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

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180<br />

At 1500 ppm, liver APDM activity was <strong>in</strong>creased and hepatic SER was <strong>in</strong>creased <strong>in</strong> both<br />

sexes at 12 and 24 months, and <strong>in</strong> females at 150 ppm at 24 months (Table 6). These changes were<br />

considered to be adaptations, and not of toxicological significance.<br />

Table 6. Liver am<strong>in</strong>opyr<strong>in</strong>e N-demethylase activity and smooth endoplasmic reticulum<br />

p roliferation a <strong>in</strong> rats fed diets conta<strong>in</strong><strong>in</strong>g cypermethr<strong>in</strong> for 2 years<br />

F<strong>in</strong>d<strong>in</strong>g Sex Dietary concentration (ppm)<br />

0 0 20 150 1500<br />

Am<strong>in</strong>opyr<strong>in</strong>e N-demethylase activity M 15.3 17.1 17.6 (8) 17.1 (4) 20.9 (7)<br />

(μmol formaldehyde/h per g liver) F 9.8 11.0 (5) 11.4 10.9 16.1**<br />

Smooth endoplasmic reticulum proliferation§ M 141 (7) 127 (7) 138 (7) 132 156*<br />

F 104 (7) 119 (5) 113 (5) 135** 137**<br />

From Milburn et al. (1982a)<br />

F, female; M, male.<br />

a<br />

Means based on six observations per group unless otherwise <strong>in</strong>dicated by the number <strong>in</strong> parentheses.<br />

b<br />

Figures represent the number of analysis po<strong>in</strong>ts <strong>in</strong> a 320-po<strong>in</strong>t analysis grid co<strong>in</strong>cid<strong>in</strong>g with smooth endoplasmic<br />

r eticulum.<br />

Benign neur<strong>in</strong>omas of the heart were identified <strong>in</strong> one, one, and two male rats at 20, 150 and<br />

1500 ppm, respectively. This type of tumour is not normally reported for Wistar rats, but given the<br />

flat dose–response relationship over a wide range, it is unlikely that these tumours arose as a result of<br />

treatment. Overall, there were no treatment-related neoplastic changes.<br />

The NOAEL was 150 ppm, equivalent to 7.5 mg/kg bw per day, on the basis of cl<strong>in</strong>ical signs and<br />

decreased body-weight ga<strong>in</strong> at 1500 ppm, equivalent to 75 mg/kg bw per day (Milburn et al., 1982a).<br />

2.4 Genotoxicity<br />

A battery of tests was conducted to determ<strong>in</strong>e the genotoxic potential of cypermethr<strong>in</strong> <strong>in</strong> v itro and<br />

<strong>in</strong> vivo (Table 7). The weight of evidence of the results <strong>in</strong>dicated that cypermethr<strong>in</strong> is not g enotoxic.<br />

Table 7. Results of studies of genotoxicity with cypermethr<strong>in</strong><br />

End-po<strong>in</strong>t Test object Concentration Purity (%) Results Reference<br />

In vitro<br />

Reverse mutation<br />

(Ames)<br />

S. typhimurium<br />

TA1538; E. coli WP2 uvrA<br />

0–500 μg/plate a NR c Negative Brooks (1976)<br />

Reverse mutation<br />

(Ames)<br />

Mitotic gene<br />

conversion<br />

Comet assay<br />

In vivo<br />

Chromosomal<br />

aberration<br />

Host-mediated<br />

assay<br />

S. typhimurium<br />

TA98, TA100, TA1535,<br />

TA1537, TA1538<br />

0–1000 μg/plate b NR c Negative Suzuki (1977)<br />

S. cerevesiae NR ac NR c Negative Brooks (1976)<br />

Human peripheral<br />

lymphocytes<br />

Ch<strong>in</strong>ese hamster<br />

Mouse/S. cerevesiae<br />

10, 50, 100, 200 μg/ml <strong>in</strong><br />

DMSO<br />

97.1 Positive f Undeger &<br />

Basaran (2005)<br />

0, 20, 40 mg/kg bw per<br />

day for 2 days orally <strong>in</strong><br />

DMSO d NR c Negative Dean (1977)<br />

0, 25, 50 mg/kg bw s<strong>in</strong>gle NR c Negative Brooks (1976)<br />

oral dose; killed 5 h after<br />

<strong>in</strong>traperitoneal <strong>in</strong>jection of<br />

suspension of S. cerevesiae<br />

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

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