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PubMed1988

Biological monitoring of styrene: a review.

Recent literature about the biological monitoring of styrene-exposed workers is reviewed. Styrene primarily exhibits its toxicity on the central and peripheral nervous systems, although its mutagenicity and chromosome damaging ability also may be relevant. Uptake, transformation and excretion of styrene show that beside the usual biological indicators, such as urinary mandelic and phenylglyoxylic acids (main metabolites), other indicators also may be of interest. These include styrene in expired air, in blood or in urine. Moreover, intermediate or final metabolites such as styrene glycol or mandelic acid in blood also have been proven to be useful in the interpretation of individual values. The most widely used analytical methods for these indicators are gas or high performance liquid chromatography. Correlations between exposure and the different biological indicators mentioned above show that the most reliable indicators are mandelic acid (MA) in urine sampled at the end of the work shift (but not the first day of the week) and the sum of mandelic and phenylglyoxylic acids (MA + PGA) in urine sampled 16 hr after exposure (before the next shift). The biological exposure limit values corresponding to the threshold limit value-time-weighted average (TLV-TWA) of 50 ppm of styrene are 850 mg MA/g creatinine in the end-of-shift sample and 330 mg MA + PGA/g creatinine in the next-morning sample. Other biological indexes, such as styrene glycol (phenyl ethylene glycol) in blood or styrene in urine, look promising but require further research in field situations.

Absorption↗
PubMed2000

Disposition of [Ring-U-(14)C]styrene in rats and mice exposed by recirculating nose-only inhalation.

The disposition of styrene was studied in a group of 12 Sprague Dawley rats and two groups of 30 CD1 mice exposed separately to 160 ppm [ring-U-(14)C]styrene of high specific radioactivity of 1.92 TBq x mol(-1) (52 Ci x mol(-1)) for 6 h. A nose-only exposure system was successfully adapted to (1) recirculate a portion of the flow to limit the amount of (14)C-styrene required, and (2) avoid any polymerization of the compound. The mean uptake of styrene in rats was 113 +/- 7 micromol x kg(-1) x h(-1) and stable over time. The mean uptake in mice was higher, 189 +/- 53 and 183 +/- 76 micromol x kg(-1) x h(-1), for the first and second mouse inhalation experiment, but decreased steadily over time. Some of the mice, but none of the rats, showed signs of overt toxicity. The overall excretion of styrene and its metabolites was quantitatively similar in rats and mice. Urinary excretion was the primary route of excretion while fecal excretion accounted for only a very small part of the radioactivity. There was, however, a significant difference between mice and rats in the exhalation of (14)CO(2), which must have resulted from opening and subsequent breakdown of the aromatic ring. In mice the exhalation of (14)CO(2) accounted for 6.4 +/- 1.0 and 8. 0 +/- 0.5% of the styrene retained during the first and second mouse inhalation experiment. In rats, exhalation of (14)CO(2) accounted for only 2.0 +/- 0.7% of the retained styrene. Together with the results from the quantitative whole-body autoradiography (showing significantly higher binding in mouse lung and nasal passages compared to rat) the larger production of (14)CO(2) might be indicative of the formation of reactive ring-opened metabolites in the mouse lung, which, in turn, might be related to the observed development of bronchioalveolar tumors and nasal effects in mice exposed to styrene.

Administration, Inhalation↗
PubMed2001

A health risk benchmark for the neurologic effects of styrene: comparison with NOAEL/LOAEL approach.

