Toxicological evaluation of 4-vinylcyclohexene. II. Induction of ovarian tumors in female B6C3F1 mice by chronic oral administration of 4-vinylcyclohexene

A reproductive and developmental toxicity screening study of 1,3-butadiene in Sprague-Dawley rats

1,3 Butadiene (BD) is an industrial intermediate used primarily in product manufacturing with the greatest exposure potential via inhalation. BD was evaluated for reproductive and developmental effects in a Good Laboratory Practice (GLP)-compliant, extended OECD 421 guideline study (completed 2003). Twelve-week old rats (12/sex/dose) were exposed via whole-body inhalation to BD vapor (0, 300, 1500, 6000 ppm) for 6 h/day, 7 days/week, starting 14 days prior to mating through the day prior to euthanasia (total exposures: 83-84 days for F0 males 60-70 days for F0 females). Select F1 offspring (1/sex/litter) were dosed 7 days (postnatal days 21-27 or 28-34), then necropsied. At 1500 and 6000 ppm, treatment-related facial soiling was seen in F0 males and females with decreased body weights/gains in F0 males. F1 males and females exhibited similar effects at 1500 and 6000 ppm. Importantly, the F0 generation had no evidence of altered sperm production, testicular effects, or ovarian atrophy, which were sensitive responses in mice. The no-observed-adverse-effect-level (NOAEL) is 300 ppm due to decreased body weight/gain and facial soiling at 1500 ppm, whereas 6000 ppm serves as a NOAEL for reproductive and developmental endpoints. This study contributes to the weight-of-evidence of differential BD reproductive toxicity in rats and mice.

A missense mutation in the transcription factor Foxo3a causes teratomas and oocyte abnormalities in mice

An N-ethyl-N-nitrosourea random mutation screen was used to identify recessive modifiers of gene silencing in the mouse using an epigenetically sensitive reporter transgene. One of the mutant lines, MommeR1, was identified as a suppressor of variegation and it showed female-specific age-associated infertility in homozygotes. Linkage analysis identified a region on chromosome 10, containing the Foxo3a gene, previously shown to play a critical role in female gametogenesis. Foxo3a is a transcription factor with roles in cell cycle control, apoptosis, neural and hematopoietic cell differentiation, and DNA repair. Sequencing of the Foxo3a gene in MommeR1 mice revealed a point mutation that causes an amino acid substitution in the highly conserved Forkhead DNA-binding domain. In vitro transcription assays showed that the point mutation causes loss of FOXO3a transactivation activity. Compound heterozygotes made with Foxo3a-null mice (carrying the targeted deletion of exon 2) displayed complementation with respect to both the activation of the reporter transgene and defects in folliculogenesis similar to those seen in MommeR1 homozygotes, supporting the conclusion that this is the causative mutation. Approximately one in six female MommeR1 homozygotes develop teratomas, a phenotype not reported in Foxo3a-null mice. Ovulated oocytes from MommeR1 homozygotes display a number of abnormalities. The MommeR1 mice provide a novel platform to investigate teratocarcinogenesis and link Foxo3a with parthenogenesis and ovarian cancer. The finding of Foxo3a as a modifier of epigenetic reprogramming is discussed.

Animal models of ovarian cancer

Ovarian cancer is the most lethal of all of the gynecological cancers and can arise from any cell type of the ovary, including germ cells, granulosa or stromal cells. However, the majority of ovarian cancers arise from the surface epithelium, a single layer of cells that covers the surface of the ovary. The lack of a reliable and specific method for the early detection of epithelial ovarian cancer results in diagnosis occurring most commonly at late clinical stages, when treatment is less effective. In part, the deficiency in diagnostic tools is due to the lack of markers for the detection of preneoplastic or early neoplastic changes in the epithelial cells, which reflects our rather poor understanding of this process. Animal models which accurately represent the cellular and molecular changes associated with the initiation and progression of human ovarian cancer have significant potential to facilitate the development of better methods for the early detection and treatment of ovarian cancer. This review describes some of the experimental animal models of ovarian tumorigenesis that have been reported, including those involving specific reproductive factors and environmental toxins. Consideration has also been given to the recent progress in modeling ovarian cancer using genetically engineered mice.

