Polychlorinated naphthalenes (PCNs) are thought to interact with the aryl hydrocarbon receptor (AHR) and to have enzyme-inducing properties comparable to polychlorinated dibenzo-p-dioxins, therefore activation of steroid hormone receptors in endocrine tissues is also possible. The aim of the present study was to examine the effects of PCNs mixture, Halowax 1051 on gene and protein expression of receptors: estradiol (ERα/β), androgen (AR) and AHRGene expression was evaluated by real-time PCR after 6 h of exposition and protein expression by Western blot after 24 h. Levels of sex steroids: androstenedione (A4), estradiol (E2) and testosterone (T) were measured by enzyme immunoassays. Results of the data show down-regulation of AHR gene expression after 6 h in parallel with an inhibition in AHR protein expression at doses 10 pg-10 ng/mL, down-regulation of ER at all doses used, and up-regulation of AR gene expression at doses 1 and 10 ng/mL without affecting their protein expression. To indicate the involvement of AHR, ERs and AR in the impact of PCNs on steroidogenesis, we used their specific blockers. Blocker of AHR reversed the inhibitory effect of Halowax 1051 on A4 secretion, and strengthened its effect on T secretion. Blockers of both ER and AR had no effect on Halowax 1051 action on steroids secretion. The results of this study suggest that AHR is involved in the effect of PCNs on steroidogenesis in the ovary. Additionally, we propose that cross-talk between AHR-ER and AHR-AR receptors mediates the effects of Halowax 1051 on ovarian follicles.
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http://dx.doi.org/10.1016/j.chemosphere.2015.09.026 | DOI Listing |
Int J Environ Res Public Health
February 2023
College of Life and Environmental Science, Minzu University of China, Beijing 100081, China.
The concentrations of polychlorinated biphenyls (PCBs), polychlorinated naphthalenes (PCNs), and polychlorinated dibenzo--dioxins and dibenzofurans (PCDD/Fs) were determined in soil samples collected around an industrial park in Northwest China, to investigate the potential impacts of park emissions on the surrounding environment. The total concentration ranges of PCBs, PCNs, and PCDD/Fs in the soil samples were in 13.2-1240, 141-832, and 3.
View Article and Find Full Text PDFEcotoxicol Environ Saf
January 2020
College of Life and Environmental Sciences, Minzu University of China, Beijing, 100081, China; Engineering Research Center of Food Environment and Public Health, Beijing, 100081, China.
Seventeen soil samples collected in an industrial park located in Ningxia Province, Northwestern China were analyzed for polychlorinated naphthalenes (PCNs), polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs), and polychlorinated biphenyls (PCBs). The PCN, PCDD/F, and PCB concentration ranges were 183-3340, 7.00-215, and 45.
View Article and Find Full Text PDFReprod Toxicol
April 2017
Department of Physiology and Toxicology of Reproduction, Institute of Zoology, Jagiellonian University in Krakow, Krakow, Poland. Electronic address:
We determined the effect of dioxin-like polychlorinated naphtalenes (PCN) (Halowax 1051) (100pg/ml), benzo(a)pyrene [B(a)P] (2.5ng/ml), hexachlorobenzene (HCBz) (0.2ng/ml) and non-dioxin like polybrominated diphenyl ether (BDE-47) (25ng/ml) and bisphenol A (BPA) (20ng/ml) on ovarian adiponectin secretion (ELISA) and its receptors expression (Western blot).
View Article and Find Full Text PDFChemosphere
February 2016
Department of Physiology and Toxicology of Reproduction, Institute of Zoology, Jagiellonian University in Kraków, Kraków, Poland.
Polychlorinated naphthalenes (PCNs) are thought to interact with the aryl hydrocarbon receptor (AHR) and to have enzyme-inducing properties comparable to polychlorinated dibenzo-p-dioxins, therefore activation of steroid hormone receptors in endocrine tissues is also possible. The aim of the present study was to examine the effects of PCNs mixture, Halowax 1051 on gene and protein expression of receptors: estradiol (ERα/β), androgen (AR) and AHRGene expression was evaluated by real-time PCR after 6 h of exposition and protein expression by Western blot after 24 h. Levels of sex steroids: androstenedione (A4), estradiol (E2) and testosterone (T) were measured by enzyme immunoassays.
View Article and Find Full Text PDFToxicology
August 2014
Department of Physiology and Toxicology of Reproduction, Institute of Zoology, Jagiellonian University in Kraków, Kraków, Poland.
In this study we tried to answer a question which component of Halowax 1051 is responsible for, observed in previously published study, androgenic effects of the mixture, and whether it is possible to draw conclusions about the action of mixtures by examining the effect of an indicator congener. Ovarian follicles were incubated with individual congeners of an artificial mixture for 6-24h. At the end of the incubation period, media were collected for determination of progesterone (P4), androstenedione (A4), testosterone (T) and estradiol (E2) levels by enzyme immunoassay, and follicles were retained for an examination of aryl hydrocarbon receptor (AHR), cytochrome p450 enzymes (CYP1A1, CYP17, CYP19), and 17β-hydroxysteroid dehydrogenase (17β-HSD) protein expression by Western blotting.
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