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Pesticide residues in food — 2006: Toxicological ... - ipcs inchem

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388<br />

slight (3 out of 30) hepatocellular hypertrophy <strong>in</strong> male P 2<br />

rats compared with 0 out of 30 concurrent<br />

controls. No cl<strong>in</strong>ical chemistry assays were performed <strong>in</strong> this study. Slight, bilateral <strong>in</strong>flammation<br />

of the epididymis was <strong>in</strong>creased at 100 mg/kg bw per day <strong>in</strong> parental males of both generations,<br />

relative to concurrent controls, but was with<strong>in</strong> the range for historical controls; epididymides were<br />

not <strong>in</strong>vestigated histopathologically at 20 or 5 mg/kg bw per day.<br />

Table 11. F<strong>in</strong>d<strong>in</strong>gs <strong>in</strong> a two-generation study of reproductive toxicity <strong>in</strong> rats given diets<br />

c onta<strong>in</strong><strong>in</strong>g qu<strong>in</strong>oxyfen<br />

F<strong>in</strong>d<strong>in</strong>g<br />

Nom<strong>in</strong>al dose (mg/kg bw per day)<br />

0 5 20 100<br />

F 1a<br />

/F 1b<br />

Litter size day 1 15 / 14 14 / 16 14 / 16 15 / 17<br />

Litter size day 21 14 / 14 13 / 15 14 / 14 14 / 15<br />

Pup weight day 0 (g) 6.7 / 6.9 7.1 / 6.9 6.7 / 6.9 6.6 / 6.7<br />

Pup weight day 21 (g) 43 / 41 47* / 40 42 / 41 39* / 37<br />

F 1a<br />

–P 2<br />

bw, day 83, M/F (g) 553 / 311 561 / 341* 581 / 338* 547 / 315<br />

F 2<br />

Litter size day 1 14 15 14 13<br />

Litter size day 21 13 15 13 12<br />

Pup weight day 0 (g) 6.7 6.9 6.7 6.6<br />

Pup weight day 21 (g) 42 43 41 40<br />

From Liberacki et al. (1995)<br />

* p < 0.05<br />

The NOAEL for general toxicity and pup development was 20 mg/kg bw per day on the<br />

basis of slight but consistent reduction <strong>in</strong> body-weight ga<strong>in</strong> <strong>in</strong> pups dur<strong>in</strong>g lactation and hepatocyte<br />

hypertrophy <strong>in</strong> the liver of parental males, without <strong>in</strong>vestigations on serum enzyme activity. The<br />

NOAEL for reproductive performance was 100 mg/kg bw per day as there were no adverse effects on<br />

reproductive performance at the highest test dose (Liberacki et al., 1995).<br />

(b)<br />

Developmental toxicity<br />

Rats<br />

In a GLP-compliant study, groups of 30 mated specific pathogen free (SPF) female<br />

Crl:CD(SD)BR rats (body weight, 202–239 g) were given qu<strong>in</strong>oxyfen (purity, 97.4%) at a dose<br />

of 0 (control), 100, 300 or 1000 mg/kg bw per day suspended <strong>in</strong> 1% methyl cellulose by gavage<br />

from day 6 to 15 of presumed gestation. Dams were killed on day 20 and the pups were delivered<br />

by caesarean section. The liver, kidneys, gravid uter<strong>in</strong>e weights, and the number of corpora lutea,<br />

implantations, resorptions and dead and live fetuses were recorded. Fetuses were weighed, sexed<br />

and exam<strong>in</strong>ed for external, visceral and skeletal abnormalities.<br />

There was a s<strong>in</strong>gle mortality at 1000 mg/kg bw per day that was the result of an <strong>in</strong>tubation<br />

error. The number of pregnant dams was 24, 27, 28 and 28 at doses of 0 (control), 100, 300 and<br />

1000 mg/kg bw per day. No signs of toxicity or changes <strong>in</strong> animal behaviour were observed<br />

dur<strong>in</strong>g the dos<strong>in</strong>g period. Food consumption and body-weight ga<strong>in</strong> were not affected by the<br />

treatment. At term<strong>in</strong>ation, no gross abnormalities were observed <strong>in</strong> dams. There were no<br />

significant treatment-related effects on the number of litters with external, visceral or skeletal<br />

effects. A raised <strong>in</strong>cidence of pups with extra ribs was seen at the highest dose (13% vs 8–9%<br />

<strong>in</strong> other groups) but was with<strong>in</strong> the range for historical controls (7–22%) and was not clearly<br />

treatment related.<br />

QUINOXYFEN X-X JMPR <strong>2006</strong>

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