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Rabbit pulmonary cytochrome P-450 monooxygenase system: isozyme differences in the rate and stereoselectivity of styrene oxidation.

The rate and stereoselectivity of the cytochrome P-450 (P-450)-dependent oxidation of styrene to styrene 7,8-oxide (SO) were determined in rabbit pulmonary microsomes and with purified rabbit pulmonary P-450 isozymes in reconstituted monooxygenase systems. Stereoselectivity was determined by separation of the diastereomeric SO-glutathione adducts by high-performance liquid chromatography; these four compounds accounted for more than 95% of the SO formed. Pulmonary microsomes preferentially formed (R)-SO [(R)-SO/(S)-SO = 1.6] at a rate of 7.5 nmol of SO formed/min/nmol of P-450. Antibodies to NADPH-P-450 reductase (antireductase) inhibited SO formation in pulmonary microsomes by greater than 98%. In the presence of antibodies to P-450 form 2 (anti-2), pulmonary microsomes oxidized styrene to equal amounts of (R)- and (S)-SO at a rate of 4.2 nmol of SO/min/nmol of total P-450; in the presence of antibodies to P-450 form 5 (anti-5), styrene was stereoselectively oxidized to (R)-SO [(R)-SO/(S)-SO = 2.0] at a rate of 6.5 nmol of SO/min/nmol of total P-450. In reconstituted monooxygenase systems, P-450 forms 2, 5 and 6 oxidized styrene to SO at rates of 10.0, 4.7 and 4.5 nmol of SO formed/min/nmol of P-450, respectively. The relative amounts of (R)-SO and (S)-SO produced were 2.0, 1.0 and 0.9, respectively. Predicted values for rate and stereoselectivity of styrene oxidation by pulmonary microsomes, calculated from the values obtained in the reconstitution experiments and the relative concentrations of the different P-450 isozymes, agreed well with experimentally determined values.

Animals↗

Studies of the induction of chromosomal aberration and sister chromatid exchange in rats exposed to styrene by inhalation.

A large number of studies have been reported on the genotoxicity of styrene in vitro and in vivo and the potential effects on humans of occupational exposure. Because of a variety of technical problems and difficulties in data interpretation, it has not been clearly established whether styrene can induce chromosomal aberrations and/or sister chromatid exchange (SCE) in vivo in animals or humans. The importance of clarifying this situation led to the development of the study described in this paper. Male Fischer 344 rats were exposed to styrene at concentrations of 150, 500 or 1000 ppm for 6 h/day on 5 days/week for 4 weeks. A negative control (air) was included. An additional control (ethylene oxide, 150 ppm) group was included in an attempt to establish the usefulness of rat lymphocytes for cytogenetic analysis in this protocol of long-term exposure by inhalation. The choice of agent and of exposure was based on the expectation that they would produce a positive response for SCE and/or chromosomal aberrations under the assay conditions used. Peripheral blood samples were drawn at 1, 2, 3 and 4 weeks of exposure and at 4 weeks after the end of exposure. Cultures were established, and SCE (second mitosis) and chromosomal aberrations (first mitosis) were analysed. The frequency of chromosomal aberrations was not increased over that in the air controls in the animals exposed to styrene or ethylene oxide at any of the sampling times. Styrene did not induce SCE at any of the concentrations or sampling times; however, the frequency of SCE was increased following exposure to ethylene oxide at all sampling times, with a positive exposure-response relationship with time of exposure as the variable. The data are compared with other, similar sets reported in the literature, and their significance for predicting responses in people occupationally exposed to styrene is discussed.

Administration, Inhalation↗

Peripheral markers of neurochemical effects among styrene-exposed workers.

