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Safety evaluation of certain food additives - ipcs inchem

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FURAN-SUBSTITUTED ALIPHATIC HYDROCARBONS 507<br />

statistical significance. The mean absolute and relative kidney weights for high-dose<br />

female rats were significantly greater than those <strong>of</strong> controls. Clinical chemistry did<br />

not indicate nephrotoxicity related to administration <strong>of</strong> the test material. The mean<br />

absolute and relative liver weights were significantly increased for the mid- and highdose<br />

male and female groups. Relative thymus weights for the high-dose males<br />

were significantly increased; however, this was considered to be reflective <strong>of</strong> lower<br />

terminal body weights for this group rather than related to test substance<br />

administration. No macroscopic pathology was related to treatment according to the<br />

authors <strong>of</strong> the study.<br />

Treatment-related histopathology noted for mid- and high-dose males<br />

included hyperkeratosis (5/5) and acanthosis (5/5) <strong>of</strong> the non-glandular stomach<br />

(forestomach) mucosa, hypertrophy <strong>of</strong> hepatocytes (4/5 for the mid-dose group and<br />

4/5 for the high-dose group) and an increased number <strong>of</strong> hepatocytes with enlarged<br />

nuclei (4/5 for the mid-dose group and 5/5 for the high-dose group). Females<br />

revealed hyperkeratosis and acanthosis <strong>of</strong> the non-glandular stomach mucosa,<br />

hypertrophy <strong>of</strong> the hepatocytes and increased number <strong>of</strong> hepatocytes with enlarged<br />

nuclei (4/4 for the mid-dose group and 5/5 for the high-dose group). Hypertrophy <strong>of</strong><br />

hepatocytes (1/5) and increased number <strong>of</strong> hepatocytes with enlarged nuclei (1/5)<br />

were observed for low-dose female rats. The test material was a strong gastric<br />

irritant, which accounts for the hyperkeratosis and acanthosis <strong>of</strong> the non-glandular<br />

stomach mucosa observed in mid- and high-dose rats. The study pathologist<br />

concluded that hypertrophy <strong>of</strong> the hepatocytes and enlarged nuclei <strong>of</strong> hepatocytes<br />

were considered adaptive responses to the influx <strong>of</strong> large amounts <strong>of</strong> 3-(2-furyl)acrolein<br />

via gavage to compensate for increased metabolic activity, not to any<br />

toxicity related to the test substance. The authors concluded that the no-observedadverse-effect<br />

level (NOAEL) for 3-(2-furyl)acrolein was 100 mg/kg bw per day in<br />

rats (Faber & Hosenfeld, 1992).<br />

(d) 3-(2-Furyl)acrolein (No. 1497), 2-furyl methyl ketone (No. 1503) and<br />

isobutyl 3-(2-furan)propionate (No. 1514)<br />

In a subchronic study, Sprague-Dawley rats were allocated into groups <strong>of</strong> 32<br />

per sex for the control and low dietary intake level, 12 per sex for the mid-range<br />

group and 10 per sex for the high-intake group. The rats were maintained on diets<br />

calculated to provide 3-(2-furyl)acrolein at 0, 5, 45 or 405 mg/kg bw per day, 2-furyl<br />

methyl ketone at 0, 5, 25 or 100 mg/kg bw per day or isobutyl 3-(2-furan)propionate<br />

at 0, 35, 175 or 875 mg/kg bw per day for 28 days. The animals were provided ad<br />

libitum access to <strong>food</strong> and water throughout the study. Animals were observed daily<br />

for clinical manifestations <strong>of</strong> toxicity and changes in behaviour. Body weights and<br />

<strong>food</strong> consumption were recorded weekly. Haematology, blood chemistry and<br />

urinary analyses were conducted at 4 weeks. At the end <strong>of</strong> 28 days, all <strong>of</strong> the high<br />

intake level rats and 16 per sex <strong>of</strong> the control and low intake level rats were sacrificed<br />

by ether anaesthesia and subsequent exsanguination. The remaining animals<br />

continued on test for 90 days.<br />

In the 3-(2-furyl)acrolein study, a significant decrease in body weight gain<br />

was noted for males and females in the 405 mg/kg bw per day dietary exposure<br />

group when compared with controls at week 4. At the 45 mg/kg bw per day dietary

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