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Styrene, its metabolism and the evaluation of hazards in industry.

The main products of styrene biotransformation excreted in human urine are mandelic and phenylglyoxylic acids. Phenylethylene oxide seems to be the first metabolite; this compound has been reported to be mutagenic and carcinogenic. The polarographic determination of mandelic acid has been used for about 20 years in Czechoslovakia as an exposure test for persons occupationally exposed to styrene. Only single cases of health damage have been reported to be due to styrene exposure during this time. Recently, however, elevated frequencies of chromosomal aberrations in peripheral lymphocytes have been observed in persons exposed to styrene in Czechoslovakia. The amount of phenylethylene oxide that can be formed in the human body during exposure to 50 ppm of styrene in air during a workshift is about 0.7 g. It would be hardly justifiable now to believe that styrene is not carcinogenic and mutagenic in man. The present Czechoslovakian maximum allowable concentration of styrene (200 mg/m3) should be reduced, and the concentration of 50 mg/m3 may be recommended as reasonable at this time. The corresponding biological limit value of mandelic acid might be 300 mg/l of urine from the last 2 h of the workshift.

Air Pollutants↗

[Styrene migration into wine contained in polyester resin tanks].

The use of polyester resins in wine tanks manufacture or coating has widely spread during the past five years; this type of material has been and is still the source of organoleptic damage due to non polymerized sytrene migration into urine. Sytrene is a solvant often used in resin polymerization: it act as a reticulation agent of insaturated linear polyester. Polymerization at room temperature is allowed gy additives but has to be completed in warm air or in steam. An excess of styrene is often used for a polymerisation as complete as possible and remains on a free form. Then it migrates from the tank walls into the wine. For a better understanding of the styrene migration mechanism studies were performed on two levels: from small containers (4 l) kept in the laboratory and from tanks (30 hl) set up in an I.N.R.A. wine estate in all conditions usually realized in practice. Influence of time, temperature and alcohol content were studied. Styrene migration was interpreted as a diffusion phenomenom and styrene diffusion coefficients were calculated for several temperatures. Knowledge of these coefficients and of styrene content of the tank walls allow the prediction of a tank behaviour in time. Other substances that styrene were detected in wine and in tank walls, they are impurities either from resins like ethylbenzene, or from the catalyst like mesityl oxide. The lattest has never been mentioned in the litterature. From the results obtained it is possible to give some advices to manufacturers and users of polyester resin tanks, about the quality of raw materials, resins and additives along with the conditions carried and for their use and about the control of monomer styrene content in the walls of just manufactured tank.

Food Contamination↗

A critical review of the neurotoxicity of styrene in humans.

Styrene monomer is an aromatic industrial solvent. It is used to make polystyrene, resins, rubber, reinforced material and boats. Humans are exposed to styrene in occupational situations mostly during spraying processes at work, most of which is inhaled. The major neurotoxic effects of styrene as reviewed are prenarcotic effects, electroencephalographic abnormalities, slowing of motor, sensory and distribution nerve conduction velocities that reveal the possibility of polyneuropathy, dysfunction of the autonomic nervous system, slowing of reaction times, and centrally-controlled otoneurotoxicity. In acute exposure situations reversal of adverse effects has been observed; however, the impact of long-term exposure needs further studies. Dopamine depletion has been reported as a neurochemical basis of the neurotoxicity of styrene. Styrene epoxide, a toxic intermediate metabolite, has also been reported to deplete glutathione and cause lipid peroxidation, possibly leading to neuronal membrane damage. Raised concentrations of glial fibrillary acidic protein has been reported as an indicator of neurotoxicity in rats, which may damage the brain through astrogliosis phenomenon. This damage is also correlated to the toxic effects of styrene epoxide. Recently decreased monoamine oxidase type B activity in peripheral blood cells has been investigated as biochemical indicator of neurotoxicity of styrene in workers. There is a need for long-term studies, consideration of confounding factors (smoking, alcohol, diet, drugs, working environment and exposure to other solvents), and the effects on different ethnic and racial groups. More electroencephalographic studies and computer tomographic investigations are desired. Further reduction of the exposure limit to below 50 ppm is recommended.

Animals↗

Resistance to nonspecific protein adsorption by poly(vinyl alcohol) thin films adsorbed to a poly(styrene) support matrix studied using surface plasmon resonance.

