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

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206<br />

differences <strong>in</strong> the percentage actually absorbed, permitt<strong>in</strong>g the estimation of an appropriate species<br />

ratio. The flux (i.e. rate of penetration under steady-state conditions) at the lowest, <strong>in</strong>termediate and<br />

highest concentrations, respectively, was 0.020, 0.455 and 26.0 µg/cm 2 h −1 for the rat sk<strong>in</strong> and 0.002,<br />

0.037 and 0.82 µg/cm 2 h −1 for the human sk<strong>in</strong>. The flux ratios rat : human were therefore about 1 :<br />

10, 1 : 12 and 1 : 32 at the lowest, <strong>in</strong>termediate and highest concentrations, respectively (Hassler,<br />

2003c). Comparison of the penetration rates at the different doses (concentration ratio, 1 : 25 : 5000),<br />

revealed an <strong>in</strong>crease <strong>in</strong> the penetration rates of 1 : 23 : 1300 for rat epidermal membranes, while<br />

the penetration rates for human epidermal membranes revealed a ratio of only 1 : 24 : 500 (Hassler,<br />

2003b). These data acquired <strong>in</strong> vitro are used to arrive at an estimate of dermal absorption partly<br />

because the <strong>in</strong>ter-rat variation observed <strong>in</strong> the study <strong>in</strong> vivo was very large (attributed to the irritancy<br />

of the formulation vehicle and for this reason was not considered reliable).<br />

Metabolism<br />

Metabolites were isolated from the ur<strong>in</strong>e and faeces of male and female rats given [ 14 C-phenyl]<br />

difenoconazole or [ 14 C-triazole]difenoconazole as s<strong>in</strong>gle oral dose at 0.5 or 300 mg/kg bw (Figure 1a<br />

and 1b), or 0.5 mg/kg bw after pre-treatment with 14 daily oral doses of unlabelled difenoconazole<br />

at 0.5 mg/kg bw (Cra<strong>in</strong>e, 1987a, 1987b).<br />

Balance data for the phenyl and triazole r<strong>in</strong>g labels (Cra<strong>in</strong>e 1987a, 1987b) summarized <strong>in</strong> a report<br />

by Capps et al. (1988) showed that > 97% of the radiolabel <strong>in</strong> all cases was excreted with > 78%<br />

<strong>in</strong> all cases elim<strong>in</strong>ated <strong>in</strong> the faeces. Three ma<strong>in</strong> metabolites, A, B and C, were isolated from faeces<br />

and together accounted for an average of 68% of the adm<strong>in</strong>istered dose. Metabolite B (hydroxy-CGA<br />

169374) was hydroxylated <strong>in</strong> the outer phenyl r<strong>in</strong>g and spectral analysis showed that that it comprised<br />

two isomers, one with a rearrangement of the chlor<strong>in</strong>e on the outer phenyl r<strong>in</strong>g, attributed to<br />

a mechanism analogous to an NIH shift.1 Metabolite C (CGA 205375) was the hydroxyl product of<br />

cleavage of the dioxolane r<strong>in</strong>g from the difenoconazole molecule and was present only <strong>in</strong> the faeces<br />

of rats given the higher dose. Metabolite A (hydroxy-CGA 205375) was the outer phenyl-r<strong>in</strong>g hydroxylated<br />

product of metabolite C and comprised two diastereoisomers, as described for metabolite<br />

B. The profile of ur<strong>in</strong>ary metabolites was more complex and showed more variability between the two<br />

radiolabelled forms. Free 1,2,4-triazole was identified <strong>in</strong> male ur<strong>in</strong>e, account<strong>in</strong>g for less than 10% of<br />

the adm<strong>in</strong>istered dose and represented cleavage of the alkyl bridge between the r<strong>in</strong>g systems. Other<br />

ur<strong>in</strong>ary metabolites <strong>in</strong>cluded metabolite C, its sulfate conjugate, r<strong>in</strong>g-hydroxylated metabolite C and<br />

its sulfate conjugate, as well as an hydroxyacetic acid metabolite of the chlorophenoxy-chlorophenyl<br />

moiety, all of which were present <strong>in</strong> m<strong>in</strong>or quantities, each represent<strong>in</strong>g less than 3% of the adm<strong>in</strong>istered<br />

dose. One metabolite CGA 189138 (chlorophenoxy-chlorobenzoic acid) was also isolated<br />

from the liver. The difenoconazole molecule was therefore extensively metabolized, although with<br />

limited cleavage of the triazole and dioxolane r<strong>in</strong>gs. The extensive biliary elim<strong>in</strong>ation observed was<br />

consistent with the major metabolites be<strong>in</strong>g of relatively high molecular mass.<br />

The major steps of the metabolism of difenoconazole <strong>in</strong> the rat were deduced to <strong>in</strong>volve hydrolysis<br />

of the ketal <strong>in</strong> difenoconazole, result<strong>in</strong>g <strong>in</strong> CGA 205375 (1-[2-chloro-4-(4-chloro-phenoxy)-phenyl]-2-<br />

(1,2,4-triazol)-1-yl-ethanol), with the ketone CGA 205374 (1-(2-chloro-4-(4-chloro-phenoxy)-phenyl)-<br />

2-(1,2,4-triazol)-1-yl-ethanone) as a postulated but not identified <strong>in</strong>termediate, and hydroxylation on the<br />

outer phenyl r<strong>in</strong>g of the parent (hydroxy-CGA 169374) and <strong>in</strong> CGA 205375 (hydroxy-CGA 205375).<br />

As a m<strong>in</strong>or process, cleavage of the alkyl cha<strong>in</strong> between the triazole and the <strong>in</strong>ner phenyl r<strong>in</strong>g occurs,<br />

result<strong>in</strong>g <strong>in</strong> a hydroxyacetic acid (NOA 448731) or CGA 189138 (2-chloro-4-(4-chlorophenoxy)-benzoic<br />

acid) and free triazole. Sulfate conjugates were identified for CGA 205375 and for hydroxy-CGA<br />

205375. The proposed metabolic pathway <strong>in</strong> mammals is shown <strong>in</strong> Figure 3 (Capps et al., 1990).<br />

1<br />

An NIH shift is a chemical rearrangement (first described <strong>in</strong> studies from the United States National Institutes<br />

of Health, NIH) <strong>in</strong> which a hydrogen atom on an aromatic r<strong>in</strong>g undergoes an <strong>in</strong>tramolecular migration primarily<br />

d ur<strong>in</strong>g a hydroxylation reaction.<br />

DIFENOCONAZOLE 201–272 JMPR <strong>2007</strong>

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