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

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388<br />

Table 31. Metabolite concentrations (μg equivalent/g) <strong>in</strong> plasma and tissues from female rats<br />

(n = 3) receiv<strong>in</strong>g procymidone metabolites at 62.5 mg/kg bw<br />

Metabolite<br />

Concentration of metabolite (μg equivalent/g)<br />

Plasma Liver Kidney Ovary<br />

Six h after dos<strong>in</strong>g with PCM-CH 2<br />

OH<br />

PCM-CH 2<br />

OH 2.9 33.8 20.9 16.8<br />

PCM-COOH 7.3 3.0 15.1 1.8<br />

PA-CH 2<br />

OH 12.9 6.0 6.2 3.1<br />

PA-COOH 2.3 1.4 2.8 0.5<br />

Others 3.1 1.4 2.6 0.6<br />

Four h after dos<strong>in</strong>g with PCM-CH 2<br />

OH<br />

PCM-CH 2<br />

OH 0.6 16.4 12.7 10.6<br />

PCM-COOH 2.7 5.1 10.4 2.0<br />

PA-CH 2<br />

OH 12.8 2.0 5.4 0.5<br />

PA-COOH 3.0 2.9 3.8 0.7<br />

Others 4.2 0.6 1.3 0.3<br />

From Tarui (2005a)<br />

PA, procymidone acid; PA-CH 2<br />

OH, hydroxyprocymidone acid; PA-COOH, carboxyprocymidone acid; PCM,<br />

procymidone; PCM-CH 2<br />

OH, hydroxyprocymidone; PCM-NH-COOH, carboxyprocymidone.<br />

exam<strong>in</strong>ation records were checked for 1991–2000 for adverse effects on body weight, vital capacity,<br />

hear<strong>in</strong>g acuity, chest X-ray, blood pressure, ur<strong>in</strong>e analysis, haematology and cl<strong>in</strong>ical biochemistry.<br />

An annual questionnaire that was completed at the time of the medical exam<strong>in</strong>ation was also exam<strong>in</strong>ed.<br />

This recorded headaches, dizz<strong>in</strong>ess, irritability, restlessness, fatigue, loss of appetite, full stomach,<br />

diarrhoea, cough, dyspnoea, hear<strong>in</strong>g problems, t<strong>in</strong>nitus, abnormal taste, gastroenteric problems<br />

or any other abnormalities.<br />

The number of hours spent pack<strong>in</strong>g ranged from 10 to 83 per year. Four of the workers had<br />

been engaged <strong>in</strong> pack<strong>in</strong>g for 10 years or more, four for between 5 and 9 years and seven for less<br />

than 4 years. Five of the workers were aged at least 50 years, two were aged between 40 and 49, five<br />

were aged between 30 and 39 and three were aged less than 29 years. All workers wore protective<br />

equipment consist<strong>in</strong>g of long-sleeved cotton clothes, plastic helmets, masks, glasses and gloves. No<br />

abnormalities were apparent from the medical records that could be related to the manufacture or<br />

handl<strong>in</strong>g of technical-grade procymidone (Kurihara, 2001). A similar study <strong>in</strong> <strong>2007</strong> confirmed that<br />

there were no adverse health effects <strong>in</strong> the monitored workforce (Kumagai, <strong>2007</strong>).<br />

The sponsor reported there were no documented cases of <strong>in</strong>toxication with procymidone and<br />

no <strong>in</strong>formation on effects of exposure of the general population to procymidone.<br />

Comments<br />

Biochemical aspects<br />

Studies with 14 C-labelled procymidone showed that radiolabel was rapidly absorbed (C max<br />

,<br />

2–8 h) and rapidly elim<strong>in</strong>ated (> 80% <strong>in</strong> 24 h) <strong>in</strong> mice and rats. Absorption was extensive, as shown<br />

by the high level of ur<strong>in</strong>ary excretion (> 80% of the adm<strong>in</strong>istered dose), with similar results obta<strong>in</strong>ed<br />

<strong>in</strong> mice and rats receiv<strong>in</strong>g doses of up to 100 mg/kg bw. At higher doses, the proportion of the adm<strong>in</strong>istered<br />

dose excreted <strong>in</strong> the faeces <strong>in</strong>creased: at 250 mg/kg bw, 24–33% was elim<strong>in</strong>ated by that route<br />

after 168 h; the <strong>in</strong>crease <strong>in</strong> faecal radioactivity was ma<strong>in</strong>ly attributable to an <strong>in</strong>crease <strong>in</strong> unabsorbed<br />

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

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