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

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326<br />

respectively; range for historical controls, 7.5–21.8%) and <strong>in</strong> females at the two higher doses (1 out<br />

of 79, 3 out of 80, 11 out of 77 and 43 out of 76 at 0, 100, 1000 and 2000 ppm, respectively; range<br />

for historical control, 0–2.6%). The <strong>in</strong>crease <strong>in</strong> <strong>in</strong>cidence of tumours was not dose-related nor statistically<br />

significant <strong>in</strong> males, but found to be dose-dependent and statistically significant <strong>in</strong> females. On<br />

the basis of these results, no NOAEL for systemic toxicity could be identified. The overall NOAEL<br />

for oncogenicity was 200 ppm (36 mg/kg bw per day) for females and 1000 ppm (144 mg/kg bw per<br />

day) for males (Keller, 1992b).<br />

Rats<br />

In a GLP-compliant study, groups of 70 male and 70 female rats of stra<strong>in</strong> Crl:CD(SD)BR were<br />

given diets conta<strong>in</strong><strong>in</strong>g flusilazole technical (purity, 95.6%) at a concentration of 0, 10, 50 or 250 ppm<br />

(equal to 0, 0.4, 2.0, and 10 mg/kg bw per day <strong>in</strong> males and 0, 0.5, 2.6 and 13 mg/kg bw per day <strong>in</strong><br />

females) for 2 years. Each group had two satellite groups of 10 males and 10 females for <strong>in</strong>terim<br />

kill<strong>in</strong>g at 6 months and 1 year, respectively. At approximately 100 days after the start of treatment, 20<br />

males and 20 females from each group were mated for the reproduction phase of the study. These rats<br />

were returned to the long-term study after wean<strong>in</strong>g of the second litter. The rats killed at 6 months<br />

were exam<strong>in</strong>ed for bladder lesions only. No treatment-related effect on mortality was observed; survival<br />

rate was > 50% <strong>in</strong> all groups until week 98. No signs of systemic toxicity were evident at the<br />

lowest dose of 10 ppm. At the next higher dose of 50 ppm, there was a dose-related <strong>in</strong>crease <strong>in</strong> the<br />

<strong>in</strong>cidence of pyelonephritis <strong>in</strong> females at 2 years (3 out of 66, 3 out of 62, 8 out of 67 and 10 out of 65<br />

at 0, 10, 50, and 250 ppm, respectively). Increases <strong>in</strong> relative liver weight (females) and <strong>in</strong>cidence of<br />

hydronephrosis (males) were also observed at <strong>in</strong>terim kill at 1 year. These effects were not considered<br />

adverse. At the highest dose of 250 ppm, additional treatment-related changes <strong>in</strong>cluded: <strong>in</strong>creased<br />

<strong>in</strong>cidence of hepatic lesions <strong>in</strong> females (centrilobular hepatocellular hypertrophy and polyploidy)<br />

and hydro-nephrosis <strong>in</strong> males at 1 year; and <strong>in</strong>creased <strong>in</strong>cidence of acidophilic foci of hepatocellular<br />

alteration (13 out of 65 compared with 3 out of 66 <strong>in</strong> controls) and hepatic diffuse fatty changes<br />

(23 out of 65 compared with 9 out of 66 <strong>in</strong> controls) <strong>in</strong> females at 2 years. No hepatic lesions were<br />

observed <strong>in</strong> males at any time dur<strong>in</strong>g the study and no lesions of the ur<strong>in</strong>ary bladder were evident <strong>in</strong><br />

either sex at either <strong>in</strong>terim (6 or 12 months) or term<strong>in</strong>al kill. There was no treatment-related <strong>in</strong>crease<br />

<strong>in</strong> <strong>in</strong>cidence of any tumour type at any dose tested <strong>in</strong> the study. At 250 ppm, males showed a slightly<br />

higher <strong>in</strong>cidence of squamous cell carc<strong>in</strong>omas of the oral and nasal cavities (0 out of 66, 1 out of 63,<br />

0 out of 67 and 3 out of 64, at 0, 10, 50, and 250 ppm, respectively). On the basis of data on historical<br />

controls from six 2-year feed<strong>in</strong>g studies <strong>in</strong> rats (five studies with no tumours of this type and one<br />

study with an <strong>in</strong>cidence of 2 out of 60), the <strong>in</strong>cidence of nasal tumours <strong>in</strong> this study was judged to be<br />

<strong>in</strong>cidental. Flusilazole technical was, therefore, not oncogenic <strong>in</strong> the rat under the conditions of this<br />

study. The NOAEL for systemic toxicity was 50 ppm, equal to 2.0 mg/kg bw per day. The Meet<strong>in</strong>g<br />

noted, however, that the systemic effects reported <strong>in</strong> this study were relatively mild and higher doses<br />

might have been tolerated (Pastoor et al., 1986).<br />

In a more recent study, groups of 65 male and 65 female Crl:CD(SD)BR rats were fed diets<br />

conta<strong>in</strong><strong>in</strong>g flusilazole technical (purity, 95%) at a concentration of 0, 125, 375, or 750 ppm (equal to<br />

0, 5.03, 14.8, and 30.8 mg/kg bw per day <strong>in</strong> males and 0, 6.83, 20.5 and 45.6 mg/kg bw per day <strong>in</strong><br />

females) for 2 years. Each group <strong>in</strong>cluded a satellite group of 10 males and 10 females dest<strong>in</strong>ed for<br />

<strong>in</strong>terim kill at 1 year. The study complied with GLP and test guidel<strong>in</strong>e OECD 451.<br />

At the lowest dose of 125 ppm (equal to 5.03 mg/kg bw per day), dose-related <strong>in</strong>creases <strong>in</strong> <strong>in</strong>cidence<br />

of hepatocellular hypertrophy were observed <strong>in</strong> both sexes at either <strong>in</strong>terim (males, 0 out of 10,<br />

4 out of 10, 8 out of 10 and 8 out of 10; females, 0 out of 10, 7 out of 10, 10 out of 10 and 10 out of<br />

10; at 0, 125, 375 and 750 ppm, respectively) or term<strong>in</strong>al kill (males, 2 out of 53, 2 out of 51, 10 out<br />

of 53 and 19 out of 53; females, 2 out of 56, 4 out of 55, 12 out of 53 and 25 out of 54; values exclude<br />

FLUSILAZOLE 317–347 JMPR <strong>2007</strong>

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