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

Ovarian toxicity of 4-vinylcyclohexene diepoxide: a mechanistic model

Female mammals are born with a finite number of ovarian primordial follicles that cannot be regenerated; thus, chemicals that destroy oocytes contained in these follicles can produce premature ovarian failure (early menopuase in women). Exposure of women to known ovotoxicants, such as contaminants in cigarette smoke, is associated with early menopause. Thus, the potential risks posed by ovotoxic chemicals is of concern. Our studies have focused on the environmental chemical 4-vinylcyclohexene (VCH), which is produced during the manufacture of rubber tires, flame retardants, insecticides, plasticizers, and antioxidants. Dosing of female rats and mice with the ovotoxic diepoxide metabolite of VCH, 4-vinylcyclohexene diepoxide (VCD), for 30 days destroyed the majority of ovarian primordial follicles. Using VCD in rats as a generalized model for ovotoxicity, we determined that 1) repeated daily dosing is required, 2) cell death is via apoptosis, and 3) altered expression of specific genes is involved. An integrated approach at the morphologic, biochemical, and molecular level was used to support these conclusions. Studies in isolated rat small preantral follicles (targeted for VCD-induced ovotoxicity) focused on the role of cell death genes, mitochondrion-associated events, and VCD metabolism. We also evaluated how this information relates to human risk for early menopause. These animal research results provide a better understanding of the potential risk of human exposure to environmental ovarian toxicants and greater insight as to the impact of these toxicants on reproductive health in women.

Ovotoxicity in female Fischer rats and B6 mice induced by low-dose exposure to three polycyclic aromatic hydrocarbons: comparison through calculation of an ovotoxic index

Extensive destruction of primordial follicles by exposure to ovarian toxicants can cause early menopause in women. Primordial follicle destruction is known to result from dosing of mice and rats with three polycyclic aromatic hydrocarbons (PAHs), contaminants commonly found in cigarette smoke. Therefore, the purpose of this study was to compare relative ovotoxicity in mice and rats using the PAHs, 9, 10-dimethylbenzanthracene (DMBA), 3-methylcholanthrene (3-MC), and benzo[a]pyrene (BaP). Female B6C3F(1) mice and Fischer 344 rats (age 28 days) were dosed daily (ip) with vehicle control or a range of doses of the PAHs. Two groups were dosed with the occupational chemicals 4-vinylcyclohexene (VCH; 500 mg/kg ip) or its diepoxide metabolite (VCD; 80 mg/kg ip), other known ovotoxicants. After 15 days, ovaries were collected, histologically prepared, and follicles were microscopically classified (primordial, primary, or secondary) and counted. The dose of each chemical that produced 50% loss of primordial follicles (p < 0.05) was determined (ED50) and used to calculate an ovotoxic index (OI) in mice and rats (ED50 x 15 days). Thus, a chemical with a lower OI is more toxic. Primordial follicles in mice displayed a lower OI than rats to all chemicals tested (mouse: DMBA, 0.0012; 3-MC, 0.003; BaP, 0.18; VCD, 6.8; VCH, 69; rat: DMBA, 0.45; 3-MC, >3.4; BaP, >3.6; VCD, 8.6; VCH, >69). In mice, DMBA targeted primordial follicles at a 10-fold lower concentration than primary and secondary follicles, whereas 3-MC exposure targeted primordial and primary follicles to a similar degree. BaP exposure targeted primordial and primary follicles at a 100-fold higher concentration than DMBA or 3-MC. Although BaP and 3-MC did not target secondary follicles in mice, secondary follicles in rats were most susceptible to 3-MC. Furthermore, all three PAHs were more ovotoxic (lower OI) with repeated low-dose exposure compared with OIs calculated from other studies using single high-dose exposures. The earliest day of impending primordial follicle loss (increase in percentage of unhealthy follicles, p < 0.05) in mice was factored into the OI (ED50 x first day of damage, p < 0.05 x % healthy follicles remaining, relative to control). The revised OI became DMBA d15, 0.0006; 3-MC d12, 0.0008; BaP d15, 0.132; and VCD d8, 2.96. These results predict that DMBA is the most potent ovarian toxicant (lower OI) in both species but VCD damages primordial follicles after shorter exposures. Calculation of the OI in mice and rats represents a method for comparing the relative potential risk of a variety of chemicals that produce ovarian damage at low levels following repeated exposures. The results also demonstrate that low-dose repeated exposures are substantially more toxic to the ovary than a single high-dose exposure. This finding is particularly important in view of the implications for chronic low-dose exposures of women to environmental chemicals.

