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

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350<br />

Explanation<br />

Procymidone is the International Organization for Standardization (ISO) approved name for<br />

N-(3,5-dichlorophenyl)-1,2-dimethylcyclopropane-1,2-dicarboximide (International Union of Pure<br />

and Applied Chemistry, IUPAC), Chemical Abstracts Service, CAS No. 32809-16-8. It is a dicarboximide<br />

fungicide that is used on a range of vegetables, fruits, soya bean, sunflowers, tobacco and<br />

oil seed rape, as well as on ornamental plants and flower bulbs. The mechanism of pesticidal action<br />

<strong>in</strong>volves the <strong>in</strong>hibition of triglyceride synthesis <strong>in</strong> fungi.<br />

Procymidone was previously evaluated by JMPR <strong>in</strong> 1981, 1982 and 1989 (Annex 5, references<br />

37, 39, 58). No acceptable daily <strong>in</strong>takes (ADIs) were established when procymidone was evaluated<br />

by the JMPR <strong>in</strong> 1981 and 1982. In 1989, an ADI of 0–0.1 mg/kg bw was established based on the<br />

NOAEL of 12.5 mg/kg bw per day identified <strong>in</strong> studies of reproductive toxicity <strong>in</strong> rats. Procymidone<br />

was re-evaluated by the present Meet<strong>in</strong>g as part of the periodic review programme of the Codex Committee<br />

on Pesticude Residues (CCPR). A range of new studies was submitted to the present Meet<strong>in</strong>g;<br />

these studies addressed k<strong>in</strong>etics, developmental toxicity and hormonal effects <strong>in</strong> different species.<br />

Many of the conventional studies of toxicity with procymidone were relatively old, were performed<br />

before the widespread use of good laboratory practice (GLP) and some conta<strong>in</strong>ed relatively<br />

limited <strong>in</strong>formation. Overall, the Meet<strong>in</strong>g considered that the database was adequate for the risk<br />

assessment.<br />

Procymidone used <strong>in</strong> the ma<strong>in</strong> studies of toxicity was considered to be representative of current<br />

production material, which is typically of > 99% purity. The Food and Agriculture Organization (FAO)<br />

specification for procymidone specifies a m<strong>in</strong>imum content of 98.5% w/w 1 . Procymidone has also<br />

been known under the development code S7131 or ‘Sumilex’; ‘Sumisclex’ is a 50% formulation.<br />

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

1. Biochemical aspects<br />

1.1 Absorption, distribution and excretion<br />

(a)<br />

Oral route<br />

Mice<br />

Groups of five male ICR mice were given [phenyl- 14 C]procymidone (radiochemical purity,<br />

> 99%; specific activity, 22.8 mCi/mmol (843.6 MBq/mmol) as a s<strong>in</strong>gle oral dose at 100 mg/kg bw<br />

<strong>in</strong> corn oil. Ur<strong>in</strong>e and faeces were collected for 7 days from one group of mice. Other groups of mice<br />

were killed 2, 4, 6, 8, 12, 24 and 72 h after dos<strong>in</strong>g and a range of tissues removed for radiochemical<br />

analysis. Rapid elim<strong>in</strong>ation was observed, with 92% of the adm<strong>in</strong>istered dose excreted <strong>in</strong> the first<br />

24 h, ma<strong>in</strong>ly <strong>in</strong> the ur<strong>in</strong>e (73.5%). Over a 7-day period, faeces and ur<strong>in</strong>e accounted for 22% and 82%,<br />

respectively, of the adm<strong>in</strong>istered dose. There was no evidence of tissue accumulation <strong>in</strong> this study; the<br />

highest concentration of radioactivity (429 μg equivalent/g) was found <strong>in</strong> fat 2 h after dos<strong>in</strong>g, but the<br />

concentration had decl<strong>in</strong>ed to low concentrations (2 μg equivalent/g) by the end of the experimental<br />

period. Radioactivity <strong>in</strong> adrenals, blood, bra<strong>in</strong>, kidneys, liver, prostate, epididymis and testes reached<br />

a maximum 2–8 h after dos<strong>in</strong>g (133, 17, 27, 58, 67, 88, 48 and 17 μg equivalent/g respectively) and<br />

subsequently decreased with a half-life of 4–14 h. This study did not claim to be compliant with GLP<br />

(Kimura et al., 1988).<br />

1<br />

http://www.fao.org/ag/AGP/AGPP/Pesticid/Specs/docs/Pdf/new/procymid.pdf<br />

PROCYMIDONE 349–401 JMPR <strong>2007</strong>

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