Effect of 4-vinylcyclohexene on micronucleus formation in the bone marrow of rats and mice

This study was conducted to evaluate the potential of 4-vinylcyclohexene (VCH) to induce micronuclei in the bone marrow of mice and rats. Male and female Crl:CD BR (Sprague-Dawley) rats and B6C3F1/CrBR mice were exposed to VCH 6 hr/day for 2 days or for 13 weeks. In the 2-day study, mice were exposed by inhalation to 0, 250, 500, or 1000 ppm, and rats were exposed to 0, 500, 1000, or 2000 ppm. In the 13-week study, mice were exposed to 0, 50, 250, or 1000 ppm, and rats were exposed to 0, 250, 1000, or 1500 ppm. In each study, a separate group of mice was exposed to 1000 ppm 1,3-butadiene (BD) so that a comparison could be made between the two compounds. Likewise, cyclophosphamide was also included for rats as a positive control. Bone marrow was collected from VCH-exposed animals approximately 24 h and 48 h after the final exposure. There were no statistically significant increases in micronucleatedpolychromatic erythrocytes (MN-PCEs) among VCH-treated mice and rats at any dose level or sampling interval at either 2-days or 13-weeks. Also, no statistically significant differences in the polychromatic erythrocytes (PCE) to normochromatic erythrocytes (NCE) ratios were observed in any of the VCH-treated mice and rats compared to air-exposed animals. As expected, both the butadiene-treated mice and the cyclophosphamide-treated rats showed significantly more MN-PCEs than the control animals.

In vitro metabolism of 4-vinylcyclohexene in rat and mouse liver, lung, and ovary

4-Vinylcyclohexene (4-VCH), the dimer of 1,3-butadiene, is an ovarian toxicant in mice due to the formation of a diepoxide metabolite, but the tissue-specific site of formation of the metabolites is unknown. Microsomal preparations from liver, lung, and ovaries obtained from female Crl:CD BR rats and female B6C3F1 mice were tested for their ability to metabolize the following reactions: 4-VCH to 4-VCH-1,2-epoxide and 4-VCH-7,8-epoxide; 4-VCH-1,2-epoxide to 4-VCH diepoxide and 4-VCH-1,2-diol; 4-VCH-7,8-epoxide to 4-VCH diepoxide and 4-VCH-7,8-diol; and hydrolysis of 4-VCH diepoxide. Microsomes were incubated with the test chemical and the reaction products were analyzed by gas chromatography. Rat liver and lung microsomes and mouse liver and lung microsomes metabolized 4-VCH to 4-VCH-1,2-epoxide at detectable rates. Mouse liver had a Vmax for the reaction that was 56-fold higher than that for rat liver (11.1 and 0.20 nmol/min/mg protein, respectively). The Vmax for mouse lung was 2-fold higher than that for rat lung. 4-VCH-1,2-epoxide formation was not detected in ovarian microsomes from rats or mice. Metabolism of 4-VCH to 4-VCH-7,8-epoxide was detected in microsomes from rat liver and mouse liver and lung, at rates very low compared to those for metabolism to the 1,2-epoxide. Rat and mouse liver had very similar K(m) and Vmax values for metabolism of 4-VCH-1,2-epoxide to 4-VCH diepoxide. The Vmax for rat liver was 3.69 and for mouse liver was 5.35 nmol/min/mg protein. Rat and mouse ovaries did not have detectable capacity to metabolize 4-VCH-1,2-epoxide to the diepoxide. Rat and mouse liver and lung have very similar K(m) and Vmax values for metabolism of 4-VCH-7,8-epoxide to the diepoxide, while ovaries did not have detectable rates for this reaction. Hydrolysis of 4-VCH-1,2-epoxide to 4-VCH-1,2-diol was at similar rates in rat and mouse liver microsomes. Hydrolysis of 4-VCH-7,8-epoxide to 4-VCH-7,8-diol was detected only in rat liver microsomes. Hydrolysis of 4-VCH diepoxide was detected in rat and mouse liver and lung, and in rat ovary microsomes. The Vmax for rat liver was 9-fold greater than that for mouse liver (5.51 and 0.63 nmol/min/mg protein, respectively), and lung and ovary tissues were not as active as rat liver. The balance of activation versus detoxication reactions in rats and mice suggests that the mouse may be more susceptible to 4-VCH toxicity because of generation of high levels of epoxide metabolites. In general, the mouse is more efficient at metabolism of 4-VCH to epoxides than is the rat. In contrast, the rat may be more efficient at hydrolysis of epoxides. Thus, the rat would tend to produce a lower concentration of epoxide metabolites than the mouse, at equal doses of 4-VCH.