Influence of 2-bromopropane on reproductive system--short-term administration of 2-bromopropane inhibits ovulation in F344 rats

The present study was performed to investigate the toxic effects of 2-bromopropane (2BP) on the female reproductive system. Female F344 rats were administered 2BP (500 or 1000 mg/kg, i.p.) at intervals of 2 or 3 days for 15-17 days. The body weights were measured and estrous stages were observed throughout the experimental period. Ovulation, organ weights, ovarian histology, and blood biochemistry were investigated on the terminal day of the experiment. Uterine weights in rats treated with 2BP were significantly lower than those in control animals. Body, liver, kidney, and adrenal weights in 2BP-treated rats showed no significant differences from control values. 2BP treatment prolonged estrous cycles and decreased the number of ovulated ova in spontaneous ovulation. In addition, histological examinations showed that the preovulatory follicles in the ovary were altered markedly in 2BP groups. These results show that even in short-term treatment, 2BP injured the ovary, particularly the preovulatory follicles. It appears that these damages of the preovulatory follicles induced by 2BP reduced the numbers of spontaneously ovulated ova in female F344 rats.

2-Bromopropane causes ovarian dysfunction by damaging primordial follicles and their oocytes in female rats

Ovarian dysfunction induced by 2-bromopropane (2-BP) has been described in female factory workers and experimental animals. However, the underlying mechanism is still unclear. To establish the reproductive target site and define mechanisms of 2-BP toxicity in adult female rats, we examined the effects of different doses and duration of exposure to 2-BP in female rats. In the dose-dependent experiments, female rats were exposed to 2-BP at 100, 300, or 1000 ppm or fresh air (n = 9 each) in exposure chambers for 8 h/day for 9 weeks. In the time-course experiments, female rats were exposed to 2-BP at 3000 ppm for 8 h (n = 7 each). The rats were then euthanized 1, 3, 5, and 17 days after exposure. Differential follicle counts and in situ terminal deoxynucleotidyl transferase assay were used to evaluate 2-BP effect on primordial, growing, and antral follicles. Exposure to 2-BP at 300 and 1000 ppm produced a significant reduction in the percentage of primordial, growing, and antral follicles in a dose-dependent manner. Significant reduction in the percentage of primordial follicles at 17 days after exposure was observed in time-course experiments. Exposure to 2-BP at 3000 ppm for 8 h resulted in histological changes in primordial follicles complex at 5 and 17 days after exposure. These changes consisted of distortion of the symmetry of oocytes and their nuclei at Day 5 after exposure and appearance of eccentric pyknotic cells and shrinkage of oocyte nuclei at Day 17 after exposure. In situ end labeling showed increased numbers of apoptotic oocytes and granulosa cells in primordial follicles at Days 5 and 17 after exposure. Our results suggested that ovarian dysfunction induced by 2-BP was caused by the destruction of primordial follicle and its oocyte due to the induction of apoptosis. Our studies also show that the follicle differential count is a more sensitive method than the vaginal smear in monitoring the female reproductive disorders induced by 2-BP.