Thin films of poly(vinyl alcohol) (PVA) polymer were prepared on a flat, nonporous, poly(styrene) support matrix by adsorption from aqueous solution and were characterized in order to investigate the nonspecific adsorption of proteins to a chromatographically relevant surface. The integrity and surface coverage of the PVA thin films were established by surface analysis and atomic force microscopy imaging. The adsorption of the PVA polymers to the poly(styrene) substrate and the nonspecific adsorption of proteins to the PVA-coated surface were monitored using surface plasmon resonance. PVA was strongly bound to the poly(styrene) surface, but the surface density of the adsorbed PVA polymers was affected substantially by the concentration, molecular weight, and degree of hydrolysis of PVA polymers used. There was evidence of increasing degrees of unfolding of the PVA polymer onto the poly(styrene) surface as the concentration of the the PVA coating solution increased. Complete PVA coverage of the poly(styrene) surface was observed at PVA concentrations of 0.1 mg/mL or greater but with significant influence of both molecular weight and degree of hydrolysis of the PVA polymers. Resistance of the PVA-coated poly(styrene) surface to the nonspecific adsorption of human serum albumin (HSA) correlated with the degree of surface coverage of the PVA. The use of anti-HSA as a probe for adsorbed HSA suggested that HSA was displacing PVA from the poly(styrene) surface at the lower PVA surface coverage. A complete barrier to nonspecific protein adsorption was observed with a PVA coating solution concentration of greater than 0.1 mg/ mL with a degree of hydrolysis of <88%.

Adsorption↗

Kinetic mechanism of the enantioselective conversion of styrene oxide by epoxide hydrolase from Agrobacterium radiobacter AD1.

Epoxide hydrolase from Agrobacterium radiobacter AD1 catalyzes the enantioselective hydrolysis of styrene oxide with an E value of 16. The (R)-enantiomer of styrene oxide is first converted with a k(cat) of 3.8 s(-1), and the conversion of the (S)-enantiomer is inhibited. The latter is subsequently hydrolyzed with a k(cat) of 10.5 s(-1). The pre-steady-state kinetic parameters were determined for both enantiomers with stopped-flow fluorescence and rapid-quench techniques. For (R)-styrene oxide a four-step mechanism was needed to describe the data. It involved the formation of a Michaelis complex that is in rapid equilibrium with free enzyme and substrate, followed by rapid and reversible alkylation of the enzyme. A unimolecular isomerization of the alkylated enzyme precedes the hydrolysis of the covalent intermediate, which could be observed due to an enhancement of the intrinsic protein fluorescence during this step. The conversion of (S)-styrene oxide could be described by a three-step mechanism, which also involved reversible and rapid formation of an ester intermediate from a Michaelis complex and its subsequent slow hydrolysis as the rate-limiting step. The unimolecular isomerization step has not been observed for rat microsomal epoxide hydrolase, for which a kinetic mechanism was recently established [Tzeng, H.-F., Laughlin, L. T., Lin, S., and Armstrong, R. N. (1996) J. Am. Chem. Soc. 118, 9436-9437]. For both enantiomers of styrene oxide, the Km value was much lower than the substrate binding constant K(S) due to extensive accumulation of the covalent intermediate. The enantioselectivity was more pronounced in the alkylation rates than in the rate-limiting hydrolysis steps. The combined reaction schemes for (R)- and (S)-styrene oxide gave an accurate description of the epoxide hydrolase catalyzed kinetic resolution of racemic styrene oxide.

Binding Sites↗

Torsional barriers for planar versus twisted singlet styrenes.

Kinetic modeling of the temperature-dependent lifetimes of styrene and several methyl-substituted styrenes has been used to obtain the torsional barriers for singlet-state C=C rotation. The barrier for C=C torsion is found to be correlated with the ground-state phenyl-vinyl dihedral angle, varphi, planar styrenes having barriers of approximately 6.5 kcal/mol and moderately twisted styrenes having smaller barriers. Highly twisted styrenes undergo exceptionally rapid intersystem crossing. This unexpected dependence of excited-state behavior on varphi is attributed to a change in the character of the excited states from delocalized for planar styrenes to localized for highly twisted styrenes.

