3-Methylcholanthrene impacts on the female germ cells of rats without causing systemic toxicity.

We have previously shown that daily exposure to the environmental pollutant 3-methylcholanthrene (3MC) alters the ovarian function by affecting follicle growth and ovulation. To extend our findings, the aims of this work were to study the effects of daily and non-daily exposure to 3MC on oocyte morphology and integrity and the meiosis process. To this end, immature female rats were daily (0.1-1.0 mg/kg) and non-daily (0.1 mg/kg, three times a week) exposed to 3MC and/or α-naphthoflavone (αNF) (80 mg/kg) for 19 and 20 days, respectively. The latter was used to study its ability to prevent the 3MC action. Follicular growth was examined by histology, apoptosis by in situ cell death detection, oocyte integrity by morphological parameters and fluorescent dyes, and the meiotic spindle by immunostaining. Compared with controls (C), and in a dose-dependent manner, all 3MC-treated rats showed i) increased presence of apoptotic cells in antral follicles and decreased percentage of healthy oocytes, ii) increased oocyte area, perimeter and perivitelline space and decreased thickness of the zona pellucida, and ii) increased percentage of oocytes with abnormal meiotic spindle. In addition, the non-daily dose of 3MC caused DNA damage in oocytes, but not in blood or bone marrow cells. All 3MC-induced changes were prevented with the co-treatment with αNF. These results suggest that low doses of 3MC severely disrupt the ovarian function and that germ cells seem to be more sensitive to this environmental pollutant than other cells such as peripheral blood and bone marrow cells.

Apoptosis induction and inhibition of HeLa cell proliferation by alpha-naphthoflavone and resveratrol are aryl hydrocarbon receptor-independent.

Human papilloma viruses 16 and 18 express E6 and E7 oncoproteins. E6 activates and redirects E6-associated protein (E6AP), an E3 ubiquitin ligase. E6AP interacts with Ube2l3, an E2 ubiquitin conjugating enzyme protein (also known as UbcH7), to promote p53 ubiquitination and degradation by the 26S proteasome. Therefore, blocking E6-mediated p53 degradation might be an alternative treatment for cervical cancer. In addition, activation of the aryl hydrocarbon receptor (AHR) induces Ube2l3 expression, resulting in p53 ubiquitination and degradation. The aim of the present study was to determine whether inhibition of AHR in HeLa cells resulted in an increase in p53 and apoptosis along with a decrease in cell proliferation. The results demonstrate that two AHR antagonists, α-naphthoflavone (α-NF) and resveratrol, decreased cell proliferation, arrested cells in the gap 1/synthesis (G1/S) phases, and increased p53 levels and apoptosis. However, knocking out the Ahr gene did not abrogate the effects of α-NF and resveratrol. Moreover, Ahr-null cells presented similar cell proliferation rates and apoptosis levels when compared to control HeLa cells. Taken together, the results indicate that α-NF's and resveratrol's cytostatic and cytotoxic actions, respectively, occur through an AHR-independent mechanism, and that AHR is not required for HeLa cell proliferation.

Methylated polycyclic aromatic hydrocarbons and/or their metabolites are important contributors to the overall estrogenic activity of polycyclic aromatic hydrocarbon-contaminated soils.

In the present study 42 polycyclic aromatic compounds (PACs) were investigated for their estrogenic potential using the VM7Luc4E2 transactivation assay. Relative potencies were determined for mass-balance analysis. In addition, compounds were tested in combination with the estrogen receptor (ER) antagonist ICI182,780 (ICI) and the aryl hydrocarbon receptor antagonist/CYP1A1 inhibitor α-naphthoflavone. Luciferase induction and CYP1A1-dependent ethoxyresorufin-O-deethylase (EROD) activity were measured to assess whether the estrogenic activity was elicited by the compound itself and/or by its metabolites. Relative potencies ranged between 10-7 and 10-4 . The ability of ICI to decrease luciferase activity stimulated by all compounds indicated that the induction responses were ER-dependent. The aryl hydrocarbon receptor antagonist/CYP1A1 inhibitor α-naphthoflavone decreased luciferase induction and EROD activity by several compounds, including the methylated chrysenes, suggesting that metabolites of these chemicals contributed to ER activation. Several PACs, such as acridine and its derivatives, appear to directly activate the ER. Furthermore, extracts of soils from industrial areas were examined using this bioassay, and estrogenic activity was detected in all soil samples. Mass-balance analysis using a combination of relative potencies and chemical analysis of the samples suggested that polycyclic aromatic hydrocarbons (PAHs) and alkylated PAHs, such as 1- and 3-methylchrysene, are important contributors to the overall estrogenic activity. However, these results revealed that a considerable proportion of the estrogenic activity in the soil remained unexplained, indicating the presence of other significant estrogenic compounds. Environ Toxicol Chem 2018;37:385-397. © 2017 SETAC.

