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

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473<br />

Analysis of dos<strong>in</strong>g solutions <strong>in</strong>dicated that the formulations were homogenous and the measured<br />

concentrations were with<strong>in</strong> 15% of the target concentrations. Maternal toxicity at 300 mg/kg<br />

bw per day <strong>in</strong>cluded significant decreases <strong>in</strong> body weight (6–8%), body-weight ga<strong>in</strong> (29%) and decreases<br />

<strong>in</strong> <strong>food</strong> consumption (35–42%). Decreased <strong>food</strong> consumption resulted <strong>in</strong> <strong>in</strong>creased <strong>in</strong>cidence<br />

of rabbits with reduced production and size of faecal pellets. In addition, three rabits became emaciated,<br />

due to the decreased consumption, and were subsequently sacrificed on days 24, 15 and 22 of<br />

gestation. At 45 mg/kg bw per day, a slight <strong>in</strong>crease <strong>in</strong> the number of dams with reduced production<br />

and size of faecal pellets (less frequent and of shorter duration) was seen, but was not considered to<br />

be an adverse treatment-related effect. At 7 mg/kg bw per day, no treatment-related maternal effects<br />

were noted. Treatment-related developmental f<strong>in</strong>d<strong>in</strong>gs at 300 mg/kg bw per day, when compared<br />

with those for concurrent controls, <strong>in</strong>cluded decreases <strong>in</strong> fetal weight (10%), <strong>in</strong>creases <strong>in</strong> fetal runts,<br />

<strong>in</strong>creases <strong>in</strong> the <strong>in</strong>cidence of retarded fetal bone ossification, and <strong>in</strong>creases <strong>in</strong> the <strong>in</strong>cidence of extra<br />

thoracic vertebrae and ribs. The <strong>in</strong>creased number of fetal runts was outside the range for historical<br />

controls. The Meet<strong>in</strong>g requested a clarification on the criteria used by the study authors <strong>in</strong> describ<strong>in</strong>g<br />

fetal runts to the submitter dur<strong>in</strong>g the meet<strong>in</strong>g. Fetal runts were def<strong>in</strong>ed based on reduced weights<br />

only and not by fetal size. S<strong>in</strong>ce the decreased <strong>in</strong> fetal body weights were observed <strong>in</strong> the presence<br />

of severe maternal toxicity (moribund condition, decreased body weights), the Meet<strong>in</strong>g considered<br />

that these effects were secondary to maternal toxicity and were not treatment-related. No treatmentrelated<br />

developmental effects were observed at 45 or 7 mg/kg bw per day.<br />

The NOAEL for maternal toxicity was 45 mg/kg bw per day on the basis of deaths <strong>in</strong> three<br />

rabbits (kiled), decrease <strong>in</strong> body-weight ga<strong>in</strong> (29%), a decrease <strong>in</strong> <strong>food</strong> consumption (35–42% and<br />

reduced production and size of faecal pellets seen at the LOAEL of 300 mg/kg bw per day. The NO-<br />

AEL for developmental toxicity was 300 mg/kg bw per day, the highest dose tested (Irv<strong>in</strong>e, 1991).<br />

2.6 Special studies<br />

(a)<br />

Acute neurotoxicity<br />

In a study of acute oral neurotoxicity, groups of 12 male and 12 female non-fasted Sprague-<br />

Dawley CD (Crl:CD [SD] IGS BR) rats were given a s<strong>in</strong>gle dose of pyrimethanil (purity, 99.8%) at a<br />

dose of 0, 30, 100, or 1000 mg/kg bw by gavage <strong>in</strong> 0.5% (w/v) methylcellulose (5 ml/kg). In a separate<br />

study, the time of peak effects for pyrimethanil was estimated to be 1.5–4 h after dos<strong>in</strong>g. Functional<br />

observational battery (FOB) and motor activity were evaluated on days −6, 1 (approximately<br />

1.5–2 h after dos<strong>in</strong>g), 8, and 15. On day 16, five males and five females per group were perfused <strong>in</strong><br />

situ for neurohistological exam<strong>in</strong>ation, and tissues from rats <strong>in</strong> the control group and group at the<br />

highest dose were exam<strong>in</strong>ed microscopically. Data for positive controls were provided and were<br />

judged to be adequate, but were several years old.<br />

No unscheduled deaths occurred. Cl<strong>in</strong>ical signs, body weights, body-weight ga<strong>in</strong>s, <strong>food</strong> consumption,<br />

gross pathology, bra<strong>in</strong> weights and measurements, and neuropathology were unaffected by<br />

treatment. At 1000 mg/kg bw, the follow<strong>in</strong>g transient FOB effects were noted on day 1: (i) slight to<br />

moderate overall gait <strong>in</strong>capacity, <strong>in</strong>dicated by slight to moderate ataxia; (ii) moderately dilated pupils<br />

<strong>in</strong> females; (iii) decreased h<strong>in</strong>dlimb-grip strength (24%; p < 0.01) <strong>in</strong> the males; and (iv) decreased<br />

body temperature (0.56–1.49 °C; p < 0.01). Total motor activity was also decreased by 52–110%<br />

(p < 0.001) at 1000 mg/kg bw on day 1 <strong>in</strong> males and females compared with controls. Habituation of<br />

motor activity was unaffected by treatment. All rats appeared to be normal on days 8 and 15. These<br />

effects were considered to be non-specific, transient and occurred at high doses.<br />

The NOAEL was 100 mg/kg bw on the basis of decreased motor activity, ataxia, and decreased<br />

body temperature <strong>in</strong> males and females, decreased h<strong>in</strong>dlimb-grip strength <strong>in</strong> males, and dilated p upils<br />

<strong>in</strong> females on day 1 seen at 1000 mg/kg bw (Beyrouty, 2001a, 2001b).<br />

PYRIMETHANIL 445–486 JMPR <strong>2007</strong>

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