Inhalation toxicity of methylglutaronitrile in rats

Methylglutaronitrile (MGN) is a high-boiling (263 degrees C) solvent/intermediate used in the fiber industry. Twenty male rats per group were exposed nose-only to condensation aerosol/vapor concentrations of approximately either 5, 25, or 200 mg/m3 of MGN for 6 h/day, 5 days/week over a 4-week period. Ten rats/group were sacrificed one day after the final exposure and the remaining rats after a four-week recovery period. No effects were observed in clinical observations during the exposure period, but body-weight depression was observed in the 200 mg/m3 group. The 200 mg/m3 group showed minimal decreases in red blood cell count, hemoglobin, and hematocrit values accompanied by increases in reticulocytes. There were no other effects observed in clinical or pathologic evaluations in the study. A neurobehavioral battery of tests (including grip strength, functional observational battery, and motor activity tests) given at the end of the exposure and recovery periods showed no MGN effects. During the 4-week recovery, body weights in the 200 mg/m3 group returned to normal and the hematologic findings in all groups were normal. Based on the above findings of body weight depression at 200 mg/m3, the no-observed-adverse-effect level (NOAEL) for this study was considered to be 25 mg/m3.

Effects of the rat hepatic peroxisome proliferator, Wyeth 14,643, on the lactating goat

Some peroxisome proliferators have been reported to reduce body weight gain in suckling rats, possibly through a lactational effect. Decreases in milk production or nutritional quality, either as a result of peroxisome proliferator-induced reductions in lipid content or alterations in the hormonal milieu necessary for milk production, could result in pup growth retardation. Wyeth-14,643 (WY) is hypolipidemic agent and a potent inducer of hepatic peroxisome proliferation in rats and mice. As is commonly seen with rodent hepatic peroxisome proliferators, WY produces minimal or no peroxisome induction in guinea pigs or non-human primates. Goats are an excellent model for studying lactation, however, their sensitivity to peroxisome proliferating chemicals is not known. The present study was performed to assess the sensitivity of goats to the hypolipidemic and peroxisome proliferator properties of WY and to determine the effects of WY on milk quantity and quality. Six lactating adult female goats were assigned to either control or treated groups. Goats in the treated group were administered WY (40 mg/kg/day) for 14 consecutive days. The goats were milked twice daily in order to maintain lactation and the quantity of milk collected was recorded. Milk quality was evaluated by determining the content of total fat, protein, and carbohydrate in milk samples collected following 7 and 14 days of treatment. WY administration had no effects on final body weight, liver weight or, gross and histopathological findings. Milk quantity and quality were unaffected by treatment. Serum cholesterol and triglyceride levels were reduced by 25% compared to controls, although only the difference in cholesterol was statistically significant. Hepatic beta-oxidation (3 x control) and aromatase (1.5 x control) activities were significantly greater in the treatment group; however, there was no treatment-related effect in the total content of hepatic cytochrome P450. There was no difference in aromatase activity in a pooled ovarian microsome sample. Milk estradiol and prolactin concentrations were not affected by treatment. These findings indicate that goats are weak responders to the hepatic peroxisome proliferator effects of WY. Additionally, the slight serum hypolipidemic effect does not impact milk production or nutritional value.

Time- and concentration-dependent increases in cell proliferation in rats and mice administered vinyl acetate in drinking water

Chronic administration of vinyl acetate (VA) in drinking water to rats and mice has produced upper digestive tract neoplasms. These tumors were believed to arise from the intracellular metabolism of VA by carboxylesterases to cytotoxic and genotoxic compounds. We hypothesized that prolonged VA exposure at high concentrations would induce cytotoxicity and a restorative cell proliferation (CP). These endpoints were measured in F-344 rats and BDF1 mice administered drinking water containing 0, 1000, 5000, 10,000, or 24,000 ppm VA for 92 days. On test days, Days 1, 8, 29, and 92, upper digestive tract histopathology and oral cavity CP (pulsed 5-bromodeoxyuridine [BrdU] to measure S-phase DNA synthesis) were evaluated. Analysis of test solutions showed that VA spontaneously hydrolyzed, slowly releasing acetic acid and thereby lowering pH. Statistically significant, concentration-related increases in CP occurred in basal cells of the mandibular oral cavity mucosa of mice at 10,000 and 24,000 ppm but only after 92 days. CP increases were approximately 2.4- and 3.4-fold above controls and were considered to be toxicologically significant. Some statistically significant increases in CP were also measured in the oral cavity mucosa of rats; however, these changes were considered to be of equivocal biological relevance. No histopathological evidence of mucosal injury was seen in either species. The absence of cytotoxicity in the upper digestive tract mucosa suggests that the increased CP at high administered VA concentrations may be due to a mitogenic response, ostensibly from the loss of cell growth controls in oral cavity mucosa.

Mechanisms of extrahepatic tumor induction by peroxisome proliferators in male CD rats

Wyeth-14,643 (WY) and ammonium perfluorooctanoate (C8) belong to a diverse class of compounds which have been shown to produce hepatic peroxisome proliferation in rodents. From previous work, WY, but not C8, has been shown to produce hepatocellular carcinoma in rats, while C8 has been shown to produce Leydig cell adenomas. In addition, based on a review of bioassay data a relationship appears to exist between peroxisome-proliferating compounds and Leydig cell adenoma and pancreatic acinar cell hyperplasia/adenocarcinoma formation. To further investigate the relationship between peroxisome-proliferating compounds and hepatic, Leydig cell, and pancreatic acinar cell tumorigenesis, a 2-year feeding study in male CD rats was initiated to test the hypothesis that peroxisome proliferating compounds induce a tumor triad (liver, Leydig cell, pancreatic acinar cell), and to examine the potential mechanism for the Leydig cell tumors. The study was conducted using 50 ppm WY and 300 ppm C8. The concentration of WY in the diet was decreased to 25 ppm on test day 301 due to increased mortality. In addition to the ad libitum control, a second control was pair-fed to the C8 group. Interim sacrifices were performed at 1- or 3-month intervals. Peroxisome proliferation measured by beta-oxidation activity and cell proliferation were measured in the liver and testis at all time points and in the pancreas beginning at the 9-month time point (cell proliferation only). Serum hormone concentrations (estradiol, testosterone, LH, FSH, and prolactin) were also measured at each time point. Increased relative liver weights and hepatic beta-oxidation activity were observed in both the WY- and C8-treated rats at all time points. In contrast, hepatic cell proliferation was significantly increased only in the WY-treated group. Neither WY nor C8 significantly altered the rate of Leydig cell beta-oxidation or Leydig cell proliferation when compared to the control groups. Moreover, the basal rate of beta-oxidation in Leydig cells was approximately 20 times less than the rate of hepatic beta-oxidation. There were no biologically meaningful differences in serum testosterone, FSH, prolactin, or LH concentrations in the WY- and C8-treated rats when compared to their respective controls. There were, however, significant increases in serum estradiol concentrations in the WY- and C8-treated rats at 1, 3, 6, 9, 15, 18, and 21 months. At 12 months, only the C8-treated rats had elevated serum estradiol concentrations when compared to the pair-fed control. Histopathological evaluation revealed compound-related increases in liver, Leydig cell, and pancreatic acinar cell tumors in both WY- and C8-treated rats. The data support the hypothesis that the peroxisome-proliferating compounds induce the previously described tumor triad. In addition, both C8 and WY produced a sustained increase in serum estradiol concentrations that correlated with the potency of the 2 compounds to induce Leydig cell tumors (i.e., WY caused a more consistent sustained increase in serum estradiol throughout the entire study, and more specifically at the end of the study, than did C8). This study suggests that estradiol may play a role in enhancement of Leydig cell tumors in the rat, and that peroxisome proliferators may induce tumors via a non-LH type mechanism.

