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Pesticide residues in food — 2006: Toxicological ... - ipcs inchem

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41<br />

Multigeneration study of<br />

reproductive toxicity a<br />

Carc<strong>in</strong>ogenicity<br />

Parental toxicity<br />

Offspr<strong>in</strong>g toxicity<br />

160 ppm, equal to —<br />

9.7 mg/kg bw per day c<br />

20 ppm, equal to<br />

1.5 mg/kg bw per day<br />

200 ppm equal to<br />

15.3 mg/kg bw per day<br />

80 ppm, equal to<br />

6.1 mg/kg bw per day<br />

Developmental toxicity b Maternal toxicity 10 mg/kg bw per day 100 mg/kg bw per day<br />

Embryo/fetotoxicity 500 mg/kg bw per day c —<br />

Rabbit Developmental toxicity b Maternal toxicity 200 mg/kg bw per day c __<br />

Embryo-fetotoxicity 200 mg/kg bw per day —<br />

Dog 90-day study of toxicity a Toxicity 40 ppm, equal to<br />

0.9 mg/kg bw per day<br />

One-year study of toxicity a Toxicity 40 ppm, equal to 1.0<br />

mg/kg bw per day<br />

a<br />

Dietary adm<strong>in</strong>istration<br />

b<br />

Gavage adm<strong>in</strong>istration<br />

c<br />

Highest dose tested<br />

400 ppm, equal to<br />

10.4 mg/kg bw per day<br />

400 ppm, equal to<br />

8.9 mg/kg bw per day<br />

Estimate of acceptable daily <strong>in</strong>take for humans<br />

0–0.01 mg/kg bw<br />

Estimate of acute reference dose<br />

Unnecessary<br />

Information that would be useful for cont<strong>in</strong>ued evaluation of the compound<br />

Results from epidemiological, occupational health and other such observational studies of<br />

human exposure<br />

Critical end-po<strong>in</strong>ts for sett<strong>in</strong>g guidance values for exposure to bifenazate<br />

Absorption, distribution, excretion, and metabolism <strong>in</strong> mammals<br />

Rate and extent of oral absorption<br />

Distribution<br />

Potential for accumulation<br />

Rate and extent of excretion<br />

Metabolism <strong>in</strong> animals<br />

<strong>Toxicological</strong>ly significant compounds<br />

Moderate and <strong>in</strong>complete; maximum blood concentration reached<br />

by 5–6 h; later at higher doses. Approximately 79–85% and 22–29%<br />

absorbed with<strong>in</strong> 72 h at 10 and 1000 mg/kg bw, respectively<br />

Widely distributed <strong>in</strong> tissues<br />

No evidence of significant accumulation<br />

Approximately 90% (27% <strong>in</strong> ur<strong>in</strong>e and 63% <strong>in</strong> faeces) with<strong>in</strong> 48 h at<br />

10 mg/kg bw per day<br />

Extensive; metabolic pathways <strong>in</strong>clude hydraz<strong>in</strong>e oxidation,<br />

demethylation, r<strong>in</strong>g hydroxylation, cleavage of the hydraz<strong>in</strong>e-carboxylic<br />

acid portion of the molecule and conjugation with glucuronic acid and<br />

sulfate<br />

Bifenazate and bifenazate-diazene (compounds readily <strong>in</strong>terconvert)<br />

BIFENAZATE X-X JMPR <strong>2006</strong>

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