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

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154<br />

Table 12. Inhibition of plasma, erythrocyte and bra<strong>in</strong> chol<strong>in</strong>esterase activity <strong>in</strong> F 0<br />

and <strong>in</strong> F 1<br />

pups<br />

of rats fed diets conta<strong>in</strong><strong>in</strong>g az<strong>in</strong>phos-methyl<br />

Dietary<br />

concentration<br />

(ppm)<br />

Chol<strong>in</strong>esterase activity (% of values for controls)<br />

F 0<br />

males F 0<br />

females F 1<br />

pups<br />

End of<br />

m at<strong>in</strong>g<br />

End of pretreatment<br />

Post-coital<br />

day 11<br />

Postnatal<br />

day 5<br />

Postnatal<br />

day 28<br />

Postnatal<br />

day 5<br />

Postnatal<br />

day 28<br />

Plasma<br />

5<br />

15<br />

2.3<br />

14***<br />

ND<br />

25*<br />

ND<br />

18<br />

26*<br />

46***<br />

5<br />

39**<br />

ND<br />

45 43*** 62*** 60*** 66*** 63***<br />

Erythrocytes<br />

5 19** ND ND 25** 47***<br />

15 69*** 46*** 52*** 75*** 84***<br />

ND<br />

45 94*** 71*** 81*** 91*** 89***<br />

Bra<strong>in</strong><br />

5 1 10* ND ND 12 ND ND<br />

15 ND 4 21** 38** 48*** 1 14<br />

45 19** 55*** 69*** 66*** 68*** 17* 46***<br />

From Holzum (1990); Annex 1, reference 64, modified by reference to orig<strong>in</strong>al data.<br />

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

ND, not determ<strong>in</strong>ed.<br />

ND<br />

ND<br />

Table 13. Chol<strong>in</strong>esterase activity <strong>in</strong> dams (and their fetuses) given az<strong>in</strong>phos-methyl by gavage on<br />

days 6–15 of gestation<br />

Tissue<br />

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

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

0 0.5 1.0 2.0<br />

Day 16<br />

Plasma, kU/l (% of control) 1.73 (100%) 1.56 (90%) 1.64 (95%) 1.08 (63%)<br />

Erythrocytes, kU/l (% of control) 0.38 (100%) 0.34 (90%) 0.34 (90%) 0.08* (21%)<br />

Bra<strong>in</strong>, U/g (% of control) 2.53 (100%) 2.70 (107%) 2.55 (101%) 1.55* (61%)<br />

Day 20<br />

Plasma, kU/l (% of control) 1.44 (100%) 1.47 (102%) 1.40 (97%) 1.32 (92%)<br />

Erythrocytes, kU/l (% of control) 0.58 (100%) 0.59 (103%) 0.61 (106%) 0.44 (77%)<br />

Bra<strong>in</strong>, U/g (% of control) 2.67 (100%) 2.72 (102%) 2.46 (92%) 1.91* (72%)<br />

Fetal bra<strong>in</strong>, U/g (% of control) 1.04 (100%) 0.96 (91%) 1.04 (100%) 1.00 (96%)<br />

From Kowalski et al. (1987a; 1987b); Annex 1, reference 64, modified by reference to orig<strong>in</strong>al data; Astroff & Young<br />

(1998).<br />

* p < 0.05.<br />

developmental toxicity was 2.0 mg/kg bw per day, on the basis of the absence of any effects at the<br />

highest tested dose. The NOAEL for maternal toxicity was 1.0 mg/kg bw per day, on the basis of<br />

the <strong>in</strong>hibition of bra<strong>in</strong> chol<strong>in</strong>esterase activity seen on day 16 of gestation at 2.0 mg/kg bw per day<br />

(Kowalski et al., 1987a, 1987b; Annex 1, reference 64, modified by reference to orig<strong>in</strong>al data; Astroff<br />

& Young, 1998).<br />

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

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