Monoamine oxidase B (MAO-B) activity in platelets, serum dopamine-beta-hydroxylase (DBH) activity, and serum prolactin (PRL) were measured during a cross-sectional investigation in workers occupationally exposed to styrene. The study group consisted of 53 workers (33 men and 20 women) employed for 9.3 years on average (range 1-22) in reinforced plastics plants. Sixty industrial workers with no known exposure to chemicals and comparable as to age, sex and confounding variables were recruited as controls. The activities of MAO-B in platelet-rich plasma and of DBH in serum from exposed and control subjects were measured within the same run, using methods based on the liquid-chromatographic determination of the reaction products. Serum PRL was determined by both EIA and RIA. Blood samples had been collected between 8:00 and 9:00 a.m. A lower DBH activity was found in exposed as compared to control workers (GM: 7.25 U/ml serum vs. 10.11 U/ml serum; p < 0.01), whereas MAO-B activity was significantly lower in a heavily exposed subgroup (10.1 vs. 13.8 U/10(7) platelets; p = 0.05), but not in the whole sample (p = 0.07). Serum PRL was higher both in male (GM: 8.90 ng/ml vs. 6.05 ng/ml; p < 0.01) and female (GM: 12.6 ng/ml vs. 9.33 ng/ml; p < 0.05) styrene-exposed workers as compared to their respective controls. Dose-response relationships were found for abnormally low DBH and abnormally high PRL values, with a threshold occurring at metabolite levels corresponding to 8h-TWA styrene concentrations in air around 25 ppm. In summary, this study shows that long-term exposure to relatively low levels of styrene can affect DBH activity and basal serum PRL. Owing to its sensitivity, PRL is a useful biomarker to show impairments of dopaminergic control on pituitary secretion. Since DBH is expression of catecholamine secretion, its decreased activity could represent an indirect index of altered turnover rate of the physiological substrate (i.e.dopamine) at the neuronal level. However, a direct interference by styrene metabolites on enzyme activity cannot be ruled out. Platelet MAO-B activity seems to be less sensitive to styrene exposure.

Adult↗

Exposure assessment for study of olfactory function in workers exposed to styrene in the reinforced-plastics industry.

BACKGROUND: This study was undertaken in conjunction with an evaluation of the olfactory function of 52 persons exposed to styrene vapors to provide quantitative styrene exposure histories of each subject for use in the interpretation of the results of olfactory function testing. METHODS: Current and historic exposures were investigated. Historic exposures were reconstructed from employment records and measurements of styrene exposure made in the subject facilities over the last 15 years. Current exposures were estimated for every exposed subject though personal air sampling and through pre- and post-shift measurements of urinary metabolites of styrene. RESULTS: The study population had been employed in the reinforced-plastics industry for an average of 12.2 +/- 7.4 years. Their mean 8-hr time weighted average (TWA) respirator-corrected annual average styrene exposure was 12.6 +/- 10.4 ppm; mean cumulative exposure was 156 +/- 80 ppm-years. The current respirator-corrected 8-hr TWA average exposure was 15.1 +/- 12.0 ppm. The mean post-shift urinary mandelic and phenylglyoxylic acid (PGA) concentrations were 580 +/- 1,300 and 170 +/- 360 mg/g creatinine, respectively and were highly correlated with air concentrations of styrene. CONCLUSIONS: This quantitative exposure evaluation has provided a well-characterized population, with documented exposure histories stable over time and in the range suitable for the purposes of the associated study of olfactory function.

Adult↗

Developmental neurotoxicity study of styrene by inhalation in Crl-CD rats.