A single dose of the ovotoxicant 4-vinylcyclohexene diepoxide is protective in rat primary ovarian follicles

Repeated dosing of rats with the ovotoxic chemical, 4-vinylcyclohexene diepoxide (VCD), destroys primordial and primary ovarian follicles via apoptosis (physiological cell death) by accelerating the normal rate of atresia. The present study investigated the effect of a single dose (1x) of VCD. Immature (d28) female Fischer 344 rats were dosed 1x or 15x with VCD (80 mg/kg ip). Ovaries were collected 24 h or 15 days following 1x VCD or after 15x for classification and evaluation. Following 1x VCD the number of healthy primary follicles was greater (p < 0.05) than control 24 h and 15 days later. This effect reflected a slowing of the normal rate of atresia seen in control ovaries. There was no effect of a single dose on primordial or growing follicles at any time. Expression of mRNA encoding the cell death gene bax was reduced (p < 0.05) on d1 after 1x VCD in isolated primordial and primary follicles. These observations were in contrast to a decreased (p < 0. 05) number of healthy primary and primordial follicles in ovaries and increased (p < 0.05) bax mRNA in isolated follicles from rats dosed 15x for 15 days. Immunofluorescence staining revealed that, the distribution of Bax protein was similar between ovaries from controls and 1x or 15x VCD-treated rats. These data provide evidence for a "protective" response against the normal rate of atresia in primary ovarian follicles following exposure to 1x VCD. Additionally, changes in expression of bax mRNA paralleled alterations in the rate of atresia.

Environmental toxicants and female reproduction

OBJECTIVE

To review current knowledge on the potential effects of environmental toxicants on female reproduction in laboratory animals, wildlife, and humans.

DESIGN

Published literature about the effects of endocrine disruptors, heavy metals, solvents, pesticides, plastics, industrial chemicals, and cigarette smoke on female reproduction.

RESULT(S)

Published data indicate that chemical exposures may cause alterations in reproductive behavior and contribute to subfecundity, infertility, pregnancy loss, growth retardation, intrauterine fetal demise, birth defect, and ovarian failure in laboratory animals and wildlife. Data on the association of chemical exposures and adverse reproductive outcomes in humans are equivocal and often controversial. Some studies indicate that chemical exposures are associated with infertility, spontaneous abortion, or reproductive cancer in women. In contrast, other studies indicate that there is no association between chemical exposures and adverse reproductive outcomes. The reasons for ambiguous findings in human studies are unknown but likely include the fact that many studies are limited by multiple confounders, inadequate methodology, inappropriate endpoints, and small sample size. The mechanism by which chemicals alter reproductive function in all species is complex and may involve hormonal and/or immune disruption, DNA adduct formation, altered cellular proliferation, or inappropriate cellular death.

CONCLUSION(S)

Studies are needed to clarify which toxicants affect human reproduction and by which mechanisms of action. Furthermore, methods should be developed to minimize exposure to known reproductive toxicants such as dioxins and cigarette smoke.

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.

Species difference in the ovarian toxicity of 1,3-butadiene epoxides in B6C3F1 mice and Sprague-Dawley rats

1,3-Butadiene (BD) is an ovarian carcinogen in mice, but not in rats. Since species variation in metabolism of BD has been associated with the greater sensitivity of mice to BD-induced carcinogenicity, the extent of biotransformation and detoxification of BD and its epoxides may play a critical role in other ovotoxic effects of this compound. Thus, the ovotoxic potency of the BD epoxides was determined. Butadiene monoepoxide (BMO, 0.005-1.43 mmol/kg b.w.), butadiene diepoxide (BDE, 0.002-0.29 mmol/kg b.w.), or vehicle was administered i.p. to female B6C3F1 mice and Sprague-Dawley rats for 30 days. Following day 30, tissues were removed and weighed, and the number of pre-antral ovarian follicles counted. BMO was ovotoxic in mice as demonstrated by decreases in reproductive organ weights (1.43 mmol/kg b.w.) and follicular counts, but not in rats at any dose tested. In mice the ED50 values for BMO for small and growing follicles were 0.29 and 0.40 mmol/kg b.w., respectively. BDE was ovotoxic in both species, however mice were more sensitive to BDE than rats. Ovarian and uterine weights were decreased in mice at 0.14 and 0.29 mmol/kg b.w. of BDE treatment, and in rats at 0.29 mmol/kg b.w. only. The ED50 values for BDE in mice were 0.10 and 0.14 mmol/kg b.w. for small and growing follicles, respectively, ED50 values could not be determined in rats since only 32% of the follicular population was depleted at the highest concentration tested. Thus, BMO and BDE exhibited a greater ovotoxic potential in mice, as compared to rats. In addition, in each species the diepoxide was the most potent ovotoxicant.

