Inhibition of stage-specific DNA synthesis in rat spermatogenic cells by polycyclic aromatic hydrocarbons

Assessment of gonadal and thyroid histology in Gulf killifish (Fundulus grandis) from Barataria Bay Louisiana one year after the Deepwater Horizon oil spill

We examined gonads and thyroid glands of Gulf killifish (Fundulus grandis) 1yr after the Deepwater Horizon oil spill. F. grandis were trapped from two impacted sites in Barataria Bay (Bayou St. Denis, Bay Jimmy) and an un-impacted site in East Texas (Sabine Pass). The greatest number of F. grandis were collected at Sabine Pass. F. grandis collected at Bayou St. Denis were smaller and had smaller Fulton condition factor scores than fish collected at Sabine Pass. Sex ratios were biased roughly 2:1 in favor of females at Sabine Pass and Bayou St. Denis. Gonad-somatic index (GSI) in males from Sabine Pass was double that of fish from Bay Jimmy while germinal epithelium thickness of the testes was 2.7 fold smaller in males from the impacted site. GSI and oocyte diameters in females from Bayou St. Denis were significantly smaller than females from Bay Jimmy or the reference site. There were no differences in thyroid follicle cell height. While total polyaromatic hydrocarbons at the impacted sites were no different from the reference site, the impacted sites did have greater concentrations of benzo[a]pyrene in sediment pore water. The finding of smaller GSI and testicular germinal epithelium in males from an impacted site suggest that exposure to a combination of oil and dispersants may adversely impact testicular function.

Effects of benzo[a]pyrene as an environmental pollutant and two natural antioxidants on biomarkers of reproductive dysfunction in male rats

Benzo[a]pyrene (B[a]P) is an environmental toxicant and endocrine disruptor. Therefore, the aim of the present study was to investigate the toxicity of B[a]P in testis of rats and also to study the role of silymarin and thymoquinone (TQ) as natural antioxidants in the alleviation of such toxicity. Data of the present study showed that levels of testosterone, estrogen and progesterone were significantly decreased after treatment of rats with B[a]P. In addition, B[a]P caused downregulation of the expressions of steroidogenic enzymes including CYP17A1 and CP19A1, and decreased the activity of 17-β hydroxysteroid dehydrogenase (17β-HSD). Moreover, B[a]P decreased the activities of antioxidant enzymes including catalase (CAT), glutathione peroxidase (GPX) and superoxide dismutase (SOD), and significantly increased free radicals levels in testis of male rats. However, pretreatment of rats with silymarin prior to administration of B[a]P was found to restore the level of free radicals, antioxidant status, and activities of steroidogenic enzymes to their normal levels in testicular tissues. Moreover, histopathological finding showed that silymarin recovered the abnormalities occurred in tubules caused by B[a] P in testis of rats. On the other hand, TQ showed pro-oxidant effects and did not ameliorate the toxic effects of B[a] P on the testicular tissue since it decreased antioxidant enzymes activities and inhibited the protein expression of CYP11A1 and CYP21A2 compared to control rats. Moreover, TQ decreased the levels of testosterone, estrogen, and progesterone either in the presence or absence of B[a]P. It is concluded that B[a]P decreased testosterone levels, inhibited antioxidant enzymes activities, caused downregulation of CYP isozymes involved in steroidogenesis, and increased free radical levels in testis. Moreover, silymarin was more effective than TQ in restoring organism health and alleviating the deleterious effects caused by B[a]P in the testis of rats. Due to its negative impact, it is highly recommended to limit the use of TQ as a dietary supplement since millions of people in the Middle East are using it to improve their health.

Alteration of sperm quality and hormone levels by polycyclic aromatic hydrocarbons on airborne particulate particles

The objective of this study was to assess whether polycyclic aromatic hydrocarbons (PAHs) affect male reproductive functions in vivo. Male reproductive parameters included testis weight, sperm counts and motility, circulating follicle-stimulating hormone (FSH), luteinizing hormone (LH), and testosterone. The average body weight, testis weight, and epididymis weight in the exposed group were not significantly lower than that in the control group (p < 0.01). The daily numbers of sperm in the PAH-exposed groups were significantly lower than those in the control group. The motility of sperm in the PAH-exposed groups was significantly less than those in the control group. Plasma LH concentrations increased at the end of the exposure period and continued to increase after post-cessation of exposure to PAHs. Testosterone decreased at the end of the exposure period and increased after post-cessation of exposure. However, the follicle-stimulation hormone level remained relatively stable during the study period. The present study showed that PAHs can compromise sperm functions and alter endocrine hormone levels.

