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

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373<br />

b<br />

Each test was conducted <strong>in</strong> triplicate.<br />

c<br />

Two separate experiments were conducted.<br />

d<br />

S9 was prepared from livers of Sprague Dawley rats pre-treated with polychlor<strong>in</strong>atedbiphenyl mixture..<br />

e<br />

S9 was prepared from livers of Sprague Dawley rats pre-treated with phenobarbital and β-naphthoflavone.<br />

f<br />

The study was performed <strong>in</strong> compliance with good laboratory practice and accord<strong>in</strong>g to United States Environmental<br />

Protection Agency (EPA) study guidel<strong>in</strong>e 84-2.<br />

g<br />

One hundred cells from duplicate cultures were analysed at 10 and 18 h after treatment.<br />

h<br />

Fifty metaphases were analysed at each concentration.<br />

i<br />

Three replicates of 50 cells were analysed <strong>in</strong> each experiment.<br />

j<br />

Hepatocytes were prepared from Sprague-Dawley rats; at each concentration, six replicates of 50 cells were analysed.<br />

k<br />

Six mice were treated for 6, 24 and 48 h after <strong>in</strong>traperitoneal adm<strong>in</strong>istration; 50 metaphases <strong>in</strong> bone-marrow cells were<br />

analysed for each mouse.<br />

l<br />

Six mice were treated at each concentration.<br />

were based on a prelim<strong>in</strong>ary study that showed decreased litter size and fem<strong>in</strong>ization of male pups<br />

at ≥ 1000 ppm. After 12 weeks, the rats were mated and allowed to rear the F 1a<br />

litters to wean<strong>in</strong>g and<br />

then paired aga<strong>in</strong> to produce the F 1b<br />

litters. F 1<br />

parents selected from the F 1a<br />

litters were mated to produce<br />

two further litters (F 2a<br />

and F 2b<br />

). Body weight, <strong>food</strong> <strong>in</strong>take and cl<strong>in</strong>ical condition were recorded<br />

weekly. Reproductive parameters (fertility, length of gestation, precoital <strong>in</strong>terval, litter size, viability<br />

and number of live and dead pups) were recorded for each generation and litter. The parental rats<br />

were given a postmortem, the liver and reproductive organs were weighed and tissues were exam<strong>in</strong>ed<br />

histopathologically. Cl<strong>in</strong>ical observations, body weights, organ weights and pathology f<strong>in</strong>d<strong>in</strong>gs were<br />

also recorded for the offspr<strong>in</strong>g. Additional pathological exam<strong>in</strong>ations were performed subsequently<br />

and were reported <strong>in</strong> addenda.<br />

Achieved <strong>in</strong>takes of procymidone throughout the study were not tabulated; data for premat<strong>in</strong>g<br />

periods only were presented <strong>in</strong> Wickramaratne & Milburn (1990), but actual concentrations, stability<br />

and homogeneity <strong>in</strong> diet were confirmed as acceptable. All parental rats at the highest dose showed<br />

reductions <strong>in</strong> body-weight ga<strong>in</strong> from the start of compound adm<strong>in</strong>istration; statistically significant<br />

for F o<br />

rats of both sexes and F 1<br />

and F 2<br />

females. There were no consistent effects on body weight or<br />

body-weight ga<strong>in</strong> at 250 ppm. Precoital <strong>in</strong>terval was generally reduced <strong>in</strong> pair<strong>in</strong>gs at 750 ppm. In F 1<br />

males at the highest dose (but not F o<br />

), there was a significant reduction <strong>in</strong> fertility (Table 20), associated<br />

with hypospadias (Table 20). Relative liver and relative testes weights were <strong>in</strong>creased at 250 and<br />

750 ppm (Table 20). The duration of gestation was similar <strong>in</strong> all groups. Litter size was reduced <strong>in</strong> the<br />

F 1b<br />

mat<strong>in</strong>g at 750 ppm, but not <strong>in</strong> any other mat<strong>in</strong>gs. Penile abnormalities were noted at both gross<br />

and microscopic exam<strong>in</strong>ations <strong>in</strong> rats at 750 ppm. No effects were observed on sperm parameters.<br />

Sex<strong>in</strong>g pups at birth was made difficult by reductions <strong>in</strong> anogenital distance (qualitative assessment)<br />

<strong>in</strong> male offspr<strong>in</strong>g at 750 ppm. Liver weight and testes-weight f<strong>in</strong>d<strong>in</strong>gs <strong>in</strong> parents were repeated <strong>in</strong><br />

offspr<strong>in</strong>g; the <strong>in</strong>crease <strong>in</strong> testes weights at 50 ppm <strong>in</strong> the F 1b<br />

pups was < 10%, and not statistically<br />

significant <strong>in</strong> the F 2b<br />

pups and was not considered to be adverse. Reductions <strong>in</strong> weights of the prostate<br />

and epididymis were seen at 250 ppm (F 1b<br />

) and 750 ppm (Table 20). There were no adverse effects<br />

on the sex organs of female pups.<br />

The NOAEL for pup development was 50 ppm, equivalent to 3 mg/kg bw per day, on the basis<br />

of alterations <strong>in</strong> testes, prostate and epididymis weights at 250 ppm. The NOAEL for reproductive<br />

effects was 250 ppm, equivalent to 17 mg/kg bw per day, on the basis of reduced male fertility at<br />

750 ppm. The NOAEL for parental toxicity was 250 ppm on the basis of reduced body weights at<br />

750 ppm. The study was <strong>in</strong>spected by a quality assurance unit and complied with OECD test guidel<strong>in</strong>e<br />

416 (1983) (Wickramaratne et al., 1988a; Milburn & Moreland, 1991).<br />

A modified study of reproduction <strong>in</strong> rats was performed to provide <strong>in</strong>formation on the development<br />

of reproductive organs of F 1<br />

males aged 5 weeks and at sexual maturity (aged 10 weeks). Groups<br />

of 26 male and 26 female Alpk:APfSD (Wistar-derived) rats received diets conta<strong>in</strong><strong>in</strong>g procymidone<br />

(purity, 98.7–99.1%) at a constant dose equal to 0, 2.5, 12.5 or 37 mg/kg bw per day throughout the<br />

PROCYMIDONE 349–401 JMPR <strong>2007</strong>

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