Journal Article↗

Synthesis, structure, and reactions of stable oxametallacycles from styrene oxide on Ag(111).

Styrene oxide undergoes an activated ring opening on Ag(111) at temperatures above 200 K. The product of this reaction is a stable oxametallacycle intermediate. The structure of this species has been obtained by density functional theory calculations and the computed vibrational spectrum is consistent with the experimental spectrum obtained using high-resolution electron energy loss spectroscopy. The oxametallacycle formed by ring-opening styrene oxide is structurally analogous to that previously observed for ring opening of epoxybutene on Ag(110) and represents the largest member of this adsorbate structure class yet isolated. In both cases, the epoxide ring opens at the carbon bearing the pendant unsaturated group, and the pendant group (phenyl in styrene oxide) is oriented nearly parallel to the surface plane. The oxametallacycle formed from styrene oxide reacts at 485 K to regenerate styrene oxide plus small amounts of phenylacetaldehyde. This peak temperature is similar to that previously reported for generation of styrene oxide from adsorbed styrene and oxygen atoms on Ag(111), suggesting that the epoxidation proceeds via the oxametallacycle intermediate isolated in the present work.

Journal Article↗

Role of manganese oxide octahedral molecular sieves in styrene epoxidation.

Manganese oxide octahedral molecular sieves having 2 x 2 tunnel structure (OMS-2) and synthesized by different methods were used for studying styrene oxidation with tert-butyl hydroperoxide (TBHP) as the oxidant. The catalytic activity of the as-synthesized OMS-2 materials was investigated. The physical and chemical properties of the OMS-2 materials are related to their activity in styrene oxidation. This particular study emphasizes the acid-base properties and the porous nature of these materials, and their role in styrene oxidation. Results of styrene oxidation reveal that acidity coupled with high porosity play a crucial role in these catalytic reactions. A desired acidity coupled with pore volume found in OMS-2 synthesized by reflux methods (OMS-2(R)) and high-temperature methods (OMS-2(HT)) produces materials with higher styrene conversion and styrene oxide selectivity when compared with OMS-2 synthesized by solvent free (OMS-2(S)), microwave (OMS-2(MW)), or hydrothermal methods (OMS-2(HY)). Transition metal doped OMS-2 catalysts show better selectivity of styrene oxide when compared to their undoped catalysts.

Journal Article↗

Adhesion of L1210 cells to modified styrene copolymer surfaces in the presence of serum.

The static adhesion of living L1210 cells (in serum-containing medium) to the surface of (styrene/methylmethacrylate) copolymers differing in styrene content (from 5% to 50% of styrene units) was investigated. The examination of wettability of the copolymer surfaces showed that the contact angle of water on the hydrophobic surfaces is an increasing linear function of styrene content in the copolymer. Cell adhesion to the unwettable surfaces is low (within 2-4%). A novel method of modification of the styrene copolymer surfaces was used to render these surfaces suitable for cell attachment. The modification consists of sulfonation of the surfaces with sulfur trioxide at the gas/solid interface. The contact angle of sulfonated copolymer surfaces is a decreasing linear function of styrene content in the copolymer. The contact angle decreases due to the increased number of highly hydrophilic sulfonic groups bonded to styrene. By acetylation of the sulfonated surfaces it was shown that cell adhesion to acetylated surfaces is not diminished and is at the same level as cell adhesion to sulfonated copolymer surfaces. Thus, it can be concluded that sulfonation of copolymer surfaces does not form hydroxyl groups. Cell adhesion to substrata of high wettability stabilizes after 30s. The relative number of cells adhering to the sulfonated copolymer surfaces is a decreasing linear function of the contact angle. For the copolymer surfaces containing 50% of styrene units the contact angle decreases sevenfold, due to sulfonation, and the number of adhering cells increases 40-fold. The results obtained show that for cell-substratum adhesive interaction the presence of sulfonic groups at the substratum surface is important.

Animals↗

Ototoxic effects of styrene alone or in concert with other agents: A review.