This study was conducted to assess potential adverse functional and/or morphological effects of styrene on the neurological system in the F2 offspring following F0 and F1 generation whole-body inhalation exposures. Four groups of male and female Crl:CD (SD)IGS BR rats (25/sex/group) were exposed to 0, 50, 150, and 500 ppm styrene for 6 hr daily for at least 70 consecutive days prior to mating for the F0 and F1 generations. Inhalation exposure continued for the F0 and F1 females throughout mating and through gestation day 20. On lactation days 1 through 4, the F0 and F1 females received styrene in virgin olive oil via oral gavage at dose levels of 66, 117, and 300 mg/kg/day (divided into three equal doses, approximately 2 hr apart). Inhalation exposure of the F0 and F1 females was re-initiated on lactation day 5 and continued through weaning of the F1 or F2 pups on postnatal day (PND) 21. Developmental landmarks were assessed in F1 and F2 offspring. The neurological development of randomly selected pups from the F2 generation was assessed by functional observational battery, locomotor activity, acoustic startle response, learning and memory evaluations, brain weights and dimension measurements, and brain morphometric and histologic evaluation. Styrene exposure did not affect survival or the clinical condition of the animals. As expected from previous studies, slight body weight and histopathologic effects on the nasal olfactory epithelium were found in F0 and F1 rats exposed to 500 ppm and, to a lesser extent, 150 ppm. There were no indications of adverse effects on reproductive performance in either the F0 or F1 generation. There were exposure-related reductions in mean body weights of the F1 and F2 offspring from the mid and high-exposure groups and an overall pattern of slightly delayed development evident in the F2 offspring only from the 500-ppm group. This developmental delay included reduced body weight (which continued through day 70) and slightly delayed acquisition of some physical landmarks of development. Styrene exposure of the F0 and F1 animals had no effect on survival, the clinical condition or necropsy findings of the F2 animals. Functional observational battery evaluations conducted for all F1 dams during the gestation and lactation periods and for the F2 offspring were unaffected by styrene exposure. Swimming ability as determined by straight channel escape times measured on PND 24 were increased, and reduced grip strength values were evident for both sexes on PND 45 and 60 in the 500-ppm group compared to controls. There were no other parental exposure-related findings in the F2 pre-weaning and post-weaning functional observational battery assessments, the PND 20 and PND 60 auditory startle habituation parameters, in endpoints of learning and memory performance (escape times and errors) in the Biel water maze task at either testing age, or in activity levels measured on PND 61 in the 500-ppm group. Taken together, the exposure-related developmental and neuromotor changes identified in F2 pups from dams exposed to 500 ppm occurred in endpoints known to be both age- and weight-sensitive parameters, and were observed in the absence of any other remarkable indicators of neurobehavioral toxicity. Based on the results of this study, an exposure level of 50 ppm was considered to be the NOAEL for growth of F2 offspring; an exposure level of 500 ppm was considered to be the NOAEL for F2 developmental neurotoxicity.

Animals↗

Influence of genetic polymorphisms on biomarkers of exposure and genotoxic effects in styrene-exposed workers.

A study on 44 workers exposed to styrene and 44 matched referents was performed in order to examine the influence of genetic polymorphisms in biotransformation and DNA repair enzymes on the levels of N-terminal hemoglobin adducts and genotoxicity biomarkers. Urinary mandelic acid concentration averaged 201.57 mg/g creatinine +/-148.32 in exposed workers, corresponding to a calculated average airborne styrene exposure of 9.5 ppm +/-9.6. Individuals with a high level of N-terminal valine adducts had higher levels of DNA damage, as evaluated by the Comet assay (r = 0.29, P = 0.008). Frequencies of micronucleated mononucleated lymphocytes (MNMC) (0.71 +/- 0.88 vs 0.11 +/- 0.20, P<0.0001), micronucleated binucleated lymphocytes (MNBC) (3.93 +/- 2.75 vs 2.65 +/- 1.94, p = 0.02) and micronucleated nasal epithelial cells (0.52 +/- 0.49 vs 0.23 +/- 0.31, p = 0.04) differed significantly between the exposed and referent groups. In the whole group of 88 individuals, higher frequencies of MNMC were found in individuals possessing the XRCC3 Met(241) allele and those individuals with the XRCC1 Gln( (399) ) allele showed higher frequencies of MNMC and MNCB. In vitro DNA repair capacity, as measured by residual DNA strand breaks in peripheral blood leukocytes after a styrene oxide challenge, was also influenced by styrene exposure, with an apparent induction of early repair mechanisms associated with the intensity of recent exposure and a reduction of late (24 h) repair capacity that was associated with the duration of employment. After 1 h of repair, lower levels of residual DNA damage were found in individuals possessing GSTT1 (P = 0.043). After 24 h of repair, lower residual DNA damage was found in individuals homozygous for XRCC1 Arg(194) (P = 0.013). Multivariate regression analysis indicated that the duration of exposure, smoking habits and polymorphisms of XRCC1 at codon 399 were important variables affecting the genotoxic responses. Our data suggest that DNA damage is formed in workers exposed to low concentrations of styrene, and that genotypes of metabolising and DNA-repair genes are important for the assessment of individual genotoxic risk to styrene. The in vitro DNA repair phenotype assay might be a valuable method to estimate the susceptibility of workers.