A comparison of in vitro and in vivo EDSTAC test battery results for detecting antiandrogenic activity

The androgen receptor (AR) transactivation, binding, and Hershberger assays are being developed for large-scale screening of chemicals for endocrine activity. The goal of this study was to evaluate the correlation between in vitro and in vivo antiandrogenicity assays using a variety of compounds (p,p'-DDE, flutamide (FLUT), spironolactone, procymidone, RU486, methoxychlor (MXC), benzo(a)pyrene (BAP), and selected metabolites). For the AR transactivation assay, AR(+) LNCaP prostate carcinoma cells were transfected with an inducible luciferase reporter construct (pGudLuc7ARE) and exposed for 24 h to test materials (< or = 10 microM) in the presence and absence of 1 nM of the AR agonist R-1881. Each of these materials, including the hydroxlated metabolites of BAP and MXC, produced significant antiandrogenic activity in vitro as evidenced by their inhibition of the response to R-1881. Similarly, in vitro AR binding experiments using the recombinant ligand-binding domain (LBD) of the human AR and fluorescence polarization (FP) methodology yielded IC50s comparable to that of testosterone for RU486 and 9-OH-BAP. Other parent compounds and metabolites exhibited lesser binding affinity. In vivo antiandrogenic activity was evaluated with the Hershberger assay, wherein castrated male CD rats were dosed by gavage for 10 days with (mg/kg per day): MXC (10, 50, 100, and 200), BAP (1, 10, 50, and 100), RU486 (1, 5, 10, and 25), and FLUT (10) in the presence of 0.4 mg/kg per day (sc) of testosterone propionate (TP). Neither BAP nor MXC produced significant decreases in accessory sex tissue (AST) weights relative to TP control. However, 200 MXC resulted in a significant decrease in body weight and 100 BAP significantly increased absolute and relative liver weights. RU486 (25) produced significant decreases in ventral prostate, seminal vesicle, and Cowper's gland weights without affecting body weight. FLUT (10) decreased all AST weights measured. The antiandrogenic activities of the remaining materials (p,p'-DDE, spironolactone, and procymidone) have been demonstrated in previous Hershberger assays. These data indicate the importance of including in vivo results in assessing the endocrine activity of test materials and further stress the importance of a weight of evidence approach in assessing endocrine activity of test materials.

ATSDR evaluation of health effects of chemicals. IV. Polycyclic aromatic hydrocarbons (PAHs): understanding a complex problem

Polycyclic Aromatic Hydrocarbons (PAHs) are a group of chemicals that are formed during the incomplete burning of coal, oil, gas, wood, garbage, or other organic substances, such as tobacco and charbroiled meat. There are more than 100 PAHs. PAHs generally occur as complex mixtures (for example, as part of products such as soot), not as single compounds. PAHs are found throughout the environment in the air, water, and soil. As part of its mandate, the Agency for Toxic Substances and Disease Registry (ATSDR) prepares toxicological profiles on hazardous chemicals, including PAHs (ATSDR, 1995), found at facilities on the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) National Priorities List (NPL) and which pose the most significant potential threat to human health, as determined by ATSDR and the Environmental Protection Agency (EPA). These profiles include information on health effects of chemicals from different routes and durations of exposure, their potential for exposure, regulations and advisories, and the adequacy of the existing database. Assessing the health effects of PAHs is a major challenge because environmental exposures to these chemicals are usually to complex mixtures of PAHs with other chemicals. The biological consequences of human exposure to mixtures of PAHs depend on the toxicity, carcinogenic and noncarcinogenic, of the individual components of the mixture, the types of interactions among them, and confounding factors that are not thoroughly understood. Also identified are components of exposure and health effects research needed on PAHs that will allow estimation of realistic human health risks posed by exposures to PAHs. The exposure assessment component of research should focus on (1) development of reliable analytical methods for the determination of bioavailable PAHs following ingestion, (2) estimation of bioavailable PAHs from environmental media, particularly the determination of particle-bound PAHs, (3) data on ambient levels of PAHs metabolites in tissues/fluids of control populations, and (4) the need for a critical evaluation of current levels of PAHs found in environmental media including data from hazardous waste sites. The health effects component should focus on obtaining information on (1) the health effects of mixtures of PAHs particularly their noncarcinogenic effects in humans, and (2) their toxicokinetics. This report provides excerpts from the toxicological profile of PAHs (ATSDR, 1995) that contains more detailed information.

