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

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361<br />

resorptions. A sample of bra<strong>in</strong> (from the frontal cortex) of approximately 0.1 g was removed from the<br />

same six animals <strong>in</strong> each group and exam<strong>in</strong>ed for bra<strong>in</strong> chol<strong>in</strong>esterase activity. Fetuses were weighed,<br />

sexed and exam<strong>in</strong>ed for external, <strong>in</strong>ternal and skeletal abnormalities and anomalies. Statements of<br />

adherence to quality assurance and GLP were <strong>in</strong>cluded.<br />

No treatment-related deaths or toxicologically relevant cl<strong>in</strong>ical effects were observed. Body<br />

weight and <strong>food</strong> consumption were not significantly affected. The effects of treatment on plasma,<br />

erythrocyte and bra<strong>in</strong> chol<strong>in</strong>esterase activity are described <strong>in</strong> Table 3.<br />

Table 3. Plasma, erythrocyte and bra<strong>in</strong> chol<strong>in</strong>esterase<br />

activity (% of control values) <strong>in</strong> rabbits given<br />

pirimiphos-methyl by gavage<br />

Time-po<strong>in</strong>t Chol<strong>in</strong>esterase Dose (mg/kg bw per day)<br />

12 24 48<br />

Day 5 Plasma 102 93 92<br />

Erythrocyte 98 110 107<br />

Day 19 Plasma 87 63* 50*<br />

Erythrocyte 79 56* 38*<br />

Day 29 Plasma 102 94 106<br />

Erythrocyte 110 91 82<br />

Bra<strong>in</strong> 142 160 62*<br />

From Barton & Hast<strong>in</strong>gs (1994).<br />

* p < 0.05, statistically significant<br />

At the <strong>in</strong>termediate and highest doses, maternal toxicity was <strong>in</strong>dicated by depressed erythrocyte<br />

chol<strong>in</strong>esterase activity on day 19. In the group at the highest dose, bra<strong>in</strong> chol<strong>in</strong>esterase activity was<br />

decreased at term<strong>in</strong>ation. No toxicologically relevant effects were observed <strong>in</strong> dams <strong>in</strong> groups at<br />

the lowest dose. On the basis of reduced erythrocyte chol<strong>in</strong>esterase activity at day 19 <strong>in</strong> dams at the<br />

<strong>in</strong>termediate dose, the NOAEL for maternal toxicity was 12 mg/kg bw per day.<br />

Pirimiphos-methyl did not <strong>in</strong>duce irreversible structural changes and had no toxicologically<br />

relevant effects <strong>in</strong> fetuses. Therefore the NOAEL for embryo/fetotoxicity was 48 mg/kg bw per day,<br />

i.e. the highest dose tested (Barton & Hast<strong>in</strong>gs, 1994).<br />

2.4 Special studies: neurotoxicity<br />

Rats<br />

A group of 25 male rats (stra<strong>in</strong> unknown) received a s<strong>in</strong>gle dose (method of adm<strong>in</strong>istration<br />

not specified) of pirimiphos-methyl (purity, 90.5%) at 1000 mg/kg bw. An additional group of 25<br />

rats served as controls. Five rats per group were sacrificed at 4, 8, 24, 48 or 72 h after dos<strong>in</strong>g and<br />

plasma and bra<strong>in</strong> chol<strong>in</strong>esterase and non-specific carboxylesterase activities were measured. Plasma<br />

chol<strong>in</strong>esterase <strong>in</strong>hibition was rapid (60% <strong>in</strong>hibition by 4 h), while <strong>in</strong>hibition of bra<strong>in</strong> chol<strong>in</strong>esterase<br />

activity was slower (36% by 8 h). Both atta<strong>in</strong>ed maximum <strong>in</strong>hibition by 24 h (93% for plasma and<br />

61% for bra<strong>in</strong>). Partial recovery was apparent at 48–72 h for both enzymes, but that for bra<strong>in</strong> was<br />

slower. Inhibition of non-specific carboxylesterase activity atta<strong>in</strong>ed maximum levels (plasma, 80%;<br />

and bra<strong>in</strong>, 47%) at 24 h; compared with chol<strong>in</strong>esterase, <strong>in</strong>hibition was slightly less, and recovery<br />

<strong>in</strong> plasma was more rapid. In bra<strong>in</strong>, recovery of non-specific carboxylesterase and chol<strong>in</strong>esterase<br />

activity were comparable (Raj<strong>in</strong>i & Krishnakumari, 1988).<br />

PIRIMIPHOS-METHYL X-X JMPR <strong>2006</strong>

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