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Epidemiological association studies have revealed a role for pesticides in cancer occurrence, while a growing number of reports have highlighted the deleterious epigenetic modifications that can be produced by environmental factors. However, epidemiological data currently lack molecular support to unravel the epigenetic impact of pesticides on carcinogenesis. Based on epidemiological studies of melanoma, our data show for the first time that trans-nonachlor (TNC), a component of the pesticide chlordane, modulates the microRNA miR-141-3p in human melanocytic cells in vitro, with effects on melanomagenesis parameters. TNC downregulates the level of miR-141-3p in normal melanocytes to levels found endogenously in several melanoma cell lines. Ectopic expression of either a synthetic miRNA mimic or inhibitor in human melanocytic cells revealed that TNC counteracts the inhibitory effects of miR-141-3p on melanoma cell anchorage-independent growth ability, their invasive potential, and expression of a multipotent, embryonic-like, aggressive cancer phenotype (termed vasculogenic mimicry), involving VE-Cadherin. In addition, the data suggest that miR-141-3p regulates vasculogenic mimicry through extracellular signal-regulated kinase 1/2 (ERK1/2) and phosphatidyl inositol-3-kinase (PI3K). Notably, in the Drosophila animal model, TNC also decreased the level of miR-8, the sole miR-141-3p fly ortholog. Importantly, the downregulation of miR-8 levels induced by TNC in ancestors was transmitted through multigenerations, with a progressive reversion over time. Such a decrease in miR-8 levels translated to a loss-of-weight phenotype in offspring. Providing support to epidemiological data, these results altogether suggest that TNC may favor melanomagenesis by lowering the levels of miR-141-3p, thereby activating melanoma cell processes. Although any such conclusions in humans are yet to be determined, these experiments in Drosophila demonstrate that TNC can promote an epigenetic multigenerational inheritance of the miR-141-3p/miR-8 defect. This study therefore justifies the development of molecular investigations to decipher the toxic epigenetic heritable impact of pesticides on cancer occurrence., (Copyright © 2016 Elsevier Ireland Ltd. All rights reserved.)

Humans are chronically exposed to multiple exogenous substances, including environmental pollutants, drugs and dietary components. Many of these compounds are suspected to impact human health, and their combination in complex mixtures could exacerbate their harmful effects. Here we demonstrate that a pharmaceutical oestrogen and a persistent organochlorine pesticide, both exhibiting low efficacy when studied separately, cooperatively bind to the pregnane X receptor, leading to synergistic activation. Biophysical analysis shows that each ligand enhances the binding affinity of the other, so the binary mixture induces a substantial biological response at doses at which each chemical individually is inactive. High-resolution crystal structures reveal the structural basis for the observed cooperativity. Our results suggest that the formation of 'supramolecular ligands' within the ligand-binding pocket of nuclear receptors contributes to the synergistic toxic effect of chemical mixtures, which may have broad implications for the fields of endocrine disruption, toxicology and chemical risk assessment.

Chronic exposure to low doses of pesticides present in the environment is increasingly suspected to cause major health issues to humans. Toxicological evaluations become more complex when the exposure concerns chemical combinations. Atrazine, chlorpyrifos, and endosulfan are pesticides used worldwide in agriculture and are therefore currently found at residual levels in food and the environment, even in countries in which they are now banned. Our study aimed to use Real-Time Cell Impedance Analyzer to investigate changes in phenotypical status of primary human hepatocytes and differentiated HepaRG cells induced by short and chronic exposures to these three chemicals. In contrast to the traditionally used endpoint cytotoxicity test, this technology allows kinetic measurements in real-time throughout the entire experiment. Our data show significantly higher cytotoxic effects of mixtures as compared to individual pesticides and a greater susceptibility of human hepatocytes as compared to HepaRG to short-term exposure (24 h). Repeated exposure over 2 weeks to endosulfan and endosulfan-containing mixture induced HepaRG cell death in a time- and dose-dependent manner. Of the typical genes involved in metabolism and cell-response to xenobiotics, we found an exposure time- and condition-dependent deregulation of the expression of CYP3A4 and UGT1A in HepaRG cells exposed to low doses of pesticides and mixtures. Our data demonstrate the usefulness of real-time cell monitoring in long-term toxicological evaluations of co-exposure to xenobiotics. In addition, they support but at the same time highlight certain limitations in the use of HepaRG cells as the gold standard liver cell model in toxicity studies.