Detection of dopaminergic modulators in a tier I screening battery for identifying endocrine-active compounds (EACs)

Apomorphine (APO; D(2) receptor agonist), haloperidol (HAL; D(2) receptor antagonist), and reserpine (RES; a dopamine depletor that acts to lower brain dopamine levels by depleting central nervous system monoamines via disrupting storage vesicle function) have been examined in a Tier I screening battery, which has been designed to detect endocrine-active compounds (EACs). The Tier I battery incorporates two short-term in vivo tests (a 5-day ovariectomized female battery and a 15-day intact male battery using Sprague-Dawley rats) and an in vitro yeast transactivation system (YTS). In addition, two blood collection procedures were evaluated for their utility in detecting HAL-induced increases in serum prolactin (PRL) levels (i.e., the stress associated with each procedure). In the in vivo female battery, both HAL and RES increased serum PRL concentrations as expected, although the increase caused by RES was marginal. Increases in serum PRL levels are enhanced when daily dosages are administered via multiple-daily dosing of the test compound, which results in higher sustained blood levels of the test compounds. APO failed to decrease serum PRL concentrations in the female battery. In the in vivo male battery, HAL increased serum PRL concentrations as expected. However, APO and RES failed to affect serum PRL concentrations. The blood collection comparison experiment demonstrated that possible confounding of the data can occur with serum PRL concentrations when animals are exposed to stress. Basal levels of PRL were approximately fourfold higher in animals that were bled via the tail vein procedure when compared to PRL levels from animals that were bled under CO(2) anesthesia at euthanization. As a result of the higher basal PRL levels, the HAL-induced increase in serum PRL concentrations was completely attenuated in the tail-vein bled animals (1.3-fold). In contrast, HAL produced a fivefold increase in serum PRL in animals where blood was collected under CO(2) anesthesia at euthanization. Hence, collection of blood from animals under CO(2) anesthesia at euthanization is an acceptable approach for detection of compounds that increase PRL. In summary, HAL-like compounds would be identified in the Tier I male and female battery primarily via increased serum PRL concentrations. RES-like compounds would be identified in the Tier I male battery via decreased gonadotropins and steroids and possibly in the Tier I female battery by a minimal increase in serum PRL concentrations. Compounds that produce a marginal increase in serum PRL when administered using single daily dosing can also be confirmed in an in vivo female battery with multiple dosing because this regimen increases the magnitude of the PRL increase. APO, a D(2) receptor agonist, was not detected in the in vivo male or female batteries, but in both instances the top dosage produced minimal decreases in body weight (99 to 96% of control). Hence, the proposed Tier I battery needs to be further evaluated with higher dosages of APO and other D(2) receptor agonists to determine whether it is capable of detecting such agents.

Evaluation of a Tier I screening battery for detecting endocrine-active compounds (EACs) using the positive controls testosterone, coumestrol, progesterone, and RU486

After previously examining 12 compounds with known endocrine activities, we have now evaluated 4 additional compounds in a Tier I screening battery for detecting endocrine-active compounds (EACs): a weak estrogen receptor (ER) agonist (coumestrol; COUM), an androgen receptor (AR) agonist (testosterone; TEST), a progesterone receptor (PR) agonist (progesterone; PROG), and a PR antagonist (mifepristone; RU486). The Tier I battery incorporates 2 short-term in vivo tests (5-day ovariectomized female battery; 15-day intact male battery) and an in vitro yeast transactivation system (YTS). The Tier I battery is designed to identify compounds that have the potential to act as agonists or antagonists to the estrogen, androgen, progesterone, or dopamine receptors; steroid biosynthesis inhibitors (aromatase, 5alpha-reductase, and testosterone biosynthesis); or compounds that alter thyroid function. In addition to the Tier I battery, a 15-day dietary restriction experiment was performed using male rats to assess confounding due to treatment-related decreases in body weight. In the Tier I female battery, TEST administration increased uterine weight, uterine stromal cell proliferation, and altered hormonal concentrations (increased serum testosterone [T] and prolactin [PRL]; and decreased serum FSH and LH). In the male battery, TEST increased accessory sex gland weights, altered hormonal concentrations (increased serum T, dihydrotestosterone [DHT], estradiol [E2], and PRL; decreased serum FSH and LH), and produced microscopic changes of the testis (Leydig cell atrophy and spermatid retention). In the YTS, TEST activated gene transcription in the yeast containing the AR or PR. In the female battery, COUM administration increased uterine weight, uterine stromal cell proliferation, and uterine epithelial cell height, and increased serum PRL concentrations. In the male battery, COUM altered hormonal concentrations (decreased serum T, DHT, E2; increased serum PRL) and, in the YTS, COUM activated gene transcription in the yeast containing the ER. In the female battery, PROG administration increased uterine weight, uterine stromal cell proliferation, and uterine epithelial cell height and altered hormonal concentrations (increased serum progesterone and decreased serum FSH and LH). In the male battery, PROG decreased epididymis and accessory sex gland weights, altered hormonal concentrations (decreased serum T, PRL, FSH, and LH; increased serum progesterone and E2), and produced microscopic changes of the testis (Leydig cell atrophy). In the YTS, PROG activated gene transcription in the yeast containing the AR or PR. In the female battery, RU486 administration increased uterine weight and decreased uterine stromal cell proliferation. In the male battery, RU486 decreased epididymis and accessory sex gland weights and increased serum FSH and LH concentrations. In the YTS, RU486 activated gene transcription in the yeast containing the ER, AR, or PR. Dietary restriction data demonstrate that confounding due to decrements in body weight are not observed when body weight decrements are 10% or less in the Tier I male battery. In addition, minimal confounding is observed at body decrements of 15% (relative liver weight, T3, and T4). Hence, compounds can be evaluated in this Tier I at levels that produce a 10% decrease in body weight without confounding of the selected endpoints. Using the responses obtained for all the endpoints in the Tier I battery, a distinct "fingerprint" was produced for each type of endocrine activity against which compounds with unknown activity can be compared. These data demonstrate that the described Tier I battery is useful for identifying EACs and they extend the compounds evaluated to 16.

Detection of the environmental antiandrogen p,p-DDE in CD and long-evans rats using a tier I screening battery and a Hershberger assay

In this report, p,p'-DDE, a weak androgen receptor (AR) antagonist, has been examined in a Tier I screening battery designed to detect endocrine-active compounds (EACs). The screening battery that was used to examine p,p'-DDE was an abbreviated version of a proposed Tier I screening battery (Cook et al., 1997, Regul. ToxicoL Pharmacol. 26, 60-68) that consisted of a 15-day intact male in vivo battery and an in vitro yeast transactivation system (YTS). In addition, strain sensitivity differences were evaluated using male Crl:CDIGS BR (CD) and Long-Evans (LE) rats. Finally, p,p'-DDE was examined in a Hershberger assay designed to detect AR agonists. In the in vivo male battery using CD rats, responses to p,p'-DDE included organ weight changes (increased relative liver weight and decreased absolute epididymis weight) and hormonal alterations (increased serum estradiol [E2] levels and decreased serum FSH and T4 levels). Responses to p,p'-DDE in LE rats included organ weight changes (increased relative liver weight, absolute epididymis weight, relative accessory sex gland [ASG] unit weight, as well as the individual component weights of the ASG [prostate and seminal vesicles]), and hormonal alterations (increased serum testosterone [T], E2, dihydrotestosterone [DHT], thyroid-stimulating hormone [TSH], and decreased T4 levels). These data demonstrate that there are considerable strain-sensitivity differences to p,p'-DDE exposure. The described in vivo male battery using CD rats did not identify p,p'-DDE as an EAC. In contrast, the in vivo male battery using LE rats identified p,p'-DDE as a EAC. Evaluation of the data for the LE rats demonstrate that p,p'-DDE appears to be acting as an AR antagonist whose primary effects are more potent centrally than peripherally. In the YTS for the AR, p,p'-DDE had an EC50 value of 3.5 x 10(-4) M; however, in the AR YTS competition assay, p,p'-DDE did not inhibit DHT binding to the AR. p,p'-DDE was inactive in the YTS containing the estrogen receptor or progesterone receptor at the concentrations evaluated. In the Hershberger assay, p,p'-DDE administration caused antiandrogen-like effects characterized by attenuation of the testosterone propionate-induced increases in reproductive-organ weights. In summary, these data suggest that strain selection will affect the ability to detect certain weak EACs. However, a Tier I screening battery consisting of both in vivo and in vitro endpoints would reduce the chance that weak-acting compounds such as p,p'-DDE would not be identified as potential EACs.