Application of the TGx-28.65 transcriptomic biomarker to classify genotoxic and non-genotoxic chemicals in human TK6 cells in the presence of rat liver S9.

In vitro transcriptional signatures that predict toxicities can facilitate chemical screening. We previously developed a transcriptomic biomarker (known as TGx-28.65) for classifying agents as genotoxic (DNA damaging) and non-genotoxic in human lymphoblastoid TK6 cells. Because TK6 cells do not express cytochrome P450s, we confirmed accurate classification by the biomarker in cells co-exposed to 1% 5,6 benzoflavone/phenobarbital-induced rat liver S9 for metabolic activation. However, chemicals may require different types of S9 for activation. Here we investigated the response of TK6 cells to higher percentages of Aroclor-, benzoflavone/phenobarbital-, or ethanol-induced rat liver S9 to expand TGx-28.65 biomarker applicability. Transcriptional profiles were derived 3 to 4 hr following a 4 hr co-exposure of TK6 cells to test chemicals and S9. Preliminary studies established that 10% Aroclor- and 5% ethanol-induced S9 alone did not induce the TGx-28.65 biomarker genes. Seven genotoxic and two non-genotoxic chemicals (and concurrent solvent and positive controls) were then tested with one of the S9s (selected based on cell survival and micronucleus induction). Relative survival and micronucleus frequency was assessed by flow cytometry in cells 20 hr post-exposure. Genotoxic/non-genotoxic chemicals were accurately classified using the different S9s. One technical replicate of cells co-treated with dexamethasone and 10% Aroclor-induced S9 was falsely classified as genotoxic, suggesting caution in using high S9 concentrations. Even low concentrations of genotoxic chemicals (those not causing cytotoxicity) were correctly classified, demonstrating that TGx-28.65 is a sensitive biomarker of genotoxicity. A meta-analysis of datasets from 13 chemicals supports that different S9s can be used in TK6 cells, without impairing classification using the TGx-28.65 biomarker.

Aggregation induced emission from α-napthoflavone microstructures and its cyto-toxicity.

α-Napthoflavone (ANF) microstructures of various morphologies were synthesized using reprecipitation method. Sodium Dodecyl Sulfate (SDS) was used as morphology directing agent. The morphologies of the particles were characterized using optical and scanning electron microscopy (SEM). Single crystal data of ANF suggests that the aromatic units of ANF are in parallel slipped conformation in its aggregated form. Photophysical properties of aggregated ANF hydrosol were studied using UV-Vis absorption, steady state and time resolved spectroscopy. Red shift and broadening of UV-Vis spectra of ANF hydrosol are explained due to strong π-π and H-π interactions among the neighboring ANF molecules within the aggregated microstructures. Though ANF is non-luminescent in good solvent, a strong emission is observed in its aggregated state. This aggregation induced emission (AIE) has been explained due to restriction of intramoleculer rotation and large amplitude vibrational modes of ANF in its aggregated state. Our Photophysical study also reveals that AIE effect decreases after an optimum concentration of ANF and this has been explained due to softening of crystal lattice. Cytotoxicity of ANF hydrosol was examined to get an idea of the toxic level of this hydrosol toward cultured normal human cells. It is observed that ANF hydrosol may draw beneficial effect in biological application as it has no higher toxic activity but has antioxidant property.