Adult↗

Effects of prenatal styrene exposure on postnatal development and brain serotonin and catecholamine levels in rats.

Maternal reproductive effects in Wistar rats exposed to 0, 50, or 300 ppm styrene for 6 h/day during gestational days 6 to 20 were evaluated. Their offspring were observed postnatally for neurochemical changes, growth, and physical landmarks of development. Mothers exposed to styrene were compared with pair-fed and ad-lib-fed controls in order to adjust nutrient conditions. Prolongation of the gestational period, food intake, and the number of neonatal deaths or stillbirths in 300-ppm-exposed dams showed evidence of styrene-related effects. Other reproductive parameters, such as litter size, birth weight, and sex ratio, were found to exhibit no effects within the variation range studied. A neurochemical effect was observed in that the 5-HT and HVA concentrations in cerebrum were significantly decreased. Incisor eruption (mandible), eye opening, and the air-righting reflex were delayed in rat pups born to dams receiving 300 ppm styrene exposure compared with the pair-fed and ad lib control groups. Pups born to dams exposed to 50 ppm styrene also had a significantly delayed air-righting reflex compared with ad lib controls. These results suggest that the offspring were susceptible to the effects of styrene on a few developmental landmarks even when nutritional effects were controlled.

Animals↗

Styrene inhalation toxicity studies in mice. III. Strain differences in susceptibility.

Inhalation toxicity studies were conducted to evaluate mouse strain differences in the susceptibility to styrene vapors. Male and female B6C3F1, C57BL/6, Swiss, and DBA/2 mice (8 weeks old) were exposed to 0, 125, 250, or 500 ppm styrene 6 hr/day, for 4 days (20/sex/dose). Histopathological changes and changes in liver weights were evaluated as a measure of hepatotoxicity. Styrene uptake and styrene-7,8-oxide (SO) formation were estimated by measuring levels of styrene and SO in blood. An estimate of SO detoxification by conjugation with GSH was obtained by measuring hepatic GSH depletion. In general, mortality, increased liver weights, and hepatocellular necrosis were observed in the 250 and 500 ppm dose groups for all strains and both sexes. Considerable sex and strain differences were observed. Mortality, increased liver weights, and hepatocellular necrosis were greatest in B6C3F1 and C57BL/6 mice in the 250 ppm dose group and in males; hepatotoxicity was similar in both strains. Swiss mice exhibited dose-dependent increases in mortality, liver weights, and in hepatocellular necrosis, with only slight sex differences at early time points. Hepatotoxicity in DBA/2, B6C3F1, and C57BL/6 strains was greater at 250 than 500 ppm; however, toxicity was less severe in DBA/2 than in other strains based on absence of mortality in either sex and less extensive liver necrosis at both 250 and 500 ppm. Blood styrene and SO levels did not correlate well with strain differences in toxicity.(ABSTRACT TRUNCATED AT 250 WORDS)

Administration, Inhalation↗

Functional and morphological effects of styrene on the auditory system of the rat.

