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

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500<br />

No cl<strong>in</strong>ical signs or <strong>in</strong>creased mortalities were detected at any dose; the appearance and behaviour<br />

of the dams was unaffected by treatment up to and <strong>in</strong>clud<strong>in</strong>g 50 mg/kg bw per day. Feed consumption<br />

of the dams was dist<strong>in</strong>ctly decreased, especially dur<strong>in</strong>g the first few days after <strong>in</strong>itiation of treatment at<br />

50 mg/kg bw, lead<strong>in</strong>g to body-weight losses dur<strong>in</strong>g the first few days after <strong>in</strong>itiation of treatment and<br />

to a reduction of total body-weight ga<strong>in</strong>, so that cumulative and corrected body-weight ga<strong>in</strong>s dur<strong>in</strong>g<br />

gestation were significantly decreased at 50 mg/kg bw per day (Table 32). Water consumption and<br />

the amount of excreted faeces were decreased dur<strong>in</strong>g the first few days after <strong>in</strong>itiation of treatment at<br />

50 mg/kg bw per day, while <strong>in</strong>creased water consumption and ur<strong>in</strong>e excretion were observed towards<br />

and dur<strong>in</strong>g the second half of gestation at the highest dose (50 mg/kg bw per day). At gross necropsy no<br />

test compound-related gross pathological f<strong>in</strong>d<strong>in</strong>gs were evident <strong>in</strong> any of the experimental groups.<br />

At caesarean section, an <strong>in</strong>creased <strong>in</strong>cidence of late resorptions and one total resorption<br />

were observed at 50 mg/kg bw per day, result<strong>in</strong>g <strong>in</strong> a slightly decreased number of live fetuses<br />

and mean litter size at the highest dose. Also, mean fetal weight was decreased at the highest<br />

dose. (Table 32). There was no effect on placental weight. An <strong>in</strong>creased <strong>in</strong>cidence of placental<br />

border necrosis was apparent <strong>in</strong> all dose groups; however, values were with<strong>in</strong> the range for<br />

historical controls for the laboratory (0–17.65% of placentas with f<strong>in</strong>d<strong>in</strong>gs; 0–42.86% of litters<br />

with f<strong>in</strong>d<strong>in</strong>gs).<br />

The external exam<strong>in</strong>ation of the fetuses revealed forelimb deviations <strong>in</strong> two fetuses from a<br />

s<strong>in</strong>gle litter at 50 mg/kg bw per day. These limb f<strong>in</strong>d<strong>in</strong>gs were considered to be treatment-related<br />

s<strong>in</strong>ce they were confirmed by skeletal evaluation (bone dysplasia) and similar f<strong>in</strong>d<strong>in</strong>gs were observed<br />

at 50 mg/kg bw per day <strong>in</strong> other fetuses <strong>in</strong> several litters which were <strong>in</strong>completely evaluated.<br />

Visceral exam<strong>in</strong>ation of fetuses revealed an apparent <strong>in</strong>crease <strong>in</strong> the <strong>in</strong>cidence and severity of<br />

renal pelvis dilatation <strong>in</strong> groups at 10 mg/kg bw per day and greater. S<strong>in</strong>ce the comb<strong>in</strong>ed <strong>in</strong>cidence<br />

of slight renal pelvis dilatation and renal pelvis dilatation did not display dose-dependency and <strong>in</strong><br />

the group at the highest dose was only marg<strong>in</strong>ally greater than (fetal <strong>in</strong>cidence) or less than (litter<br />

<strong>in</strong>cidence) the control value for a study of a developmental toxicity with comparable study design (fetal<br />

<strong>in</strong>cidence, 23.2%; litter <strong>in</strong>cidence, 69.2%), the f<strong>in</strong>d<strong>in</strong>g was not considered to be related to treatment.<br />

Table 32. Relevant f<strong>in</strong>d<strong>in</strong>gs <strong>in</strong> a study of developmental toxicity <strong>in</strong> rats given thiacloprid by<br />

gavage<br />

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

Dose (mg/kg bw per day)<br />

0 2 10 50<br />

Body weight (g):<br />

Day 6 228.4 231.6 228.4 230.5<br />

Day 9 236.0 238.8 234.2 212.8**<br />

Day 14 255.6 256.9 252.8 232.2**<br />

Day 20 314.7 314.1 308.8 279.6**<br />

Bosy-weight ga<strong>in</strong> (g), days 6–19 77.6 74.0 71.7 42.0**<br />

Feed consumption (g/animal per day):<br />

Days 6–11 17.7 17.6 16.9 6.4**<br />

Days 11–16 19.1 19.1 19.0 16.4**<br />

Days 16–20 21.6 21.4 20.9 19.6**<br />

No. of dams with implantations (a) 28 31 32 30<br />

No. of dams with viable fetuses (b) 28 31 32 29<br />

No. of implantations per dam (b) 12.4 11.5 11.4 11.8<br />

% Implantations per dam (b) 91.1 92.5 95.7 79.3**<br />

% Postimplantation loss per dam (a) 0.9 0.9 0.5 2.8*<br />

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

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