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Pesticide residues in food — 2007: Toxicological ... - ipcs inchem

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221<br />

and 357. This reduced <strong>food</strong> consumption corresponded to reduced body-weight ga<strong>in</strong>s among the<br />

group of females at 1500 ppm. Food consumption was not affected <strong>in</strong> females at 20, 100 and 500 ppm<br />

or <strong>in</strong> any of the groups of males.<br />

Physical exam<strong>in</strong>ations, <strong>in</strong>clud<strong>in</strong>g heart rate, rectal temperature, hear<strong>in</strong>g tests and ophthalmoscopic<br />

exam<strong>in</strong>ations, revealed no treatment-related f<strong>in</strong>d<strong>in</strong>gs. A s<strong>in</strong>gle <strong>in</strong>cidence of ocular change<br />

(corneal opacity) was seen <strong>in</strong> one female <strong>in</strong> the control group.<br />

There were no treatment-related differences among the groups <strong>in</strong> haematology parameters. A statistically<br />

significant reduction <strong>in</strong> reticulocyte count from 0.8% to 0.3% <strong>in</strong> females at 1500 ppm was observed<br />

at week 52, but this difference was considered to be spurious, there be<strong>in</strong>g no accompany<strong>in</strong>g reductions <strong>in</strong><br />

erythrocyte parameters that could <strong>in</strong>dicate a response to toxicity; furthermore, the results showed little consistency<br />

<strong>in</strong> that the reticulocyte count <strong>in</strong> females at 1500 ppm at 25 weeks <strong>in</strong>creased to 0.8% from a control<br />

mean of 0.5%. Differentials were also unremarkable; the only apparent difference among the groups was<br />

a statistically significant decrease <strong>in</strong> relative eos<strong>in</strong>ophils among females at 100 ppm at week 13, which<br />

was not considered to be related to treatment. Blood chemistry analysis showed significantly higher alkal<strong>in</strong>e<br />

phosphatase activity <strong>in</strong> the groups of males at 1500 ppm at all measurement times and <strong>in</strong> males at<br />

500 ppm at week 52. All other statistical differences (reduced BUN <strong>in</strong> the groups of males receiv<strong>in</strong>g 100<br />

and 1500 ppm, <strong>in</strong>creased total bilirub<strong>in</strong> concentration <strong>in</strong> males at 100 ppm, <strong>in</strong>creased sodium concentration<br />

<strong>in</strong> females at 1500 ppm) were considered to be <strong>in</strong>cidental and with<strong>in</strong> the range for normal biological<br />

variation. Measurements at weeks 13 and 26 were not noticeably different from those at week 52.<br />

No significant or remarkable changes <strong>in</strong> ur<strong>in</strong>e analysis were observed.<br />

There were no treatment-related differences <strong>in</strong> organ weights among the groups. The few differences<br />

noted were not considered to be toxicologically relevant. Decreased adrenal weights <strong>in</strong> males at<br />

20 and 500 ppm and <strong>in</strong>creased thyroid weights <strong>in</strong> females at 20 ppm were statistically different from<br />

the respective control animals but not mean<strong>in</strong>gful due to the absence of a dose–response relationship<br />

and correspond<strong>in</strong>g histopathology. No treatment-related observations were recorded at autopsy or<br />

upon microscopic exam<strong>in</strong>ation of the organs and tissues.<br />

The NOAEL <strong>in</strong> dogs given diets conta<strong>in</strong><strong>in</strong>g difenoconazole for 52 weeks was 100 ppm, equal<br />

to 3.7 mg/kg bw per day, on the basis of reduced body-weight ga<strong>in</strong> <strong>in</strong> females at 500 ppm, equal to<br />

19.4 mg/kg bw per day (Rudzki et al., 1988).<br />

2.3 Long-term studies of toxicity and carc<strong>in</strong>ogenicity<br />

Mice<br />

Groups of 60 male and 60 female CD-1®(ICR) mice were given diets conta<strong>in</strong><strong>in</strong>g difenoconazole<br />

technical—first batch, of 94.5% purity, was given dur<strong>in</strong>g weeks 1–20 and the second batch, of 95%<br />

purity, was given <strong>in</strong> weeks 21–80—at a concentration of of 0, 10, 30, 300, 3000 or 4500 ppm for 18<br />

months. The diet conta<strong>in</strong><strong>in</strong>g difenoconazole at 3000 ppm was exchanged after the first 3 weeks for<br />

one conta<strong>in</strong><strong>in</strong>g difenoconazole at 2500 ppm and the group of females at 4500 ppm was discont<strong>in</strong>ued<br />

because of excessive toxicity very early <strong>in</strong> the study. The doses had been selected on the basis of the<br />

results of a 3-month study (Cox, 1987a). These dietary exposures were equal to 0, 1.5, 4.7, 46.3, 423<br />

and 819 mg/kg bw per day for males and 0, 1.9, 5.6, 57.8 and 513 mg/kg bw per day for females <strong>in</strong> the<br />

groups at 0, 10, 30, 300, 2500 ppm (and 4500 ppm <strong>in</strong> males), respectively. Additional groups of 10 male<br />

and 10 female mice were fed diets conta<strong>in</strong><strong>in</strong>g difenoconazole at 0, 3000 or 4500 ppm then allowed a<br />

recovery phase after 12 months of treatment. However, all of the females at 4500 ppm and 16 of the<br />

females at 3000 ppm died or were killed because of their moribund condition with<strong>in</strong> the first 2 weeks.<br />

Food consumption and body weights were recorded weekly for weeks 1–16 and every 4 weeks<br />

thereafter. Mortality was checked twice per day, cl<strong>in</strong>ical signs were recorded once per day and detailed<br />

physical exam<strong>in</strong>ations (<strong>in</strong>clud<strong>in</strong>g palpation) were performed weekly. Eye exam<strong>in</strong>ations were<br />

DIFENOCONAZOLE 201–272 JMPR <strong>2007</strong>

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