Benchmark dose (BMD) analysis was used to estimate an inhalation benchmark concentration for styrene neurotoxicity. Quantal data on neuropsychologic test results from styrene-exposed workers [Mutti et al. (1984). American Journal of Industrial Medicine, 5, 275-286] were used to quantify neurotoxicity, defined as the percent of tested workers who responded abnormally to > or = 1, > or = 2, or > or = 3 out of a battery of eight tests. Exposure was based on previously published results on mean urinary mandelic- and phenylglyoxylic acid levels in the workers, converted to air styrene levels (15, 44, 74, or 115 ppm). Nonstyrene-exposed workers from the same region served as a control group. Maximum-likelihood estimates (MLEs) and BMDs at 5 and 10% response levels of the exposed population were obtained from log-normal analysis of the quantal data. The highest MLE was 9 ppm (BMD = 4 ppm) styrene and represents abnormal responses to > or = 3 tests by 10% of the exposed population. The most health-protective MLE was 2 ppm styrene (BMD = 0.3 ppm) and represents abnormal responses to > or = 1 test by 5% of the exposed population. A no observed adverse effect level/lowest observed adverse effect level (NOAEL/LOAEL) analysis of the same quantal data showed workers in all styrene exposure groups responded abnormally to > or = 1, > or = 2, or > or = 3 tests, compared to controls, and the LOAEL was 15 ppm. A comparison of the BMD and NOAEL/LOAEL analyses suggests that at air styrene levels below the LOAEL, a segment of the worker population may be adversely affected. The benchmark approach will be useful for styrene noncancer risk assessment purposes by providing a more accurate estimate of potential risk that should, in turn, help to reduce the uncertainty that is a common problem in setting exposure levels.

Air Pollutants, Occupational↗
PubMed2000

Physiological analysis of the expression of the styrene degradation gene cluster in Pseudomonas fluorescens ST.

The effects of different carbon sources on expression of the styrene catabolism genes in Pseudomonas fluorescens ST were analyzed by using a promoter probe vector, pPR9TT, which contains transcription terminators upstream and downstream of the beta-galactosidase reporter system. Expression of the promoter of the stySR operon, which codes for the styrene two-component regulatory system, was found to be constitutive and not subject to catabolite repression. This was confirmed by the results of an analysis of the stySR transcript in P. fluorescens ST cells grown on different carbon sources. The promoter of the operon of the upper pathway, designated PstyA, was induced by styrene and repressed to different extents by organic acids or carbohydrates. In particular, cells grown on succinate or lactate in the presence of styrene started to exhibit beta-galactosidase activity during the mid-exponential growth phase, before the preferred carbon sources were depleted, indicating that there is a threshold succinate and lactate concentration which allows induction of styrene catabolic genes. In contrast, cells grown on glucose, acetate, or glutamate and styrene exhibited a diauxic growth curve, and beta-galactosidase activity was detected only after the end of the exponential growth phase. In each experiment the reliability of the reporter system constructed was verified by comparing the beta-galactosidase activity and the activity of the styrene monooxygenase encoded by the first gene of the styrene catabolic operon.

Bacterial Proteins↗
PubMed1990

Urinary excretion of mandelic, phenylglyoxylic, and specific mercapturic acids in rats exposed repeatedly by inhalation to various concentrations of styrene vapors.

Adult male Sprague-Dawley rats were exposed by inhalation to various concentrations of styrene vapors (25, 50, 100, or 200 ppm) 6 h/day, 5 days/week, for 4 consecutive weeks. The concentrations were varied from day to day according to a random pattern allowing treated animals to be exposed five times to each concentration of styrene. Each day, the following urinary metabolites were analysed from samples collected during exposure (0-6 h) and after exposure (6-24 h): mandelic acid; phenylglyoxylic acid; and two mercapturic acids, N-acetyl-S-(1-phenyl-2-hydroxyethyl)-L-cysteine (M1) and N-acetyl-S-(2-phenyl-2-hydroxyethyl)-L-cysteine (M2). Various parameters of renal toxicity and hepatic microsomal and cytosolic enzyme activities were also measured. The results show that there is a very good relationship between the excretion of all four styrene metabolites and the degree of daily exposure to styrene over the entire period of urine collection, with correlation coefficients ranging from 0.82 to 0.98. The correlation was poor for mandelic acid during the 0-6 h period. There was no evidence that repeated exposure to styrene caused renal toxicity, nor induced hepatic microsomal enzyme activities; cytosolic glutathione S-transferase activity was increased moderately by 1.5 times. Thus, under conditions of exposure to styrene likely to be found in the workplace, all four metabolites measured were good indicators of styrene exposure throughout the length of the experiment. Since mercapturic acids result from the conjugation of styrene oxide with glutathione, the data suggest that measurement of these metabolites offers the possibility to monitor internal exposure to a toxic electrophilic compound more directly.

