Richard Wiger

Organochlorines Affect the Major Androgenic Hormone, Testosterone, in Male Polar Bears (Ursus Maritimus) at Svalbard

Normal sexual development and subsequent reproductive function are dependent on appropriate testosterone production and action. The regulation of steroid hormones, including androgens, can be influenced by both biological and environmental factors, including environmental chemicals. Concentrations of organochlorines are considerably greater in Svalbard polar bears than in polar bears from other regions. Between 1995 and 1998, samples were collected from 121 male polar bears (Ursus maritimus) from the Svalbard area. In this study, testosterone concentration variations were described for male polar bears during different seasons and for all age groups. To study possible relationships between plasma testosterone concentrations and biological factors, such as age, axial girth, and extractable plasma fat, and organochlorine contaminants including hexachlorocyclohexanes, hexachlorobenzene, chlordanes, p,p′–DDE, and 16 individual polychlorinated biphenyl (PCB) congeners, identical statistical analyses were performed on the total population and a subsample of reproductively active adults. Of the biological factors, axial girth showed a significant positive relationship and percentage extractable fat and a significant negative relationship with the testosterone concentrations. Both the Σpesticides and ΣPCBs made significant negative contributions to the variation of the plasma testosterone concentration. The continuous presence of high concentrations of organochlorines in male polar bears throughout their life could possibly aggravate any reproductive toxicity that may have occurred during fetal and early postnatal development.

A COMPARATIVE STUDY OF CHEMICALLY INDUCED DNA DAMAGE IN ISOLATED HUMAN AND RAT TESTICULAR CELLS

Testicular cells prepared from human organ transplant donors or from Wistar rats were used to compare 15 known reproductive toxicants with respect to their ability to induce DNA damage, measured as single-strand DNA breaks and alkali labile sites (ssDNA breaks) with alkaline filter elution. The compounds tested included various categories of chemicals (i.e., pesticides, industrial chemicals, cytostatics, and mycotoxins) most of which are directly acting genotoxicants (i.e., reacting with DNA either spontaneously or via metabolic activation). In addition, a few indirect genotoxic and nongenotoxic reproductive toxicants were included. Six of the chemicals induced no significant levels of ssDNA breaks in human and rat testicular cells; methoxychlor (10 to 100 microM, human and rat), benomyl (10 to 100 microM, human and rat), thiotepa (10 to 1000 microM, human and rat), cisplatin (30 to 1000 microM, human; 100 to 1000 microM, rat), Cd2+ (30 to 1000 microM, human; 100 to 1000 microM, rat), and acrylonitrile (30 to 1000 microM, human; 30 to 300 microM, rat). Four chemicals induced significant levels of ssDNA breaks in testicular cells from both species: styrene oxide (> or = 100 microM, rat and human), 1,2-dibromoethane (EDB) (> or = 100 microM, rat; 1000 microM human), thiram (> or = 30 microM, rat; > or = 100 microM, human), and chlordecone (300 microM, rat; > or = 300 microM, human). Finally, five chemicals induced ssDNA breaks in one of the two species. Four chemicals induced significant ssDNA breaks in rat testicular cells only: 1,2-dibromo-3-chloropropane (DBCP) (> or = 10 microM), 1,3-dinitrobenzene (1,3-DNB) (> or = 300 microM), Cr6+ (1000 microM), and aflatoxin B1 (> or = 100 microM), the last two of these produced only a minor positive response. One chemical, acrylamide, induced a marginal increase in ssDNA breaks in human at 1000 microM, but not in rat testicular cells. Although based on a limited number of donors, the data indicate a close correlation between the induction of DNA damage in human and rat testicular cells in vitro. For some chemicals, however, there appears to be differences in the susceptibility to chemically induced ssDNA breaks of isolated testicular cells from the two species. The data indicate that the parallel use of human and rat testicular cells provides a valuable tool in the assessment of human testicular toxicity.

