SO may disrupt the pre-existing oxidative status in white blood cells. This disruption would alter the balance between oxidants and antioxidants in cells. Styrene exposure can also result in oxidative DNA damage. A significant increase of 8-hydroxy-2;-deoxyguanosine (8-OHdG) has been found in white blood cells of styrene-exposed workers. According to these findings we propose a new hypothesis for the genotoxic risk assessment of styrene. Depletion of glutathione and increase in lipid peroxidation, similarity in the decrease of high molecular weight (HMW) DNA fragments after SO exposure compared to hydrogen peroxide (H(2)O(2)) exposure, oxidative DNA damage (increased amounts of 8-OHdG and an increased level of DNA strand-breaks) following styrene or SO exposure are due to oxidative stress which can be a result of the imbalance between oxidants and antioxidants. Formation of protein-, RNA- and DNA-adducts, changes in DNA repair capacity and styrene metabolism following styrene exposure could cause this imbalance between oxidants and antioxidants. Oxidative stress seems to be the basis for genotoxic risk assessment of styrene.

Humans↗

Perspectives on the genotoxic risk of styrene.

Styrene is a highly reactive monomer widely used in the plastics industry. The potential for styrene to produce genotoxic effects has been studied extensively in experimental systems. Styrene can induce sister chromatid exchanges (SCE) and chromosome aberrations (CA) in vitro under test conditions that enhance metabolism of styrene to styrene 7,8-oxide (SO)or reduce detoxification of 50 by epoxide hydrolase. The in vivo animal data indicate that styrene is not clastogenic at concentrations (doses) likely encountered by humans under ambient or occupational exposure conditions. DNA binding studies with styrene in rats and mice demonstrated no increased adducts in mice compared to rats or in mouse lung compared to liver. As a result, DNA adducts in the lungs are unlikely to be the sole explanation of the development of lung tumors in mice exposed to styrene for 2 yr. Some epidemiological studies reported that DNA and/or protein adducts and DNA strand breaks result from occupational exposure to styrene and/or 50. Results of some of these studies, how-ever, are difficult to interpret, given that the statistical significance of reported effects (SCE, CA, and micronucleus formation) was often near or at p values of .05; dose and/or temporal response relationships often were missing; confounding variables could not be excluded; and, concomitant exposures to other industrial chemicals that are potentially genotoxic may also have occurred. These studies suggest that styrene, through metabolism to SO, could be clastogenic in humans at workplace levels in excess of 125 mg/m3. However, results from controlled animal studies involving in vivo exposure to styrene alone do not show clastogenic effects at exposures of up to 1500 mg/m3/d. In any event, these studies show that there is an apparent threshold for styrene-mediated effects.

Animals↗