Acetylcysteine↗
PubMed2006

Enhancement of styrene removal efficiency in biofilter by mixed cultures of Pseudomonas sp. SR-5.

The styrene-degrading bacterium Pseudomonas sp. SR-5 exhibited a high styrene removability in a biofilter. However, the styrene removal efficiency (RE) of SR-5 decreased with time. We carried out styrene gas removal in a biofilter inoculated with mixed cultures of SR-5 and other microorganisms to determine the possibility of obtaining an enhanced RE for a long period. The following three inocula were carried out: (i) styrene-degrading bacteria, strains 1 and 3, (ii) a benzoic acid-degrading bacterium Raoultella sp. A, and (iii) wastewater from a chemical company dealing with styrene. These biofilters with mixed SR-5 showed an enhanced RE compared with those with a single culture of SR-5. The complete styrene elimination capacities for ensuring 100% styrene removal in those mixed cultures were 151, 108 and 124 g/m(3)/h, compared with a single culture of SR-5.

Bioreactors↗
PubMedDate not supplied

Combined effects of noise and styrene on hearing: comparison between active and sedentary rats.

In this study, two investigations were carried out with adult Long-Evans rats exposed to increasing concentrations of styrene. In the first experiment, the hearing of rats, which were forced to walk in a special wheel during the exposure, was compared to that of rats which were sleepy in their cage. The active rats were exposed to styrene concentrations ranging from 300 to 600 ppm, whereas the sedentary rats were exposed from 500 to 1000 ppm for 4 weeks, 5 days per week, 6 hours per day. In the second experiment, designed to evaluate the hearing risks at threshold limit values, active rats were exposed either to a noise having a Leq8h of 85 dB (equivalent level of a continuous noise for a typical 8-h workday), or to 400-ppm styrene or to a simultaneous exposure to noise and styrene. In both experiments, auditory function was tested by auditory-evoked potentials from the inferior colliculus and completed by morphological analyses of the organ of Corti. The results of the first experiment showed that the same amount of styrene-induced hearing loss can be obtained by using concentrations approximately 200 ppm lower in active rats than in sedentary rats. The second investigation showed that, in spite of the low-intensity noise and the low-concentration of styrene, there is a clear risk of potentiation of styrene-induced hearing loss by noise. These findings and exposure conditions were discussed and extrapolated with regard to the risk assessment for human beings. The authors propose to decrease the French threshold limit value of styrene for ensuring a high level of protection for human hearing.

Animals↗
PubMed2000

Styrene-induced changes in amacrine retinal cells: an experimental study in the rat.

Dopamine (DA) is synthesized in amacrine cells and released upon membrane depolarization in a calcium-dependent way. Thus, it is recognized to function as a major neurotransmitter or modulator in vertebrate retina. Owing to DA modulating activity on cone-horizontal cells transmission, depletion or dysfunction of amacrine cells could interfere with chromatic processing, accounting for the acquired dyschromatopsia described among styrene-exposed workers. The present study has been designed to test the hypothesis that amacrine cells represent a vulnerable target of styrene in subchronically exposed rats. Ten female Sprague-Dawley rats were exposed to 300 ppm styrene 6 h/day, 5 days/week, for 12 weeks; ten rats exposed to fresh air served as a control group. Whole mounted retinas were used for the morphometry of tyrosine hydroxylase (TH) immunoreactive cells (IR). DA content and TH activity were measured by HPLC and electrochemical detection and glutathione (GSH) was measured by HPLC tandem mass spectrometry (LC-MS/MS). In treated rats, morphometric analysis showed a loss of TH-IR amacrine cells (6.2/mm2 vs. 8.7/mm2 recorded in controls, p = 0.002), without any peripheral-central variation in cell loss. DA content was also lower in exposed, as compared to control animals (208.64 vs. 267.98 microg/g w.w., p = 0.004). The activity of TH in the whole retina was similar in styrene-exposed and control rats when expressed as a function of the wet weight, whereas it was much higher in styrene-exposed rats (+64%) when expressed as a function of the number of TH-IR amacrine cells (p < 0.001). Finally, retinal GSH was reduced by 30% in exposed as compared to control rats (p = 0.01). In summary, retinal TH-IR cells were sensitive to styrene exposure, which seems to cause both structural and functional changes, represented by cell loss and DA depletion, respectively. These findings confirm the vulnerability of dopaminergic systems to styrene toxicity, providing some insights on the possible mechanism of loss in chromatic discrimination recorded among workers occupationally-exposed to styrene.