Detection of thyroid toxicants in a tier I screening battery and alterations in thyroid endpoints over 28 days of exposure

Phenobarbital (PB), a thyroid hormone excretion enhancer, and propylthiouracil (PTU), a thyroid hormone-synthesis inhibitor, have been examined in a Tier I screening battery for detecting endocrine-active compounds (EACs). The Tier I battery incorporates two short-term in vivo tests (5-day ovariectomized female battery and 15-day intact male battery using Sprague-Dawley rats) and an in vitro yeast transactivation system (YTS). In addition to the Tier I battery, thyroid endpoints (serum hormone concentrations, liver and thyroid weights, thyroid histology, and UDP-glucuronyltransferase [UDP-GT] and 5'-deiodinase activities) have been evaluated in a 15-day dietary restriction experiment. The purpose was to assess possible confounding of results due to treatment-related decreases in body weight. Finally, several thyroid-related endpoints (serum hormone concentrations, hepatic UDP-GT activity, thyroid weights, thyroid follicular cell proliferation, and histopathology of the thyroid gland) have been evaluated for their utility in detecting thyroid-modulating effects after 1, 2, or 4 weeks of treatment with PB or PTU. In the female battery, changes in thyroid endpoints following PB administration, were limited to decreased serum tri-iodothyronine (T3) and thyroxine (T4) concentrations. There were no changes in thyroid stimulating hormone (TSH) concentrations or in thyroid gland histology. In the male battery, PB administration increased serum TSH and decreased T3 and T4 concentrations. The most sensitive indicator of PB-induced thyroid effects in the male battery was thyroid histology (pale staining and/or depleted colloid). In the female battery, PTU administration produced increases in TSH concentrations, decreases in T3 and T4 concentrations, and microscopic changes (hypertrophy/hyperplasia, colloid depletion) in the thyroid gland. In the male battery, PTU administration caused thyroid gland hypertrophy/hyperplasia and colloid depletion, and the expected thyroid hormonal alterations (increased TSH, and decreased serum T3 and T4 concentrations). The dietary restriction study demonstrated that possible confounding of the data can occur with the thyroid endpoints when body weight decrements are 15% or greater. In the thyroid time course experiment, PB produced increased UDP-GT activity (at all time points), increased serum TSH (4-week time point), decreased serum T3 (1-and 2-week time points) and T4 (all time points), increased relative thyroid weight (2- and 4-week time points), and increased thyroid follicular cell proliferation (1- and 2-week time points). Histological effects in PB-treated rats were limited to mild colloid depletion at the 2- and 4-week time points. At all three time points, PTU increased relative thyroid weight, increased serum TSH, decreased serum T3 and T4, increased thyroid follicular cell proliferation, and produced thyroid gland hyperplasia/hypertrophy. Thyroid gland histopathology, coupled with decreased serum T4 concentrations, has been proposed as the most useful criteria for identifying thyroid toxicants. These data suggest that thyroid gland weight, coupled with thyroid hormone analyses and thyroid histology, are the most reliable endpoints for identifying thyroid gland toxicants in a short-duration screening battery. The data further suggest that 2 weeks is the optimal time point for identifying thyroid toxicants based on the 9 endpoints examined. Hence, the 2-week male battery currently being validated as part of this report should be an effective screen for detecting both potent and weak thyroid toxicants.

Analysis of vinyl acetate metabolism in rat and human nasal tissues by an in vitro gas uptake technique

Physiologically based pharmacokinetic (PBPK) models require estimates of catalytic rate constants controlling the metabolism of xenobiotics. Usually, these constants are derived from whole tissue homogenates wherein cellular architecture and enzyme compartmentation are destroyed. Since the nasal cavity epithelium is composed of a heterogeneous cell population measurement of xenobiotic metabolizing enzymes using homogenates could yield artifactual results. In this article a method for measuring rates of metabolism of vinyl acetate, a metabolism-dependent carcinogen, is presented that uses whole-tissue samples and PBPK modeling techniques to estimate metabolic kinetic parameters in tissue compartments. The kinetic parameter estimates were compared to those derived from homogenate experiments using two methods of tissue normalization. When the in vitro gas uptake constants were compared to homogenate-derived values, using a normalization procedure that does not account for tissue architecture, there was poor agreement. Homogenate-derived values from rat nasal tissue were 3- to 23-fold higher than those derived using the in vitro gas uptake method. When the normalization procedure for the rat homogenate-derived values took into account tissue architecture, a good agreement was observed. Carboxylesterase activity in homogenates of human nasal tissues was undetectable. Using the in vitro gas uptake technique, however, carboxylesterase activity was detected. Rat respiratory carboxylesterase and aldehyde dehydrogenase activities were about three and two times higher than those of humans, respectively. Activities of the rat olfactory enzymes were about equivalent to those of humans. K(m) values did not differ between species. The results suggest that the in vitro gas uptake technique is useful for deriving enzyme kinetic constants where effects of tissue architecture are preserved. Furthermore, the results suggest that caution should be exercised when scaling homogenate-derived values to whole-organ estimates, especially in organs of cellular heterogeneity.

Chronic toxicity, oncogenicity, and mutagenicity studies with chlorotetrafluoroethane (HCFC-124)

The chronic toxicity, oncogenicity, and mutagenicity of chlorotetrafluoroethane (HCFC-124) were evaluated. In the chronic toxicity/oncogenicity study, male and female rats were exposed to 0, 2000, 10,000, or 50,000 ppm HCFC-124 for 6 hr/day, 5 days/week, for 2 years. Body weights were obtained weekly during the first three months of the study and every other week for the remainder of the study. Food consumption was determined weekly. Clinical signs of toxicity were monitored throughout the study. An ophthalmological examination was performed on all animals prior to study start, and all surviving rats were examined at approximately 3, 12, and 24 months after study start. Clinical pathology was evaluated at 3, 6, 12, 18, and 24 months. An interim termination was conducted at 12 months. All surviving rats were necropsied at 24 months. A complete set of tissues was collected for microscopic examination, and selected tissues were weighed. There were no compound-related, adverse effects on body weight, food consumption, survival, clinical signs of toxicity, ophthalmoscopically observable ocular lesions, serum hormone concentrations, or clinical pathology parameters at any exposure concentration in either male or female rats. Compared to controls, urine fluoride was increased in males and females at all exposure concentrations, and plasma fluoride was increased in females at all exposure concentrations. Excretion of fluoride represents conversion of the parent molecule, and as such is not considered to be an adverse effect. There were no toxicologically significant, compound-related organ weight changes or gross or microscopic findings in male or female rats at any of the exposure concentrations tested. HCFC-124 was not toxic or carcinogenic in rats of either sex after inhalation exposure at concentrations of up to 50,000 ppm in this two-year chronic toxicity/oncogenicity study. After exposure to HCFC-124 for six hours per day, five days per week, for 24 months, the no-observed-adverse-effect level for male and female rats was 50,000 ppm. HCFC-124 was not mutagenic in Salmonella typhimurium strains TA1535, TA97, TA98, and TA100 with and without activation when evaluated at concentrations up to 60% HCFC-124 for 48 hours. No evidence of clastogenic activity was observed in cultured human lymphocytes at atmospheric concentrations up to 100% HCFC-124 for 3 hours, with and without metabolic activation. In vivo, no micronuclei were induced in mouse bone marrow cells following exposure of mice to concentrations of 99,000 ppm HCFC-124 6 hours/day for 2 days.

An ongoing validation of a Tier I screening battery for detecting endocrine-active compounds (EACs)

After previously examining an estrogen receptor agonist (17beta-estradiol), several additional compounds have been evaluated in a Tier I screening battery for detecting endocrine-active compounds (EACs): an estrogen receptor antagonist (ICI-182,780, ICI), an androgen receptor antagonist (flutamide, FLUT), a testosterone biosynthesis inhibitor (ketoconazole, KETO), a 5alpha-reductase inhibitor (finasteride, FIN), and an aromatase inhibitor (anastrozole, ANA). The Tier I battery incorporates two short-term in vivo tests (a 5-day ovariectomized female battery and a 15-day intact male battery) and an in vitro yeast transactivation system (YTS). The Tier I battery is designed to identify compounds that have the potential to act as agonists or antagonists to the estrogen, androgen, progesterone, or dopamine receptors, steroid biosynthesis inhibitors (aromatase, 5alpha-reductase, and testosterone biosynthesis), or compounds that alter thyroid function. ICI administration decreased uterine estrogen and progesterone receptor number in the female battery, increased serum follicle-stimulating hormone (FSH) levels and caused spermatid retention in the male battery, and activated gene transcription in the YTS containing the estrogen receptor. FLUT administration increased uterine stromal cell proliferation in the female battery and decreased weights for all androgen-dependent tissues, induced Leydig cell hyperplasia, and caused hormonal alterations (increased testosterone (T), estradiol (E2), dihydrotestosterone (DHT), luteinizing hormone (LH), and FSH) in the male battery, and competed for binding to the androgen receptor in the YTS competition assay. In the male battery KETO decreased weights for all androgen-dependent tissues, caused hormonal alterations (decreased T and DHT and increased LH and FSH), and induced spermatid retention. FIN decreased seminal vesicle and accessory sex gland (ASG) unit weight and caused hormonal alterations (decreased DHT and increased LH, and PRL) in the male battery. KETO was judged not to affect any of the endpoints in the female battery. ANA decreased ASG unit weight and serum E2 levels in the male battery. Using the responses obtained for all the endpoints in the Tier I battery, a distinct "fingerprint" was produced for each type of endocrine activity against which compounds with unknown activity can be compared. These data demonstrate that the described Tier I battery is useful for identifying EACs.

