Reproductive dysfunction in wildlife populations can be a result of environmental contaminants binding to aryl hydrocarbon receptor (AhR) or estrogenic receptors. Signaling by both types of receptors can be affected by polycyclic aromatic hydrocarbons (PAHs), which are potential endocrine disruptors. However, our knowledge regarding the effects of oxygenated (oxy)-PAHs and azaarenes on AhR-mediated and estrogenic activities is incomplete. In the present study, we have identified 9-fluorenone, anthrone, anthraquinone, benzanthrone, benz[a]anthracene-7,12-dione, benz[c]acridine, and dibenz[a,h]acridine as prevalent oxy-PAHs and azaarenes found in river sediments. Their concentrations in sediment samples ranged from 2.1 to 165.2 ng g(-1) for oxy-PAHs and up to 27.3 ng g(-1) for azaarenes. Their relative AhR-inducing and estrogenic potencies were quantified in vitro using two cell lines that were stably transfected with a luciferase reporter gene system and expressed as induction equivalency factors (IEFs). The only oxy-PAHs with detectable levels of in vitro AhR-mediated activity were benzanthrone and benz[a]anthracene-7,12-dione. However, their IEFs were approximately three to four orders of magnitude lower than those of benzo[a]pyrene. On the other hand, azaarenes showed a strong AhR-mediated activity, with dibenzo[a,h]acridine being a far more potent inducer of activity than benzo[a]pyrene. Benzanthrone, benz[a]anthracene-7,12-dione, anthraquinone, and benz[a]acridine were weak inducers of in vitro estrogenic activity, with IEFs similar to that of benzo[a]pyrene. Based on concentrations and relative potencies, our results suggest that dibenzo[a,h]acridine can significantly contribute to the overall AhR-mediated activity in river sediments, whereas the remaining compounds do not. No studied compound was found to contribute significantly to estrogen receptor-mediated activity in vitro.

Reproductive dysfunction in wildlife populations can be a result of environmental contaminants binding to aryl hydrocarbon receptor (AhR) or estrogenic receptors. Signaling by both types of receptors can be affected by polycyclic aromatic hydrocarbons (PAHs), which are potential endocrine disruptors. However, our knowledge regarding the effects of oxygenated (oxy)-PAHs and azaarenes on AhR-mediated and estrogenic activities is incomplete. In the present study, we have identified 9-fluorenone, anthrone, anthraquinone, benzanthrone, benz[a]anthracene-7,12-dione, benz[c]acridine, and dibenz[a,h]acridine as prevalent oxy-PAHs and azaarenes found in river sediments. Their concentrations in sediment samples ranged from 2.1 to 165.2 ng g(-1) for oxy-PAHs and up to 27.3 ng g(-1) for azaarenes. Their relative AhR-inducing and estrogenic potencies were quantified in vitro using two cell lines that were stably transfected with a luciferase reporter gene system and expressed as induction equivalency factors (IEFs). The only oxy-PAHs with detectable levels of in vitro AhR-mediated activity were benzanthrone and benz[a]anthracene-7,12-dione. However, their IEFs were approximately three to four orders of magnitude lower than those of benzo[a]pyrene. On the other hand, azaarenes showed a strong AhR-mediated activity, with dibenzo[a,h]acridine being a far more potent inducer of activity than benzo[a]pyrene. Benzanthrone, benz[a]anthracene-7,12-dione, anthraquinone, and benz[a]acridine were weak inducers of in vitro estrogenic activity, with IEFs similar to that of benzo[a]pyrene. Based on concentrations and relative potencies, our results suggest that dibenzo[a,h]acridine can significantly contribute to the overall AhR-mediated activity in river sediments, whereas the remaining compounds do not. No studied compound was found to contribute significantly to estrogen receptor-mediated activity in vitro.

Extracts of sediment samples collected from the Morava River and its tributaries (Czech Republic) were examined for mutagenic, dioxin-like, and estrogenic activities. Moreover, the human leukemic HL-60 cell line was tested as a potential model for the detection of effects of environmental contaminants on cell proliferation and differentiation processes. Analytical data indicate that the sediments were contaminated predominantly with polycyclic aromatic hydrocarbons (PAHs) and phthalate esters. The sums of concentrations of 16 U.S. Environmental Protection Agency priority PAHs ranged from 0.8 to 13.2 micrograms/g and those of phthalates reached up to 3,000 ng/g, while only low levels of chlorinated hydrocarbons were found. The main goal of the present study was to determine effects of PAH prevalence on in vitro bioassays, with special emphasis on dioxin-like activity. The dioxin-like activity was tested using a reporter gene assay based on chemical-activated luciferase expression (the CALUX assay). Significant dioxin-like activity (2.6-40.1 micrograms/g benzo[a]pyrene equivalents and 5.9-48.2 ng/g 2,3,7,8-tetrachlorodibenzo-p-dioxin equivalents) was detected in all samples, and the results obtained with various exposure times or with both crude and PAH-deprived extracts indicate that the response was probably caused almost exclusively by the presence of high concentrations of PAHs. This corresponds with results of chemical analyses and indicates that various exposure times would allow a discrimination between dioxin-like activities of persistent compounds and easily metabolized aryl hydrocarbon (Ah) receptor inducers. Only sediment extracts containing the highest concentrations of PAHs were mutagenic, as determined by the umu assay. Estrogenic activity was found in several samples (4.75-22.61 pg/g estradiol equivalents) using cells stably transfected with an estrogen-responsive element linked to a luciferase promoter. Noncytotoxic doses of extracts had no effects on HL-60 cell proliferation, while two of the tested crude extracts significantly enhanced their all-trans retinoic acid-induced differentiation. These activities were not associated with phthalate esters and/or PAHs. Our results indicate that cellular and biochemical in vitro assays based on various specific modes of action may yield data complementary to results of mutagenicity tests and that they could be useful in environmental risk assessment. High levels of PAHs are apparently associated with dioxin-like and mutagenic activities rather than with estrogenic activity.