Styrene is an organic solvent employed in many manufacturing industries, as well as in other economic sectors. Recently, evidence is beginning to accumulate on the hazardous effects that styrene exposures have on the auditory system. In rats, a well-suited metabolic animal model for these studies, aromatic solvents seem to affect the auditory sensitivity mainly in the cochlear mid-frequency range. Outer hair cells are the primary targets within the organ of Corti, although the spiral ganglions are not spared. Therefore, styrene must be considered as an ototoxic chemical agent that can be potentially neurotoxic. Finally, noise-styrene exposures can have synergistic effects on the auditory system. The findings reported in both human and animal studies indicate that exposures to styrene, or to styrene associated to noise, may dramatically impact occupational hearing conservation practices and legislation. Human and animal studies will be summarized in discussing the effects of styrene alone or in combination with noise and other chemicals. Gaps in scientific knowledge are highlighted to assist future research.

Journal Article↗

Bioassay of Styrene for Possible Carcinogenicity (CAS No.100-42-5).

Styrene, a widely used intermediate in the manufacture of plastics, elastomers, and resins, was selected for bioassay by the National Cancer Institute because of the widespread use of this compound and a lack of adequate carcinogenicity data. A bioassay for the possible carcinogenicity of styrene was conducted using Fischer 344 rats and B6C3F1 mice. Styrene was administered by gavage to groups of 50 male and 50 female animals of each species. Forty rats of each sex and twenty mice of each sex were placed on test as vehicle controls. The high, medium, and low dosages of styrene administered to rats were, respectively, 2,000, 1,000, and 500 mg/kg. The high and low dosages administered to mice were 300 and 150 mg/kg, respectively. The compound was administered for 78 weeks to high and medium dose rats, for 103 weeks to low dose rats, and for 78 weeks to mice. The period of compound administration was followed by an observation period of 27 weeks for high and medium dose rats, 1 week for low dose rats, and 13 weeks for mice. Mortality among male and female high dose rats was significantly higher than that among their respective vehicle controls. In response to this elevated and early mortality, an additional dosed group of each sex was included in the chronic bioassay. No significant positive association was apparent between dosage and mortality among any other dosed rat groups. For mice, there was a significant positive association between mortality and the dosages of styrene administered to males, but not to females. Adequate numbers of animals in all groups, except for the high dose male and female rats, survived sufficiently long to be at risk from late-developing tumors. Slight dose-related mean body weight depression was apparent when male rats and female mice were compared to their respective vehicle controls, indicating that the dosages administered to these animals during the chronic bioassay may have approximated the maximum tolerated dosages. There was no distinct depression in mean body weight when dosed female rats anddosed male mice were compared to their respective vehicle controls. However, since there was significant accelerated mortality among high dose female rats, it is possible that the dosage administered to the medium dose female rats may have exceeded the maximum tolerated dosage. In male mice, there was a significant positive association between styrene dosage and the incidences of a combination of adenomas and carcinomas of the lung. This finding was supported by the high dose to control Fisher exact comparison. However, the variation of the incidence of these neoplasms in historical control male mice at this laboratory does not permit a firm conclusion of carcinogenicity. There was no significant difference between tumor incidence at any other site in male mice, or at any site in rats or female mice, when dosed groups were compared to vehicle controls. The findings of an increased incidence of a combination of adenomas and carcinomas of the lung provided suggestive evidence for the carcinogenicity of styrene in male B6C3F1 mice. However, it is concluded that, under the conditions of this bioassay, no convincing evidence for the carcinogenicity of the compound was obtained in Fischer 344 rats or B6C3F1 mice of either sex. Levels of Evidence of Carcinogenicity: Male Rats: Negative Female Rats: Negative Male Mice: Equivocal Female Mice: Negative Synonyms: ethenylbenzene; vinylbenzene; vinylbenzol; styrolene; styrol; styrole; styropol; styropor; styron; cinnamene; cinnamol; phenethylene; phenylethylene; phenylethene

Journal Article↗

Estimation of the styrene 7,8-oxide-detoxifying potential of epoxide hydrolase in glutathione-depleted, perfused rat livers.

