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

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177<br />

In a comparative study, the absorption, distribution, excretion, and metabolism of s<strong>in</strong>gle oral<br />

doses of lambda-cyhalothr<strong>in</strong> (purity, 99.0%) and cyhalothr<strong>in</strong> (a 50 : 50 mixture of lambda-cyhalothr<strong>in</strong><br />

and the opposite enantiomer pair A (see Figure 1); purity, 97.4%) was <strong>in</strong>vestigated <strong>in</strong> groups of four<br />

male rats (Alpk/AP). One group was given [ 14 C]cyclopropyl-labelled lambda-cyhalothr<strong>in</strong> (1 mg/kg<br />

bw), a second group was given [ 14 C]cyclopropyl-labelled lambda-cyhalothr<strong>in</strong> (1 mg/kg bw) plus the<br />

unlabelled enantiomeric pair A (1 mg/kg bw), and a third group was given [ 14 C]cyclopropyl-labelled<br />

cyhalothr<strong>in</strong> (1 mg/kg bw). The ur<strong>in</strong>ary and faecal excretion of radioactivity was monitored for 3 days<br />

and the residual radioactivity was then determ<strong>in</strong>ed <strong>in</strong> selected tissues. The metabolite profile of the<br />

excreta was determ<strong>in</strong>ed by TLC. Statements of adherence to QA and GLP were <strong>in</strong>cluded.<br />

The results of this study <strong>in</strong>dicated that coadm<strong>in</strong>istration of enantiomer pair A with lambdacyhalothr<strong>in</strong><br />

had little or no effect upon the absorption, distribution, or tissue retention of radioactivity,<br />

and there was no effect upon the metabolite profile of lambda-cyhalothr<strong>in</strong>. Similarly, the absorption,<br />

distribution, excretion, and metabolism of cyhalothr<strong>in</strong> was <strong>in</strong>dist<strong>in</strong>guishable from that of lambdacyhalothr<strong>in</strong><br />

(Prout & Howard, 1985).<br />

Dogs<br />

Groups of three male and three female beagle dogs received gelat<strong>in</strong> capsules conta<strong>in</strong><strong>in</strong>g either<br />

[ 14 C]cyclopropyl-labelled cyhalothr<strong>in</strong> or [ 14 C]benzyl-labelled cyhalothr<strong>in</strong> (purity, > 97%) as a s<strong>in</strong>gle<br />

oral dose at 1 and 10 mg/kg bw dissolved <strong>in</strong> corn oil. The same dogs also received [ 14 C]benzyl- or<br />

[ 14 C]cyclopropyl-labelled material as a s<strong>in</strong>gle <strong>in</strong>travenous <strong>in</strong>jection at 0.1 mg/kg bw (<strong>in</strong> ethanol : 0.9%<br />

sal<strong>in</strong>e <strong>in</strong> a 3.2 : 1.2 ratio). There was an <strong>in</strong>terval of at least 3 weeks between each dose. Blood samples<br />

and excreta were collected over 7 days after dos<strong>in</strong>g and were analysed for radiolabel by liquid sc<strong>in</strong>tillation<br />

count<strong>in</strong>g (LSC). Metabolites were measured by TLC, and the identities of selected metabolites<br />

were confirmed by mass spectrometry. Statements of adherence to QA and GLP were <strong>in</strong>cluded.<br />

Overall recovery ranged from 82% to 93%. After a s<strong>in</strong>gle oral adm<strong>in</strong>istration at a dose of 1 or<br />

10 mg/kg bw, approximately 30% and 50% of the [ 14 C]benzyl-label was excreted <strong>in</strong> the ur<strong>in</strong>e and<br />

faeces respectively. In dogs that were dosed <strong>in</strong>travenously, 37% and 42% of [ 14 C]benzyl-label was<br />

excreted <strong>in</strong> the ur<strong>in</strong>e and faeces respectively. Excretion of radioactivity after both oral and <strong>in</strong>travenous<br />

dos<strong>in</strong>g was <strong>in</strong>itially rapid, with most of the adm<strong>in</strong>istered radioactivity be<strong>in</strong>g excreted <strong>in</strong> the first<br />

48 h after dos<strong>in</strong>g. When [ 14 C]cyclopropyl-cyhalothr<strong>in</strong> was given orally, the proportion of residue <strong>in</strong><br />

the ur<strong>in</strong>e was slightly lower (19%) and the amount <strong>in</strong> the faeces was higher (68%). The proportions<br />

of residue <strong>in</strong> the ur<strong>in</strong>e and <strong>in</strong> the faeces were approximately equal when the two radiolabelled forms<br />

of cyhalothr<strong>in</strong> were given <strong>in</strong>travenously. A large proportion (46–87%) of the faecal residue was <strong>in</strong><br />

the form of unchanged cyhalothr<strong>in</strong> after oral dos<strong>in</strong>g, but only small amounts of parent substance<br />

(1.4–1.5% of faecal radiolabel) were found <strong>in</strong> faeces after <strong>in</strong>travenous <strong>in</strong>jection, suggest<strong>in</strong>g that the<br />

oral dose of cyhalothr<strong>in</strong> was only partially absorbed from the gut lumen, leav<strong>in</strong>g unabsorbed cyhalothr<strong>in</strong><br />

<strong>in</strong> the faeces. No marked sex differences were observed (Harrison, 1984c).<br />

1.2 Biotransformation<br />

(a)<br />

In vivo<br />

Rats<br />

Groups of six male and six female Alderley Park Wistar (Alpk/Ap) (SPF) rats were given [ 14 C]<br />

cyhalothr<strong>in</strong> (purity, > 99%) as a s<strong>in</strong>gle dose at 1 or 25 mg/kg bw <strong>in</strong> corn oil by gavage. Cyhalothr<strong>in</strong><br />

was labelled either at the 3-phenoxybenzyl side-cha<strong>in</strong> (i.e. the carbon to which the cyanide moiety is<br />

attached: 14 CHCN) or at the 1 position of the cyclopropyl moiety (for structure see Figure 1). Ur<strong>in</strong>e<br />

and faeces were collected for up to 7 days after dos<strong>in</strong>g and analysed for metabolites by TLC. Bile<br />

samples were also collected at various times up to 48 h and analysed for metabolites.<br />

LAMBDA-CYHALOTHRIN 173–200 JMPR <strong>2007</strong>

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