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

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474<br />

Thyroid weight (mg):<br />

Week 12 6 8 9 9 10* 7 8 6 7 8<br />

Week 17r 8 — — — 10 8 — — — 8<br />

Thyroid weight, relative<br />

(mg/100 g bw)<br />

Week 12 1 2 2* 2 3** 3 3 2 3 4<br />

Week 17r 2 — — — 2 3 — — — 4<br />

Liver cell hypertrophy:<br />

Week 12 0 0 0 9 10 0 0 0 2 10<br />

Week 17r 0 — — — 3 0 — — — 0<br />

Liver cell cytoplasmic<br />

change, week 12<br />

0 0 0 9 10 0 0 0 2 10<br />

From Kroetl<strong>in</strong>ger & Geiss (1997)<br />

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

ALD, aldr<strong>in</strong> epoxidase; ECOD, 7-ethoxycoumar<strong>in</strong> deethylase; EH, epoxide hydrolase; EROD, 7-ethoxyresoruf<strong>in</strong><br />

d eethylase; GST, glutathione-S-transferase; N-DEM, N-demethylase; O-DEM, O-demethylase; r, recovery group; T3,<br />

triiodothyron<strong>in</strong>e TBI, thyroid b<strong>in</strong>d<strong>in</strong>g <strong>in</strong>dex; UDP-GT, urid<strong>in</strong>e diphosphate glucuronosyl transferase.<br />

The NOAEL was established at 400 ppm (equal to 28.6 and 35.6 mg/kg bw <strong>in</strong> males and<br />

females, respectively) on the basis of reduced body weight, cl<strong>in</strong>ical chemistry changes (<strong>in</strong>creased<br />

cholesterol and prote<strong>in</strong> concentrations <strong>in</strong> plasma) and thyroid effects (<strong>in</strong>creased weight) at 1600 ppm,<br />

the highest dose tested (Kroetl<strong>in</strong>ger & Geiss, 1997).<br />

In a pilot study on <strong>in</strong>halation toxicity, groups of 10 male and 10 female Wistar (Hsd W<strong>in</strong>:WU)<br />

rats were exposed (nose only) to aerosolized thiacloprid (purity, 97.2%) at analytical concentrations<br />

of 0, 1.97, 19 or 205 mg/m³ air under dynamic conditions for 6 h per day on five consecutive days.<br />

The exposure period was followed by a recovery period of 3 days (<strong>in</strong>terim sacrifice, 50% of the<br />

animals) or 2 weeks (term<strong>in</strong>al sacrifice). The MMADs (GSDs) of the particles were 3.3 μm (2.3),<br />

2.9 μm (2.1) or 3.3 μm (1.8) at 1.97, 19 or 205 mg/m³ air, respectively. Between 44–55% of aerosol<br />

mass was less than 3 μm.<br />

Cl<strong>in</strong>ical observations, body weight and feed <strong>in</strong>take were recorded at suitable time-po<strong>in</strong>ts.<br />

Reflexes and the rectal temperatures were evaluated dur<strong>in</strong>g the course of the study. Fifty per cent of<br />

the animals were sacrificed on the third post-exposure day. The rema<strong>in</strong><strong>in</strong>g animals were sacrificed<br />

at the end of the 2-week observation period after exposure. All the animals received a macroscopic<br />

exam<strong>in</strong>ation at necropsy. The follow<strong>in</strong>g organs were removed and weighed: bra<strong>in</strong>, kidneys, liver,<br />

thymus, thyroid, heart, lung, and spleen. Liver samples were taken for enzyme determ<strong>in</strong>ations.<br />

At each sacrifice, blood was sampled for basic haematological and biochemical determ<strong>in</strong>ations.<br />

Histopathology was not performed <strong>in</strong> this study.<br />

No deaths occurred dur<strong>in</strong>g the study. Cl<strong>in</strong>ical signs were observed at the highest dose and<br />

<strong>in</strong>cluded ungroomed pelt, piloerection, reduced motility, tremor, bradypnea, laboured breath<strong>in</strong>g<br />

pattern, flaccid appearance, mydriasis and emaciation. Based on the respiratory effects, the report<br />

concluded that the test aerosol had a m<strong>in</strong>or potential to act as an upper respiratory tract irritant. All<br />

animals showed normal reflexes. An <strong>in</strong>crease <strong>in</strong> grip strength was observed <strong>in</strong> both males and females<br />

at 19 mg/m³ and greater on day 4, but this f<strong>in</strong>d<strong>in</strong>g was not confirmed by grip measurements made<br />

3 days later. Rectal temperatures were significantly reduced at 205 mg/m³.<br />

Significant reductions <strong>in</strong> body weight were observed <strong>in</strong> both sexes at 205 mg/m³ on day 4 (last<br />

exposure day) and day 7 (third day after exposure). Thereafter, the body weights of the control<br />

and treatment groups were similar. Feed <strong>in</strong>take was reduced <strong>in</strong> both sexes at 205 mg/m³ on day 4<br />

(last exposure day).<br />

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

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