Individual and joint toxic effects of cadmium sulfate and α-naphthoflavone on the development of zebrafish embryo.

This paper aims to evaluate the individual and joint toxicities of cadmium sulfate (CdSO4) and α-naphthoflavone (ANF) in zebrafish embryos. As a result, CdSO4 caused both lethal and sub-lethal effects, such as 24 h post-fertilization (hpf) death and 72 hpf delayed hatching. However, ANF only caused sub-lethal effects, including 48 hpf cardiac edema and 72 hpf delayed hatching. Taking 24 hpf death and 48 hpf cardiac edema as endpoints, the toxicities of CdSO4 and ANF were significantly enhanced by each other. Consistently, both CdSO4 and ANF caused significant oxidative stress, including decreases in the reduced glutathione (GSH) level, inhibition of superoxide dismutase (SOD) activity, as well as increases in malondialdehyde (MDA) content in zebrafish embryos, but these mixtures produced much more significant alterations on the biomarkers. Co-treatment of CdSO4 and ANF significantly down-regulated the mRNA level of multidrug resistance-associated protein (mrp) 1 and cytochrome P450 (cyp) 1a, which constituted the protective mechanisms for zebrafish embryos to chemical toxins. In conclusion, co-treatment of CdSO4 and ANF exhibited a much more severe damage in zebrafish embryos than individual treatment. Meanwhile, production of oxidative stress and altered expression of mrp1 and cyp1a could be important components of such joint toxicity.

Genomic and physiological responses to strong selective pressure during late organogenesis: few gene expression changes found despite striking morphological differences.

BACKGROUND: Adaptations to a new environment, such as a polluted one, often involve large modifications of the existing phenotypes. Changes in gene expression and regulation during critical developmental stages may explain these phenotypic changes. Embryos from a population of the teleost fish, Fundulus heteroclitus, inhabiting a clean estuary do not survive when exposed to sediment extract from a site highly contaminated with polycyclic aromatic hydrocarbons (PAHs) while embryos derived from a population inhabiting a PAH polluted estuary are remarkably resistant to the polluted sediment extract. We exposed embryos from these two populations to surrogate model PAHs and analyzed changes in gene expression, morphology, and cardiac physiology in order to better understand sensitivity and adaptive resistance mechanisms mediating PAH exposure during development. RESULTS: The synergistic effects of two model PAHs, an aryl hydrocarbon receptor (AHR) agonist (ß-naphthoflavone) and a cytochrome P4501A (CYP1A) inhibitor (α-naphthoflavone), caused significant developmental delays, impaired cardiac function, severe morphological alterations and failure to hatch, leading to the deaths of reference embryos; resistant embryos were mostly unaffected. Unexpectedly, patterns of gene expression among normal and moderately deformed embryos were similar, and only severely deformed embryos showed a contrasting pattern of gene expression. Given the drastic morphological differences between reference and resistant embryos, a surprisingly low percentage of genes, 2.24% of 6,754 analyzed, show statistically significant differences in transcript levels during late organogenesis between the two embryo populations. CONCLUSIONS: Our study demonstrates important contrasts in responses between reference and resistant natural embryo populations to synergistic effects of surrogate model PAHs that may be important in adaptive mechanisms mediating PAH effects during fish embryo development. These results suggest that statistically significant changes in gene expression of relatively few genes contribute to the phenotypic changes and large morphological differences exhibited by reference and resistant populations upon exposure to PAH pollutants. By correlating cardiac physiology and morphology with changes in gene expression patterns of reference and resistant embryos, we provide additional evidence for acquired resistance among embryos whose parents live at heavily contaminated sites.

[Tissue-specific expression of hormonal carcinogenesis target genes in rats treated with polycyclic aromatic hydrocarbons].