The effect of inhaled styrene on the structure and function of the auditory organ of the male Wistar rat was studied. The animals were exposed either to 600, 300 or 100 ppm styrene (12 h/day, 5 days/week, for 4 weeks). Auditory sensitivity was tested prior to and after the exposure by auditory brain stem audiometry (ABR) at frequencies of 1.0, 2.0, 4.0 and 8.0 kHz. Inner ear morphological changes were studied by light- and electron-microscopy. Exposure to 600 ppm styrene caused a 3 dB hearing loss only at the highest test frequency (8 kHz). Quantitative morphological analysis of cochlear hair cells (cytocochleograms) showed that 600 ppm styrene caused a severe outer hair cell (OHC) loss particularly in the third OHC row of the upper basal and lower middle coil. The inner hair cells were usually intact. Exposure to lower styrene concentrations (100 and 300 ppm) caused no unequivocal functional deficit or hair cell damage. We conclude that there appears to be a concentration threshold for styrene ototoxicity in rats (between 300 and 600 ppm).

Administration, Inhalation↗

Effects of 5-day styrene inhalation on serum prolactin and dopamine levels and on hypothalamic and striatal catecholamine concentrations in male rats.

In several studies a hypersecretion of the pituitary hormone prolactin (PRL) in styrene-exposed workers has been described. This should cause reproductive problems like oligomenorrhea, secondary amenorrhea and reduced fertility [Arfini et al. (1987) J Occup Med 29:826-830, Bergamaschi et al. (1996) Neurotoxicology 17:753-760, Mutti and Smargiassi (1998) Toxicol Ind Health 14:311-323]. Secretion of PRL is tonically inhibited by the catecholamine dopamine (DA), which is released from hypothalamic neurons. It has been suggested that the activity of the enzyme dopamine-beta-hydroxylase (DBH) in the serum is a peripheral marker of central dopaminergic function. A slight reduction of such enzymatic activity was observed in styrene-exposed workers, which was associated with hypersecretion of PRL. To further investigate the putative effects of styrene on PRL release, male rats were exposed to styrene vapors (645, 2150 and 6450 mg/m(3)) for 6 h/day on 5 consecutive days. Animals were killed either directly following the last exposure (immediate group) or after a recovery period of 24 h (recovery group). Serum PRL and DA levels were measured by radioimmunoassay. Concentrations of catecholamines and their metabolites in the striatum and mediobasal hypothalamus (MBH) were determined by high performance liquid chromatography with electrochemical detection. Neither in the immediate nor in the recovery group were any statistically significant changes of serum PRL levels observed. Likewise, concentrations of catecholamines and their metabolites in the striatum and MBH remained unaffected. We conclude from these data that styrene, even at very high concentrations, has no adverse effects on the neuroendocrine mechanisms regulating PRL release and DA levels in the brain. With the limitations inherent in any animal model, we suggest that our data indicate that styrene also has no adverse neuroendocrine effects in humans.

Administration, Inhalation↗

Styrene degradation by Pseudomonas sp. SR-5 in biofilters with organic and inorganic packing materials.

Pseudomonas sp. SR-5 was isolated as a styrene-degrading bacterium. In liquid culture containing 1% (v/v) styrene, more than 90% styrene was degraded in 53 h and the doubling time of SR-5 was 2 h. The removal of styrene gas was investigated in biofilters for 31 days using an organic packing material of peat and an inorganic packing material of ceramic inoculated with SR-5. The maximum-styrene-elimination capacities for peat and ceramic packing materials were 236 and 81 g m(-3) h(-1), respectively. The percentage of styrene converted to low molecular weight compounds including CO(2) in the peat and ceramic biofilters during a 10-day operation were estimated to be 90.4 and 36.7%, respectively. As the pressure drop in the peat bioflter at the end of experiment was significantly higher than that in ceramic biofilter, a biofilter using a mixture of peat and ceramic was tested. We determined that the maximum elimination capacity was 170 g m(-3) h(-1) and the production of low molecular weight compounds was 95% at a low pressure drop for this mixed packing material filter.