Endocrine Disruption Induced by Organochlorines (OCs): Field Studies And Experimental Models

Long-range transport of persistent organic compounds by air and ocean currents from industrialized areas resulted in high levels of these pollutants in food webs in the Svalbard area. With the aim to test if organochlorine (OC) exposure in free-living polar bears from Svalbard affected their plasma steroid hormone concentrations, it was found that polychlorinated biphenyls (PCBs) were associated with increased progesterone levels in females. The sum of pesticides (∑pesticides) and ∑PCBs contributed significantly negative to the variation of the plasma testosterone in males, and the overall contribution of the OCs to the plasma cortisol variation was negative. A second objective was to study the effects of selected OCs (i.e., PCB 153 and PCB 126) on animal health as a consequence of effects on endocrine-regulated functions such as reproduction and immunity in a goat model focusing on long-term and low-level exposure during the periods of fetal development and in the neonatal period. Additionally, acute exposure was studied in adult mice. The results indicated that exposure to low doses of PCB 153 in utero and in the suckling period influenced reproductive functions and both PCB 153 and PCB 126 exerted immunomodulatory effects on the offspring, whereas acute exposure of adult mice had minor effects on male reproductive function.

Expression of Cyp2B1 in Freshly Isolated and Proliferating Cultures of Epithelial Rat Lung Cells

Bronchiolar Clara cells and alveolar type 2 cells of the lung are known to express relatively high levels of P450 enzymes compared to other pulmonary cells. Populations of enriched type 2 cells and Clara cells were isolated from rat lung by a procedure including lung perfusion, protease digestion, centrifugal elutriation, and differential attachment. Alveolar macrophages were removed by lavage. The purity of the type 2 cell-enriched population was approximately 90%, and the purity of the Clara cell-enriched population was 40-50%. Both type 2 cells and the cells of the Clara cell-enriched population proliferated in culture. CYP2B1 mRNA was expressed approximately to the same level in type 2 cells and the Clara cell-enriched population. The mRNA levels remained roughly constant for both cell types throughout the culture period, except for an early transient reduction. The apoenzyme level of CYP2B1 was 2-3 times higher in freshly isolated cells of the Clara cell-enriched population than in the type 2 cells. Both epithelial cell types showed decreased level of CYP2B1 apoenzyme in culture. The differences in the CYP2B1 mRNA and apoenzyme expression levels in freshly isolated cells and cultured cells suggest the existence of a post-transcriptional regulatory mechanism for CYP2B1 expression in lung cells. The characterization of specific functions of lung cells in culture, such as P450 gene expression, provides necessary information for the use of the cells in in vitro pulmonary toxicology.

Effects of acetaminophen and hydroxyurea on spermatogenesis and sperm chromatin structure in laboratory mice

High doses of acetaminophen (400 mg/kg) or hydroxyurea (200 mg/kg) given intraperitoneally daily for 5 d caused reduction in relative testicular weight in mice (B6C3/F1/BOM M). Testicular atrophy of several tubules was seen in the hydroxyurea-treated mice 5 d after the last exposure, whereas acetaminophen did not lead to such changes. Exposure to acetaminophen caused neither a depletion of glutathione in the testis nor a marked increase in covalent binding. In contrast, significant decreases in the incorporation of thymidine into the testis were observed during the first 3 h following a single treatment with acetaminophen (100 to 400 mg/kg) or hydroxyurea (100 to 200 mg/kg). In mice treated with acetaminophen (400 mg/kg) or hydroxyurea (200 mg/kg) daily for 5 d, flow cytometric analysis revealed large reductions in one of the tetraploid populations of testicular cells (mostly early pachytene spermatocytes) on days 5 and 10. Changes in the populations of the various spermatid stages occurred later; thus, both compounds appeared to cause a delay in spermiogenesis. Indications of abnormal chromatin structure were seen in an increased frequency of vas deferens sperm on days 27 and 33 after the last exposure, when measured as increased susceptibility towards DNA denaturation in situ. In conclusion, high doses of acetaminophen or hydroxyurea inhibit DNA synthesis in the testis. The present data indicate that this leads to reduced testicular weight, a reduction in the number of early pachytene spermatocytes, changes in the proportions of the various spermatid stages, and an apparent alteration in sperm chromatin structure.

