This work was supported by the FINEP research grant “Rede Instituto Brasileiro de Neurociência (IBN-Net)” # 01.06.0842-00 and the INCT for Excitotoxicity and Neuroprotection – MCT/CNPq. J.B.T.R and F.A.A.S. receive a fellowship from CNPq and Guilherme Pires Amaral, Rômulo Pillon Barcelos, Fernando Dobrashinski receive a fellowship from CAPES. Additional support was provided by FAPERGS. “
“Triclocarban (3,4,4′-trichlorocarbanilide, TCC) is an antimicrobial agent commonly added to detergents and personal

hygiene products including liquid soaps or soap bars. Apart from its diphenylurea moiety TCC is structurally similar to other widely used antimicrobials such as triclosan (TCS) and hexachlorophene (HCP) (Fig. 1). The Navitoclax mw use in soaps results in direct human exposure. Liquid soaps contain up to 1.5% of TCC (SCCP, 2005) and for a single shower the absorption of TCC is estimated to be 0.6% (Schebb et al., 2011). Based

on an average use of 20 g of soap per shower TCC can therefore be expected to reach concentrations CAL-101 molecular weight of approximately 1 μM in the blood stream. This was recently confirmed in a study with human volunteers, where the use of TCC containing soap resulted in half-maximal blood concentrations of up to 530 nM (Schebb et al., 2012). Moreover, in the US its ubiquitous use has led to concentrations as high as 6.8 μg/l in environmental water samples (Halden and Paull, 2005). As a halogenated hydrocarbon TCC is hardly biodegradable (Aken et al., 2010, Furukawa and Fujihara, 2008 and Solyanikova and Golovleva, 2004) and subsequent levels in sewage sludge easily exceed 50 mg/kg (Heidler et al., 2006). In combination with the frequent use

of sewage as fertiliser the poor biodegradability thus further adds to human exposure (Wu et al., 2012). The high levels of TCC in water and sewage have raised concerns because TCC has been shown to amplify estrogenic and androgenic responses in cell-based reporter assays (Ahn et al., 2008). Androgenic effects Glycogen branching enzyme were also observed in vivo. In castrated rats the co-administration of TCC and testosterone resulted in higher weights of sex accessory organs ( Chen et al., 2008). Respective hyperplasias were also found in juvenile animals after they had been treated with TCC ( Duleba et al., 2011). Meanwhile the estrogenic effects of TCC in vivo are less well investigated. In zebrafish coexposure to 17β-estradiol (E2) and TCC enhanced the transcriptional induction of aromatase AroB, while the combination of TCC with the xenoestrogen bisphenol A (BPA) led to reduced expression of aroB ( Chung et al., 2011). Estrogens exert their effects mainly via two nuclear receptors, that is estrogen receptor alpha (ERα) and beta (ERβ). Following cognate ligand binding these transcription factors dimerise and bind to specific estrogen response elements (EREs) at the DNA, where subsequent recruitment of co-activators induces target gene expression (Heldring et al., 2007).