Toxicological considerations in evaluating indoor air quality and human health: impact of new carpet emissions

This review article considers evidence regarding the toxicological impact of new carpet emissions on indoor air quality and human health. It compares emissions data from several studies and describes the dominant compounds found in those emissions. The toxicity of each these compounds is assessed for animal and human data, with a focus on inhalation exposure. Data for acute and chronic exposures are presented, and synergistic effects are considered. Differences and similarities between health responses caused by toxicity and/or by immunological reactions are discussed. Possible neurogenic pathways and associations between these and immune changes are considered as they might relate to inflammatory-based human reactions. Additionally, factors affecting human odor responses are described. The roles that a variety of psychological factors may also play in the etiology of potentially related phenomena, such as the sick building syndrome, pathogenic illness, and multiple chemical sensitivity, are considered. Gaps in the literature are identified within the article and suggestions for future research are offered. In particular, it is noted that few, if any, prior studies have evaluated both neurogenic and immune-mediated inflammation status within the same study. Based on the present information available, it is concluded that under normal environmental circumstances, VOC emissions from new carpets are sufficiently low such that they should not adversely affect indoor air quality or pose significant health risk to people.

Long-term ovarian and gonadotropin changes in mice exposed to 4-vinylcyclohexene

This study investigated the relationships between 4-vinylcyclohexene-induced follicular destruction, plasma FSH levels, and the development of ovarian preneoplastic changes. Female, 28-day-old, B6C3F1 mice were administered VCH (800 mg/kg/day, ip) or sesame seed oil, ip daily for 30 days. At 30, 60, 120, 240, and 360 days following the beginning of treatment, groups were killed, their ovaries were harvested, and plasma was collected for measurement of FSH. Ovarian weight was less and oocytes contained in preantral follicles were significantly fewer than controls at all time points. Plasma FSH concentrations in VCH-treated animals were increased significantly above controls at 240 d and 360 d. Histologically, there was oocyte loss at all times, whereas at 240 and 360 days, small to medium, irregularly shaped foci of hypertrophic cells were present. In addition, at 360 days 80% of the VCH-treated mice had a 1- to 2-mm, blood-filled cystic structure present in one or both ovaries. These studies indicate that VCH-induced oocyte destruction and follicle loss are associated with increases in plasma FSH, are associated with ovarian failure at 360 days, and are temporally related to ovarian cellular hypertrophy and the formation of blood-filled cystic ovarian structures. These events are possibly related to ovarian neoplasms produced by long-term exposure to VCH.

Comparison of the disposition and in vitro metabolism of 4-vinylcyclohexene in the female mouse and rat

4-Vinylcyclohexene (VCH) is a chemical to which humans are exposed in the rubber industry. A chronic carcinogenicity bioassay conducted by the National Toxicology Program showed that oral administration of VCH induced tumors in the ovaries of mice but not in those of rats. The hypothesis tested was that the species and organ specificity of VCH toxicity was due to differences in the disposition of VCH between the female rat and mouse. Therefore, the disposition of a single oral dose of 400 mg/kg [14C]VCH was studied in female B6C3F1 mice and Fischer 344 rats. Mice eliminated greater than 95% of the dose in 24 hr, whereas rats required 48 hr to eliminate greater than 95% of the dose. The major routes of excretion of [14C]VCH-derived radioactivity were in the urine (50-60%) and expired air (30-40%). No evidence was obtained to indicate that the ovaries of either species retained VCH as a parent compound or as radioactive equivalents. A dramatic difference was observed between the rat and mouse in the appearance of a monoepoxide of VCH in blood from 0.5 to 6 hr after VCH administration (800 mg/kg, ip). VCH-1,2-epoxide was present in the blood of mice with the highest concentration at 2 hr (41 nmol/ml). The blood concentration of VCH-1,2-epoxide in rats was less than 2.5 nmol/ml at all times examined. VCH-7,8-epoxide was not present in the blood of either species at the level of detection. These findings were supported by in vitro studies of VCH epoxidation by liver microsomes. The rate of epoxidation of VCH (1 mM) to VCH-1,2-epoxide was 6.5-fold greater in mouse liver microsomes than that in rat liver microsomes. The species difference in the rate of epoxide formation by the liver may be an important factor in the species difference in susceptibility to VCH-induced ovarian tumors.

