Effects of pre- and postnatal exposure to the UV-filter Octyl Methoxycinnamate (OMC) on the reproductive, auditory and neurological development of rat offspring
Introduction
The UV-filter Octyl Methoxycinnamate (OMC), also known as Ethylhexyl Methoxycinnamate, is a very frequently used chemical in sunscreens and cosmetics worldwide. OMC is absorbed though the skin and is detectable in human blood and urine samples after topical application (Janjua et al., 2004). OMC has also been found in milk samples of women who have used OMC containing products (Schlumpf et al., 2008a), which indicates that humans are systemically exposed to this compound. Findings in several studies indicate that the substance acts as an endocrine disruptor (Schlumpf et al., 2001, Schlumpf et al., 2008b, Schmutzler et al., 2004, Seidlova-Wuttke et al., 2006, Klammer et al., 2007).
Some in vitro studies have shown OMC to act as an estrogenic compound, as it enhanced proliferation of breast cancer cells (Schlumpf et al., 2001) and activated transcription in human cell lines via the estrogen receptor (Schreurs et al., 2002, Gomez et al., 2005). In an ecotoxicology study, Inui et al. (2003) demonstrated that in male medaka, OMC caused increased production of vitellogenin, a classical marker of estrogenic action in fish. In several studies in rats, OMC exposure has lead to increased uterine weight. This has been observed in an uterotropic test with immature female rats after 4 days of dosing with 1035 mg OMC/kg bw/day (Schlumpf et al., 2001), in ovariectomized (OVX) adult rats treated for 5 days with 1000 mg OMC/kg bw/day (Klammer et al., 2005), and in OVX rats fed OMC for 12 weeks, at a dose of approximately 1100 mg/kg bw/day (Seidlova-Wuttke et al., 2006). These results indicate that OMC possesses estrogenic activity, as estradiol causes similar effects on uterine weight. However, OMC also significantly increased serum LH levels (Seidlova-Wuttke et al., 2006) and upregulated expression of the estrogen receptor beta (Klammer et al., 2005) which are effects opposite those observed after estradiol treatment. Thus, OMC seems to exert both estrogenic and estrogen-independent activities in vivo.
In a large two-generation study, pregnant dams were treated with OMC in doses of 150, 450 or 1000 mg/kg bw/day in the feed. Exposure began before mating and continued throughout gestation, lactation, adolescence, mating of the F1 generation and until weaning of the F2 generation. Exposure caused no adverse effects on reproduction and development. The authors concluded that OMC displayed no estrogenic potential in vivo (Schneider et al., 2005), but no behavioral or thyroid endpoints were included in this study.
There is however good reason to assume that OMC does interfere with the hypothalamo-pituitary-thyroid (HPT) axis, and therefore could also affect brain development. Schmutzler et al. (2004) found that treatment of OVX rats for 12 weeks with 1100 mg OMC/kg bw/day, reduced thyroxine (T4) levels in the blood as well as activity of 5′-deiodinase (the enzyme that converts T4 to triiodothyronine (T3)) in the liver. Reduction of deiodinase activity in peripheral tissues is also one of the mechanisms by which the potent anti-thyroid drug Propylthiouracil (PTU) exerts its effects (Cavalieri and Pitt-Rivers, 1981, Leonard and Rosenberg, 1978, Visser et al., 1979). Decreased T4 levels were also observed in OVX rats treated with 200 and 1100 mg OMC/kg bw/day for 12 weeks, although a statistically significant effect was only observed in the low dose group (Seidlova-Wuttke et al., 2006). In OVX females treated with 10, 33, 100, 333 or 1000 mg OMC/kg/day for 5 days, the two highest doses also reduced T4 levels in serum and deiodinase activity in the liver (Klammer et al., 2007).
Altogether, many studies indicate that OMC possesses endocrine disrupting properties, and especially the reductions in T4 levels seem consistent across studies. The aim of the present study was to address the potential endocrine disrupting properties of OMC on the developing reproductive and thyroid hormone systems, and to investigate how OMC induced changes in thyroid hormone levels would be related to the neurological development of the offspring. Altered hormone levels during shorter periods of adulthood may not lead to adverse effects, but during early pre- and postnatal development, such alterations can affect both the physiological and neurological development of the offspring, as developmental hypothyroidism can cause delayed development, reduced growth, hearing loss and persistent neurobehavioral effects, in both experimental animals and humans (Zoeller and Crofton, 2005, Miller et al., 2009, Pop et al., 1999, Haddow et al., 1999). Previously our group has shown that hearing loss, hyperactivity and impaired maze learning in rats could be directly correlated to decreases in early developmental T4 levels—when these decreases were induced by developmental exposure to the anti-thyroid drug PTU (Axelstad et al., 2008). In order to gain more knowledge on how hypothyroxinemia in the pre- and postnatal period is related to subsequent neurotoxicity in rats, when caused by an environmentally relevant chemical with more possible modes of action, we wanted to examine if correlations between reduced T4 levels and altered behavior would also exist after developmental OMC exposure.
Section snippets
Test compound
The test compound was 2 Ethylhexyl 3-(4-Methoxyphenyl)-2 Propenoate, also called 2-ethylhexyl-4-methoxycinnamate or simply Octyl Methoxycinnamate (OMC). CAS no 5466-77-3, product number ACR291160250, purity 98.0% (VWR Bie & Berntsen, Herlev, Denmark). Corn oil (VWR Bie & Berntsen, Herlev, Denmark) was used as vehicle.
Animals and treatment
The animal studies were performed under conditions approved by the Danish Agency for Protection of Experimental Animals and by the Inhouse Animal Welfare Committee. Seventy-two
Pregnancy data and postnatal growth
Maternal body weight gain was significantly reduced during the gestation period in the OMC exposed groups (Table 1). Body weight gains from GD 7 to the day before birth (GD 21) were significantly lowered in the two highest dose groups compared to controls (p = 0.032 and p = 0.0004). When adjusted for weight and number of offspring (BW gain GD 7-PND 1), the effect on maternal weight gain was even more marked and statistically significantly different from controls in all three dose groups (p = 0.0092, p
Discussion
In the present study, pre- and postnatal OMC exposure was associated with changes in both reproductive and thyroid hormone levels, and altered development of some reproductive organs, semen quality as well as some behavioral endpoints.
Table 6 summarizes the endpoints that were significantly affected by OMC treatment. Serum T4 levels in dams were almost completely reduced on both GD 15 and PND 15, while T4 levels in the offspring were only reduced about 30% in the males, and were unaffected in
Acknowledgments
We thank Dorte Hansen, Lillian Sztuk, Bo Herbst, Sarah Simonsen, Kenneth Worm, Heidi Letting, Birgitte Møller Plesning, Vibeke Kjær, Ulla El-Baroudy and Gitte Bondegaard Kristiansen for their excellent technical assistance in the conduct of the study.
The financial support from the Danish Environmental Protection Agency is gratefully acknowledged.
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