Review of reproductive and developmental toxicity of 1,3-butadiene

Toxic doses of 1,3-butadiene (BD) have been reported to cause reproductive and/or developmental toxicity. Regardless of the strain used, mice were always affected by BD at lower doses than rats, an expected observation, based on well recognized differences in pharmacokinetic (PK) parameters in these two species. Because the mouse is particularly sensitive to BD in comparison with other laboratory species, and there are important functional and anatomical differences between humans and mice, the NOELs and LOELs identified for BD for various reproductive endpoints in mice may not be relevant to human reproductive risk. In mice, the LOELs for reproductive endpoints include developmental toxicity at 200 ppm, genotoxic effects at 500 ppm (mouse spot test), ovarian atrophy in females at 6.25 ppm (carcinogenicity study), reduced testicular weights at 200 ppm and testicular atrophy at 625 ppm BD in males (carcinogenicity studies), low incidences of abnormal sperm heads at 1000 and 5000 ppm BD (sperm head morphology study), small reversible increases in resorption at 1250/1300 ppm or 5000 ppm (dominant lethal studies), and other possible sequelae of genotoxicity resulting from exposure of male mice at 12.5 ppm BD and higher (dominant lethal study). When available, the much higher NOELs and LOELs of other species tested for the same endpoints should be considered. For example, maternal and developmental NOELs for BD in the rat were 200 and 1000 ppm, respectively, and 40 ppm in the mouse. Likewise, exposure of cohabited pairs of rats, guinea pigs and rabbits or of female dogs to BD concentrations as high as 6700 ppm for 8 months did not impair fertility or cause testicular or ovarian atrophy in these species. Thus, consideration of these remarkable species-dependent differences in toxicity is necessary. In addition, there are alternative scientific interpretations for some of the mouse studies and this review attempts to address these areas. For example, it may be incorrect to categorize results indicating weak in vivo genotoxic effects in male mice (sperm head morphology and dominant lethal studies) at 12.5 ppm BD and higher as reproductive effects because concentrations of BD as high as 5000 ppm did not affect mating, fertility or live litter sizes, even in this sensitive species. Similarly, it may be inappropriate to identify the ovary as a target organ for reproductive risk since the ovarian atrophy in mice was identified after completion of the normal reproductive life and after more than 15 months of exposure. Neither ovarian nor testicular atrophy occurred in Sprague-Dawley rats after exposure to BD concentrations as high as 8000 ppm for 105 (females) or 111 (males) weeks.

In vitro and in vivo (32)P-postlabeling analysis of 4-vinyl-1-cyclohexene (butadiene dimer) diepoxide-DNA adducts

4-Vinyl-1-cyclohexene diepoxide (VCD), and industrial chemical, and its parent compound, 4-vinyl-1-cyclohexene (VCH), are potential health hazards, a they destroy oocytes in follicles in rodents. VCD is also a skin carcinogen at the site of application in both female and male mice and rats and after gavage, induces ovarian tumors in mice and forestomach tumors in rats. A (32)P-postlabeling assay was developed for the detection and measurement of VCD-DNA adducts. VCD, a direct-acting carcinogen, was reacted with DNA in vitro, as well as through mouse skin painting for 3 days with different doses of VCD. (32)P-Labeled adducts were separated by polyethyleneimine (PEI)-cellulose TLC and detected by screen-enhanced autoradiography. Comparable adduct profiles were obtained in vitro and in vivo. At higher doses (36-225 micro mol/mouse), adduct levels in vivo showed a linear dose response, while there was no difference between 14 and 36 micro mol/mouse. The limit of detection was estimated to be 1-3 adducts in 10(8) DNA nucleotides. The results show that VCD exposure gives rise to (presumably pre-mutagenic) DNA adducts in vivo and that (32)P-postlabeling can be applied to biomonitoring of VCD exposure.