Biodegradation, Environmental↗

Peripheral markers of catecholaminergic dysfunction and symptoms of neurotoxicity among styrene-exposed workers.

AIM: A cross-sectional investigation was carried out to assess possible relations between styrene-induced changes in three peripheral markers of catecholaminergic dysfunction and self-reported symptoms of neurotoxicity. SUBJECTS: Male workers (n = 46) aged 14-60 (mean 29.5) years who had been exposed to styrene for an average of 6 (0.2-29) years were recruited in glassfiber reinforced plastics plants. A control group of 30 blue-collar workers aged 22-52 (mean 35) years and with no history of exposure to chemicals was recruited from local industries. Styrene exposure ranged from 5 to 120 ppm (8 h-TWA), the median level being relatively low (25 ppm, 8 h-TWA). Styrene metabolites, mandelic and phenylglycoxylic acids (MAPGA) in the "next morning" urine spot samples ranged from 32.0 to 931.1 mg/g creatinine (median 186.5). METHODS: Platelet monoamine oxidases B (MAO B) and dopamine beta-hydroxylase (DBH) activities were assessed using methods based on HPLC and electrochemical detection. Plasma prolactin (PRL) was measured by a commercially available immunoassay. Questionnaire 16 (Q16) was used to survey self-reported symptoms. RESULTS: Although there was no difference in DBH activity between exposed workers and controls, the most highly exposed workers had significantly lower activity than control subjects. A tendency to lower platelet MAO B activity in exposed than in control subjects was observed. The prevalence of plasma DBH and platelet MAO B values below the lower reference limit was similar in the two groups. PRL values exceeding the upper reference limit were higher (14/46 vs 2/30) among styrene-exposed workers, who also exhibited significantly higher median levels (10.0 vs 5.7 micrograms/l) than control subjects. Although the number of reported symptoms was similar among exposed and control subjects, in the exposed group it was positively associated with urinary MAPGA (Rho = 0.30, P = 0.04). Of the three peripheral markers of catecholaminergic dysfunction, plasma DBH was the only parameter negatively related to both urinary MAPGA (F = 9.56, P = 0.003) and the number of reported symptoms (Rho = 0.23, P = 0.05). CONCLUSIONS: Plasma PRL appears to be a sensitive marker of styrene-induced tubero-infundibular dopaminergic dysfunction in male subjects. DBH in plasma and MAO B in platelets seem to be less suitable markers for biomonitoring effect at the individual level, although DBH was related to the number of reported symptoms and to internal dose. Further studies on a larger and more exposed population are necessary to clarify the significance of these markers for health and their predictive value with regard to both subjective disturbances and concurrently administered performance tests.

Adolescent↗

Vinyl chloride and vinyl benzene (styrene)--metabolism, mutagenicity and carcinogenicity.

Vinyl chloride and vinyl benzene (styrene) are mutagenic in microbial tests, in Drosophila, in yeast, and in mammalian cells. Reports from various countries have shown an excess of chromosomal aberrations in the lymphocytes of workers exposed to vinyl chloride monomer when the workers were compared with controls. Workers occupationally exposed to styrene also revealed a clear increase in the rate of chromosome aberrations in their lymphocytes. Both chloroethylene oxide and styrene oxide, the primary biotransformation products of vinyl chloirde and styrene respectively, bind covalently to cellular macromolecules. Vinyl chloride is a carcinogen in both animals and man. Styrene is currently being tested in animals. These findings, the demonstration of mutagenic response via microbial and other test systems and with observations of significant excesses of chromosomal aberrations among workers exposed to these agents, raise scientific and health oriented concern about the possible genetic risks of vinyl chloride and styrene to man.

Animals↗

Chromosomal aberrations and sister-chromatid exchanges in lymphocytes of men occupationally exposed to styrene in a plastic-boat factory.