Animals↗
PubMedDate not supplied

Critical period for styrene ototoxicity in the rat.

The current experiments were undertaken to determine whether or not styrene-induced hearing loss in the rat depends more on the existence of a critical period between 14 and 21 weeks of age than on body weight. For these purposes, two experiments were carried out with mature Long-Evans rats. In the first experiment, two groups of 5-month old rats, but having different body weight (slim: 314 g vs. fat: 415 g) were exposed to 700 ppm styrene for 4 consecutive weeks, 5 days per week, 6 hours per day. In the second experiment, two groups of rats having the same weight: 345 g, but different ages (14- vs. 21- week old) were exposed to styrene in strictly identical experimental conditions. Auditory sensitivity was tested by recording evoked potentials from the inferior colliculus. Surface preparations of the organ of Corti were also performed to complete the investigation. At the end of the six week recovery period following the styrene exposure, a 7 dB permanent threshold shift (PTS) was obtained with the same age animals regardless of the body weight. Consequently, weight was not a major factor in styrene-induced hearing loss. Age was a more critical factor in determining higher sensitivity to styrene. Indeed, the three months old group had 23.5 dB PTS, whereas the five months old group had only a 7.7 dB PTS at 16 kHz. Thus, a 15 dB difference of PTS was obtained between the rats having the same weight but different age. While the weight does not play a major role in styrene ototoxicity, there is a critical period whose duration lasts more than three months and for which the susceptibility to styrene is enhanced.

Age Factors↗
PubMed1978

Interaction of styrene and acetone with drug biotransformation enzymes in rat liver.

In the presence of hepatic microsomes, styrene produced a type I difference spectrum, which demonstrates that styrene binds to the catalytic site of ferricytochrome P-450. A comparison of the binding parameters for the interaction of styrene with noninduced, phenobarbital-induced, and 3-methylcholanthrene-induced microsomes indicated that styrene is predominantly bound by cytochrome P-450 and not by cytochrome P-448. Inhalation exposure to a mixture of acetone (1,000 ppm, 6 h/d) and styrene (300 ppm, 6 h/d) for 5 d caused a distinct decrease in hepatic free nonprotein sulfhydryl groups. This decrease could be observed both with and without phenobarbital treatment. Acetone inhalation alone also enhanced ethoxycoumarin O-deethylase activity in rats without pretreatments. Acetone inhalation also increased the cytochrome P-450 content of liver microsomes, but it had no effect on NADPH cytochrome c reductase or epoxide hydratase activity. Combined exposure to styrene and acetone enhanced NADPH cytochrome c reductase activity in nonphenobarbital-treated rats, but no effect was seen in the phenobarbital-treated animals. Phenobarbital treatment of animals can greatly modify the biotransformation and toxicity of styrene, phenobarbital inducible P-450 hemoprotein playing a predominant role in its metabolism. Simultaneous inhalation exposure to acetone also interacts with the metabolism of styrene.

Acetone↗
PubMed1978

The role of glutathione in the toxicity of styrene.

