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PubMedDate not supplied

[Mercapturates and biologic monitoring: styrene].

The biological monitoring of styrene exposure is currently performed by the measurement of the urinary excretion of mandelic acid (MA) and phenylglyoxylic acid (PGA), which originate from the conversion of styrene 7,8-epoxide (SO), an electrophilic compound considered responsible for most toxic effects of styrene. In rats, an alternative pathway in the detoxification processes of SO has been shown, which involves its conjugation with glutathione (GSH), leading to the excretion of N-acetyl-S-(1-phenyl-2-hydroxyethyl)-cysteine (M1) and N-acetyl-S-(2-phenyl-2-hydroxyethyl)-cysteine (M2). Giving the chiral nature of SO, which is present in two enantiomeric forms (R and S), both M1 and M2 consist of two diastereoisomers: thus, four specific mercapturic acids are excreted in styrene-exposed rats, namely M1-R, M1-S, M2-R and M2-S. Until now, the excretion of these compounds in man has not been confirmed directly, giving the analytical difficulties in measuring the low levels of urinary mercapturic acids which are expected following styrene exposure in the working environment. In the present study we applied an analytical method, based on HPLC with fluorometric detection, to measure the excretion of M1-R, M1-S, and M2 in post-shift urines from 22 workers exposed to styrene and in 10 unexposed subjects. The results clearly demonstrated that the GSH pathway is involved in the detoxification processes of styrene, even if to a low extent (the biotransformation rates of styrene to mercapturic acids varied from 0.021 to 0.325%) and that M1 and M2 are specific for styrene exposure, in fact unexposed subjects showed no detectable amounts of these metabolites. In spite of the marked interindividual variability, significative correlations were found between mercapturic acids excretion and environmental styrene concentration or urinary levels of MA and PGA. The urinary levels of M1-S and M1-R were significantly different, thus indicating a stereoselectivity of the enzymes involved in the biotransformation of styrene to mercapturic acids.

Acetylcysteine↗
PubMed1978

Styrene use and occupational exposure in the plastics industry.

The commercial production of styrene was started in the 1930s. Currently 7 million tons of styrene a year is made worldwide by the catalytic dehydrogenation of ethylbenzene or by a process in which styrene is produced as a coproduct with propylene oxide. An estimated 62% of the styrene monomer is consumed in the manufacture of polystyrene, 12% in acrylonitrile-butadiene-styrene resins, 17% in styrene-butadiene rubber and latex, 7% in unsaturated polyester resins, and 2% in other applications. Occupational exposure to styrene occurs in monomer production and polymerization plants, during the fabrication of plastic products from monomeric or partly prepolymerized styrene, and during the transportation and handling of liquid styrene. Due to unreacted residual monomer or thermal degradation of the polymer, low concentrations of styrene can be detected during the use of plastic products. The most extensive and intensive exposure occurs in the reinforced plastics industry, in which over 200,000 workers are exposed to a styrene concentration typically ranging from 20 to 300 ppm.

Air Pollutants↗
PubMed1998

Deamination and Dimroth rearrangement of deoxyadenosine-styrene oxide adducts in DNA.

In reactions between styrene oxide and the ring nitrogen at the 1-position of deoxyadenosine, the epoxide is opened at both the alpha- (benzylic) and beta-carbons. The 1-substituted nucleosides formed are unstable and subsequently undergo either Dimroth rearrangement to give N6-substituted deoxyadenosines or deamination to give 1-substituted deoxyinosines. alphaN6-Substituted compounds are also formed from direct reaction at the exocyclic nitrogen. Kinetic experiments revealed that relative rates of deamination of 1-substituted deoxyadenosine-styrene oxides and 1-substituted adenosine-styrene oxides were similar. However, the rate of Dimroth rearrangement in beta1-substituted adenosine-styrene oxides was approximately 2.3-fold greater than that of beta1-substituted deoxyadenosine-styrene oxides and approximately 1.5-fold greater in alpha1-substituted adenosine-styrene oxides relative to alpha1-substituted deoxyadenosine-styrene oxides. Analysis of the products formed from reactions of styrene oxide with [3H]deoxyadenosine and [3H]deoxyadenosine incorporated into native and denatured DNA showed that the double-helical DNA structure reduced the levels of adducts formed 5-fold relative to denatured DNA but did not present a complete barrier to formation of either N6-substituted deoxyadenosine- or 1-substituted deoxyinosine-styrene oxide adducts in native DNA. Additionally, in denatured and native DNA the product distributions were altered in favor of formation of beta1-substituted deoxyinosine-styrene oxide adducts with respect to reactions of the nucleoside. The ratio of retained to inverted configuration of alphaN6-substituted products was higher in DNA than in nucleoside reactions. These experiments indicate that in addition to the N6-position, the ring nitrogen at the 1-position of deoxyadenosine is available, to some extent, for reaction in native DNA. In styrene oxide-DNA reactions, formation of 1-substituted adenines can lead to deaminated products where both Watson-Crick hydrogen-bonding sites are disrupted.