Follicular mechanisms associated with 4-vinylcyclohexene diepoxide-induced ovotoxicity in rats

The mechanism of 4-vinylcyclohexene diepoxide (VCD)-induced oocyte destruction in small preantral follicles of rats and mice has not been elucidated. This study examined the effects of daily dosing of female rats with VCD on protein synthesis and follicle viability. An investigation of granulosa cells as a target for VCD was also made. Small preantral follicles (25 to 100 microns) isolated from untreated immature rats (day 28) as well as from rats injected daily for 10 d with VCD (0.57 mmol/kg, IP) or vehicle control (sesame oil) were incubated for 3, 6, or 10 h in vitro with or without VCD. Viability (trypan blue dye exclusion) or protein synthesis (3H-leucine incorporation) in follicles was measured. Large preantral follicles (100 to 250 microns), isolated oocytes or granulosa cells from small preantral follicles, hepatocytes, and adrenal cells served as controls. Viability was not compromised in small follicles isolated from untreated or VCD-injected rats. However, following in vitro incubation of small preantral follicles with VCD, there was a significant decrease in viability by 6 h. This loss in viability was observed in granulosa cells and was even greater in follicles from dosed as compared with undosed animals. The various cell types were incubated in vitro with or without VCD for 3 h and the rate of protein synthesis was measured by 3H-leucine incorporation during the last hour of incubation. Incubation of small preantral follicles from untreated animals with VCD for 3 h produced significant inhibition in the rate of protein synthesis. This effect was reversed and significantly stimulated after 6 and 10 h of incubation with VCD. Follicles from animals that had been dosed daily with VCD for 10 d demonstrated similar inhibition of protein synthesis following 3 h in vitro incubation with VCD; however, unlike those from undosed rats, follicles from dosed rats did not recover from this inhibition after 6 or 10 h of in vitro incubation with VCD. In vitro incubation with VCD stimulated the rate of protein synthesis in large preantral follicles; however, no effect on the rate of protein synthesis was observed in isolated oocytes and granulosa cells, hepatocytes, or adrenal cells. These observations suggest that VCD affects follicular viability via an effect on granulosa cells and that daily dosing of rats with VCD makes small preantral follicles more susceptible to ovotoxicity by VCD.

Testicular germ cell toxicity caused by vinylcyclohexene diepoxide in mice

Vinylcyclohexene diepoxide (VCD) produces ovarian toxicity in female mice and rats, whereas testicular damage occurs only in mice. The objectives of these studies were to determine the target cell(s) and spermatogonial survival following VCD administration. In addition, the effects of 4-vinylcyclohexene (VCH) and two epoxide metabolites, vinylcyclohexene 1,2-monoepoxide and VCD were compared. Male mice were dosed daily with VCD (320 mg/kg/d, i.p.) and killed at 5, 10, 15, 20, 25, or 30 d. Two groups were dosed daily for 30 d and allowed to recover for 30 or 60 d. Decreases in testis weight began at 5 d and continued to 30 d. These decreases corresponded to progressive necrosis of germ cells. After 5 d of VCD, there was loss of Type I and B spermatogonia in Stages II to VI and of preleptotene spermatocytes in Stages VI to VIII. After 30 d of dosing, seminiferous tubules were devoid of germ cells except for spermatogonial stem cells. Following 30 d of recovery, 100% of the seminiferous tubules were repopulated. Epididymal spermatozoa were present after 60 d of recovery. Increasing doses of VCD (0 to 320 mg/kg/d) resulted in increasing testicular toxicity. Neither VCH (800 mg/kg, i.p.) nor VCM (200 mg/kg, i.p.) caused testicular damage. VCD administration initially results in destruction of spermatogonia and spermatocytes, which are undergoing DNA synthesis and cell replication, followed by loss of maturing cells. Neither VCH nor VCM caused testicular germ cell destruction, although all three compounds destroy germ cells in female mice. Therefore, further investigation will be necessary to understand these differences in chemical-induced toxicity between ovaries and testes.

