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IARC MONOGRAPHS ON THE EVALUATION OF CARCINOGENIC ...

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500<br />

Styrene caused a dose-dependent increase in serum sorbitol dehydrogenase activity, an<br />

indicator of hepatotoxicity. Pretreatment of the animals with pyridine and β-naphthoflavone,<br />

inducers of CYP enzymes, increased the toxicity of styrene, but pretreatment<br />

with phenobarbital had no such effect. Trichloropropene oxide, an inhibitor of epoxide<br />

hydrolase, increased the hepatotoxicity of styrene 7,8-oxide, while buthionine sulfoximine,<br />

a glutathione depletor, did not. When given at the same dose (300 mg/kg bw), the<br />

racemic mixture of styrene 7,8-oxides and R-styrene 7,8-oxide caused a greater hepatotoxic<br />

effect than did S-styrene 7,8-oxide. However, differences in pulmonary toxicity<br />

between the enantiomers were not statistically significant. In a subsequent study to assess<br />

the susceptibility of mouse strains to the effects of styrene and styrene 7,8-oxide, male<br />

mice (A/J, C57BL/6 or CD-1) were given an intraperitoneal injection of 800 mg/kg bw<br />

styrene and killed 24 h later (Carlson, 1997b). Biomarkers of hepatotoxicity and<br />

pneumotoxicity were evaluated as in the study mentioned above (Gadberry et al., 1996).<br />

CD-1 mice were not as sensitive as the other strains to the hepatotoxic or pneumotoxic<br />

effects of styrene, but were equally sensitive to the toxic effects of styrene 7,8-oxide<br />

given by intraperitoneal injection at 300 mg/kg bw.<br />

Hepatotoxicity and cell proliferation induced in male B6C3F 1 mice by a single 6-h<br />

exposure to 500 ppm [2130 mg/m 3 ] styrene was compared with that caused by repeated<br />

exposures to 500 ppm styrene for 6 h per day for up to 14 days (Mahler et al., 1999).<br />

Single or repeated inhalation exposure of mice to styrene caused severe necrosis of<br />

centrilobular hepatocytes followed by regeneration of necrotic zones. Re-exposure to<br />

styrene of mice that had received only a single dose of styrene resulted in hepatocellular<br />

necrosis, indicating that regenerated centrilobular cells were again susceptible to the<br />

cytolethal effect of styrene following a 14-day recovery. In contrast, continuous styrene<br />

exposure induced hepatocellular resistance to the cytolethal effect of styrene. New<br />

hepatocytes were produced with reduced metabolic activity. Centrilobular hepatocytes<br />

were resistant to styrene while they were actively synthesizing DNA and continued<br />

styrene exposure was required for sustained DNA synthesis.<br />

4.3 Reproductive and developmental effects<br />

Reproductive and developmental effects of styrene have been reviewed by <strong>IARC</strong><br />

(1994a) and very extensively by Brown et al. (2000). The present evaluation is mainly<br />

based on these reviews and recent studies not included therein.<br />

4.3.1 Humans<br />

<strong>IARC</strong> <strong>M<strong>ON</strong>OGRAPHS</strong> VOLUME 82<br />

Early human studies suggested an association between occupational exposure to<br />

styrene and congenital central nervous system malformation (Holmberg, 1977, 1979),<br />

but subsequent, more extensive studies by the same and other investigators did not<br />

confirm the association (Brown et al., 2000).

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