Chromatography, High Pressure Liquid↗
PubMed1995

Retention of styrene following controlled exposure to constant and fluctuating air concentrations.

An experiment was designed to determine whether the respiratory retention of styrene vapor, as estimated from measurements of end-exhaled air, was the same during periods of both constant and fluctuating exposure. Six human subjects were exposed to styrene inside a experimental chamber. A computer-controlled system was used to generate time-varying air concentrations of styrene over 4-5h in both multistep sequences of constant exposure (four subjects exposed to 15-99 ppm of styrene in 100-min steps) and fluctuating patterns representative of occupational exposures (two subjects exposed to mean concentrations of styrene of 50 ppm). In the latter case, lognormally distributed exposures, which fit one of two first-order autoregressive models, were generated at intervals of 2.5 min. It was found that the concentration of styrene in end-exhaled air was reduced by about half if the subject inhaled one to three breaths of clean air prior to sampling. This suggests that significant amounts of styrene were desorbed from the lining of the lungs during the initial exhalation. The retention of styrene vapor during constant exposures was 0.935 and was independent of the level. During each of the two sets of fluctuating exposure the retention of styrene was also constant and was independent of both the variance and autocorrelation coefficient. However, the retention of styrene during the fluctuating exposure (estimates ranged from 0.957 to 0.973) was significantly higher than that observed during the constant exposures.(ABSTRACT TRUNCATED AT 250 WORDS)

Adult↗
PubMed1994

Kinetics of styrene urinary metabolites: a study in a low-level occupational exposure setting in Singapore.

Biological monitoring of styrene exposure commonly involves measurement of styrene metabolites, mainly mandelic acid (MA) and phenylglyoxylic acid (PGA), in the urine of exposed subjects. Previous studies on the kinetics of styrene metabolites in urine were mostly conducted in a controlled environment on subjects exposed to high concentrations of styrene. In this study, we examined subjects exposed to low levels of styrene in a fiber-reinforced plastics (FRP) plant to see whether the excretion kinetics of styrene metabolites are similar under field conditions. Eight healthy Chinese male volunteers were exposed to styrene for 4 h with a mean environmental concentration of 11 ppm. Urine samples were collected continuously for 20 h after termination of the exposure and concentrations of urinary MA and PCA were determined. The results showed that MA was rapidly excreted in urine after the exposure, with a half-life of 2.1 h or 1.9 h when corrected with urine creatinine. The excretion of PGA followed that of MA and the half-life was 8.1 h or 5.1 h after correction with creatinine. The half-lives are considerably shorter compared to those in previous reports, suggesting that environmental factors, exposure conditions, or ethnic differences may affect the excretion kinetics of styrene metabolites. The fast excretion of styrene metabolites is also consistent with the observation that urine MA and PGA levels correlated better with the half-day time-weighted average (TWA) concentration of environmental styrene than with the whole-day TWA concentration. Our findings thus underscore the need for information on excretion kinetics in order to develop an appropriate biological monitoring scheme for specific exposure settings and subjects.