Sensitivity of a Tier I screening battery compared to an in utero exposure for detecting the estrogen receptor agonist 17 beta-estradiol

A Tier I screening battery for detecting endocrine active compounds (EACs) has been evaluated for its ability to identify 17 beta-estradiol, a pure estrogen receptor agonist. In addition, the responses obtained with the Tier I battery were compared to the responses obtained from F1 generation rats from a 90-day/one-generation reproduction study with 17 beta-estradiol in order to characterize the sensitivity of the Tier I battery against the sensitivity of an in utero exposure for detecting EACs. The Tier I battery incorporates two short-term in vivo tests (5-day ovariectomized female battery; 15-day intact male battery) and an in vitro yeast transactivation system (YTS) for identifying compounds that alter endocrine homeostasis. The Tier I female battery consists of traditional uterotrophic endpoints coupled with biochemical and hormonal endpoints. It is designed to identify compounds that are estrogenic/antiestrogenic or modulate dopamine levels. The Tier I male battery consists of organ weights coupled with microscopic evaluations and a comprehensive hormonal assessment. It is designed to identify compounds that have the potential to act as agonists or antagonists to the estrogen, androgen, progesterone, or dopamine receptor; steroid biosynthesis inhibitors (aromatase, 5 alpha-reductase, and testosterone biosynthesis); or compounds that alter thyroid function. The YTS is designed to identify compounds that bind to steroid hormone receptors (estrogen, androgen, and progesterone) and activate gene transcription. The profile generated for 17 beta-estradiol was characteristic of the responses expected with a pure estrogen receptor agonist. In the female battery, responses to 17 beta-estradiol included increases in uterine fluid imbibition, uterine weight, estrus conversion, uterine stromal cell proliferation, uterine epithelial cell height, uterine progesterone receptor content, serum prolactin and estradiol levels, and decreases in uterine estrogen receptor content and follicle stimulating hormone and luteinizing hormone levels. In the male battery, responses to 17 beta-estradiol included decreases in absolute testis and epididymides weights, decreases in relative weights for androgen-dependent tissues (prostate, seminal vesicles, and accessory sex gland unit), hormonal alterations (decreased serum testosterone, dihydrotestosterone, and LH and increased serum prolactin levels), and microscopic alterations of the testis and epididymides. In the YTS for the estrogen receptor, 17 beta-estradiol had an EC50 value of 7.2 x 10(-9) M, while DHT and progesterone had little cross-activation. The androgen and progesterone receptor systems were less selective in that 17 beta-estradiol activated these systems within 3 orders of magnitude of the primary ligand. In the 90-day/one-generation reproduction study, responses to dietary administration of 17 beta-estradiol included alterations in organ weights, developmental landmarks, and hormonal levels. Comparison of the responses obtained with our Tier I battery and an in utero exposure demonstrates that the Tier I screening battery is as sensitive as an in utero exposure for detecting 17 beta-estradiol-induced alterations in hormonal homeostasis.

90-day feeding and one-generation reproduction study in Crl:CD BR rats with 17 beta-estradiol

Over the past several years, there has been increasing concern that chemicals and pesticides found in the environment may mimic endogenous estrogens, potentially producing adverse effects in wildlife and human populations. Because estrogenicity is one of the primary concerns, a 90-day/one-generation reproduction study with 17 beta-estradiol was designed to set dose levels for future multigenerational reproduction and combined chronic toxicity/oncogenicity studies. The purpose of these studies is to evaluate the significance of a range of responses as well as to provide benchmark data for a risk assessment for chemicals with estrogen-like activities. This 90-day/one-generation reproduction study was conducted in male and female Crl:CD BR rats using dietary concentrations of 0, 0.05, 2.5, 10, and 50 ppm 17 beta-estradiol. Endpoints were chosen in order to evaluate both subchronic and reproductive toxicity. In addition, several mechanistic/biochemical endpoints were evaluated for their usefulness in follow-up studies. In the P1 generation, dietary administration of 2.5, 10, and 50 ppm 17 beta-estradiol produced dose-dependent decreases in body weight, body weight gain, food consumption, and food efficiency. At 10 and 50 ppm 17 beta-estradiol, minimal to mild nonregenerative anemia, lymphopenia, decreased serum cholesterol (50 ppm only), and altered splenic lymphocyte subtypes were also observed in the P1 generation. Additionally, at these concentrations, there were changes in the weights of several organs. Evidence of ovarian malfunction, characterized by reduced numbers of corpora lutea and large antral follicles, was observed at 2.5 ppm 17 beta-estradiol and above. Other pathologic changes in males and females fed 10 and 50 ppm 17 beta-estradiol included centrilobular hepatocellular hypertrophy; diffuse hyperplasia of the pituitary gland; feminization of the male mammary glands; mammary gland hyperplasia in females; increased number of cystic follicles in the ovary; hypertrophy of the endometrium and endometrial glands in the uterus; degeneration of seminiferous epithelium; and atrophy of the testes and the accessory sex glands. In the reproduction portion of this study, rats fed 10 or 50 ppm 17 beta-estradiol did not produce litters. While there was no evidence that the 50 ppm treated rats mated, 33.3% of the rats fed 10 ppm mated but did not produce litters. No effects on mating and fertility indices were observed in rats fed 0.05 and 2.5 ppm 17 beta-estradiol. Pup weights at birth were statistically decreased relative to control in the groups fed 0.05 and 2.5 ppm 17 beta-estradiol. Weights of the rats in the 0.05 ppm group recovered by postnatal day 4 and remained similar to control throughout the remainder of the study. The mean gestation length of the 0.05 ppm group was slightly, albeit not statistically significantly, shorter (0.5 days) than that of the control group, which may have contributed to the decrease in birth weight of the 0.05 ppm group. In contrast, the weights of the F1 generation rats fed 2.5 ppm 17 beta-estradiol remained decreased relative to the control group throughout the study. Parental administration of 17 beta-estradiol did not alter anogenital distance in male or female pups. The onset of sexual maturation, as measured by day of preputial separation in males and day of vaginal opening in females, was delayed in male rats fed 2.5 ppm (by 8.2 days) and was hastened in female rats fed 0.05 and 2.5 ppm (by 1.6 and 8.8 days, respectively). The age at vaginal opening ranged from 26 to 37, 26 to 35, and 21 to 25 days for rats fed 0, 0.05, and 2.5 ppm 17 beta-estradiol, respectively. Hence, the range of age at vaginal opening was similar between the control and 0.05 ppm group. The organ weight and pathologic alterations observed in the adult F1 generation rats were similar to those observed in the P1 generation rats. (ABSTRACT TRUNCATED)

Effects of dietary 17 beta-estradiol exposure on serum hormone concentrations and testicular parameters in male Crl:CD BR rats

