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IARC MONOGRAPHS ON THE EVALUATION OF CARCINOGENIC ...

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498<br />

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

pancreatic lobules, inflammatory reactions around pancreatic islets (in mice only), and<br />

altered serum insulin levels but no change in blood glucose levels.<br />

Early studies reported morphological changes in the kidney of Sprague-Dawley rats<br />

after intraperitoneal injections of styrene (2.9 and 5.8 mmol/kg bw on five days per week<br />

for six weeks) (Chakrabarti et al., 1987) and in the respiratory mucosa of SD rats exposed<br />

to styrene by inhalation (150 or 1000 ppm [639–4260 mg/m 3 ], 4 h per day, five days per<br />

week, three weeks) (Ohashi et al., 1986). Effects in kidney and lung are associated with<br />

depletion of glutathione (Chakrabarti & Tuchweber, 1987; Elovaara et al., 1990) and<br />

possibly with direct toxicity of glutathione conjugates to the kidney, as was shown in<br />

experiments with a synthetic glutathione–styrene conjugate (Chakrabarti & Malick,<br />

1991). Viau et al. (1987) reported that Sprague-Dawley rats given intraperitoneal injections<br />

of styrene (1 g/kg bw, which is one-fifth the oral LD 50) daily for 10 days showed<br />

only mild tubular damage. In female Sprague-Dawley rats exposed to styrene (300 ppm<br />

[1280 mg/m 3 ], 6 h per day, five days per week, for 12 weeks), a small increase was<br />

observed in the urinary excretion of plasma proteins, with minor changes in kidney histopathology<br />

consisting of interstitial fibrosis, cystic dilatations and hyaline tubules (Mutti<br />

et al., 1999).<br />

Early studies reported that styrene caused hepatotoxicity in rats concomitantly with<br />

a depletion of glutathione, which may be either a direct effect of styrene or mediated by<br />

lipid peroxidation (Srivastava et al., 1983; Katoh et al., 1989). Male albino rats [strain<br />

not stated] were dosed orally with 200 or 400 mg/kg bw styrene on six days per week for<br />

100 days (Srivastava et al., 1982). Liver changes were observed only after the high dose<br />

and were characterized by tiny areas of focal necrosis composed of a small number of<br />

degenerated hepatocytes and inflammatory cells.<br />

Exposure of B6C3F 1 mice to 0, 125, 250 or 500 ppm [0, 530, 1060 or 2130 mg/m 3 ]<br />

styrene for 6 h per day for 14 days caused severe centrilobular hepatic necrosis and death<br />

after one 6-h exposure to 500 ppm or two 6-h exposures to 250 ppm styrene (Morgan<br />

et al., 1993a). Mortality was higher in male than in female mice and, after 14 days of<br />

exposure, the incidence and severity of liver lesions were also greater in male mice. In a<br />

subsequent study, the greater sensitivity of male mice to styrene exposure compared with<br />

females could not be explained by differences in glutathione depletion or styrene or<br />

styrene 7,8-oxide concentrations in blood (Morgan et al., 1993b). Further investigation<br />

of the role of metabolism in the toxicity of styrene in mice revealed that styrene and<br />

styrene 7,8-oxide concentrations in blood did not correlate well with strain differences in<br />

sensitivity (Morgan et al., 1993c). Mortality and hepatotoxicity induced by exposure to<br />

styrene were greater in B6C3F 1 and C57BL/6 mice than in Swiss mice, while DBA/2<br />

mice were the least sensitive. Styrene and styrene 7,8-oxide concentrations in blood as<br />

well as glutathione depletion were similar in B6C3F 1 and DBA/2 mice but greater than<br />

those in Swiss mice. Although strain and gender differences in sensitivity to styrene toxicity<br />

have been suggested to be due to differences in metabolism, styrene 7,8-oxide<br />

concentrations in blood did not correlate with toxicity in these studies. Morgan et al.<br />

(1995) further investigated strain and gender differences in styrene toxicity at inhalation

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