We have investigated the effect of polycyclic aromatic hydrocarbons (PAHs) on estrogen-metabolizing genes CYP1A1, CYP1B1, CYP19 and ERalpha and cyclin D1 genes, which control of cell division in estrogen-depended tissues. Treatment of rats with benzo(a)pyren (BP) or 3-methylcholantrene (MC) significantly up-regulated CYP1A1, CYP1B1 gene expression in liver, uterus and ovary, whereas alfa-naphthoflavone (alpha-NF) did not have any effect. The high level of aromatase gene (CYP19) expression was detected in ovary only. Treatment of rats with BP or MC significantly down-regulated expression of this gene (15- and 5,5-fold, respectively), whereas alpha-NF did not have any effect. BP produced an increase in ERalpha and cyclin D1 gene expression in rat liver. This effect was not seen with MC and alpha-NF. ERalpha and cyclin D1 mRNA levels were unchanged in uterus of rats after PAHs treatment. On the other hand, BP treatment caused an increase of the ERalpha and cyclin D1 mRNA levels (3,5- and 2,5-fold, respectively) in ovary, whereas MC and alpha-NF did not have any effects. Thus, our results give evidence for tissue-specific effects of PAHs on expression of genes, which participate in hormonal carcinogenesis. Moreover, the fact that BP and MC treatment affects the expression of estrogen-metabolizing genes and genes, which control of cell division, supports the view that PAHs may be one of the causes of endocrine disorder and consequent hormonal carcinogenesis.

Daily treatment with α-naphthoflavone enhances follicular growth and ovulation rate in the rat.

The aryl hydrocarbon receptor (AhR) is a ligand-activated transcription factor and the first protein involved in a variety of physiological and toxicological processes, including those of xenobiotic metabolizing enzymes. AhR has been found in the ovary of many species and seems to mediate the ovarian toxicity of many environmental contaminants, which are AhR ligands. However, the role of AhR in the ovarian function is unknown. Therefore, the aim of this work was to study the action of α-naphthoflavone (αNF), known to be an AhR antagonist, on both follicular growth and ovulation. Immature Sprague-Dawley rats were daily injected intraperitoneally with αNF (0.1-80 mg/kg) or vehicle for 12 days, and primed with gonadotrophins (eCG/hCG) to induce follicular growth and ovulation. Ovaries were obtained 20 h after hCG administration. By means of immunohistochemistry, we found that the numbers of primordial, primary and antral follicles were increased in rats treated with 80 mg/kg αNF and that there were no differences with other doses. Likewise, the ovarian weight and the ovulation rate, measured by both number of oocytes within oviducts and corpora lutea in ovarian sections, were increased when the rats received either 1 or 10mg/kg daily. Although further studies are necessary to know the mechanism of action of αNF, it is possible that the different ovarian processes can be differentially responsive to the presence of different levels of αNF, and that the same or different endogenous AhR ligands can be involved in these ovarian processes in a cell type-dependent manner.

2-Amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx)-induced hepatocarcinogenesis is not enhanced by CYP1A inducers, alpha- and beta-naphthoflavone: relationship to intralobular distribution of CYP1A expression.

Interaction of more than two chemicals from foods is a very important factor for carcinogenic risk assessment and management. 2-Amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx), one of the most abundant carcinogenic heterocyclic amines in cooked foods, is speculated to be a human liver carcinogen. MeIQx is metabolically activated by CYP1A2 and then N-acetyltransferase (NAT), findings that suggest that its carcinogenic potential might be enhanced by simultaneous exposure to chemical(s) inducing CYP1A2. Therefore, we here investigated the effects of alpha- and beta-naphthoflavone as CYP1A2 inducers on MeIQx-induced rat hepatocarcinogenesis in a medium-term rat liver bioassay. Unexpectedly, no modifying influence of naphthoflavones on MeIQx-induced hepatocarcinogenesis was demonstrated with reference to glutathione S-transferase placental form (GST-P) positive foci in the liver, although up-regulation of CYP1A2 was detected on Western blot analysis. Activity of NAT was not affected. In MeIQx-treated rats, CYP1A expression was mainly detected in zone 3 of the liver where GST-P positive foci were preferentially located, while naphthoflavones alone or combinations of naphthoflavones and MeIQx induced CYP1A expression in zone 1. This difference in intralobular distribution of CYP1A might be related to the fact that MeIQx hepatocarcinogenesis was not modified by the two CYP1A inducers.