A 90-day/one-generation reproduction study was conducted in male and female Crl:CD BR rats using dietary levels of 0, 0.05, 2.5, 10, and 50 ppm 17 beta-estradiol. The goals of this study were to set dose levels and evaluate several mechanistic endpoints for inclusion in multigeneration reproduction and combined chronic toxicity/oncogenicity studies with 17 beta-estradiol. In this report we discuss the effects of dietary 17 beta-estradiol exposure on serum hormonal levels and sperm parameters from P1 and F1 male rats. Sperm parameters were also evaluated in recovery P1 and F1 male rats that were fed control diets for 105 and 103 days, respectively, following 97 and 86-94 days of estradiol exposure, respectively. Measurement of Sertoli cell number from F1 male rats was performed to test the hypothesis that in utero exposure to estrogens will decrease Sertoli cell number and sperm production. Other findings from this 90-day/one-generation reproduction study are summarized elsewhere. 17 beta-Estradiol produced a dose-dependent decrease in body weight in P1 male rats at > or = 2.5 ppm and in the F1 male rats at 2.5 ppm. This decrease in body weight was due to a combination or reduced food consumption and food efficiency. In the recovery P1 males, body weight increased in the affected groups, albiet not to control levels, due to food consumption returning to control levels accompanied by an increase in food efficiency. However, in F1 males there was no corresponding rebound in body weight. In the P1 rats, exposure to 17 beta-estradiol decreased testis and epididymis weights in the 10 and 50 ppm groups, while no effects were seen in the P1 2.5 ppm group. In contrast, epididymis weights in the F1 and F1 recovery 2.5 ppm groups were statistically decreased; however, there were no histopathological effects observed. The decreases in testis weights in the P1 generation correlated with histopathologic evidence of interstitial cell atrophy and seminiferous tubule degeneration and reduced sperm production. Correlative changes in the epididymides of P1 rats were characterized by oligospermia or aspermia, the presence of germ cell debris in the lumen of tubules, and atrophy of epididymal tubules. 17 beta-Estradiol decreased testicular spermatid numbers, epididymal sperm numbers, and sperm motility in the P1 males in the 10 and 50 ppm groups, but not in the 2.5 ppm group. Following a 105-day recovery period in the P1 males, all sperm parameters and reproductive organ weights returned to control values except for the epididymal sperm count. Overall, the decline in testicular spermatid and epididymal sperm numbers in the P1 rats correlated with the reduced organ weights and the observed histopathological changes and appeared primarily related to the decrease in serum testosterone levels. In the F1 rats, no significant decreases were noted in the testicular spermatid number but a slight decrease in epididymal sperm number was seen in the 2.5 ppm group, which showed no evidence of recovery. Using morphometric analysis, no change was seen in the number of Sertoli cell nuclei per testis in F1 males. The pattern of hormonal responses seen in this study was characteristic of an estrogen receptor agonist such as 17 beta-estradiol: increased serum prolactin and decreased testosterone, luteinizing hormone, and follicle stimulating hormone levels. The data demonstrate that in utero and postnatal dietary administration of 17 beta-estradiol at levels which increased serum estradiol levels to approximately 400% of control and decreased testosterone levels to 33% of control did not reduce the number of Sertoli cell nuclei per testis.

Mitogenic responses of rat nasal epithelium to hexamethylphosphoramide inhalation exposure

Hexamethylphosphoramide (HMPA) is a rat nasal carcinogen that induces squamous cell carcinomas in the anterior portions of the nasal cavity following chronic inhalation exposures as low as 50 ppb. These tumors may arise as a result of P-450-mediated release of formaldehyde (HCHO), a known rat nasal carcinogen. The goal of this research was to investigate early responses of the nasal epithelium to inhaled HMPA. Rats were exposed nose-only to approximately 3 ppm HMPA for 6 h, and killed 18, 48, 96 or 144 h post-exposure. In a separate study, rats were exposed nose-only for 6 h for 1, 2, 3, or 5 consecutive days and killed 18 or 96 h post-exposure. With both single and repeated doses of HMPA, there was no evidence of cytotoxicity in the anterior nose. Olfactory degeneration and necrosis of the dorsal meatus, Bowman's glands and tips of the ethmoid turbinates increased in severity with repeated exposures to HMPA. Cell proliferation was assessed in levels of nasal tissue that included regions of squamous, respiratory, transitional and olfactory epithelium. Regional induction of cell proliferation was measured by BrdU incorporation, and reported as the number of labeled cells/mm basement membrane. At 18 h after a single exposure, there was an increase in cell proliferation in squamous epithelium, which returned to control levels within 48 h. A transitory increase in cell proliferation was observed regions of respiratory and transitional epithelium, although the response of each tissue, in terms of magnitude and peak time of response post-exposure, also differed. Along the dorsal meatus in Level 9, olfactory labeling initially decreased, returned to control levels by 96 h, but again declined at 144 h post-exposure. In repeat dose studies, the squamous epithelium response was variable 18 h post-exposure. For respiratory and transitional epithelium, increased cell proliferation 18 h post-exposure was correlated with increased dose (exposure) of HMPA. Cell proliferation responses following two or more exposures returned to near control levels within 96 h post-exposure. In conclusion, HMPA induced cell proliferation, but not cytotoxicity, in the anterior nose at approximately 3 ppm. These data suggest that HMPA induces proliferative, perhaps mitogenic, responses in the nasal epithelium, and this response may facilitate the fixation of low level genetic damage induced by liberated HCHO.

Lung proliferative and clearance responses to inhaled para-aramid RFP in exposed hamsters and rats: comparisons with chrysotile asbestos fibers

This study compared pulmonary effects of para-aramid respirable-sized, fiber-shaped particles (RFP) (p-aramid fibrils) and chrysotile asbestos fiber exposures in rats. Additional p-aramid inhalation studies were conducted in hamsters to compare species responses. The hamster results are preliminary. The parameters studied were clearance/biopersistence of inhaled p-aramid RFP or size-separated asbestos fibers as well as pulmonary cell proliferation and inflammation indices after 2-week inhalation exposures. Rats were exposed nose only to chrysotile asbestos fibers at concentrations of 459 and 782 fibers/ml or to p-aramid RFP at 419 or 772 fibrils/ml. Hamsters were exposed whole body to p-aramid RFP at concentrations of 358 and 659 fibrils/ml. Subsequently, animals were assessed immediately (time 0) as well as 5 days (10 days for hamsters), 1, 3, 6, and 12 months postexposure. Lung burdens for the p-aramid-exposed rats were 4.8 x 10(7) and 7.6 x 10(7) fibrils/lung, with similar numbers of chrysotile fibers > 5 microns recovered from the lungs of asbestos-exposed rats. In comparison, 1.4 x 10(6) fibrils/lung were recovered in the high-dose hamster group. Biopersistence studies in p-aramid-exposed rats and hamsters demonstrated an initial increase (relative to time 0) in retained p-aramid fibrils during the first month postexposure, which indicated breakage or shortening of inhaled fibrils. This result was associated with a progressive reduction, and increased residence time in the lung, in the mean lengths of the fibrils, which signified biodegradability of inhaled p-aramid fibrils in both species. In contrast, clearance of short chrysotile asbestos fibers was rapid, but clearance of the long chrysotile fibers was slow or insignificant, as evidenced by a progressive increase over time in the mean lengths of fibers recovered from the lungs of exposed rats. Two-week, high-dose exposures to p-aramid in both rats and hamsters produced transient increases in pulmonary inflammatory and cell proliferative responses. In contrast, inhalation of size-separated chrysotile asbestos fibers in rats produced persistent increases in cell labeling indices of airway, alveolar, and subpleural cells measured through a period of 1 to 3 months postexposure. These results suggest that inhaled p-aramid RFP are biodegradable in the lungs of exposed rats and hamsters. In contrast, exposures to chrysotile asbestos fibers in rats resulted in a selective pulmonary retention of long chrysotile fibers.

Evidence that A8947 enhances pancreas growth via a trypsin inhibitor mechanism

A8947 is a member of the sulfonyl urea class of compounds and is the active ingredient in a commercial broad leaf herbicide. This compound has been shown to produce pancreatic hypertrophy in rats, mice, and dogs. The objectives of this study were to investigate the mechanism(s) for the A8947 induction of pancreatic acinar cell hypertrophy and proliferation and to evaluate whether these pancreatic changes are reversible. A8947 was fed to male Crl:CD BR rats for up to 28 days (0, 300, 10,000, 30,000 ppm) or 56 days (0, 30,000 ppm). Rats were terminated on Test Days 7, 14, and 28 to assess the time course and dose response for the A8947-induced pancreatic changes, while rats terminated on Test Day 56 were used to assesss the reversibility of the pancreas effects at 30,000 ppm A8947. A8947 produced significant increases in pancreatic weight and acinar cell proliferation and diffuse acinar cell hypertrophy in 7 days at 10,000 and 30,000 ppm dose levels. By Day 14, absolute pancreas weights in the 10,000 and 30,000 ppm groups were maximally increased and remained at these levels throughout the study. In contrast, acinar cell proliferation in the 30,000 ppm group was still elevated at Test Day 14, but attenuated relative to the 7-day response, and returned to control levels by Test Day 28. No effects were observed at 300 ppm after a 28-day exposure period, while complete reversibility of A8947-induced pancreatic effects was demonstrated at 30,000 ppm following a 1-month recovery period (Test Day 56). Cholecystokinin (CCK) levels were increased by A8947 and closely followed the time course for pancreatic changes. MK-329, a specific CCKA receptor antagonist, completely ablated the ability of 30,000 ppm A8947 to increase pancreas weight following 7 days of exposure. A8947 did not bind the CCKA receptor in a receptor competition assay, negating any potential agonist mechanism. A8947 did, however, inhibit trypsin in vitro, suggesting a mechanism of action similar to that of raw soy protein, in which trypsin inhibition in vivo results in increased CCK levels followed by pancreatic acinar cell hypertrophy and proliferation.

