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

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4<br />

All pivotal studies with bifenazate were certified as comply<strong>in</strong>g with good laboratory practice<br />

(GLP).<br />

Figure 1. Chemical structure of bifenazate<br />

CH 3<br />

*<br />

O<br />

NH<br />

NH<br />

O<br />

O<br />

CH 3<br />

CH<br />

CH 3<br />

* Position of the bifenazate radiolabel used <strong>in</strong> the pharmacok<strong>in</strong>etic studies <strong>in</strong> rats<br />

Evaluation for acceptable daily <strong>in</strong>take<br />

1. Biochemical aspects: absorption, distribution, and excretion<br />

Rats<br />

The position of the radiolabel on bifenazate used <strong>in</strong> absorption, distribution, metabolism and<br />

excretion studies is shown <strong>in</strong> Figure 1.<br />

In a dose range-f<strong>in</strong>d<strong>in</strong>g study, groups of two male and two female fasted Sprague-Dawley<br />

rats were treated with [methoxyphenyl U-r<strong>in</strong>g 14 C]bifenazate (lot No. CSL-94-516-73-20; purity,<br />

> 98%) <strong>in</strong> corn oil at 10 or 1000 mg/kg bw by gavage. Rats were housed <strong>in</strong>dividually <strong>in</strong> glass<br />

metabolism cages with <strong>food</strong> and water freely available. Dose preparations were analysed for chemical<br />

concentration and radiochemical purity by high pressure liquid chromatography (HPLC). Expired air<br />

from each animal passed through two trapp<strong>in</strong>g vessels that conta<strong>in</strong>ed 40% (w/v) potassium hydroxide<br />

(KOH) and water (to trap carbon dioxide) and one trapp<strong>in</strong>g tube that conta<strong>in</strong>ed Chromosorb (to<br />

trap radiolabelled volatile organic compounds). The trapp<strong>in</strong>g vessels were placed <strong>in</strong> a dry-ice bath.<br />

Expired air, ur<strong>in</strong>e and faeces were collected at <strong>in</strong>tervals after dos<strong>in</strong>g for 168 h, with cage washes<br />

done at the same <strong>in</strong>tervals. At the end of the collection period, rats were killed and blood collected.<br />

Carcasses were weighed, homogenized and analysed. All samples were analysed for radioactivity by<br />

liquid sc<strong>in</strong>tillation count<strong>in</strong>g (LSC).<br />

The recovery of radiolabel was 93.77% and 100.85% of the adm<strong>in</strong>istered dose of 10 and<br />

1000 mg/kg bw, respectively. Radioactivity <strong>in</strong> the expired air was 0.21% and 0.6% of the 10 and<br />

1000 mg/kg bw doses, respectively. Excretion via ur<strong>in</strong>e made up 12.4% of the dose at 10 mg/kg<br />

bw and 4.79% at 1000 mg/kg bw. Ur<strong>in</strong>ary excretion was 96% complete after 72 h at 10 mg/kg<br />

bw, and 61% complete after 72 h at 1000 mg/kg bw. Faecal excretion accounted for 68.9% of the<br />

adm<strong>in</strong>istered dose at 10 mg/kg bw, and 91.6% at 1000 mg/kg bw. At 10 mg/kg bw, faecal excretion<br />

was 95% complete after 48 h, and at 1000 mg/kg, 61% complete at 72 h. Overall, more than 90%<br />

of excretion (via all routes) was complete after 72 h at 10 mg/kg bw, and after 96 h at 1000 mg/ kg<br />

bw. At 168 h after dos<strong>in</strong>g, blood accounted for 0.13% of the dose at 10 mg/kg bw and 0.14% at<br />

1000 mg/ kg bw. Concentrations <strong>in</strong> the carcass were 0.55% of the dose at 10 mg/kg bw and 0.33% of<br />

the dose at 1000 mg/kg bw (Andre & McClanahan, 1997).<br />

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

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