Inhibition of meiotic divisions of rat spermatocytes in vitro by polycyclic aromatic hydrocarbons

The toxic effects of polycyclic aromatic hydrocarbons (PAH) on spermatogenic cells undergoing meiotic division were investigated in vitro. Toxicity was assayed as alterations in cell nucleus morphology and cell survival and by DNA flow cytometry. Benzo[a]pyrene (BP) and 7,12-dimethylbenz[a]anthracene (DMBA) inhibited the progression of spermatocytes through meiotic division and were highly cytotoxic at concentrations higher than 1 microM. These results were obtained upon addition of a drug-metabolizing system, indicating that the seminiferous tubules lack the enzymes required for the initiation of PAH metabolism. The spindle poisons, e.g., vincristine and Colcemid, a group of direct-acting agents, affected spermatogenesis during meiotic division in a manner similar to that observed with PAH. In contrast, adriamycin did not inhibit meiotic division, although it did induce the formation of meiotic micronuclei as a result of chromosome breakage. It is concluded that low concentrations, i.e., 0.1 microM of PAH, strongly inhibit meiotic division, presumably after metabolic activation to reactive molecules functionally resembling direct-acting alkylating agents. High concentrations of PAH are cytotoxic.

The interaction of Sertoli and Leydig cells in the testicular toxicity of tri-o-cresyl phosphate

Previous studies have shown that after dosing with tri-o-cresyl phosphate (TOCP), the testis contains more active intermediate (saligenin cyclic-o-tolyl phosphate; SCOTP) than do other organs or blood. SCOTP is produced by a cytochrome P450-dependent reaction, and the Sertoli cells, although containing little P450, are the testicular cells that show the first signs of damage after TOCP administration. The present studies evaluated (i) whether testicular Leydig cell production of SCOTP might explain the elevated testicular concentration of SCOTP, (ii) if this production affected testosterone secretion, and (iii) if Sertoli cells cocultured over TOCP-exposed Leydig cells would show effects similar to those found after SCOTP exposure of Sertoli cells in vitro, indicating a cell interaction. Previous data showed that a target enzyme for SCOTP in Sertoli cells, nonspecific esterase (NSE), was inhibited by exposure in vitro to SCOTP, but not to TOCP. In the present experiments, HPLC analysis identified SCOTP in media from Leydig cells cultured with radiolabeled TOCP, demonstrating activation. TOCP addition to Leydig cells decreased testosterone output after stimulation with hCG, an effect that was replicated by subsequent in vivo experiments. Addition of various intermediates in the testosterone biosynthesis pathway indicated that both mitochondrial- and microsomal-based steps in the pathway were affected. Collectively, these data indicate that Leydig cells can activate TOCP. To model whether this activation might affect Sertoli cells in vivo, Sertoli cells were plated in culture-well inserts suspended above (cocultured with) isolated Leydig cells in the presence of TOCP. Sertoli NSE activity was diminished, while remaining unchanged when cultured in the presence of TOCP but without Leydig cells, or over Leydig cells alone. These results show that the Leydig cells in the testis are capable of activating TOCP to SCOTP, and that this can produce effects in Sertoli cells. This in situ activation of TOCP to SCOTP may help explain why the testis contains high concentrations of SCOTP after in vivo dosing with TOCP, and why the testis is a target organ for TOCP toxicity.

Cellular localization of cytochrome(s) P-450 metabolizing polycyclic aromatic hydrocarbons in the rat adrenal cortex

Cells were dispersed from the capsular, as well as the inner portion of female rat adrenal glands and subsequently separated on discontinuous Percoll gradients. The adrenal cells were distributed within a density interval ranging from 1.016 to 1.075 g/cm3 and different subpopulations showed distinct morphological appearances in suspension, as well as in culture. The total cells from the inner portion of the adrenals metabolized [14C]7,12-dimethylbenz(a)anthracene at a rate of 4.04 pmol/min 10(6) cells and synthesized corticosterone in response to ACTH stimulation at a rate of 1.07 micrograms/hr/10(6) cells. These activities were 4- and 2.5-fold higher, respectively, than the corresponding activities in cells isolated from the capsular portion. 7,12-Dimethylbenz(a)anthracene monoxygenase activity and ACTH-stimulated steroidogenesis were enriched in two subpopulations of cells obtained on the Percoll gradient and were estimated to be 13.1 pmol/min/10(6) cells and 3.21 micrograms/hr/10(6) cells, respectively, in the most active fraction (at the 1.034/1.040 g/cm3 interface). On the basis of cellular morphology, density and steroidogenic properties, it was concluded that adrenal 7,12-dimethylbenz(a)anthracene monoxygenase activity is localized mainly in the cells of the zona fasciculata.