Workers in a Swedish factory making boats from plastics reinforced with glass fibre are exposed to a variety of chemicals, including styrene which is mutagenic after metabolic activation. The concentration of styrene in the air was measured in the breathing zones of workers occupied with various processes in boat making. Samples of air were taken 6 times during the years 1973-1978. The total exposure to styrene for the workers during this period was calculated and expressed as the average concentration in mg per m3 air during an 8-h workshift multiplied by the number of years of employment. A low-dose group (mean = 137 mg x m-3) and a high-dose group)mean - 1204 mg x m-3) were identified. Blood samples were taken in 1978 from workers belonging to the exposed groups and from a matched control group of employees in the same factory not exposed to styrene. Lymphocytes were cultured and examined for chromosomal aberrations and sister-chromatid exchanges. Exposed workers had a significantly (p less than 0.001) higher number of chromosomal aberrations (36 persons, mean = 7.9 aberrations/100 cells) compared with employees in the control group (37 persons, mean = 3.2 aberrations/100 cells). There was no significant difference between the mean values of the number of chromosomal aberrations between the highly exposed and the less exposed groups. But in the less exposed group there was an increase in the frequency of chromosomal aberrations with increasing exposure to styrene (r = 0.576). In the highly exposed group this dose response was not observed (r = 0.231). For the frequency of sister-chromatid exchanges (SCE) a slight (p less than 0.05) increase was found in the styrene-exposed group (20 persons, mean = 8.4 SCE/cell). The control group (21 persons) had a mean value of 7.5 SCE/cell. Again there was no difference between the highly exposed and the less exposed groups. Other environmental factors that may have clastogenic effects were studied, but multiple regression analysis failed to show a candidate responsible for the increase in chromosomal abnormalities in the exposed group.

Cells, Cultured↗

Neurobehavioral effects of occupational exposure to low-level styrene.

Eighty-six workers in six fiberglass-reinforced plastics manufacturing plants in Taiwan were given a detailed evaluation including medical and occupational questionnaires, symptom questionnaires, blood sampling, and neurobehavioral tests, including cognitive performance, vibratory perception threshold, and thermal perception threshold. A Chinese version of cognitive tests modified from the Neurobehavioral Evaluation System 2 was applied. Forty-one workers directly exposed to styrene at the mean concentration of 22 ppm are compared with 45 workers not subject to styrene exposure. Multiple linear regression analysis controlling for age, sex, education, and alcohol intake revealed significant associations between styrene exposure and responses in some neuropsychologic measurements. No acute or chronic symptom had significant correlation with styrene exposure. Among the neurobehavioral tests, only the continuous performance test and vibration threshold were significantly and adversely affected in workers exposed to styrene. Significant changes in the central and peripheral nervous system were thus detected at a mean styrene exposure of 22 ppm.

Adolescent↗

Multiple headspace single-drop microextraction-a new technique for quantitative determination of styrene in polystyrene.

Single-drop microextraction (SDME), an emerging miniaturised extraction technique, was for the first time combined with multiple headspace extraction (MHE) to enable the quantitative determination of volatiles in solid matrixes by SDME technique. The concept of multiple headspace single-drop microextraction (MHS-SDME) was then applied for quantitative determination of styrene in polystyrene (PS) samples. Good linearity for the multiple headspace extraction was obtained when the migration of styrene was facilitated by grinding the samples and incubating them for 1 h at 150 degrees C prior the first extraction. Two microlitres of butyl acetate was used as the single-drop microextraction solvent and the extraction time was 5 min per cycle. The relative standard deviation (RSD) for single-drop microextraction of styrene standard at n=6 was 7.6%. Linearity was shown for styrene concentrations between 0.005 and 0.75 microg/ml (R2=0.999). This corresponds to total amount of styrene between 0.1 and 15 microg. The limit of quantitation for styrene standard at S/N 10 was 0.005 microg/ml. The developed method was validated against and showed good agreement with an earlier reported dissolution-precipitation method.