The role of glutathione in the toxicity of styrene has been proposed based on the observations that glutathione inhibits the covalent binding of styrene and styrene oxide in vitro and that the administration of these compounds to animals decreases the glutathione content in the liver in vivo. In this study methionine (a precursor of reduced glutathione) or diethylmaleate (a depletor or reduced glutathione) was administered to hamsters concomitantly with styrene. Methionine protected the liver against the hepatotoxicity of styrene as indicated by the serum alanine aminotransferase activity. Diethylmaleate potentiated the hepatotoxic effect of styrene. A threshold value for hepatic glutathione of about 1 mmol/l was found for styrene toxicity. Cell damage occurred when the concentration of reduced glutathione in the liver has a central role in the development of cell damage caused by styrene.

Alanine Transaminase↗
PubMed1997

Recombinant expression of human microsomal epoxide hydrolase protects V79 Chinese hamster cells from styrene oxide- but not from ethylene oxide-induced DNA strand breaks.

Styrene 7,8-oxide and ethylene oxide are widely used genotoxic bulk chemicals, which have been associated with potential carcinogenic hazard for occupationally exposed workers. Both epoxides alkylate DNA preferentially at the N-7 position of guanine and consequently produce single-strand breaks and alkali labile sites in the DNA of exposed cells. In order to study the role of human microsomal epoxide hydrolase (hmEH) in protecting cells against genotoxicity of styrene 7,8-oxide and ethylene oxide, we expressed the cDNA of hmEH in V79 Chinese hamster cells. We obtained a number of cell clones that expressed functionally active epoxide hydrolase. Among these, the clone 92hmEH-V79 revealed an especially high enzymatic mEH activity toward styrene 7,8-oxide (10 nmol converted per mg of protein per min, measured in the 9,000 x g supernatant of the cell homogenate), that was 100 times higher than that determined in mock-transfected cells and within the range of mEH activity in human liver. Styrene 7,8-oxide-induced DNA single-strand breaks/alkali labile sites (dose range 10 microM to 1 mM styrene 7,8-oxide) measured by the alkaline elution technique were significantly lower in the 92hmEH-V79 cells as compared to the mock-transfected cells. The protection against styrene 7,8-oxide genotoxicity in 92hmEH-V79 cells could be abolished by addition of valpromide, a selective inhibitor of microsomal epoxide hydrolase. These results clearly show that the metabolism of styrene 7,8-oxide by hmEH in 92hmEH-V79 cells was responsible for the protection against styrene 7,8-oxide genotoxicity. On the other hand, no protective effect of epoxide hydrolase expression could be observed on ethylene oxide-induced DNA damage with the recombinant cell line over a dose range of 0.5-2.5 mM ethylene oxide. This selectivity of the protective effect on epoxide genotoxicity thus appears to be an important factor that must be taken into account for the prediction of the genotoxic risk of epoxides themselves or compounds that can be metabolically activated to epoxides.

Animals↗
PubMed1997

Measurement of styrene oxide in polystyrenes, estimation of migration to foods, and reaction kinetics and products in food simulants.

The concentration of styrene-7,8-oxide has been measured in nine base resins and 16 samples of polystyrene articles intended for food contact. The epoxide was not detected in the resins (limit of detection 0.5 mg/kg) but was found in 11 of the 16 packaging samples at up to 2.9 mg/kg. Assuming that the propensity of styrene oxide to migrate is the same as styrene monomer, and using existing survey data for styrene monomer in packaging and foods, the migration levels expected for styrene oxide were calculated. Estimates were from 0.002 to 0.15 microgram/kg styrene oxide in foods. The stability of styrene oxide in the four standard EU food simulants was studied at 40, 100, 150 and 175 degrees C, to establish the transformation products to be expected following migration testing. The half-life at 40 degrees C in distilled water, 15% aqueous ethanol, 3% aqueous acetic acid and olive oil was 15, 23, < 1, > 2000 hr, respectively. The principal product was the diol from hydrolysis of the epoxide group. Ring opening in aqueous ethanol simulant gave the diol and also the glycol monoethyl ether. It is concluded that this instability of styrene oxide will reduce concentrations in foods, from an already low migration level to even lower levels with the formation of hydrolysis products that are less toxic than the parent epoxide.