Destruction of preantral follicles in adult rats by 4-vinyl-1-cyclohexene diepoxide

4-vinyl-1-cyclohexene diepoxide (VCD) is known to destroy oocytes in ovaries of immature rats. Since ovaries functionally differ between immature and adult animals, we examined the effect of VCD on oocytes in adult rats. Adult (58 days) and immature (28 days) rats were injected daily (30 days) with vehicle or VCD. Each group contained 10 rats. During this time, cyclicity was determined daily by vaginal cytology. Animals were terminated on day 31 and tissues were collected. Oocytes were counted; livers, spleens, and uteri were weighed. VCD reduced the number of regular estrous cycles/30 days in adults, but not immature rats (n = 20, P < 0.05). VCD reduced the number of oocytes in adult and immature rats (n = 20, P < 0.05). Liver, spleen, or ovarian weights were not affected by VCD in either group. VCD reduced uterine weight in adult (n = 20, P < 0.05) but not in immature rats. These results demonstrate that VCD decreases uterine weight in adult rats and as with immature rats, selectively destroys oocytes in ovaries of adults.

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.

Hexachlorobenzene toxicity in the monkey primordial germ cell without induced porphyria

Hexachlorobenzene is a persistent chlorinated organic chemical that has been detected in many tissues from a variety of species including human ovary and human ovarian follicular fluid. When administered in high dosage to nonhuman primates, hexachlorobenzene causes destruction of ovarian primordial germ cells in association with systemic toxicity. The purpose of these experiments was to assess relative ovarian germ cell sensitivity at much lower dosages of hexachlorobenzene that do not produce systemic effects and additionally to evaluate oocyte function by means of the response to superovulation, fertilization, and embryo cleavage during a cycle of in vitro fertilization in the cynomolgus monkey. Hexachlorobenzene in dosages of 0.1, 1.0, and 10.0 mg/kg/day was administered orally by gelatin capsule for 90 days. There was a dose-dependent accumulation of HCB in serum and other tissues without any change in the serum estradiol response to human menopausal gonadotropin, oocyte recovery, oocyte maturation, oocyte fertilization in vitro, and early embryo cleavage rate. There was a dose-related toxic effect observed in primordial germ cells at the lowest dose despite no evidence of systemic or hepatic effects. As there were no changes in the urinary porphyrin excretion, the mechanism of hexachlorobenzene ovotoxicity may be distinct from hexachlorobenzene-induced cytochrome P-450-dependent inhibition of uroporphobilinogen decarboxylase in the liver, although such intraovarian metabolism cannot be excluded.

Comparison of random and serial sections in assessment of ovarian toxicity

Assessment of ovarian toxicity by follicle quantitation and morphometric analysis of serial sections is time consuming and expensive. This report compares the estimation of follicle number obtained from counting oocytes in serial sections or 5 random sections of mouse ovaries. Ovaries were obtained from C57BL/6N and B6C3F1 mice treated with ovarian toxicants. C57BL/6N mice were treated with cyclophosphamide (0, 75, 200, and 500 mg/kg, ip) and killed at 24, 72, and 168 h. B6C3F1 mice were treated daily, ip, with 4-vinylcyclohexene (0, 100, 400, and 800 mg/kg/day for 30 days), vinylcyclohexene diepoxide (0, 10, 40, and 80 mg/kg/day for 30 days), or benzo(a)pyrene (100 mg/kg, single dose) and killed on day 31. Ovarian serial sections were prepared and oocytes counted in every tenth section. When serial sections were evaluated, 30 to 60 sections were counted. Random section counting involved randomly selecting 5 sections from the 30 to 60 sections previously counted by the serial method. Chemically-induced follicle loss was evident by the reduction in follicle counts relative to control animals when estimating follicle number using serial or random section counting. Furthermore, a linear regression analysis of follicle counts over all treatment groups showed that the highest correlation between random and serial section counting and was for primordial follicles. Correlation coefficients (R2) for each follicle type were: primordial--C57BL/6N 0.82, B6C3F1 0.86; growing--C57BL/6N 0.16, B6C3F1 0.46; antral--C57BL/6N 0.07, B6C3F1 0.11. Although other screens may need to be developed for growing and antral follicles, primordial follicle toxicity is adequately defined by counting 5 random sections.