Endosulfan is an organochlorine pesticide commonly used in agriculture yet classified by the Stockholm Convention in 2011 as a persistent organic pollutant (POP). Its potential toxicity makes its continued use a major public health concern. Despite studies in laboratory animals, the molecular mechanisms underlying the carcinogenic effects of endosulfan in human liver remain poorly understood. In this study, we investigated the phenotypical effects of endosulfan on HepG2 liver cells. First, we found that endosulfan disrupted the anoikis process. Indeed, cells exposed to endosulfan were initially sensitized to anoikis and thereafter recovered their resistance to this process. This phenomenon occurred in parallel to the induction of the epithelial to mesenchymal (EMT) process, as demonstrated by: (1) reorganization of the actin cytoskeleton together with activation of the FAK signaling pathway; (2) repression of E-cadherin expression; (3) induction of Snail and Slug; (4) activation of the WNT/β-catenin pathway; and (5) induction and reorganization of mesenchymal markers (S100a4, vimentin, fibronectin, MMP-7). Secondly, despite the acquisition of mesenchymal characteristics, HepG2 cells exposed to endosulfan failed to migrate. This incapacity to acquire a motile phenotype could be attributed to a disruption of the interaction between the ECM and the cells. Taken together, these results indicate that endosulfan profoundly alters the phenotype of liver cells by inducing cell detachment and partial EMT as well as disrupting the anoikis process. All these events account, at least in part, for the carcinogenic potential of endosulfan in liver., (Copyright © 2012 Elsevier Ireland Ltd. All rights reserved.)

Lindane, a persistent organochlorine pesticide, is recognized as a major public health concern because of its potential toxic effects on human health. Despite observations pointing to the toxicity of lindane, mechanisms underlying its deleterious effects in liver have yet to be understood. In this study, we investigated the effects of lindane on autophagic, apoptotic and necrotic cell death in primary cultured rat hepatocytes. We found that lindane deregulated the autophagic process as demonstrated by (1) the formation of enlarged acidic vesicles labeled with LC3, Rab7 and LAMP1 (specific markers of autophagic vacuole maturation), (2) the conversion of LC3-I (the cytosolic form) into LC3-II (membrane bound), (3) the deregulation of the Beclin 1 protein expression and (4) the enhanced formation of the Bcl-xL/Beclin 1 complex. Lindane induced vacuolization together with the inhibition of spontaneous and intrinsic apoptosis. This disruption of cell suicide was linked to Bcl-xL up-regulation, Bax down-expression, prevention of cytochrome c release, and inhibition of caspase-9 and -3 activities. Lindane-induced disruption of apoptosis and autophagy occurred in parallel with necrosis induction in rat hepatocytes. In consequence, we proposed that lindane toxicity in primary rat hepatocytes could be jointly attributed to the disruption of autophagic process, the inhibition of apoptotic cell death and the induction of necrosis. These events account, at least in part, for the involvement of both cytotoxic and carcinogenic signaling pathways in the action of lindane in the liver.

Organochlorine pesticides (OCs) are reported as potential carcinogens in humans. The aim of this study was to investigate the effects of four OCs (dieldrin, endosulfan, heptachlor, and lindane) on mitogen-activated protein kinase (MAPK) cascades and more specifically to identify the mechanism underlying OC-induced ERK1/2 activation. Organochlorine pesticides increased phosphorylated Raf, MEK1/2, ERK1/2, and c-Jun in human HaCaT cells, but they had no effect on p38 MAPK activation. Moreover, blockade of Raf, MEK1/2, or PKC activation with geldanamycin, U0126, or calphostin C inhibited ERK1/2 phosphorylation, demonstrating a PKC-Raf-MEK1/2 pathway. We also showed that these insecticides induced the production of reactive oxygen species (ROS). Pre-treatment with the antioxidant molecule N-acetyl cysteine sharply decreased the level of phospho-ERK1/2 and had no effect on Raf and MEK1/2 activation, suggesting a Raf-independent mechanism. This study indicates that OCs strongly activate the ERK1/2 pathway, and it identifies a critical role of ROS in OC-induced ERK activation, probably by stabilizing its phosphorylation.

