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

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110<br />

supported by a number of short-term mechanistic studies. Additional experiments suggested that the<br />

effects of atraz<strong>in</strong>e on LH and prolact<strong>in</strong> secretion are mediated via a hypothalamic site of action.<br />

The postulated mode of action for atraz<strong>in</strong>e-<strong>in</strong>duced mammary tumours <strong>in</strong> female Sprague-<br />

Dawley rats <strong>in</strong>volved disruption of the hypothalamic–pituitary–ovary axis. Atraz<strong>in</strong>e modifies<br />

catecholam<strong>in</strong>e function and the regulation of GnRH pulsatility <strong>in</strong> the rat hypothalamus, with the<br />

consequence that the pulse of LH released from the pituitary gland is of <strong>in</strong>sufficient amplitude or<br />

duration to trigger the ovulation. The failure to ovulate results <strong>in</strong> persistent secretion of estrogen,<br />

which provides a feedback to the pituitary lead<strong>in</strong>g to <strong>in</strong>creased secretion of prolact<strong>in</strong>. As a result,<br />

atraz<strong>in</strong>e accelerates the normal reproductive age<strong>in</strong>g process <strong>in</strong> female Sprague-Dawley rats whereby<br />

reproductive senescence is characterized by persistent exposure to estrogen and prolact<strong>in</strong>. In contrast,<br />

women respond to reduced levels of LH by reductions <strong>in</strong> estrogen concentrations. Thus, the Meet<strong>in</strong>g<br />

considered that the mode of carc<strong>in</strong>ogenic action <strong>in</strong> certa<strong>in</strong> susceptible rat stra<strong>in</strong>s is not relevant for<br />

risk assessment <strong>in</strong> humans.<br />

Investigations of other modes of action did not provide any evidence that atraz<strong>in</strong>e had <strong>in</strong>tr<strong>in</strong>sic<br />

estrogenic activity or that it <strong>in</strong>creased aromatase activity <strong>in</strong> vivo.<br />

The Meet<strong>in</strong>g concluded that atraz<strong>in</strong>e is not likely to pose a carc<strong>in</strong>ogenic risk to humans.<br />

Although carc<strong>in</strong>ogenicity <strong>in</strong> humans was not a concern ow<strong>in</strong>g to the rat-specific mode of action,<br />

alterations <strong>in</strong> neurotransmitter and neuropeptide function regulat<strong>in</strong>g LH and secretion of prolact<strong>in</strong><br />

may potentially <strong>in</strong>duce adverse effects dur<strong>in</strong>g critical periods of development (as found <strong>in</strong> special<br />

studies show<strong>in</strong>g pregnancy loss, delayed puberty <strong>in</strong> males and females, and decreased suckl<strong>in</strong>g-<strong>in</strong>duced<br />

prolact<strong>in</strong> release <strong>in</strong> lactat<strong>in</strong>g dams). Unlike the carc<strong>in</strong>ogenic effects, the developmental effects<br />

do not appear to be specific to certa<strong>in</strong> stra<strong>in</strong>s of rats and the Meet<strong>in</strong>g therefore considered these<br />

effects to be relevant for risk assessment <strong>in</strong> humans.<br />

In special studies of reproductive toxicity, exposure of rats dur<strong>in</strong>g early pregnancy (i.e. the LHdependent<br />

period) caused <strong>in</strong>creased pre- or postimplantation losses, <strong>in</strong>clud<strong>in</strong>g full-litter resorptions.<br />

Effects were seen at doses of 50 mg/kg bw per day and greater after treatment on days 6–10 of gestation,<br />

with a NOAEL of 25 mg/kg bw per day. In contrast, exposure on days 11–15 of gestation (after<br />

the LH-dependent period of pregnancy) at a dose of 200 mg/kg bw per day did not <strong>in</strong>duce full-litter<br />

resorptions.<br />

Suppression of the suckl<strong>in</strong>g-<strong>in</strong>duced release of prolact<strong>in</strong> <strong>in</strong> lactat<strong>in</strong>g rats was seen with atraz<strong>in</strong>e<br />

at doses of 25 mg/kg bw per day and greater, with a NOAEL of 12.5 mg/kg bw per day. Treatment<br />

of lactat<strong>in</strong>g rats on postnatal days 1–4 affected the development of tubero<strong>in</strong>fundibular dopam<strong>in</strong>ergic<br />

neurons <strong>in</strong> the pups (presumably due to the lack of prolact<strong>in</strong> derived from the dam’s milk), with the<br />

consequence of impaired regulation of prolact<strong>in</strong> secretion, hyperprolact<strong>in</strong>aemia before puberty and<br />

prostatitis <strong>in</strong> the adult male offspr<strong>in</strong>g.<br />

A delay <strong>in</strong> sexual development was observed <strong>in</strong> female rats after exposure on postnatal days<br />

21–46 at doses of 30 mg/kg bw per day and greater, with a NOAEL of 10 mg/kg bw per day, and <strong>in</strong><br />

male rats after exposure on postnatal days 23–53 at doses of 12.5 mg/kg bw per day and greater, with<br />

a NOAEL of 6.25 mg/kg bw per day.<br />

In a standard two-generation study of reproduction (conducted accord<strong>in</strong>g to earlier guidel<strong>in</strong>es,<br />

which did not <strong>in</strong>clude end-po<strong>in</strong>ts such as estrous cyclicity and sexual development) <strong>in</strong> rats, there<br />

was no effect on fertility at 500 ppm, the highest dose tested. The NOAEL for parental toxicity was<br />

50 ppm, equal to 3.6 mg/kg bw per day, on the basis of decreased body-weight ga<strong>in</strong>s and <strong>food</strong> consumption<br />

at 500 ppm, equal to 36.1 mg/kg bw per day. The NOAEL for reproductive toxicity was<br />

50 ppm on the basis of decreased body weights of male pups at postnatal day 21 at 500 ppm.<br />

In two studies of prenatal developmental toxicity <strong>in</strong> rats given atraz<strong>in</strong>e on days 6–15 of gestation,<br />

the NOAELs for maternal toxicity were 10 or 25 mg/kg bw per day on the basis of decreased<br />

body-weight ga<strong>in</strong> and <strong>food</strong> <strong>in</strong>take at 70 or 100 mg/kg bw per day, respectively. The NOAELs for<br />

ATRAZINE 37–138 JMPR <strong>2007</strong>

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