28.01.2014 Views

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

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

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

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

141<br />

methylation and oxidation of mercaptomethyl-benzazimide forms benzazimide, methylthiomethylbenzazimide<br />

and its correspond<strong>in</strong>g oxidized metabolites. Hydrolysis of glutathionyl methylbenzazimide<br />

may result <strong>in</strong> the formation of cyste<strong>in</strong>ylmethyl-benzazimide. Subsequent oxidation of<br />

cyste<strong>in</strong>yl-methylbenzazimide forms its correspond<strong>in</strong>g sulfoxide and sulfone (Kao, 1988; Annex 1,<br />

r eference 64).<br />

The rate of disappearance of az<strong>in</strong>phos-methyl via a hepatic oxidative desulfurat<strong>in</strong>g system and<br />

a demethylat<strong>in</strong>g system was <strong>in</strong>vestigated <strong>in</strong> liver homogenates from four different species (rat, gu<strong>in</strong>ea-pig,<br />

chicken and monkey). Az<strong>in</strong>phos-methyl was metabolized by both systems and homogenates<br />

from all species were uniformly active (Rao & McK<strong>in</strong>ley, 1969; Annex 1, reference 64).<br />

1.3 Effect on enzymes and other biochemical parameters<br />

The acute oral toxicity of az<strong>in</strong>phos-methyl, dissolved <strong>in</strong> propylene glycol, was <strong>in</strong>vestigated<br />

<strong>in</strong> groups of female mice and the effect of the oxime antidote, toxogon<strong>in</strong> (80 mg/kg bw <strong>in</strong>traperitoneally,<br />

15 m<strong>in</strong> before oral dos<strong>in</strong>g), was determ<strong>in</strong>ed. Antidote treatment reduced the toxicity of<br />

az<strong>in</strong>phos-methyl by <strong>in</strong>creas<strong>in</strong>g the median lethal dose (LD 50<br />

) by a factor of 2 (Sterri et al., 1979;<br />

Annex 1, reference 64).<br />

2. <strong>Toxicological</strong> studies<br />

2.1 Acute oral toxicity<br />

The results of studies to establish the acute toxicity of az<strong>in</strong>phos-methyl are summarized <strong>in</strong><br />

Table 1.<br />

The acute oral toxicity of az<strong>in</strong>phos-methyl technical <strong>in</strong> mammals was high. Consistent with the<br />

chol<strong>in</strong>ergic effects observed with other organophosphorus compounds, signs of acute <strong>in</strong>toxication<br />

with az<strong>in</strong>phos-methyl <strong>in</strong>cluded diarrhoea, salivation, lacrimation and vomit<strong>in</strong>g (muscar<strong>in</strong>ic effects),<br />

muscular tremors and paralysis (nicot<strong>in</strong>ic effects), and restlessness, ataxia and convulsions (central<br />

nervous system effects).<br />

2.2 Short-term studies of toxicity<br />

Rats<br />

In a dose-range f<strong>in</strong>d<strong>in</strong>g study with emphasis on the most sensitive end-po<strong>in</strong>t, namely <strong>in</strong>hibition<br />

of chol<strong>in</strong>esterase activity, groups of five male and five female SPF BOR:WISW (SPF/Cpb) rats were<br />

fed diets conta<strong>in</strong><strong>in</strong>g az<strong>in</strong>phos-methyl (purity, 93.3%) at a concentration of 0, 5, 20, or 50 ppm for 28<br />

days. The average doses <strong>in</strong>gested at 5, 20, or 50 ppm were 0.35, 1.30, and 3.37 mg/kg bw per day<br />

for males and 0.46, 1.54, and 3.96 mg/kg bw per day for females, respectively. There were no effects<br />

on appearance, behaviour, mortality, body-weight ga<strong>in</strong>, <strong>food</strong> consumption, and gross pathology. A<br />

statistically significant reduction <strong>in</strong> plasma chol<strong>in</strong>esterase activity of 44–66%, relative to the control<br />

group, was seen <strong>in</strong> females at 50 ppm. Appreciably less <strong>in</strong>hibition of plasma chol<strong>in</strong>esterase activity<br />

was observed <strong>in</strong> males and this was consistent across the entire sampl<strong>in</strong>g period. Erythrocyte acetylchol<strong>in</strong>esterase<br />

activity was unaffected <strong>in</strong> males at 20 ppm, but was significantly reduced (17–22%) <strong>in</strong><br />

females. Bra<strong>in</strong> chol<strong>in</strong>esterase activity was significantly <strong>in</strong> females at 50 ppm (Table 2).<br />

The NOAEL was 20 ppm, equal to 1.30 mg/kg bw per day <strong>in</strong> males and 1.54 mg/kg bw per day<br />

<strong>in</strong> females, on the basis of <strong>in</strong>hibition of chol<strong>in</strong>esterase activity <strong>in</strong> the bra<strong>in</strong> at 50 ppm (Eiben et al.,<br />

1983).<br />

AZINPHOS-METHYL 139–172 JMPR <strong>2007</strong>

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!