Adult↗
PubMed1987

Decreased erythrocyte delta-aminolevulinate dehydratase activity after styrene exposure.

delta-Aminolevulinate dehydratase (ALA-D:porphobilinogen synthase, 5-aminolevulinate hydro-lyase, EC 4.2.1.24) activity was depressed markedly in red cells of rats exposed to 0.21 g/m3 styrene, a chemical widely used in commercial products. The depression was not restored in vitro after treatment with dithiothreitol and zinc. Consistent with this finding, radioimmunoassay of the enzyme protein demonstrated reduction in the enzyme concentration by styrene exposure. There was a good correlation between the decrease in enzyme activity and its concentration in the styrene-treated animals, suggesting that the depression of the enzyme activity was essentially due to the reduction in the enzyme content. Decrease in the enzyme content in bone marrow cells to almost the same extent as that in erythrocytes seems to indicate the decreased synthesis of ALA-D in the bone marrow. In vitro studies showed that styrene 7,8-oxide, the major intermediate of styrene metabolism, decreased the activity of purified ALA-D but that styrene, the parent compound itself, had no inhibitory effect. The activity and concentration of erythrocyte ALA-D in workers chronically exposed to styrene were also depressed significantly. These findings indicate that the styrene exposure-mediated decrease of ALA-D activity in erythrocytes was a reflection of reduction in the enzyme protein, which may have been the result of styrene 7,8-oxide action, and they suggest that a similar process may also be involved in the reduction of erythrocyte ALA-D in styrene-exposed workers.

Animals↗
PubMed1983

The nephrotoxic potential of styrene in Sprague-Dawley rats.

Pre-fasted (16 h) Sprague-Dawley male rats were treated i.p. with 0, 0.2, 0.4, 0.8 and 1.2 g/kg of styrene in corn oil. Renal functions were assessed at 0-24, 24-48 and 48-72 h after the exposure. Urinary creatinine was decreased at 0.8 g/kg of styrene during 0-24 h after the treatment compared to control, whereas such a decrease was noticed in 1.2 g/kg styrene-treated rats when compared to control groups during 0-24 and 0-48 h after the dose. Urine pH and urinary contents of sodium, potassium and chloride were all decreased in a dose-dependent manner at 0.8 and 1.2 g/kg of styrene compared to both control animals during 0-24 h, whereas urinary proteins were not affected significantly. In another experiment, groups of pre-fasted (16 h) rats were treated i.p. with 0, 0.8 and 1.2 g/kg of styrene in corn oil and were then fasted for another 24 h to induce more stress prior to collection of blood and urine. Urinary pH and excretions of sodium and potassium were all decreased in styrene-treated rats 24 h after the dose. Urinary proteins were elevated and relative kidney weights were increased in 1.2 g/kg styrene-treated rats only compared to both control and 0.8 g/kg styrene-treated groups. A significant increase in serum creatinine and an increase close to significant in blood urea nitrogen were observed at 1.2 g/kg dose. These results suggest an impairment of renal functional parameters due to acute styrene exposure and further demonstrate a possible dose-dependent nephrotoxic potential of styrene in rats.

Animals↗
PubMedDate not supplied

Effects of acute styrene and simultaneous noise exposure on auditory function in the guinea pig.

Although styrene has been demonstrated to disrupt vestibular function acutely, parallel studies have not been conducted in the auditory system. This article presents data on the effects of acute styrene administration by injection and inhalation on cochlear function. No deleterious effect of the maximally tolerated styrene dose on hearing was identified when cochlear function was assessed using a within-subjects design. When guinea pigs were administered styrene by inhalation during a single 7-h period, normal auditory function was observed both 1 and 7 days later as compared to chamber controls which did not receive styrene. In some instances, the interactive effects of noise and simultaneous styrene inhalation were studied to determine whether chemical exposure might enhance the disruptive effects of noise on hearing. While a persistent noise-induced hearing loss was observed 1 day following exposure, subjects administered styrene simultaneously did not show a greater hearing loss than those receiving noise alone. Finally, when a 7-day recovery period for noise-induced hearing loss was interposed before audiometric testing, the combined exposure to styrene and noise was not more potent than noise alone in elevating auditory thresholds. Although auditory dysfunction has been reported following subchronic styrene administration, the current results do not support an ototoxic effect of styrene at the level of the cochlea with short-term exposure.

