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

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243<br />

<strong>in</strong> the control group and <strong>in</strong> the groups at 1 and 25 mg/kg bw per day tended to decrease after the end<br />

of dos<strong>in</strong>g, while the rabbits at 75 mg/kg bw per day cont<strong>in</strong>ued to <strong>in</strong>crease their <strong>food</strong> consumption.<br />

Fifteen does that were <strong>in</strong>sem<strong>in</strong>ated were not pregnant at caesarean section on day 29: three <strong>in</strong> the<br />

control group, five at 1 mg/kg bw per day, three at 25 mg/kg bw per day and four at 75 mg/kg bw per day.<br />

Three does died (one each <strong>in</strong> the control group and the groups at 1 mg/kg bw per day and 75 mg/kg bw<br />

per day) and two does at 75 mg/kg bw per day aborted, so there were 15, 13, 16 and 12 litters for evaluation<br />

<strong>in</strong> the control group and the groups receiv<strong>in</strong>g 1, 25 and 75 mg/kg bw per day, respectively. Data from<br />

caesarean sections <strong>in</strong>dicated that the mean numbers of corpora lutea, implantation sites and live fetuses<br />

were comparable between the groups. There were no dead fetuses. The numbers of resorptions per pregnancy<br />

were only slightly and not significantly higher among the rabbits at 75 mg/kg bw per day.<br />

The weights of male and female fetuses were not significantly different between the groups,<br />

although some statistical differences were described <strong>in</strong> the orig<strong>in</strong>al report. It was subsequently determ<strong>in</strong>ed<br />

that the statistical rout<strong>in</strong>e used for generat<strong>in</strong>g the report tables ran <strong>in</strong>correctly, i.e., post hoc<br />

comparisons were <strong>in</strong>appropriately performed although the overall F statistics were not significant<br />

(p = 0.072 for males; p = 0.104 for females). It was also suggested <strong>in</strong> the orig<strong>in</strong>al report that variations<br />

<strong>in</strong> litter size could account for apparent differences <strong>in</strong> fetal weights. To this end, the data were<br />

subsequently analysed by analysis of covariance with litter size as the covariate. These analyses were<br />

also not significant at the p ≤ 0.05 level for males and females. Moreover, it was stated <strong>in</strong> the orig<strong>in</strong>al<br />

report that the weights for fetuses from the control group (males, 47.3 ± 1.6 g; females, 45.6 ± 1.5 g)<br />

were exceptionally high <strong>in</strong> comparison with the mean values for historical controls of 43.4 g for male<br />

fetuses and 42.2 g for female fetuses. The weights for the fetuses <strong>in</strong> the treated groups were closer to<br />

these values than were those for the control group <strong>in</strong> this study. Fetal sex ratios were not affected by<br />

treatment. Maternal autopsy exam<strong>in</strong>ations did not reveal any treatment-related f<strong>in</strong>d<strong>in</strong>gs<br />

Fetal exam<strong>in</strong>ations did not reveal any treatment-related effects on the <strong>in</strong>cidences of external,<br />

visceral or skeletal variations or malformations. One fetus <strong>in</strong> the group at 25 mg/kg bw per day was<br />

found dur<strong>in</strong>g external exam<strong>in</strong>ation to have a raised, discoloured area on the ventral thoracic region<br />

that may have resulted from technical manipulation and was considered to be <strong>in</strong>cidental. The only<br />

visceral f<strong>in</strong>d<strong>in</strong>gs were a horseshoe kidney <strong>in</strong> one fetus at 75 mg/kg bw per day, microencephaly <strong>in</strong><br />

one fetus at 25 mg/kg bw per day and partial cryptophthalmos <strong>in</strong> one fetus at 75 mg/kg bw per day.<br />

Skeletal alterations were seen <strong>in</strong> approximately 80–90% of the fetuses and all of the litters. There<br />

were no statistically significant or biologically mean<strong>in</strong>gful differences among the groups (by fetus or<br />

by litter) <strong>in</strong> the <strong>in</strong>cidence of any f<strong>in</strong>d<strong>in</strong>g.<br />

The NOAEL for maternal toxicity was 25 mg/kg bw per day on the basis of reduced bodyweight<br />

ga<strong>in</strong> at 75 mg/kg bw per day. The NOAEL for fetal toxicity was 75 mg/kg bw per day, the<br />

highest dose tested. There were no <strong>in</strong>dications of embryotoxicity, fetotoxicity or teratogenicity at a<br />

dose up to 75 mg/kg bw per day (Hummel et al., 1987).<br />

2.6 Special studies<br />

(a)<br />

Studies on neurotoxic potential<br />

In a study of neurotoxicity, groups of 10 male and 10 female Alpk:AP f<br />

SD (Wistar-derived) rats<br />

were given s<strong>in</strong>gle doses of difenoconazole technical (purity, 94.3 %) at a dose of 0, 25, 200 or 2000<br />

mg/kg bw <strong>in</strong> 1% carboxymethyl cellulose andthen observed for 14 days.<br />

All rats were observed before the study start and daily throughout the study for any changes <strong>in</strong><br />

cl<strong>in</strong>ical condition. In addition, a functional observation battery (FOB), <strong>in</strong>clud<strong>in</strong>g quantitative assessments<br />

of land<strong>in</strong>g foot splay, sensory perception and muscle weakness, was performed <strong>in</strong> week −1,<br />

and on days 1 (at the time of anticipated maximum effect), 8 and 15. Locomotor activity was also<br />

monitored <strong>in</strong> week −1, and on days 1, 8 and 15. Body weights and <strong>food</strong> consumption were measured<br />

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

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