Gas Chromatography-Mass Spectrometry↗

The effects of styrene on lung cells in female mice and rats.

Styrene has been shown to cause an increase in the incidence of lung tumors in CD-1 mice following chronic exposure at 40 and 160 ppm, whereas no treatment-related increase in tumors in any organ was seen in rats chronically exposed to up to 1000 ppm styrene. So far most of the mechanistic studies have been performed with male animals. The aim of the present study was to further elucidate the target cell population in mouse lungs exposed to styrene, and to investigate possible differential in vivo effects (e.g., glutathione depletion, increased lipid peroxidation, and oxidative DNA damage). Groups of female CD-1 mice were exposed to styrene at concentrations of 0, 172 or 688 mg/m3 (0, 40 or 160 ppm) for 6 h per day on 1 day, 5 consecutive days or for 20 days during a 4 week period. Groups of female Crl:CD rats were exposed to styrene at concentrations of 0, 688 or 2150 mg/m3 (0, 160 or 500 ppm) for a single 6 h period or for 6 h per day on 5 consecutive days. No signs of lung toxicity were observed in rats. The cytology of cells in lung lavage fluid provided no signs of an inflammatory response in either rats or mice. In mice, both exposure levels caused decreased CC16 protein concentrations in lung lavage fluid after 1 and 5 exposures and in mouse blood serum throughout the study, suggesting that styrene may cause destruction of Clara cells in mice. Degenerative lesions in mouse Clara cells (vacuolar cell degeneration, cell necrosis) were revealed by electronmicroscopy. After 5 and 20 exposures of mice at 160 ppm, cellular crowding, expressed as an irregular epithelial lining and indicative of a very early hyperplasia was noted. Although a depletion of glutathione was noted in mouse lung homogenates after 20 exposures, there was no evidence of oxidative stress as indicated by unchanged concentrations of 8-OH-deoxyguanosine. Malondialdehyde, an indicator of lipid peroxidation, was slightly increased in mice after 1 exposure at 160 ppm only.

Animals↗

7-Alkylguanine adduct levels in urine, lungs and liver of mice exposed to styrene by inhalation.

This study describes urinary excretion of two nucleobase adducts derived from styrene 7,8-oxide (SO), i.e., 7-(2-hydroxy-1-phenylethyl)guanine (N7alphaG) and 7-(2-hydroxy-2-phenylethyl)guanine (N7betaG), as well as a formation of N7-SO-guanine adducts in lungs and liver of two month old male NMRI mice exposed to styrene by inhalation in a 3-week subacute study. Strikingly higher excretion of both isomeric nucleobase adducts in the first day of exposure was recorded, while the daily excretion of nucleobase adducts in following time intervals reached the steady-state level at 4.32+1.14 and 6.91+1.17 pmol/animal for lower and higher styrene exposure, respectively. beta-SO-guanine DNA adducts in lungs increased with exposure in a linear way (F=13.7 for linearity and 0.17 for non-linearity, respectively), reaching at the 21st day the level of 23.0 adducts/10(8) normal nucleotides, i.e., 0.74 fmol/microg DNA of 7-alkylguanine DNA adducts for the concentration of 1500 mg/m3, while no 7-SO-guanine DNA adducts were detected in the liver after 21 days of inhalation exposure to both of styrene concentrations. A comparison of 7-alkylguanines excreted in urine with 7-SO-guanines in lungs (after correction for depurination and for missing alpha-isomers) revealed that persisting 7-SO-guanine DNA adducts in lungs account for about 0.5% of the total alkylation at N7 of guanine. The total styrene-specific 7-guanine alkylation accounts for about 1.0x10(-5)% of the total styrene uptake, while N1-adenine alkylation contributes to this percentage only negligibly.

Animals↗