Action Potentials↗
PubMedDate not supplied

Styrene metabolism by cDNA-expressed human hepatic and pulmonary cytochromes P450.

The rate of formation of styrene glycol from styrene was compared in human, rat, and mouse liver microsomes. At a low styrene concentration (0.085 mM), the rates decreased in the order, mouse (2.43 +/- 0.29 nmol/(mg of protein.min)) > rat (1.07 +/- 0.20) > human (0.73 +/- 0.45); at a high concentration (1.85 mM), the order was rat (4.21 +/- 0.72) > mouse (2.72 +/- 0.11) > human (1.91 +/- 0.84). Kinetic analysis indicated the presence of at least two forms of styrene-metabolizing cytochrome P450s with different Km values in human liver microsomes. Styrene was also metabolized in human lung microsomes: the rate of styrene glycol formation was higher in the lung microsomes from smokers than in those from current nonsmokers. The P450 forms responsible for transforming styrene to styrene glycol were determined by analyzing cDNA-expressed individual P450 forms produced in cultured hepatoma G2 cells by recombinant vaccinia viruses. Of the 12 human P450 forms studied, CYP2B6 and CYP2E1 existing in human liver and/or lungs and CYP2F1 in human lungs were the most active in the forming of styrene glycol, followed by CYP1A2 and CYP2C8. Human CYP3A3, CYP3A4, CYP3A5, and CYP4B1 also catalyzed the metabolism but were much less active. CYP2A6, CYP2C9, and CYP2D6 had only a little detectable activity. CYP1A2, CYP2B6, CYP2C8, CYP2E1, and CYP3A4/3A3 were expressed in human liver microsomes, and CYP2C8 was expressed in human lung microsomes, although the expression of CYP2F1 and CYP4B1 could not be investigated. These data indicate that several human hepatic and/or pulmonary P450 forms are capable of metabolizing styrene, albeit at different rates.

Adult↗
PubMed1989

Metabolism and hepatorenal toxicity due to repeated exposure to styrene in spontaneously hypertensive rats (SHR).

Groups of adult male rats (5 rats per group), either normotensive (WKY) or spontaneously hypertensive (SHR), were exposed by inhalation to 0, 821, and 3018 ppm styrene, 5 h per day for 3 consecutive days. After the exposure, the urines were collected for 24 h and the animals were then sacrificed. The various biochemical parameters of hepatorenal toxicity due to styrene as well as its urinary metabolites were measured. Hepatotoxicity due to styrene was not further increased at any exposure level due to hypertension. However, repeated exposure of SHR rats to 3018 ppm styrene showed significant increases in the urinary excretion of gamma-glutamyl transpeptidase, proteins, and volume of urine, compared to WKY treated rats, whereas no such changes were observed due to repeated exposure to 821 ppm styrene. Studies of in vivo metabolism of styrene at higher exposure level showed significant decrease in the urinary excretion of mandelic, phenylglyoxylic, and hippuric acids in SHR rats compared to WKY-treated rats, suggesting an inhibition of deactivation of styrene reactive intermediate involving the epoxide hydrase pathway due to hypertension. At the same time, a significant increase in the urinary excretion of a potential nephrotoxic metabolite of styrene (e.g., mercapturates or thioethers) was observed in SHR-treated rats when compared to WKY-treated rats. These results demonstrate that spontaneous hypertension has the potential to further increase the nephrotoxicity due to repeated exposure to styrene, and the metabolism of styrene plays an important role in modifying such toxicity in the hypertensive state.

Acetylglucosaminidase↗
PubMed2000

Changes in cellular immunity among workers occupationally exposed to styrene in a plastics lamination plant.

