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

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496<br />

In a two-generation study of reproductive toxicity, groups of 30 male and 30 female CD<br />

Sprague-Dawley rats were given diets conta<strong>in</strong><strong>in</strong>g thiacloprid (purity, 96.7–97.5%) at a concentration<br />

of 0, 50, 300 or 600 ppm. Animals were mated after 10 weeks to produce F 1<br />

pups. After wean<strong>in</strong>g,<br />

selected F 1<br />

pups were given diets conta<strong>in</strong><strong>in</strong>g thiacloprid for 10 weeks before mat<strong>in</strong>g and production<br />

of the F 2<br />

generation. The study complied with test guidel<strong>in</strong>e OECD 416. Determ<strong>in</strong>ations of body<br />

weights, feed consumption, cl<strong>in</strong>ical signs, estrous cycl<strong>in</strong>g, mat<strong>in</strong>g, fertility, duration of gestation<br />

and litter size were performed dur<strong>in</strong>g the study. Offspr<strong>in</strong>g were exam<strong>in</strong>ed for treatment-related<br />

effects on sex ratio, pup viability, body-weight ga<strong>in</strong> and cl<strong>in</strong>ical signs. Gross necropsy evaluations<br />

were performed on all adults and pups. Histopathological exam<strong>in</strong>ation of reproductive organs, liver,<br />

pituitary, thyroids and all gross lesions was performed on all F 0<br />

and F 1<br />

adults. Dietary analyses<br />

revealed satisfactory test substance stability and concentration. The mean daily <strong>in</strong>takes at 0, 50, 300<br />

and 600 ppm <strong>in</strong> the period before mat<strong>in</strong>g were equal to 0, 3.5, 20.9 and 40.9 mg/kg bw per day <strong>in</strong><br />

F 0<br />

males and 0, 4.2, 26,0 and 50.8 mg/kg bw per day <strong>in</strong> F 0<br />

-females, respectively, and 0, 3.5, 21,7<br />

and 43.9 mg/kg bw per day <strong>in</strong> F 1<br />

males and 0, 4.1, 25.5 and 51.0 mg/kg bw per day <strong>in</strong> F 1<br />

females,<br />

respectively.<br />

Four F 0<br />

females at 300 ppm and three females at 600 ppm were sacrificed or found dead on<br />

days 23–24 of gestation due to dystocia. These animals also exhibited pallor, per<strong>in</strong>eal and vag<strong>in</strong>al<br />

sta<strong>in</strong><strong>in</strong>g. Small numbers of deaths <strong>in</strong> other groups are not attributable to the effects of treatment. No<br />

cl<strong>in</strong>ical signs of toxicity were noted <strong>in</strong> surviv<strong>in</strong>g animals.<br />

In parental animals, body-weight ga<strong>in</strong>s were decreased at 600 ppm for F 0<br />

and F 1<br />

females<br />

dur<strong>in</strong>g the phase before mat<strong>in</strong>g and for F 1<br />

males. Dur<strong>in</strong>g the gestation phase lower body weights<br />

with normal weight ga<strong>in</strong>s were measured <strong>in</strong> the F 0<br />

and F 1<br />

groups at the highest dose. Also<br />

dur<strong>in</strong>g the lactation phase lower body weights were observed <strong>in</strong> the parental and F 1<br />

groups at the<br />

highest dose (Table 30). No consistent effect on feed consumption was seen <strong>in</strong> F 0<br />

animals. Feed<br />

consumption was significantly <strong>in</strong>creased <strong>in</strong> F 1<br />

animals of both sexes at 600 ppm dur<strong>in</strong>g the period<br />

before mat<strong>in</strong>g. No effects on feed consumption were seen dur<strong>in</strong>g gestation <strong>in</strong> dams of either<br />

generation.<br />

No effects were seen on fertility or reproductive performance. Gestation duration was <strong>in</strong>creased<br />

<strong>in</strong> some F 0<br />

animals at 300 and 600 ppm due to dystocia, however no significant effect was seen on the<br />

mean duration of gestation for these groups (Table 31).<br />

There was a possible treatment-related decrease <strong>in</strong> the live birth <strong>in</strong>dex at 600 ppm for the<br />

F 1<br />

and F 2<br />

generations when compared with the concurrent controls and also with the historical<br />

controls (97–100%; data from 10 two-generation studies). The viability <strong>in</strong>dex was statistically<br />

non-significantly but markedly lower <strong>in</strong> the F 1<br />

animals at 600 ppm (97 and 83 for the control<br />

group and the group at the highest dose, respectively). However, the low viability <strong>in</strong>dex at 600 ppm was<br />

due to the cannibalization of pups. The viability <strong>in</strong>dex for the control group and the group at<br />

the highest dose was 99 and 91, respectively, when the <strong>in</strong>dex was calculated without <strong>in</strong>clud<strong>in</strong>g<br />

the cannibalized pups as part of the litter on lactation day 0. The viability <strong>in</strong>dex of 91 was<br />

not considered a compound-related reduction <strong>in</strong> pup viability as the viability <strong>in</strong>dex for the<br />

F 2<br />

generation control group was 94 and the historical-control range for the viability <strong>in</strong>dex<br />

was 91–100. There were a markedly higher number of cannibalized pups at 600 ppm when<br />

compared with the control group; however, when the litter was used as the experimental unit,<br />

no statistically significant difference was found for the number of dams with cannibalized<br />

pups.<br />

The pup weights were decreased <strong>in</strong> the F 1<br />

and F 2<br />

groups at the <strong>in</strong>termediate and highest doses<br />

on days 14–21, and days 7–21, respectively.<br />

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

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