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

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495<br />

“Ground glass” hepatocytes 07 0/5 0/6 7/7 07 0/5 0/6 7/7<br />

Hepatocyte cytoplasmic <strong>in</strong>clusions 0/7 0/5 0/6 1/7 0/7 0/7 0/7 0/7<br />

Increased mitotic figures (liver) 0/7 0/5 0/6 4/7 0/7 0/5 0/6 4/7<br />

Thyroid follicular hypertrophy 0/7 0/5 0/6 2/7 0/7 0/5 0/6 1/7<br />

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

* p < 0.05; ** p < 0.01.<br />

Table 29. F<strong>in</strong>d<strong>in</strong>gs related to reproductive toxicity <strong>in</strong> a range-f<strong>in</strong>d<strong>in</strong>g study <strong>in</strong> female rats fed<br />

diets conta<strong>in</strong><strong>in</strong>g thiacloprid<br />

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

Dietary concentration (ppm)<br />

0 100 400 1600<br />

Mat<strong>in</strong>g <strong>in</strong>dex 100 100 100 100<br />

Fertility <strong>in</strong>dex 100 71.4 85.7 100<br />

Gestation <strong>in</strong>dex 100 100 100 100<br />

No. of litters 7 5 6 7<br />

Total No. of pups born 107 73 81 97<br />

Litter size, mean 15.3 14.6 13.5 13.9<br />

No. of stillborn pups (%) 6 (5.6) 1 (1.4) 1 (1.2) 3 (3.1)<br />

Live birth <strong>in</strong>dex (%) 95.0 98.8 99.0 96.8<br />

Total No. of dead pups (%) 9 (8.4) 3 (4.1) 1 (1.2) 21* (21.6)<br />

Pup deaths (day 0–4) 3 2 0 16<br />

Viability <strong>in</strong>dex (%) 96.4 97.4 100.0 83.9<br />

Pup deaths (days 5–21) 0 0 0 2<br />

Wean<strong>in</strong>g <strong>in</strong>dex, mean 100 100 100 96.4<br />

Mean weight of viable pups (g), birth 6.0 6.3 6.6 6.0<br />

Day 4 9.8 10.4 10.4 8.1*<br />

Day 11 26.0 27.5 26.6 19.3**<br />

Day 21 56.1 57.1 53.6 41.0**<br />

Day 28 93.3 92.7 90.2 66.8**<br />

Day 35 141.8 140.2 133.7 104.0**<br />

Body-weight ga<strong>in</strong> (g) 135.8 133.8 127.1 98.1**<br />

From Porter et al., (1995)<br />

* p < 0.05; ** p < 0.01.<br />

Histopathological effects <strong>in</strong> the liver (hepatocyte hypertrophy, “ground glass” appearance of<br />

hepatocyte cytoplasm, hepatocyte glycogenic vacuolar change) were seen at 1600 ppm and <strong>in</strong> one<br />

F 0<br />

female at 400 ppm. Thyroid follicular cell hypertrophy was also noted at 1600 ppm and <strong>in</strong> one F 0<br />

male at 400 ppm. Similar f<strong>in</strong>d<strong>in</strong>gs were noted <strong>in</strong> F 0<br />

and F 1<br />

animals.<br />

No treatment-related effects on reproductive performance were seen. The number of pup deaths<br />

(days 0–4) was significantly <strong>in</strong>creased at 1600 ppm, result<strong>in</strong>g <strong>in</strong> a slightly lower viability <strong>in</strong>dex for<br />

this dose group. Mean pup weight at 1600 ppm was significantly lower from day 4, pup weights at<br />

birth were comparable <strong>in</strong> all dose groups (Table 29).<br />

The NOAEL for parental toxicity was 400 ppm, equivalent to about 27 mg/kg bw per day, on<br />

the basis of microscopic hepatic and thyroid changes <strong>in</strong> F 0<br />

and F 1<br />

animals at 1600 ppm. The NOAEL<br />

for reproductive toxicity was 400 ppm, equivalent to about 27 mg/kg bw per day, on the basis of<br />

decreased body-weight ga<strong>in</strong> and survival <strong>in</strong> pups at 1600 ppm (Porter et al., 1995).<br />

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

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