BACKGROUND: Styrene is a widely used industrial chemical. Immune and hematological parameters were examined in 29 hand laminators and sprayers exposed to styrene for an average of 14 years and in 19 in-factory unexposed controls. The workers performed hand lamination procedures in a production area with an average area airborne styrene level of 139.5 mg/m(3). Mean concentration of styrene in the blood of exposed workers was 945.7 microg/L and the mean styrene in exhaled air was 38.8 microg/L. METHODS: Parameters of internal and external exposure, immune function assays, immunoglobulins, acute phase reactants and hematology were evaluated in exposed and non-exposed populations. RESULTS: Using multifactorial analysis of variance we found a significant decrease in proliferation of lymphocytes stimulated by Concanavalin A but not by pokeweed mitogen (PWM) in workers occupationally exposed to styrene. Proliferative response to PWM was significantly correlated with the levels of styrene in blood. Phagocytic activity of monocytes, levels of IgG, IgA, IgM, IgE and alpha-2-macroglobulin in serum were indistinguishable in the two groups. The population exposed to styrene had increased levels of C4-component of complement. Levels of C3-component of complement were positively correlated with duration of exposure. A significant elevation in the percentage and number of monocytes and a significantly decreased number of lymphocytes were seen in exposed workers. Styrene concentrations in both blood and exhaled air were associated with decreased percentage of large granular lymphocytes. CONCLUSIONS: These results suggest immune alterations of cell-mediated immune response of T-lymphocytes and imbalance in leucocyte subsets in peripheral blood of workers exposed to styrene.

Acute-Phase Proteins↗
PubMed2002

Styrene respiratory tract toxicity and mouse lung tumors are mediated by CYP2F-generated metabolites.

Mice are particularly sensitive to respiratory tract toxicity following styrene exposure. Inhalation of styrene by mice results in cytotoxicity in terminal bronchioles, followed by increased incidence of bronchioloalveolar tumors, as well as degeneration and atrophy of nasal olfactory epithelium. In rats, no effects on terminal bronchioles are seen, but effects in the nasal olfactory epithelium do occur, although to a lesser degree and from higher exposure concentrations. In addition, cytotoxicity and tumor formation are not related to blood levels of styrene or styrene oxide (SO) as measured in chronic studies. Whole-body metabolism studies have indicated major differences in styrene metabolism between rats and mice. The major differences are 4- to 10-fold more ring-oxidation and phenylacetaldehyde pathways in mice compared to rats. The data indicate that local metabolism of styrene is responsible for cytotoxicity in the respiratory tract. Cytotoxicity is seen in tissues that are high in CYP2F P450 isoforms. These tissues have been demonstrated to produce a high ratio of R-SO compared to S-SO (at least 2.4 : 1). In other rat tissues the ratio is less than 1, while in mouse liver the ratio is about 1.1. Inhibition of CYP2F with 5-phenyl-1-pentyne prevents the styrene-induced cytotoxicity in mouse terminal bronchioles and nasal olfactory epithelium. R-SO has been shown to be more toxic to mouse terminal bronchioles than S-SO. In addition, 4-vinylphenol (ring oxidation of styrene) has been shown to be highly toxic to mouse terminal bronchioles and is also metabolized by CYP2F. In human nasal and lung tissues, styrene metabolism to SO is below the limit of detection in nearly all samples, and the most active sample of lung was approximately 100-fold less active than mouse lung tissue. We conclude that styrene respiratory tract toxicity in mice and rats, including mouse lung tumors, are mediated by CYP2F-generated metabolites. The PBPK model predicts that humans do not generate sufficient levels of these metabolites in the terminal bronchioles to reach a toxic level. Therefore, the postulated mode of action for these effects indicates that respiratory tract effects in rodents are not relevant for human risk assessment.

Animals↗
PubMed2005

Acute effects of styrene inhalation on the neuroendocrinological system of rats and the different effects in male and female rats.

