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

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379<br />

a s<strong>in</strong>gle dose, which produced overt maternal toxicity, was used <strong>in</strong> the study, and the fetal f<strong>in</strong>d<strong>in</strong>gs<br />

were considered to be of uncerta<strong>in</strong> toxicological relevance. The NOAEL for developmental toxicity<br />

was 125 mg/kg bw per day, the highest dose tested. A NOAEL for maternal toxicity was not<br />

identified (Inawaka, 2003).<br />

Primates<br />

Groups of four pregnant cynomolgus monkeys (Macaca fascicularis) were given procymidone<br />

(purity, 99.0%) at a dose of 62.5 or 125 mg/kg bw per day by gavage <strong>in</strong> 0.5% methylcellulose dur<strong>in</strong>g<br />

the critical period of differentiation of the fetal external genitalia (days 20–99 of gestation). Monkeys<br />

were observed twice per day dur<strong>in</strong>g the dos<strong>in</strong>g period and once per day thereafter. Body weight and<br />

<strong>food</strong> consumption were measured at <strong>in</strong>tervals up to day 100 of gestation. Blood was taken for cl<strong>in</strong>ical<br />

chemistry and haematology on days 19 and 100 and 2, 4, 8 and 24 h after the first and last doses on<br />

days 20 and 99 for analysis of procymidone concentration. Fetal heartbeat and size were monitored<br />

by ultrasound at <strong>in</strong>tervals dur<strong>in</strong>g pregnancy. The fetuses and placentae were removed under anaesthesia<br />

by caesarean section on day 100 or 102 of gestation. The dams were then term<strong>in</strong>ated and selected<br />

organs were removed, fetuses and placenta were weighed; the fetuses were then given an external<br />

exam<strong>in</strong>ation followed by an <strong>in</strong>ternal exam<strong>in</strong>ation of visceral organs and <strong>in</strong>ternal genitalia.<br />

None of the monkeys died <strong>in</strong> either group and there were no signs of toxicity or treatment-related<br />

effects on body weight, <strong>food</strong> consumption, cl<strong>in</strong>ical chemistry or haematology. One dam <strong>in</strong> each<br />

group aborted. The major organs were unaffected. Blood concentrations of procymidone reached a<br />

maximum 2–4 h after dos<strong>in</strong>g and C max<br />

and AUC <strong>in</strong>creased <strong>in</strong> a l<strong>in</strong>ear manner with dose on day 20 but<br />

were equal at day 99 (Table 25). There were two male and one female fetuses <strong>in</strong> the group at the lower<br />

dose and three males <strong>in</strong> the group at the higher dose. There were no effects on the weight of the fetus<br />

or placenta and no <strong>in</strong>crease <strong>in</strong> adverse external or visceral f<strong>in</strong>d<strong>in</strong>gs <strong>in</strong>clud<strong>in</strong>g external genitalia of all<br />

five male fetuses treated with procymidone (Fukunishi, 2003a).<br />

A more extensive exam<strong>in</strong>ation of the fetuses was made <strong>in</strong> a second study <strong>in</strong> which groups of<br />

16 pregnant cynomolgus monkeys (Macaca fascicularis) were given procymidone (purity, 99.0%)<br />

at a dose of 0 or 125 mg/kg bw per day by gavage <strong>in</strong> 0.5% methylcellulose dur<strong>in</strong>g the critical period<br />

of differentiation of the fetal external genitalia (days 20–99 of gestation). Monkeys were observed<br />

twice per day for cl<strong>in</strong>ical signs of toxicity dur<strong>in</strong>g the dos<strong>in</strong>g period and once per day dur<strong>in</strong>g the nondos<strong>in</strong>g<br />

period; body weight and <strong>food</strong> consumption were measured at <strong>in</strong>tervals. Fetal heartbeat and<br />

size were monitored by ultrasound dur<strong>in</strong>g the treatment period to confirm pregnancy status and fetal<br />

Table 24. F<strong>in</strong>d<strong>in</strong>gs <strong>in</strong> fetuses of female rabbits given procymidone by gavage<br />

F<strong>in</strong>d<strong>in</strong>g a<br />

Dose (mg/kg bw per day)<br />

0 125<br />

Males Females Males Females<br />

Pup body weight (g) 41.5 ± 6.5 39.8 ± 6.1 40.5 ± 8.2 40.8 ± 8.3<br />

Anogenital distance (mm) 1.48 ± 0.18 1.34 ± 0.23 1.41 ± 0.16 1.35 ± 0.10<br />

Phallus boundary-genital distance (μm) 434 ± 94 286 ± 91 368 ± 113 259 ± 76<br />

Preputial lamella diameter (μm) 940 ± 58 836 ± 59 934 ± 60 833 ± 70<br />

Ventral gap of preputial lamella (μm) 46 ± 40 421 ± 114 38 ± 19 498* ± 71<br />

Ventral gap : preputial lamella ratio 0.05 0.50 0.04 0.60*<br />

Relative ventral gap : body weight (μm/g) 1.1 ± 0.8 11 ± 3.4 1.0 ± 0.6 13 ± 3.5<br />

From Inawaka (2003)<br />

a<br />

Mean ± standard deviation.<br />

* p < 0.05 relative to females <strong>in</strong> the control group.<br />

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

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