Mechanisms for the pancreatic oncogenic effects of the peroxisome proliferator Wyeth-14,643

Several peroxisome proliferators have been shown to produce pancreatic acinar cell hyperplasia/adenocarcinomas in 2-year bioassays with rats: ammonium perfluorooctanoate (C8), clofibrate, methylclofenapate, HCFC-123, and Wyeth-14,643 (WY). We have used in vitro (C8, WY) and in vivo (WY) approaches to examine several possible mechanisms of pancreatic tumorigenesis by peroxisome proliferating compounds. These mechanisms include cholecystokinin receptor agonism (CCK(A)), trypsin inhibition, alterations in gut fat content, cholestasis, and altered bile flow/composition. All of these mechanisms enhance pancreatic growth either by binding to the CCK(A) receptor or by increasing plasma CCK levels. In vitro experiments using a receptor competition binding assay demonstrated that WY and C8 do not bind directly to the CCK(A) receptor. In a continuous spectrophotometric assay, WY and C8 also failed to inhibit trypsin, a common mechanism for increasing plasma CCK levels. These in vitro results suggested that WY was not acting via the two most common mechanisms for modulation of pancreas growth. Two types of in vivo experiments were conducted. The subchronic study (2-month duration) was designed primarily to detect early changes in pancreatic growth such as those mediated by compounds that inhibit trypsin or act as CCK(A) receptor agonists. The chronic study (6 months) was designed primarily to evaluate whether the pancreatic lesions were secondary to hepatic changes such as cholestasis and/or altered bile flow/composition. In the in vivo experiments, male Crl:CDBR rats were fed diets containing 0 or 100 ppm WY. In the subchronic study WY-treated rats had a twofold increase in mean relative liver weights, an eightfold increase in hepatic peroxisomal proliferation, and a fourfold increase in hepatocyte cell proliferation after 1 week which remained elevated throughout the 2 months of treatment. In contrast, no pancreatic weight effects, increases in plasma CCK, or acinar cell proliferation was seen through 2 months in the WY group when compared to the control group. Fecal fat concentrations were also measured at 2 months and demonstrated no difference between control and WY-treated animals. The absence of any early pancreas changes in the subchronic study is consistent with the in vitro data which demonstrated that WY is not a CCK(A) agonist or a trypsin inhibitor. The chronic study demonstrated increases in pancreatic weights at 3 months (6% above control) and 6 months (17% above control), as well as increased CCK plasma levels in the WY-treated group. Liver effects in the chronic study paralleled those of the subchronic time points. Clinical pathology endpoints including increased serum concentrations of bile acids, alkaline phosphatase, and bilirubin were indicative of cholestasis in the chronic WY-treated group. The cholestasis may be responsible for the downward trend in total bile acid output, both of which may contribute to the modest increases in plasma CCK levels. These results indicate that chronic exposure to WY causes liver alterations such as cholestasis, which may increase plasma concentrations of CCK. Hence, WY may induce pancreatic acinar cell adenomas/adenocarcinomas via a mild but sustained increase in CCK levels secondary to hepatic cholestasis.

Chronic inhalation toxicity and oncogenicity of methyl methacrylate in rats and hamsters

Male and female Fischer 344 rats were exposed to methyl methacrylate (MMA) monomer vapours at 0, 25, 100 and 400 ppm, 6 hr/day, 5 days/wk for 24 months and male and female Golden hamsters were exposed to similar vapour concentrations of MMA for 18 months. Parameters monitored throughout the study included clinical signs, individual body weights, haematology, clinical chemistry (rats only) and urinalyses (rats only). 10 rats per sex per exposure group were killed after 13 and 52 wk of exposure and all surviving rats were killed during wk 104-106. All surviving hamsters were killed at wk 78. Mortality and haematological, clinical chemistry and urinalyses parameters were not affected by MMA exposure. Body weights of male rats were not affected by exposure to MMA while body weights of female rats exposed to 400 ppm were lower than control values after wk 52. Male and female hamsters exposed to 400 ppm had body weight decreases ranging from 9 to 12% after wk 48. The nasal cavity was identified as the target organ for chronic toxicity in male and female rats exposed to 100 or 400 ppm. The microscopic nasal cavity changes occurred primarily in olfactory epithelium lining the dorsal meatus and consisted of degeneration of neuroepithelium, basal cell hyperplasia and atrophy of Bowman's glands. Hamsters did not have demonstrable nasal cavity microscopic changes. Chronic exposure to MMA vapour did not cause tumours in either rats or hamsters.

Induction of coagulation effects by Wyeth-14,643 in Crl:CD BR rats

A two-year mechanistic bioassay in male Crl:CD BR rats was initiated with 50 ppm Wyeth-14,643 (WY) to investigate the relationship between peroxisome proliferating compounds and Leydig cell adenoma formation. After 154 days, the survival rate in the WY group decreased below control levels. After 300 days, the dose was lowered to 25 ppm for the remainder of the study. Gross examination of WY-treated rats either found dead or euthanized in extremis revealed hemorrhages at several sites. To investigate this observation, blood was then collected on test day 281 from 10 randomly selected control and WY-treated rats and a clinical pathological examination was performed. The WY-treated rats had significantly decreased red blood cell count, hemoglobin, and hematocrit, and elevated platelet counts. In the WY-treated rats, prothrombin times in undiluted plasma were similar to the controls, but were markedly prolonged in 2 of 10 rats when the plasma samples were diluted to 25%. Subsequently, blood was collected prior to sacrificing WY-treated rats which were exhibiting clinical signs of anemia. These rats had prolonged prothrombin times, activated partial thromboplastin time, and thrombin clot time when compared to laboratory historical control data (116.7 vs 13.3, 116.4 vs 13.7, and 42.4 vs 25.7 seconds, respectively). In a subsequent, ongoing study, Vitamin K was added to control and WY-treated diets (100 ppm). No survival differences between control and WY-treated rats occurred through 260 days in this second study. These new data suggest that deaths in the WY-treated group in our initial study were due to a vitamin K deficiency. The role of increased serum estradiol, its effects on blood coagulation, and enhanced hepatic cell proliferation in the vitamin K-dependent coagulation processes warrant further investigation.

Pulmonary effects in rats inhaling size-separated chrysotile asbestos fibres or p-aramid fibrils: differences in cellular proliferative responses

This study was designed to compare the pulmonary cellular proliferative effects of inhaled, size-separated preparations of chrysotile asbestos fibres with similar aerosol fibre concentrations of para-aramid fibrils. Following fibre preparation, rats were exposed for 2 weeks to aerosols of p-aramid fibrils or chrysotile asbestos fibres at design fibre concentrations of 750 and 400 f/cc. Two week exposures to p-aramid fibrils produced transient pulmonary inflammatory and cell labeling responses in terminal bronchiolar and subpleural regions. Similar to p-aramid, exposure to chrysotile produced a transient increase in neutrophils. In contrast, however, substantial increases compared to controls in pulmonary cell labeling indices were measured on terminal bronchiolar, parenchymal, subpleural, and mesothelial surfaces immediately after exposure, and some increases persisted for 3 months postexposure. In complementary studies we demonstrated that p-aramid is biodegradable in the lungs of exposed rats; in contrast, the clearance of long chrysotile fibres was slow or insignificant, resulting in a pulmonary retention of long chrysotile asbestos fibres. The dimensional changes of asbestos fibres as well as the pulmonary cell labeling data indicate that chrysotile asbestos fibres may produce greater long-term pulmonary effects when compared to inhaled para-aramid fibrils.