There have been several epidemiological and experimental studies about styrene from the neuroendocrinological viewpoint. Some reported that styrene exposure affected the neuroendocrinological system and enhanced prolactin (PRL) secretion, but others have denied those effects. It was assumed that styrene exposure caused depletion of dopamine (DA), which is a PRL inhibitor, and that, in consequence, the PRL level increased. However, not only DA but also many other factors control PRL secretion. Therefore, the mechanism of hypersecretion of PRL has not yet been clearly elucidated. In addition, effects of styrene on the female reproductive system have been reported, but the susceptibility needs to be further studied. Therefore, to investigate what causes hypersecretion of PRL and how different the susceptibility is in males and females, we studied acute effects of styrene exposure on the neuroendocrinological system in male and female rats. Immediately after exposure to 150 ppm styrene vapor for 10 days (8 h/day), male and female rats were killed, and blood and brain samples were collected. The styrene concentration in blood, hormones such as PRL, growth hormone (GH) and thyroid-stimulating hormone (TSH) in plasma and neurotransmitters in various brain regions were measured. The styrene concentration in the blood of female rats was higher than that in male rats, and the PRL level was significantly increased in female exposed rats compared with controls. No significant change was observed in male rats. We did not observe any significant changes in DA, 5-hydroxytryptamine (5-HT) or their metabolites. Because neurotransmitters were not affected in either male or female rats, the mechanism enhancing PRL secretion remains unclear. These results suggest that styrene exposure may cause hypersecretion of PRL and that the sensitivity to styrene exposure of the female may be higher than that of the male.

Administration, Inhalation↗
PubMed1992

Styrene migration from general-purpose and high-impact polystyrene into food-simulating solvents.

General-purpose and high-impact polystyrenes (GPPS and HIPS, respectively) are used in many food-contact applications for the packaging of aqueous-based, fatty and dry foods. The correlation of residual styrene concentrations in polystyrene with styrene migration into food-stimulating solvents is of interest in order to predict the potential exposure of consumers to styrene from food-packaging applications. Studies of the migration of styrene into 8% ethanol and cooking oil from a GPPS and a HIPS polymer, each containing three different residual styrene levels, have been completed at temperatures ranging from 70 to 180 degrees F (21 to 82 degrees C). The results showed that the amount of styrene migrating from both polymers into cooking oil was proportional to the square root of the time of exposure, and the total amount of styrene migrating was proportional to the residual levels of styrene in the polymers. The calculated diffusion coefficients were found to be independent of the residual levels of styrene in a given polymer at a given temperature. While the partition equilibrium was not approached when the polymers were exposed to cooking oil, it was observed in the 8%-ethanol exposure studies. The calculated partition coefficients between the polymers and 8% ethanol appeared to be independent of the residual levels of styrene in the polymers at a given temperature. Linear relationships were observed between the logs of the diffusion and partition coefficients and the inverse of the absolute temperature of exposure.

Diffusion↗
PubMed1993

The 'vapour-phase' migration of styrene from general purpose polystyrene and high impact polystyrene into cooking oil.

General purpose and high impact polystyrene (GPPS and HIPS, respectively) are used in many food packaging applications. In some packaging configurations, where there is no direct contact of a liquid surface with the polymer, 'vapour-phase' migration of styrene monomer from the polymer with subsequent absorption into food is thought to be a significant mode of transfer. Correlation of residual styrene concentrations in polystyrene with vapour-phase styrene migration is of interest in order to predict potential consumer exposure to styrene from food-packaging applications of this configuration. Studies of the migration of styrene from GPPS and HIPS into air with subsequent absorption of the monomer into cooking oil, 'vapour-phase' migration, was determined in a sealed system. The results showed that for both polymers the amount of styrene migrating from the polystyrene and being absorbed by the oil was proportional to the square root of the time of exposure. The diffusion coefficients calculated for the vapour-phase migration of styrene from both polymers were found to be in good agreement with the diffusion coefficients previously determined for the 'liquid-phase' migration of styrene from similar polymers where the polymers were completely submerged in the cooking oil. These results indicate that the styrene concentrations measured in both experiments were attributable to the intrinsic diffusion of styrene from polystyrene, and that contact with cooking oil did not accelerate migration in previous experiments.

Diffusion↗
PubMed2005

Effect of shutdown on styrene removal in a biofilter inoculated with Pseudomonas sp. SR-5.

Styrene gas removal was carried out in a biofilter inoculated with a styrene-degrading Pseudomonas sp. SR-5 using a mixed packing material of peat and ceramic under the non-sterile condition. More than 86% removal efficiency was obtained at styrene load of 5-93 g m(-3) h(-1) for 62 days operation period and 78% carbon of removed styrene was converted to CO2. Thereafter, three kinds of styrene shutdown experiments were conducted: (i) air and mineral medium were supplied for 4 days, (ii) complete shutdown, namely no styrene, air and moisture supply was conducted for 3 days, and (iii) only air was supplied for 11 days. When styrene gas was re-supplied after (i) and (iii) shutdown experiments, styrene removal efficiency rapidly recovered, but after (ii) shutdown, recovery of styrene removal was significantly delayed. Supply of air during shutdown period was found to be enough to resume microbial activity to degrade styrene.