Environmental exposure of the mouse germ line: DNA adducts in spermatozoa and formation of de novo mutations during spermatogenesis.

Background Spermatozoal DNA damage is associated with poor sperm quality, disturbed embryonic development and early embryonic loss, and some genetic diseases originate from paternal de novo mutations. We previously reported poor repair of bulky DNA-lesions in rodent testicular cells. Methodology/Principal Findings We studied the fate of DNA lesions in the male germ line. B[a]PDE-N2-dG adducts were determined by liquid chromatography-tandem mass spectrometry, and de novo mutations were measured in the cII-transgene, in Big Blue®mice exposed to benzo[a]pyrene (B[a]P; 3×50 mg/kg bw, i.p.). Spermatozoa were harvested at various time-points following exposure, to study the consequences of exposure during the different stages of spermatogenesis. B[a]PDE-N2-dG adducts induced by exposure of spermatocytes or later stages of spermatogenesis persisted at high levels in the resulting spermatozoa. Spermatozoa originating from exposed spermatogonia did not contain DNA adducts; however de novo mutations had been induced (p = 0.029), specifically GC-TA transversions, characteristic of B[a]P mutagenesis. Moreover, a specific spectrum of spontaneous mutations was consistently observed in spermatozoa. Conclusions/Significance A temporal pattern of genotoxic consequences following exposure was identified, with an initial increase in DNA adduct levels in spermatozoa, believed to influence fertility, followed by induction of germ line de novo mutations with possible consequences for the offspring.

Mechanisms involved in the induction of apoptosis by T-2 and HT-2 toxins in HL-60 human promyelocytic leukemia cells

T-2 and HT-2 toxins belong to a group of mycotoxins that are widely encountered as natural contaminants known to elicit toxic responses in hematopoietic cells. In the present study, HL-60 cells were used to characterize the apoptotic effects of T-2 and a major metabolite, HT-2, and to examine the mechanisms involved. Apoptotic cells were identified microscopically by chromatin condensation and nuclear fragmentation, by flow cytometric analysis, and by DNA gel electrophoresis. T-2 and HT-2 induced concentration-dependent apoptosis after 24 h in HL-60 cells, starting at concentrations of 3.1 and 6.25 ng/ml respectively. An increased number of apoptotic cells could be observed 4–6 h after exposure to 12.5 ng/ml of toxin. Little cytotoxicity (plasma membrane damage) was observed even after exposure to concentrations of toxins (25–50 ng/ml) inducing apoptosis in 60–100% of the cells. The apoptotic process was almost completely blocked in the presence of the general caspase inhibitor zVAD.fmk. In contrast, no or only minor effects were observed with the more specific caspase inhibitors DEVD.CHO, IETD.fmk, and DEVD.fmk. As judged by Western blotting, the levels of several procaspases (-3, -7, -8, -9, but not -12) were reduced 3–6 h after exposure to toxin. Substantial increases in the presumed active form(s) of caspase-8 and -9 were observed. Furthermore, poly(ADP-ribose) polymerase (PARP) was already markedly cleaved 3 h after toxin treatment, indicative of active caspase-3 and -7. No or only minor changes in Bcl-2, Bcl-XL and Bax levels were observed. BAPTA-AM and ZnCl2 blocked the degradation of procaspases, the fragmentation of PARP, and the induction of apoptosis. In summary, both T-2 and HT-2 induced apoptosis, with T-2 being somewhat more potent than HT-2. The divalent calcium concentration, [Ca2+], appears to be involved in the activation of several caspases, resulting in DNA fragmentation, chromosomal condensation, and nuclear fragmentation.