Subchronic toxicity of 4-vinylcyclohexene in rats and mice by inhalation exposure

This study was conducted to evaluate the subchronic toxicity of 4-vinylcyclohexene (VCH). Male and female Sprague-Dawley rats and B6C3F1 mice were exposed by inhalation to VCH 6 hr/day, 5 days/week for 13 weeks. Rats were exposed to 0, 250, 1000, or 1500 ppm, and mice were exposed to 0, 50, 250, or 1000 ppm. In addition, another group of rats and mice was exposed to 1000 ppm butadiene so that a comparison could be made between the two compounds. Exposure to 1000 ppm VCH resulted in deaths of all male mice and 5/10 female mice on Test Days 11 or 12. Three additional female mice exposed to 1000 ppm VCH died prior to study completion. The most notable compound-related clinical sign was lethargy observed in the 1500 ppm VCH-exposed rats and 1000 ppm VCH-exposed mice. Male rats exposed to 1500 ppm VCH had significantly lower body weights compared to controls, and male and female rats in the 1500 ppm group had significantly lower body weight gains. None of the VCH-exposed animals or butadiene-exposed rats showed any compound-related hematological effects. However, mice exposed to 1000 ppm butadiene exhibited mild macrocytic anemia. Clinical chemistry evaluation and urinalysis showed no compound-related effects in rats exposed to either VCH or butadiene. Male and female rats exposed to 1000 or 1500 ppm VCH or 1000 ppm butadiene had increased absolute and/or relative liver weights, and male rats in these same exposure groups had increased relative kidney weights. Microscopically, increased accumulation of hyaline droplets was observed in the kidneys of male rats from all VCH exposure groups. Although compound-related, the droplets were not accompanied by cytotoxicity. In mice, the most notable adverse histopathological effect was ovarian atrophy in females exposed to 1000 ppm VCH or 1000 ppm butadiene. The atrophy was slightly more severe in the VCH-exposed females than in the butadiene-exposed females. There were no other compound-related pathological effects in male or female mice exposed to VCH. Additionally, butadiene-exposed male mice had decreased testicular weights, accompanied by slight testicular degeneration and atrophy. For VCH exposure, the no-observed-adverse-effect-level is 1000 ppm for rats based on lethargy and lowered body weights and 250 ppm for mice based on mortality and ovarian atrophy.

Subchronic toxicity and teratogenicity of 2-chloro-1,1,1,2-tetrafluoroethane (HCFC-124)

Inhalation studies were conducted to determine the potential toxicity of HCFC-124. Groups of rats and mice were exposed to HCFC-124 6 hr/day, 5 days/week for 13 weeks at 0, 5000, 15,000, and 50,000 ppm. Subgroups of rats and mice were held for a 1-month recovery period. A functional observational battery (FOB) was conducted on rats at 0, 4, 13, and 16 weeks. Clinical pathology evaluations were conducted at 7, 13, and 17 weeks. Thirteen or 17 weeks after study initiation, rats and mice underwent gross and microscopic evaluation, and livers were evaluated for hepatic beta-oxidation activity. In addition, groups of female rats and rabbits were exposed to HCFC-124 by inhalation during gestation to 0, 5000, 15,000, or 50,000 ppm. Exposure of rats and mice to HCFC-124 caused minimal compound-related effects. Compound-related changes occurred in several clinical pathology parameters in rats and mice. Hepatic beta-oxidation activity was significantly higher in 5000, 15,000, and 50,000 ppm male mice; however, there were no compound-related effects on beta-oxidation activity in rats. During the daily exposures, rats, mice, and rabbits exposed to 50,000 ppm were less responsive to auditory stimuli or less active compared to controls. At the 13-week FOB, male rats exposed to 15,000 or 50,000 ppm had decreased arousal. There were no compound-related effects on mortality, clinical signs, ocular tissues, hematology parameters, organ weights, and tissue morphology at any concentration in rats or mice. Maternal toxicity in rats was evident by a significant decrease in weight gain and food consumption at 50,000 ppm. Similarly, 50,000 ppm pregnant rabbits had lower food consumption. However, for both rats and rabbits, there was no evidence of fetal toxicity at any concentration.

Inhalation oncogenicity bioassay in rats and mice with vinyl fluoride

The purpose of this study was to assess the oncogenic potential of vinyl fluoride in rats and mice when administered by inhalation. Male and female rats and mice were exposed to 0, 25, 250, or 2500 ppm vinyl fluoride 6 hr per day, 5 days per week, for 2 years (rats) or 18 months (mice). Slight body weight gain decrements were noted in groups of vinyl fluoride-exposed rats and mice. No significant clinical signs of toxicity were noted other than an increase in the incidence of palpable masses in the region of the mammary gland in female mice exposed to vinyl fluoride. Survival was decreased in male rats and mice of the 250 and 2500 ppm groups and female rats and mice of all vinyl fluoride-exposed groups compared to controls. Urinary fluoride excretion, an indicator of vinyl fluoride metabolism, increased with concentration and time although the dose relationship appeared to plateau at concentrations > or = 250 ppm. Gross observations made at necropsy of rats supported histological observations of hepatic hemangiosarcoma, hepatocellular adenoma and carcinoma, hepatic foci of clear cell and basophilic alteration, hepatic sinusoidal dilatation, metastatic lung tumors, and Zymbal's gland tumors. Hepatic hemangiosarcoma was the sentinel lesion in rats. Gross observations made at necropsy of mice supported histological observations of bronchioloalveolar adenoma and hyperplasia, hepatic hemangiosarcoma and hepatocellular hyperplasia with angiectasis and peliosis, and mammary gland adenocarcinoma and hyperplasia. Bronchioloalveolar adenoma appeared to be the sentinel lesion in mice. The spectrum of vinyl fluoride-induced tumors is similar to that induced by other monohaloethylenes in rats and mice. Under the conditions of this study, vinyl fluoride was carcinogenic in male and female rats and mice at concentrations greater than or equal to 25 ppm.

Testicular maturation in prepubertal New Zealand white rabbits

Testicular maturation was assessed in age-matched, sexually immature (13-17-week-old) New Zealand white rabbits using end points frequently evaluated in toxicity studies: testicular weight and testicular histology. Testicular weights and testicular maturity as assessed histologically were markedly variable in sexually immature rabbits, especially at > or = 14 weeks of age. The large variation in testicular weights in immature rabbits requires that large changes in a treatment group relative to controls be present for statistical detection of testicular weight effects at commonly used significance levels. Testicular weights and testicular maturity were strongly correlated to one another, but neither weight nor maturity was strongly correlated to body weight. Thus, stratification and randomization of immature rabbits to study groups based upon body weight will not assure an absence of group differences with respect to testicular maturity. The large variation in testicular weights and maturity in 13-17-week-old rabbits warrants caution in the evaluation of testicular changes when rabbits of this age range are used in toxicity studies.

Testicular degeneration and spermatid retention in young male rats

The incidence of spontaneous testicular atrophy and its morphological changes in relation to stage-specific spermatogenesis were investigated in young Crl:CD/BR male rats at 10-12 wk of age used as controls for toxicity screening during 1983-1990. The incidence of testicular degeneration was 2.5% (5/197) in control rats used for oral toxicity studies and 9.4% (31/327) in rats used for inhalation studies. The epididymal tubules of rats with testicular degeneration had exfoliated germ cells and low sperm density. The high incidence of testicular degeneration observed in the control rats used in inhalation studies may be related to the stress associated with immobilization in the restrainer during nose-only exposure conditions. The severity of testicular degeneration in the inhalation studies was mostly minimal. In these minimally affected testes, mature spermatids (step 19) were retained within normal-appearing germinal epithelium at spermatogenic stages IX-XIV. Also, eosinophilic globular bodies (EGBs) were formed with elongated or mature spermatids throughout all spermatogenic stages, but the general architecture of germinal epithelium was normal in appearance. By electron microscopy, EGBs were sequestered necrotic spermatids, and the germ cell degeneration was associated with cytoplasmic vacuolation of Sertoli cells. In moderate testicular degeneration, markedly decreased maturing spermatids (steps 15-19) and a slight depletion of round spermatids were observed in stages I-VIII. In severe testicular degeneration, seminiferous tubules were lined with 1-2 layers of round spermatids and spermatocytes with giant cell formation. The round spermatids served as a marker to identify spermatogenic stages (I-VIII) of the atrophic tubules. Also, in severe testicular degeneration, tubules in spermatogenic stages X-XIV had no elongated spermatids, and spermatocytes were exfoliated with occasional giant cell formation. Many seminiferous tubules were lined with only 1-2 layers of spermatocytes, and specific germ cell markers were not present.