The importance of epoxide hydrolase in preventing styrene 7,8-oxide-induced hepatoxicity was studied in isolated perfused rat livers depleted of GSH. GSH depletion was accomplished by treating the rats with diethyl maleate 45 min before surgical removal of their livers. Diethyl maleate itself caused mild hepatotoxicity that was observed histologically and measured biochemically by the release of hepatic transaminase enzymes into the circulation. GSH transferase activity was decreased in perfused livers from diethyl maleate-treated rats as shown by the persistence of circulating styrene oxide compared with that seen in experiments with livers from control animals. In the absence of GSH transferase activity, the rate of styrene oxide biotransformation by epoxide hydrolase was sufficient to prevent measurable hepatotoxicity, up to epoxide concentrations tolerated by livers from control rats. The administration of 500 mumol of styrene oxide to perfused livers from diethyl maleate-treated rats caused periportal necrosis and extensive covalent binding of styrene oxide-derived radioactivity to tissue protein. These effects, however, were no more severe than those seen in perfused livers from control animals given 500 mumol of styrene oxide. Due to high GSH transferase activity in perfused livers from untreated rats, the capacity of epoxide hydrolase to detoxify styrene oxide is difficult to measure in this system. The detoxication potential of epoxide hydrolase was clearly demonstrated in this study with GSH-depleted liver preparations.

Animals↗

Occupational styrene exposure: environmental and biological monitoring.

Occupational exposure to styrene was studied by environmental and biological monitoring in 22 workers employed in a fiberglass reinforced plastic factory. The mean environmental styrene concentration in individual workplaces ranged from 120 to 684 microliter/l. Blood styrene, which was tested at the end of the work shift, ranged from 450 to 3700 micrograms/l. Urinary mandelic and phenylglyoxylic acid, which were determined at the end of the work shift, ranged from 133 to 2100 and from 107 to 685 mg/l, respectively. Environmental styrene exposure was better correlated with styrenemia than with mandelicuria and phenylglyoxylicuria considered either individually or together. The ratio between environmental and blood styrene showed that styrenemia was, on average, 3.3-4.9 times higher than environmental styrene concentration.

Air↗

Mortality patterns among styrene-exposed boatbuilders.

In order to test the hypothesis that leukemia and lymphoma may be associated with exposure to styrene, cause-of-death patterns were studied at two reinforced plastic boatbuilding facilities. There were 5,021 workers who met the criterion of having worked at the two plants between 1959 and 1978. Based on industrial hygiene surveys conducted at the two plants, 2,060 individuals were determined to have worked in departments classified as having high exposure to styrene. There were 176 deaths observed among the total cohort, in comparison to 195.3 deaths expected (standardized mortality ratio [SMR] = 90). Among the high styrene exposure group, 47 deaths were observed in comparison to 41.5 deaths expected (SMR = 113). No leukemia or lymphoma deaths were observed in either the high exposure group or the total cohort. An excess of accidental deaths among the high exposure group (18 observed vs 12.4 expected) did not appear to be due to styrene's acute central nervous system effects, since none of the individuals were employed at the facilities at the time of their death. However, the possibility of a chronic effect could not be dismissed. While leukemia and lymphoma did not appear to be related to styrene exposure, the study had little statistical power to detect excesses of these diseases, due to the short length of observation and the young age of most cohort members. It was concluded that the cohort should provide increasingly useful information on chronic styrene toxicity as the population ages and the observation period increases.

Adolescent↗

Ecotoxicity hazard assessment of styrene.

The ecotoxicity of styrene was evaluated in acute toxicity studies of fathead minnows (Pimephales promelas), daphnids (Daphnia magna), amphipods (Hyalella azteca), and freshwater green algae (Selenastrum capricornutum), and a subacute toxicity study of earthworms (Eisenia fostida). Stable exposure levels were maintained in the studies with fathead minnows, daphnids, and amphipods using sealed, flowthrough, serial dilution systems and test vessels. The algae were evaluated in a sealed, static system. The earthworms were exposed in artificial soil which was renewed after 7 days. Styrene concentrations in water and soil were analyzed by gas chromatography with flame ionization detection following extraction into hexane. Test results are based on measured concentrations. Styrene was moderately toxic to fathead minnows, daphnids, and amphipods: fathead minnow: LC50 (96 hr), 10 mg/liter, and NOEC, 4.0 mg/liter; daphnids: EC50 (48 hr), 4.7 mg/liter, and NOEC, 1.9 mg/liter; amphipods: LC50 (96 hr), 9.5 mg/liter, and NOEC, 4.1 mg/liter. Styrene was highly toxic to green algae: EC50 (96 hr), 0.72 mg/liter, and NOEC, 0.063 mg/liter; these effects were found to be algistatic rather than algicidal. Styrene was slightly toxic to earthworms: LC50 (14 days), 120 mg/kg, and NOEC, 44 mg/kg. There was no indication of a concern for chronic toxicity based on these studies. Styrene's potential impact on aquatic and soil environments is significantly mitigated by its volatility and biodegradability.

