28.01.2014 Views

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

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

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

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

279<br />

and the E : Z isomer ratio was approximately 50 : 50 after dilution with non-radiolabelled dimethomorph.<br />

Non-labelled dimethomorph was 98.8% chemically pure. Another four males and four females<br />

served as a control group and were treated with vehicle only. Blood samples at different time <strong>in</strong>tervals<br />

from 0.25 h to 144 h after dos<strong>in</strong>g were collected and analysed for radioactivity. The study complied<br />

with GLP.<br />

In the groups receiv<strong>in</strong>g the lower dose, values for both sexes were comparable; t max<br />

was reached<br />

at < 3h, term<strong>in</strong>al t 1/2<br />

was 59–68 h and AUC 0–∞<br />

at 10–15 μg × h/g (Table 8). In the groups receiv<strong>in</strong>g<br />

the higher dose, <strong>in</strong>creased c max<br />

and AUC 0–∞<br />

values were found <strong>in</strong> females and this correlated with a<br />

prolonged half-life.<br />

Total radioactive <strong>residues</strong> (TRR) <strong>in</strong> plasma and erythrocytes 168 h after treatment were below<br />

the limit of detection (LOD) <strong>in</strong> both rats of groups at the lower dose and <strong>in</strong> the plasma of rats <strong>in</strong><br />

groups receiv<strong>in</strong>g the higher dose (LOD at lower dose, 0.020–0.022 ppm; LOD at higher dose, 0.201–<br />

0.223 ppm). In the groups at the higher dose, TRR <strong>in</strong> erythrocytes were 0.75 ppm and 0.939 ppm <strong>in</strong><br />

male and female rats, respectively (Afzal & Wu, 1995a).<br />

To <strong>in</strong>vestigate the tissue distribution of dimethomorph, groups of n<strong>in</strong>e male and n<strong>in</strong>e female<br />

Sprague-Dawley rats (Crl:CD BR) were given [ 14 C]dimethomorph as s<strong>in</strong>gle oral doses at 10 mg/kg<br />

bw or 500 mg/kg bw by gavage. The test compound was uniformly chlorophenyl-r<strong>in</strong>g labelled [ 14 C]<br />

dimethomorph (radiochemical purity, 96%) and had a specific activity of 0.363 GBq/mmol and the<br />

E : Z isomer ratio was approximately 50 : 50 after dilution with non-radiolabelled dimethomorph<br />

(purity, 98.8%). Another three males and three females served as a control group and were treated<br />

with vehicle only. At t max<br />

, 24 h and 168 h after dos<strong>in</strong>g, three males and three females from each group<br />

were killed and tissues collected for TRR analysis. T max<br />

values were derived from a previous study<br />

(Afzal & Wu, 1995a) consider<strong>in</strong>g the lower bounds of t max<br />

ranges <strong>in</strong> actual dos<strong>in</strong>g groups; for females<br />

at the lower dose, t max<br />

was set at 1.5 h; for males at the lower dose at 0.5 h; and for males and females<br />

at the higher dose at 8 h. The study complied with GLP.<br />

No signs of toxicity were recorded <strong>in</strong> any group. Highest TRR levels <strong>in</strong> all dosed groups at t max<br />

and 24 h after dos<strong>in</strong>g were found <strong>in</strong> the GIT and contents, followed by the carcass and liver (Table<br />

9 and Table 10). In liver, maximal TRR values were 1.05% of the adm<strong>in</strong>istered dose. In all other<br />

organs, low levels of less than 0.1% were observed even at t max<br />

and they were significantly depleted<br />

with<strong>in</strong> 24 h <strong>in</strong> the groups at the lower dose. In the groups at the higher dose, a certa<strong>in</strong> delay <strong>in</strong> depletion<br />

from organs with<strong>in</strong> 24 h was observed when compared with the groups at the lower dose. Levels<br />

at t max<br />

and 24 h were all less than 0.1% of the adm<strong>in</strong>istered dose. At 168 h, liver conta<strong>in</strong>ed the highest<br />

levels of <strong>residues</strong>, with a range of 0.04–0.1% TRR of the adm<strong>in</strong>istered dose; <strong>in</strong> all other tissues, TRR<br />

was virtually negligible (Afzal & Wu, 1995b).<br />

To <strong>in</strong>vestigate the dermal absorption of dimethomorph, groups of four male Sprague-Dawley<br />

CD rats were exposed dermally to [ 14 C]dimethomorph at a dose of 7.73 or 79.62 mg/kg bw for 8 h.<br />

The test compound was uniformly chlorophenyl-r<strong>in</strong>g labelled [ 14 C]dimethomorph (radiochemical<br />

purity, 96%; purity, 98.8%) and had a specific activity of 0.363 GBq/mmol and the E : Z isomer ratio<br />

was approximately 45 : 55. The chemical purity of dimethomorph before labell<strong>in</strong>g was 97.6%. The<br />

study complied with GLP.<br />

In the group at the lower dose, 4.75% of the applied dose was absorbed, based on the sum of<br />

radioactivity recovered 168 h after topical application <strong>in</strong> ur<strong>in</strong>e, faeces, cage wash, carcass, blood<br />

and untreated sk<strong>in</strong>. In the group at the higher dose, 1.2% of the applied dose was absorbed (Bounds,<br />

1995).<br />

1.2 Effects on enzymes and other biochemical parameters<br />

No <strong>in</strong>formation was available.<br />

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

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!