Five organochlorine pesticides, namely, chlordane, dieldrin, aldrin, endrin, and endosulfan, activate human retinoic acid receptor (RAR)-mediated gene transcription via a retinoic acid response element (RARE). Transactivation studies were performed with stable RARalpha, beta, or gamma reporter cell lines in which the RAR DNA-binding domain (DBD) was replaced by that of estrogen receptor alpha (ERalpha)? Five of the organochlorine pesticides tested activated RARbeta and RARgamma but not RARalpha; their half-maximal luciferase activity (EC(50)) was determined. Furthermore, that activity was RAR-specific and organochlorine pesticides did not activate the retinoid X receptor (RXR) pathway. However, competitive binding experiments with [(3)H]-CD367, a pan-RAR agonist, showed that only chlordane could bind RARbeta and RARgamma, albeit with low affinity. In addition, organochlorine pesticides strongly induce cytochrome P450RAI1 (P450RAI1), a key factor of retinoic acid level regulation in many tissues and whose expression and activity are strongly induced by retinoic acid. This study shows that organochlorine pesticides can activate two RAR homologues, with low-binding affinity. Although the agonistic potential of organochlorine pesticides is lower than that of (E)-4-[2-(5,6,7,8-tetrahydro-5,5,8,8-tetramethyl-2-naphthalenyl)-1-propenyl] benzoic acid (TTNPB), they are able to induce RAR-mediated gene transcription as P450RAI1 and may disrupt the retinoid signaling pathway. Because these chemicals are extremely persistent and tend to accumulate in biological tissues, these results support the hypothesis that the increase in teratogenicity observed in some developing countries could be due to prolonged exposure to organochlorine pesticides ubiquitously present in the environment.

In vivo distribution of the neonicotinoid insecticide, imidacloprid, was followed during 72 h in six biological compartments of Apis mellifera L: head, thorax, abdomen, haemolymph, midgut and rectum. Honeybees were treated orally with 100 microg of 14C-imidacloprid per kg of bee, a dose close to the median lethal dose. Elimination half-life of total radioactivity in honeybee was 25 h. Haemolymph was the compartment with the lowest and rectum that with the highest level of total radioactivity during the whole study, with a maximum 24h after treatment. Elimination half-life of imidacloprid in whole honeybee was 5 h. Imidacloprid was readily distributed and metabolised only by Phase I enzymes into five metabolites: 4/5-hydroxy-imidacloprid, 4,5-dihydroxy-imidacloprid, 6-chloronicotinic acid, and olefin and urea derivatives. The guanidine derivative was not detected. The urea derivative and 6-chloronicotinic acid were the main metabolites and appeared particularly in midgut and rectum. The olefin derivative and 4/5-hydroxy-imidacloprid preferentially occurred in head, thorax and abdomen, which are nicotinic acetylcholine receptor-rich tissues. Moreover, they presented a peak value around 4 h after imidacloprid ingestion. These results explain the prolongation of imidacloprid action in bees, and particularly the differences between rapid intoxication symptoms and late mortality.