Biodegradation, Environmental↗
PubMed2000

Styrene inhibits monoamine oxidase A, but not monoamine oxidase B in monkey brain mitochondria.

The effects of styrene on mitochondrial monoamine oxidase (MAO) activity in rat and monkey brains were compared in vitro. After preincubation at 25 degrees C for 20 min with 1 mM styrene monomer MAO-A activity in monkey brain was inhibited potently using 5-HT (for MAO-A substrate), but MAO-B activity in monkey brain and platelets were slightly inhibited using beta-PEA (for MAO-B substrate). Styrene monomer also competitively inhibited MAO-A activity in a dose-dependent manner. MAO-A in monkey brain was inhibited by styrene in ascending order of potency: styrene trimer>styrene dimer>styrene monomer. In contrast styrene monomer slightly inhibited both MAO-A and MAO-B activities in rat brain mitochondria. In the present study styrene monomer potently inhibits MAO-A activity, but not MAO-B activity, in monkey brain mitochondria in vitro. These results indicate the inhibiting action of styrene differs depending on animal species and MAO isoforms.

Animals↗
PubMed1999

An evaluation of styrene genotoxicity using several biomarkers in a 3-year follow-up study of hand-lamination workers.

A study employing several biomarkers of styrene exposure and genotoxicity was carried out in a group of lamination (reinforced plastic) workers and controls, who had been repeatedly sampled during a 3-year period. Special attention will be paid to the last sampling (S.VI), reported here for the first time. Styrene concentration in the breathing zone, monitored by personal dosimeters, and urinary mandelic acid (MA) were measured as indicators of external exposure. Blood samples were assayed for styrene-specific O6-guanine adducts in DNA, N-terminal valine adducts of styrene in haemoglobin, DNA single-strand breaks (SSB), determined by use of the single cell gel electrophoresis (Comet) assay), and hypoxanthine guanine phosphoribosyl transferase (HPRT) mutant frequencies (MF) in T-lymphocytes. O6-styrene guanine adduct levels were significantly higher in the exposed group (5.9 +/- 4.9 adducts/10(8) dNp) as compared to laboratory controls (0.7 +/- 0.8 adducts/10(8) dNp; P = 0.001). DNA adduct levels significantly correlated with haemoglobin adducts, SSB parameters and years of employment. Styrene-induced N-terminal valine adducts were detected in the lamination workers (1.7 +/- 1.1 pmol/g globin), but not in the control group (detection limit 0.1 pmol/g globin). N-terminal valine adducts correlated strongly with external exposure indicators, DNA adducts and HPRT MF. No significant correlation was found with SSB parameters. A statistically significant difference in HPRT MF was observed between the laminators (22.3 +/- 10.6/10(6)) and laboratory controls (14.2 +/- 6.5/10(6), P = 0.039). HPRT MF in the laminators significantly correlated with styrene concentration in air, MA and haemoglobin adducts, as well as with years of employment and age of the employees. No significant difference (P = 0.450) in MF between the laminators and the factory controls was observed. Surprisingly, we detected differences in MF between sexes. When data from all measurements were combined, women showed higher MF (geometric mean 15.4 vs. 11.2 in men, P = 0.020). The styrene-exposed group exhibited significantly higher SSB parameters (tail moment (TM), tail length (TL) and the percentage of DNA in the tail (TP)) than the control group (P < 0.001). SSB parameters correlated with indicators of external exposure and with O6-styrene guanine adducts. No significant correlation was found between SSB parameters and haemoglobin adducts or HPRT MF. The data encompassing biomarkers from repeated measurements of the same population over a 3-year period are discussed with respect to the mechanisms of genotoxic effects of styrene and the interrelationship of individual biomarkers.

Adult↗