Carcinogens↗
PubMed2005

Zirconocene-mediated and/or catalyzed unprecedented coupling reactions of alkoxymethyl-substituted styrene derivatives.

Reactions of o-(alkoxymethyl)styrene derivatives with a stoichiometric amount of zirconocene-butene complex (zirconocene equivalent, "Cp(2)Zr") brought about an insertion of the zirconocene species into a benzylic carbon-oxygen bond. The oxidative insertion of Cp(2)Zr to the benzylic carbon-oxygen bond is a result of sequential reactions: (i) formation of zirconacyclopropane by the ligand exchange with o-(alkoxymethyl)styrene, (ii) elimination of the alkoxy group through an aromatic conjugate system giving metalated o-quinodimethane species, and (iii) transfer of zirconium metal to the benzylic position. Through use of a catalytic amount of "Cp(2)Zr", however, unprecedented homo-coupling reactions (dimerization) of o-(alkoxymethyl)styrene derivatives occurred to give a tetracyclic compound. On the other hand, reactions of o-(1-alkoxyisopropyl)styrene derivatives gave rise to the analogous tetracyclic compounds regardless of the amount of "Cp(2)Zr" (stoichiometric or catalytic). Heterocoupling product between o-(1-alkoxyisopropyl)styrene and styrene congeners was obtained in high cis stereo- and regioselectivity by treating o-(1-alkoxyisopropyl)styrene derivatives with "Cp(2)Zr" in the presence of an excess amount of styrene derivatives.

Journal Article↗
PubMedDate not supplied

The metabolism and excretion of 14C-styrene oxide-glutathione adducts administered to the winter flounder, Pseudopleuronectes americanus, a marine teleost. Identification of the corresponding S-cysteine derivatives as major urinary metabolites.

The metabolism and excretion of intramuscularly administered 14C-glutathione conjugates of styrene oxide (Ia and IIa) were studied in the winter flounder at three dose levels. The various radiolabeled thioether metabolites excreted were separated by reverse-phase high pressure liquid chromatography, and identified and quantitated by cochromatography with synthetic standards. The urine was the major excretion route for radioactivity derived from the glutathione conjugates (up to 90%) at each dose level (1.0, 3.9, and 24.4 mg/fish) studied. The corresponding cysteine derivatives (Ic, IIc) were the major urinary metabolites although the N-acetylcysteine derivatives (Id, IId), or mercapturic acids, were also present in significant amounts at each dose and excretion interval examined. Unchanged glutathione conjugates of styrene oxide were the major radioactive constituents of 24-hr bile samples from the treated flounder, although significant amounts of the cysteinylglycine (Ib, IIb), cysteine, and N-acetylcysteine derivatives were also present in bile. Bile was a minor excretory route relative to urine. The oxidation of 14C-styrene to styrene 7,8-oxide by the cytochrome P-450-dependent monooxygenase system of hepatic microsomes of winter flounder was also demonstrated; likewise, styrene was converted to the diastereomeric glutathione conjugates of styrene 7,8-oxide by 9,000g supernatant fractions of flounder liver supplemented with glutathione. This study demonstrated that flounder liver can convert styrene to glutathione conjugates to styrene oxide and that mercapturic acid biosynthesis occurs after parenteral administration of a xenobiotic-glutathione adduct to this marine species, although the major urinary metabolites were the cysteine conjugates rather than the anticipated mercapturic acid derivatives.

Acetylcysteine↗
PubMed1981

The metabolism and excretion of styrene oxide-glutathione conjugates in the rat and by isolated perfused liver, lung and kidney preparations.