Many persistent organochlorine pesticides (OCs) have been implicated in adverse effects, that is, reproductive and developmental effects, in man and in wildlife alike. It has been hypothesized that these so-called xeno-hormones could be responsible for the increased incidence in various male sexual differentiation disorders such as hypospadias, cryptorchidism, low sperm counts and quality. In this report, OCs, called endocrine disrupters, were tested for their interaction with the androgen receptor. The stable prostatic cell line PALM, which contains a human androgen receptor (hAR) expression vector and the reporter MMTV-luciferase, was used to characterize the response of hAR to OC and was compared with synthetic androgen compound R1881. We found that all the OC pesticides tested were able to shift the agonist [(3)H]-R1881 from its binding site to the AR in competitive binding assays. In addition, these compounds antagonize-in a dose-dependent manner-the AR-mediated transcription by synthetic AR ligand R1881. None of the pesticides reacted as agonists. These results demonstrate that OC endocrine activities in vivo probably result from direct and specific binding to the AR ligand-binding domain. Although the antagonistic potential of OC pesticides is lower than that of hydroxyflutamide, they are capable of disrupting the male hormone signaling pathway. Because these chemicals are extremely persistent and tend to bioaccumulate, these results support the hypothesis that the recent increase in the incidence of male sexual disorders could be due to long exposure to ubiquitous OC pesticides found in the environment.

Endosulfan is an organochlorine insecticide described as a potential carcinogen in humans. This insecticide was recently reported to alter the mitogen-activated protein (MAP) kinase signaling pathways and is suspected to affect cell growth and differentiation in human keratinocytes. This study was designed to assess the mitogenic, apoptogenic, and genotoxic effects of endosulfan on the HaCaT cell line. We first found that 25 µM endosulfan led to persistent extracellular signal-regulated kinase (ERK)1/2 phosphorylation with an accumulation of the phosphorylated form in the nucleus, probably caused by MAP kinase phosphatase (MKP) inhibition. As previously described under sustained ERK1/2 activation, cell growth was decreased: delayed confluency and 35% decrease of BrdU incorporation was demonstrated in endosulfan-treated keratinocytes. In addition, endosulfan has been shown to generate transient reactive oxygen species (ROS), and blocking this oxidative stress by N-acetyl cysteine (NAC) strongly prevented both persistent nuclear ERK1/2 phosphorylation and cell growth decrease. Additional experiments demonstrated that unchanged endosulfan rather than its metabolites has mutagenic effects (Ames positive without S9) and increased DNA strand breaks (Comet assay) in HaCaT cells, via a ROS-dependent mechanism. Therefore, to assess the putative pro-apoptotic response of damaged cells, caspases 3/7 activity and poly(ADP-ribose)-polymerase (PARP) cleavage were measured. The results clearly indicated that endosulfan inhibited both spontaneous and staurosporine-induced apoptosis. Taken together, these findings strongly support that endosulfan induces ROS generation leading to sustained ERK1/2 phosphorylation and decrease in cell growth. Moreover, endosulfan was found to inhibit apoptosis and this could contribute to mutant cell survival and therefore have possible carcinogenic effects. J. Cell. Physiol. 213: 177–186, 2007. © 2007 Wiley-Liss, Inc. [ABSTRACT FROM AUTHOR]

In vivo distribution of the neonicotinoid insecticide, imidacloprid, was followed during 72 h in six biological compartments of Apis mellifera L: head, thorax, abdomen, haemolymph, midgut and rectum. Honeybees were treated orally with 100 µg of 14C-imidacloprid per kg of bee, a dose close to the median lethal dose. Elimination half-life of total radioactivity in honeybee was 25 h. Haemolymph was the compartment with the lowest and rectum that with the highest level of total radioactivity during the whole study, with a maximum 24 h after treatment. Elimination half-life of imidacloprid in whole honeybee was 5 h. Imidacloprid was readily distributed and metabolised only by Phase I enzymes into five metabolites: 4/5-hydroxy-imidacloprid, 4,5-dihydroxy-imidacloprid, 6-chloronicotinic acid, and olefin and urea derivatives. The guanidine derivative was not detected. The urea derivative and 6-chloronicotinic acid were the main metabolites and appeared particularly in midgut and rectum. The olefin derivative and 4/5-hydroxy-imidacloprid preferentially occurred in head, thorax and abdomen, which are nicotinic acetylcholine receptor-rich tissues. Moreover, they presented a peak value around 4 h after imidacloprid ingestion. These results explain the prolongation of imidacloprid action in bees, and particularly the differences between rapid intoxication symptoms and late mortality. [ABSTRACT FROM AUTHOR]