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

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146<br />

Table 3. Chol<strong>in</strong>esterase activity <strong>in</strong> rats given az<strong>in</strong>phos-methyl by gavage for 13 weeks<br />

Chol<strong>in</strong>esterase<br />

Chol<strong>in</strong>esterase activity (% <strong>in</strong>hibition relative to control values)<br />

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

0.22 0.86 3.44<br />

Males Females Males Females Males Females<br />

Plasma butyryl chol<strong>in</strong>esterase 18*** 3 16** 10 30*** 47***<br />

Plasma acetyl chol<strong>in</strong>esterase 18** −3 14* 7 42*** 49***<br />

Erythrocyte acetylchol<strong>in</strong>esterase 8* 9*** 17*** 29*** 77*** 78***<br />

Bra<strong>in</strong> chol<strong>in</strong>esterase 3 4 9* 3 67*** 64***<br />

From Broadmeadow et al. (1987)<br />

* p < 0.05; ** p < 0.01; *** p < 0.001.<br />

Table 4. Chol<strong>in</strong>esterase activity <strong>in</strong> dogs a fed diets conta<strong>in</strong><strong>in</strong>g az<strong>in</strong>phos-methyl for 52 weeks<br />

Chol<strong>in</strong>esterase<br />

Chol<strong>in</strong>esterase activity (% <strong>in</strong>hibition relative to control values)<br />

Dietary concentration (ppm)<br />

0 5 25 125<br />

Males Females Males Females Males Females Males Females<br />

Plasma chol<strong>in</strong>esterase<br />

Week 4 0 0 11 −18 12 14 37 52*<br />

Week 13 0 0 13 −2 15 17 53** 58**<br />

Week 26 0 0 14 −10 12 33 58** 57**<br />

Week 52 0 0 11 12 12 30 53* 53**<br />

Erythrocyte acetylchol<strong>in</strong>esterase<br />

Week 4 0 0 −9 11 22 2 66** 86**<br />

Week 13 0 0 8 16 40** 43** 87** 92**<br />

Week 26 0 0 8 21 32 38** 88** 91**<br />

Week 52 0 0 −5 15 27 35* 86** 86**<br />

Bra<strong>in</strong> chol<strong>in</strong>esterase 0 0 1 1 10 1 27** 20*<br />

From Allen et al. (1990), Annex 1, reference 64, modified with reference to the orig<strong>in</strong>al data.<br />

a<br />

n = 4<br />

* p < 0.05; ** p < 0.01.<br />

B6C3F 1<br />

mice were fed diets conta<strong>in</strong><strong>in</strong>g az<strong>in</strong>phos-methyl. Groups of 50 male and 50 female Osborne-<br />

Mendel rats were given diets conta<strong>in</strong><strong>in</strong>g az<strong>in</strong>phos-methyl for 80 weeks, and were then observed for 34<br />

or 35 weeks. Males received az<strong>in</strong>phos-methyl at a time-weighted average dietary concentration of 78<br />

or 156 ppm (equivalent to 6.25 and 12.5 mg/kg bw per day respectively), while females received 62.5<br />

or 125 ppm (equivalent to 3.12 and 6.25 mg/kg bw per day respectively). Matched controls consisted<br />

of 10 male and 10 female untreated rats; pooled controls consisted of matched controls comb<strong>in</strong>ed<br />

with 95 male and 95 female untreated rats from similar bioassays of 10 other chemicals. The study<br />

<strong>in</strong> mice was of similar design; groups of 50 mice were treated for 80 weeks, then observed for 12 or<br />

13 weeks, males received az<strong>in</strong>phos-methyl at a dietary concentration of 31.3 or 62.5 ppm (equivalent<br />

to 4.7 and 9.4 mg/kg bw per day respectively) and females received 62.5 or 125 ppm (equivalent<br />

to 9.4 and 18.75 mg/kg bw per day respectively), matched controls consisted of 10 males and 10<br />

females, pooled controls comprised 130 males and 120 females. Typical signs of organophosphate<br />

<strong>in</strong>toxication (hyperactivity, tremors and dyspnoea) were observed <strong>in</strong> a few animals of both species<br />

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

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