In vitro toxicity of 1,2-dibromo-3-chloropropane (DBCP) in different testicular cell types from rats

1,2-Dibromo-3-chloropropane (DBCP)-induced toxicity was studied in rat germ cells from different stages of spermatogenesis, separated by centrifugal elutriation, and in Sertoli cells prepared from sexually mature and immature animals. The in vitro metabolic activation of 50 to 250 microM DBCP, measured as covalent binding of 14C-DBCP to macromolecules, was highest in round spermatids, lowest in Sertoli cells and elongating/elongated spermatids, and intermediate in spermatocytes. High concentrations of DBCP (> or = 250 microM) caused a decrease in oxygen consumption and mitochondrial rhodamine 123 uptake, indicating an effect on mitochondrial function. Altered Sertoli cell function, measured as detachment of germ cells in Sertoli-germ cell cocultures, was evident at DBCP concentrations > or = 300 microM. DBCP-induced DNA damage occurred at much lower concentrations (10 to 30 microM) when compared to effects on mitochondrial function and Sertoli cell function. The extent of single strand DNA breaks and alkali-labile sites (ssDNA breaks) measured by the alkaline filter elution technique and the single cell gel electrophoresis assay, were greatest in the round spermatids > spermatocytes = Sertoli cells > elongating/elongated spermatids. The study demonstrates that various testicular cell types show differences in their rates of activation of DBCP to metabolites that bind to macromolecules. DNA is a more sensitive intracellular target in DBCP-induced testicular toxicity than mitochondria. Round spermatids appear to be more susceptible to DBCP-induced ssDNA breaks than spermatocytes, elongating/elongated spermatids, or Sertoli cells.

DNA strand breaks in testicular cells from humans and rats following in vitro exposure to 1,2-dibromo-3-chloropropane (DBCP)

Preparations of testicular cells from human organ transplant donors and from Wistar rats were compared with respect to their composition of the different testicular cell types, their ability to metabolize 1,2-dibromo-3-chloropropane (DBCP), and their relative sensitivity to induction of DNA single strand breaks and alkali labile sites (ssDNA breaks) after treatment with DBCP, 4-nitroquinoline N-oxide (4-NQO), and X rays. Flow cytometric and microscopic analysis demonstrated that the interindividual variation in the composition of testicular cell types was considerably greater in the human tissue than in that from rats. The in vitro metabolic activation of DBCP (50 to 250 microM), measured as radiolabel covalently bound to macromolecules, was three-fold faster in rat testicular cells compared to human testicular cells. X rays (1 to 10 Gy) and 4-NQO (0.5 to 2.5 microM) induced ssDNA breaks to a similar extent in both human and rat testicular cells as measured by single cell get electrophoresis (SCGE) and alkaline filter elution. In contrast, 1,2-dibromo-3-chloropropane (DBCP) (3 to 300 microM) caused no significant DNA damage in human testicular cells, whereas in rats there was a clear concentration-dependent increase in ssDNA breaks. The data show that, compared to rats, testicular cells from humans are less efficient in activating DBCP to metabolites binding covalently to macromolecules. However, from the rate of covalent binding observed one would expect a significant degree of DBCP-induced ssDNA breaks in the human testicular cells. The low level of DBCP-induced ssDNA breaks in human testicular cells could indicate that different reactive DBCP metabolites are involved in binding to cellular macromolecules compared to DNA damage, or that different rates of DNA repair exist in human and rat testicular cells.

Cell Death via Interactions of Agents with DNA

Publisher Summary This chapter reviews the evidence that DNA damage may be involved in chemical-induced cell death. The importance of DNA damage for radiation-induced cell killing has been demonstrated in experiments where the cell nucleus and the cytoplasm are selectively irradiated using suitably constructed beams of ionizing particles. It is shown that when the cytoplasm is the target, the dose required to kill a cell is larger by orders of magnitude than the dose required in the nucleus. A general problem shared by most genotoxic chemicals is that they also damage non-DNA targets, such as RNA, proteins and lipids, and cellular processes in the nucleus or in other organelles including mitochondria, endoplasmic reticulum, plasma membrane, and cytoskeleton. When evaluating the importance of chemical-induced DNA damage in organ toxicity, extranuclear injury has to be taken into consideration.