The metabolism and excretion of styrene oxide-glutathione conjugates were studied in the intact rat and by isolated perfusion techniques in rat lung, liver and kidney. The intact animals converted the styrene oxide-glutathione conjugates almost entirely to styrene oxide-n-acetylcysteine derivatives mercapturic acids), with much smaller amounts of cysteine, cysteinylglycine and (unchanged) glutathione conjugates. Only small amounts of biliary excretion (approximately 5%) and less than 1% of fecal excretion of radioactivity were found. The isolated perfused kidney retains the capacity to transform virtually all of the glutathione conjugates at the dose level studied (25-30 mumol/kidney) and the principal component in urine from the isolated kidney was the cysteine conjugate. Isolated perfused lung experiments demonstrated that this organ has a minor role in styrene oxide-thioether conjugate. Isolated perfused lung experiments demonstrated that this organ has a minor role in styrene oxide-thioether conjugate metabolism. The isolated perfused liver experiments showed that phenobarbital pretreatment has little effect on biliary excretion but barbital pretreatment has little effect on biliary excretion but that it causes profound qualitative and quantitative effects on metabolism of styrene oxide-glutathione conjugates in the perfusion medium. The high level of styrene oxide-cysteine conjugates in the perfusion medium of an isolated perfused liver, especially after phenobarbital treatment, is consistent with the theory that gamma-glutamyltransferase activity is extracellular. The high-pressure liquid chromatography system of analysis described offers the ability to simultaneously separate and quantitate the major thioether conjugates of styrene oxide and other electrophilic epoxides.

Animals↗
PubMed1993

Exposure-excretion relationship of styrene and acetone in factory workers: a comparison of a lipophilic solvent and a hydrophilic solvent.

A factory survey was conducted in the second half of a working week on 41 exposed male workers, who were engaged in fiber-reinforced plastics work and exposed to the mixed vapors of styrene and acetone. Nonexposed workers, 20 men, were recruited from the same factory. Styrene and acetone in respiratory zone air were monitored for a 8-h shift with carbon cloth- and water-equipped personal diffusive samplers, respectively. Blood and urine samples were collected at the shift-end. Acetone and styrene concentrations in whole blood, serum and urine were measured by head-space gas chromatography, and phenylglyoxylic acid in urine by high-performance liquid chromatography. All biological exposure indicators analyzed correlated significantly with the intensity of exposure to the corresponding solvent during the shift. The slopes of the regression lines indicate that a very small fraction of styrene absorbed will be excreted into urine as styrene per se, and that styrene is quite effectively excreted into urine after metabolic conversion. In contrast, the slopes of regression lines for acetone suggest that acetone distributes both in the blood and urine quite evenly. When the distribution of the solvent in serum was compared with that in the whole blood, it was found that almost all of styrene in blood is present in the serum, whereas acetone distributed very evenly in the cellular and noncellular fractions of the blood.

Acetone↗
PubMed1991

The applicability of the measurement of urinary thioethers. A study of humans exposed to styrene during diet standardization.

The excretion of thioethers was measured in the urine of 6 volunteers, who were experimentally exposed to styrene, and 18 styrene workers. In addition, 12 clerks (non-smokers) and 12 sheet-metal workers (smokers) served as control groups. Diet was standardized during the experiments. Thioethers were measured by a spectrophotometric method. The volunteers were exposed to styrene, 210 mg/m3, for 2h at a 50-W workload. An increase in thioether excretion was observed; the largest was in the urine samples collected between 0.5 and 5 h after the end of the exposure. After 43 h the excretion of thioethers was close to the pre-exposure level (3.5 mmol/mol creatinine). About 1% of the styrene absorbed was detected as thioethers in urine, which is only about 1/10 of the conversion reported for rats. From excretion rate curves a half-life of about 11 h was calculated for styrene thioethers. The styrene workers were employed at two plants. The average exposure to styrene (time-weighted average 8 h) was estimated to be about 115 mg/m3 (smokers in plant A), 55 mg/m3 (non-smokers in plant A) and less than or equal to 10 mg/m3 (non-smokers in plant B). The excretion of thioethers in exposed workers at plant A was higher by 2-4 mmol/mol creatinine than that in non-exposed controls. In plant B, where exposure was lower, an increase in that amount of thioethers excreted in the urine by exposed workers was less pronounced, and was statistically significant only when post-shift samples were compared with pre-shift samples.(ABSTRACT TRUNCATED AT 250 WORDS)

Adult↗