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Pesticide residues in food — 2007: Toxicological ... - ipcs inchem

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293<br />

0–9%, mean, 3.5%; only one out of 12 control groups with an <strong>in</strong>cidence of equal or higher <strong>in</strong>cidence<br />

than 6%, control groups were from studies performed <strong>in</strong> 1997–2002). Although the historical control<br />

groups were not contemporary, no altered time trend <strong>in</strong> the background <strong>in</strong>cidence of mammary<br />

adenocarc<strong>in</strong>omas between 1993 and 2003 was evident. In males at the highest dose, the <strong>in</strong>cidence<br />

of lung adenoma was higher than <strong>in</strong> controls but lower than <strong>in</strong> the group receiv<strong>in</strong>g the next lower<br />

dose and, also consider<strong>in</strong>g the lack of any other histological changes <strong>in</strong> the lungs, a relationship with<br />

treatment is questionable.<br />

The NOAEL was 100 mg/kg bw per day on the basis of reduced body-weight ga<strong>in</strong> <strong>in</strong> males<br />

and <strong>in</strong>creased <strong>in</strong>cidence of mammary adenocarc<strong>in</strong>omas <strong>in</strong> females at 1000 mg/kg bw per day<br />

(Smith, 1991).<br />

Rats<br />

In a 24-month study of toxicity, groups of 20 male and 20 female Sprague-Dawley rats were<br />

fed diets conta<strong>in</strong><strong>in</strong>g dimethomorph (purity, 96.6%) at a concentration of 0, 200, 750 or 2000 ppm<br />

(equal to 0, 9.4, 36.3, 99.9 mg/kg bw per day <strong>in</strong> males and 0, 11.9, 57.7, 157.2 mg/kg bw <strong>in</strong> females).<br />

The rats were daily observed for mortalities, cl<strong>in</strong>ical signs and palpable masses; body weights, feed<br />

and water consumption were recorded weekly and ophthalmoscopy was performed pre-trial and at<br />

weeks 51 and 102. Data on haematology, cl<strong>in</strong>ical chemistry, and ur<strong>in</strong>e analysis were collected from<br />

Table 23. Body-weight development <strong>in</strong> mice fed diets conta<strong>in</strong><strong>in</strong>g dimethomorph<br />

Dietary concentration (ppm) Body weight (g) Body-weight ga<strong>in</strong> Term<strong>in</strong>al body weight<br />

Week 0 Week 17 Week 52 Week 104 (g) % of control % of control<br />

Males<br />

0 30.7 38.8 43.8 43.0 12.3 — —<br />

10 30.6 37.3* 41.4* 43.4 12.8 104 101<br />

100 30.4 37.7 42.4 42.0 11.6 94 98<br />

1000 30.1 36.7** 40.5** 40.3* 10.2 83 94<br />

Females<br />

0 23.2 30.9 34.9 38.8 15.6 — —<br />

10 23.7 31.9 36.0 38.1 14.4 92 98<br />

100 23.3 31.4 34.7 37.3 14.0 89 96<br />

1000 24.2 31.7 34.6 36.4 12.2 78 94<br />

From Smith (1991)<br />

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

Table 24. Gross pathology, non-neoplastic and neoplastic histological changes <strong>in</strong> mice fed diets<br />

conta<strong>in</strong><strong>in</strong>g dimethomorph<br />

Gross histopathological change<br />

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

Males (n = 50) Females (n = 50)<br />

0 10 100 1000 0 10 100 1000<br />

Spleen, enlarged 4 4 5 7 14 12 14 20<br />

Lung, adenomas 13 14 23 17 9 5 12 5<br />

Mammary, adenocarc<strong>in</strong>oma — — — — 1 0 1 3<br />

From Smith (1991)<br />

DIMETHOMORPH 273–315 JMPR <strong>2007</strong>

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