The role of epoxidation in 4-vinylcyclohexene-induced ovarian toxicity

4-Vinylcyclohexene (VCH) is present in gases discharged during synthetic rubber production. Chronic treatment of B6C3F1 mice and F-344 rats with VCH by gavage has been shown to induce ovarian tumors in mice but not in rats. Our objective was to understand the mechanism of the species difference in VCH-induced ovarian tumors. Since a critical step in the induction of ovarian tumors is destruction of the small oocyte, small oocyte counts obtained from serially sectioned ovaries were used as an index of toxicity. VCH or its epoxide metabolites [VCH-diepoxide, VCH-1,2-epoxide, and VCH-7,8-epoxide (in mice only)] were given to 28-day-old female mice and rats in corn oil, ip, at doses ranging from 0.07 to 7.4 mmol/kg body wt/day for 30 days. The dose which reduced the small oocyte count to 50% that of control was defined as the ED50. In mice, the ED50 for the reduction in small oocytes by VCH was 2.7 mmol/kg, whereas, no detectable oocyte loss occurred in rats at the highest dose of VCH (7.4 mmol/kg). The potency of the epoxides of VCH was greater than that of VCH in both species. The ED50 for oocyte loss by VCH-1,2-epoxide in mice and rats was 0.5 and 1.4 mmol/kg, respectively. In mice, VCH-7,8-epoxide had comparable potency to VCH-1,2-epoxide (ED50 = 0.7). VCH diepoxide was even more potent with ED50 values of 0.2 and 0.4 mmol/kg, in mice and rats, respectively. The dose response of the blood concentration of VCH-1,2-epoxide in mice after VCH showed that doses of VCH which caused minimal toxicity had the lowest blood level of this ovotoxic epoxide. Pretreatment of mice with the cytochrome P450 inhibitor chloramphenicol (200 mg/kg, ip) inhibited VCH epoxidation in vivo and in vitro and partially protected mice from VCH toxicity. Thus it appears that metabolism of VCH to epoxides and their subsequent destruction of oocytes are critical steps in VCH-induced ovarian tumors. Rats may be resistant to ovarian tumor induction by VCH because the amount of VCH converted to epoxides is insufficient to produce oocyte destruction.

Toxicological evaluation of 4-vinylcyclohexene. I. Prechronic (14-day) and subchronic (13-week) gavage studies in Fischer 344 rats and B6C3F1 mice

4-Vinylcyclohexene (VCH), a dimer of 1,3-butadiene present in the gases discharged during tire curing, was examined for its toxic effects in Fischer 344 (F344) rats and B6C3F1 mice by 14-d prechronic and 13-wk subchronic testing. In the 14-d studies, VCH was administered orally by gavage in corn oil at doses of 0 (vehicle control), 300, 600, 1250, 2500, or 5000 mg/kg body weight to groups of five F344 rats and B6C3F1 mice of each sex, while the doses for the 13-wk studies (10 animals/group; 5 d/wk) were 0 (vehicle control), 50, 100, 200, 400, or 800 mg/kg body weight for rats and 0 (vehicle control), 75, 150, 300, 600, or 1200 mg/kg body weight for mice. All rats and most mice in the 14-d studies died when administered doses greater than or equal to 1250 mg/kg, although no compound-related gross or histopathologic effects were observed. In the 13-wk studies, extensive mortality was observed only in mice dosed at 1200 mg/kg. Final body weights were reduced in the 13-wk studies in male rats receiving doses greater than or equal to 400 mg VCH/kg, in female rats receiving 800 mg/kg, and in female mice receiving 600 mg/kg. Compound-related histopathologic effects in the 13-wk studies included hyaline droplet degeneration of the proximal convoluted tubules of the kidney in dosed male rats, the severity of which was dose-related, and a reduction in the number of primary follicles and mature graafian follicles in the ovaries of female mice receiving 1200 mg VCH/kg. No compound-related gross or histopathologic effects were evident in dosed female rats or male mice in the 13-wk studies.