Animals↗

Kinetic interpretation of the exposure test for styrene.

The excretion kinetics of mandelic and phenylglyoxylic acids investigated over three subsequent days after cessation of styrene inhalation could be expressed by biphasic functions, similar for both metabolites; the half-times for the first and the second phases were 2.5 and 30 h, respectively. The possibility of styrene accumulation in exposure repeated daily was assessed by kinetic modelling; it appears negligible if measurements are based on urine samples collected at the end of the working shift. The above contention has been examined in workers exposed to styrene in the polyester industry: concentrations of styrene in air monitored continuously varied from 26 to 130 mg/m3. The relationship between styrene concentration and rate of urinary excretion of the total amount of mandelic and phenylglyoxylic acids was rectilinear and demonstrated a reasonable agreement between experimental and industrial data. The trends of concentrations within the day and week gave no indication of substantial styrene cumulation under repeated industrial exposure.

Air Pollutants, Occupational↗

Investigations on neurotoxicity of chemical substances at the workplace. VII. Longitudinal study with determination of nerve conduction velocities in persons occupationally exposed to styrene.

The aim of this longitudinal study was to investigate whether long-term exposure to styrene is associated with functional disorders of the peripheral nervous system. Eleven workers (age: 24 to 54 years) of a polyester resin boat industry were studied neurophysiologically and biochemically in 1980 and 1983. The duration of styrene-exposure varied from 3 to 7 years, with a median of 4 years. The control group was comprised of 11 non-styrene-exposed workers of similar age. Air Monitoring with passive samplers was performed on different days for each person. The mean styrene concentrations were 114, 97 and 92 ppm respectively and therefore in the magnitude of the current MAK-value of 100 ppm in the Federal Republic of Germany (FRG). For Biological Monitoring styrene in blood (S-B) and mandelic acid (MA) as well as phenylglyoxylic-acid (PGA) in urine were determined in post-shift samples. The median values for MA at four different sampling times were 816, 1660, 1101 and 1224 mg/g creatinine and for PGA 200, 273, 342 and 336 mg/g creatinine respectively. These levels were below the current "Biologischer Arbeitsstoff Toleranzwert (BAT-Wert)" for MA (2000 mg/l) and MA + PGA (2500 mg/l). The S-B concentrations ranged from 0.05 mg/l to 3.26 mg/l, with mean values of 0.92 and 0.70 mg/l. The nerve conduction velocities (NCV) of motor and sensory nerve fibers (N. ulnaris and/or N. medianus) showed no significant differences between styrene-exposed workers and age-matched control persons. There were no hints of "dose-effect-relationships" by correlation analyses. Furthermore the follow-up determination revealed no significant changes regarding NCV.(ABSTRACT TRUNCATED AT 250 WORDS)

Adult↗

Biological exposure limits estimated from relations between occupational styrene exposure during a workweek and excretion of mandelic and phenylglyoxylic acids in urine.

Styrene exposure of 18 workers in fiberglass reinforced plastic industries was measured for 30-min periods throughout each workday for a week. The styrene uptake was estimated using pulmonary ventilation measurements. All urine voidings were collected separately and the styrene metabolites, mandelic acid (MA) and phenylglyoxylic acid (PGA) were determined. The relationship between both exposure and uptake versus excretion of these metabolites was studied. Styrene metabolite concentrations and excretion rates (with 95% tolerance limits) were calculated to correspond to a constant 8-h exposure at the Swedish exposure limit level (25 ppm) or an uptake of an exposure limit related styrene dose (6.3 mmol). The tightest tolerance limits were obtained for excretion rate of MA + PGA per 24 h. The calculated biological exposure limit was 3.4 (+/- 0.7) mmol MA + PGA/24h for a dose of 6.3 mmol styrene.

Air Pollutants, Occupational↗