Investigation of a mechanism for Leydig cell tumorigenesis by linuron in rats

In a previously conducted 2-year study, a concentration-dependent increase in Leydig cell adenomas was observed in Crl:CD BR(CD) rats fed diets containing the herbicide linuron. Linuron has been shown to be negative in a battery of six tests for genotoxicity; therefore, a nongenotoxic mechanism of tumorgenesis was investigated. Linuron is structurally related to the nonsteroidal antiandrogen, flutamide. Flutamide has also been shown to produce Leydig cell tumors within 1 year, presumably due to sustained hypersecretion of luteinizing hormone (LH) which occurs following disruption of the hypothalamic-pituitary-testicular (HPT) axis. To investigate whether linuron possesses antiandrogenic activity, sexually immature and mature CD rats were administered either 200 mg/kg linuron or 10 mg/kg flutamide (positive control) for 2 weeks. Accessory sex organs were weighed and serum hormone levels were measured to assess androgen status and alterations in the HPT axis. Serum from a multigeneration reproduction study with linuron was also analyzed for serum hormone levels. In addition, competitive receptor binding studies were conducted to evaluate the ability of linuron to bind to the androgen receptor. Linuron decreased accessory sex organ weights in sexually immature and mature linuron-treated rats. Increased serum estradiol and LH levels were observed in sexually mature linuron-treated rats. Serum estradiol and LH levels were also elevated in P1 and F1 male rats from the multigeneration reproduction study. These accessory sex organ and hormonal changes are consistent with those seen with the antiandrogen flutamide, the only exception being serum testosterone, which was elevated following exposure to flutamide but not to linuron. The inability of linuron to increase testosterone levels may reflect the lower potency of linuron as an antiandrogen compared with that of flutamide, which is a potent antiandrogen. Additionally, linuron competed with [3H]testosterone for binding to the androgen receptor. The IC50 data for competition to the androgen receptor suggest that linuron is approximately 3.5 times less potent than flutamide. These data are consistent with the effects seen with flutamide and demonstrate that linuron is a less potent antiandrogen than flutamide. Collectively, these data support the hypothesis that linuron produces Leydig cell tumors via an antiandrogenic mechanism where sustained hypersecretion of LH appears to be responsible for the development of Leydig cell hyperplasia and adenomas.

Comparison of the effects of Wyeth-14,643 in Crl:CD BR and Fisher-344 rats

Wyeth-14,643 (WY) belongs to a diverse class of compounds which have been shown to produce hepatic peroxisome proliferation and hepatocellular carcinoma in rodents. Based on a review of bioassay data, a relationship appears to exist between peroxisome proliferating compounds and Leydig cell adenoma formation. Most rat bioassays with peroxisome proliferators have been conducted in the Fisher-344 (F344) rat, which has a high spontaneous incidence of Leydig cell adenomas. Thus, it was necessary to use an alternative animal model to investigate this relationship further. Therefore the Crl:CD BR (CD) rat, which has a low spontaneous Leydig cell adenoma incidence, was chosen for a 2-year feeding study with WY. Before initiating this 2-year feeding study, it was necessary to investigate whether any strain differences existed between CD and F344 rats with respect to WY-induced peroxisome and cell proliferation. In this study, male CD and F344 rats were fed diets containing 0, 50, or 1000 ppm WY for 21 days. Peroxisome proliferation in the liver and testis was determined biochemically by measuring beta-oxidation activity and was confirmed ultrastructurally. Serum hormone levels and cell proliferation rates in the liver and testis were also measured. In addition, basal beta-oxidation activity and cell proliferation rates were compared between the CD and F344 rats. A significant decrease in final body weight was observed in the 1000 ppm WY groups for both CD and F344 rats.(ABSTRACT TRUNCATED AT 250 WORDS)

A microscopic and ultrastructural evaluation of dibasic esters (DBE) toxicity in rat nasal explants

Dibasic esters (DBE) solvent has been demonstrated to induce a mild degeneration of the olfactory, but not the respiratory epithelium of the rat nasal cavity following a 90-day inhalation exposure. Previous work has demonstrated that acid phosphatase release is a reliable index of DBE-induced cytotoxicity in an in vitro system of rat nasal explants. In the present study, rat nasal explants were examined microscopically and ultrastructurally following incubation in varying concentrations of a representative DBE, dimethyl adipate (DMA). DMA-induced microscopic and ultrastructural changes in rat nasal explants correlated well with biochemical perturbations associated with DBE exposure in a previous study. In both studies, olfactory epithelium was more susceptible to DMA-induced toxicity than respiratory epithelium and DMA-induced nasal toxicity was attenuated by pretreatment with a carboxylesterase inhibitor. The results of this study support the hypothesis that DBE and potentially other inhaled organic esters induce nasal toxicity via a common mechanism, carboxylesterase-mediated production of toxic acid metabolites. It was established that carboxylesterase-rich sustentacular cells are the primary target cells for DBE toxicity in rat nasal explants. It was proposed that degeneration of nasal olfactory sensory cells observed in rats following 90-day inhalation exposure to DBE may be secondary to necrosis and loss of sustentacular cells.

Inhalation toxicity of an isomeric mixture of hydrochlorofluorocarbon (HCFC) 225 in male rats

A blend of the hydrochlorofluorocarbon isomers HCFC-225ca and HCFC-225cb has been proposed as a potential substitute for CFC-113, an important solvent and cleaning agent. The toxicity following repeated inhalation of an HCFC-225 isomer mixture was assessed in male Crl:CDBR rats. Three groups of 10 male rats were exposed to the test compound in air at design concentrations of 500, 5000, and 13,000 ppm. Rats were exposed 6 hr/day, 5 days/week for 2 weeks. A control group of 10 male rats was exposed to air only. Decreased serum cholesterol, triglycerides, and glucose; dose-related increased mean absolute and relative liver weights; and microscopic hepatocellular hypertrophy were present at all exposure concentrations. Hepatocellular hypertrophy correlated ultrastructurally to proliferation of peroxisomes. Clinical chemical parameters and organ weight and morphologic changes in the liver were reversible following 14 days of recovery.

Induction of Leydig cell adenomas by ammonium perfluorooctanoate: a possible endocrine-related mechanism

Ammonium perfluorooctanoate (C8) produced an increased incidence of Leydig cell adenomas in Crl:CD BR (CD) rats fed 300 ppm for 2 years. A hormonal (nongenotoxic) mechanism was examined since C8 was negative in short-term tests for genotoxicity. Adult male CD rats were gavaged with either 0, 1, 10, 25, or 50 mg/kg C8 for 14 days. In addition, a control group was pair-fed to the 50 mg/kg C8 group. A dose-dependent decrease in body and relative accessory sex organ (ASO) weights was seen, with the relative ASO weights of the 50 mg/kg group significantly less than those of the pair-fed control. Serum estradiol levels were elevated in the 10, 25, and 50 mg/kg C8-treated animals. Estradiol levels in the 50 mg/kg C8 group were 2.7-fold greater than those in the pair-fed control. The increase in serum estradiol levels occurred at the same dose levels as the increase in hepatic beta-oxidation activity. A statistically significant downward trend with dose was seen in serum testosterone levels when compared with the ad libitum control. However, when the 50 mg/kg C8-treated rats were compared with their pair-fed control, no significant differences were seen. Challenge experiments, which can identify the presence and location of a lesion in an endocrine axis, were undertaken to clarify the significance of this downward trend in serum testosterone following C8 exposure. In the challenge experiments, adult CD rats were gavaged with either 0 or 50 mg/kg C8 for 14 days. One hour before termination, rats received either a human chorionic gonadotropin (hCG), gonadotropin-releasing hormone (GnRH), or naloxone challenge. Following hCG challenge, serum testosterone levels in the 50 mg/kg C8 were significantly decreased (50%) from those in the ad libitum controls. Similar decreases, although not significant, were seen in serum testosterone following GnRH and naloxone challenge. The challenge experiments suggest that the decrease in serum testosterone following C8 exposure is due to a lesion at the level of the testis. In addition, progesterone, 17 alpha-hydroxyprogesterone, and androstenedione were examined in the 50 mg/kg C8-treated males following hCG challenge. A 60% decrease was observed in androstenedione levels in the C8-treated animals from those in the ad libitum controls; no other differences were seen. These data suggest that the decrease in serum testosterone following hCG challenge may be due to a decrease in the conversion of 17 alpha-hydroxyprogesterone to androstenedione. The observed effects described above can be attributed to the elevated serum estradiol levels.(ABSTRACT TRUNCATED AT 400 WORDS)

Naturally occurring mucocutaneous histoplasmosis in a rabbit

Mucocutaneous histoplasmosis was diagnosed in a pet rabbit. A mass protruding through the anal opening was histologically composed of a densely cellular infiltrate of macrophages which expanded the anorectal submucosa. Macrophages contained abundant yeast forms of fungi morphologically consistent with Histoplasma capsulatum. Infection appeared to be localized. Histoplasmosis should be considered in the differential diagnosis of granulomatous inflammatory disease in the rabbit.

Hereditary junctional mechanobullous disease in a foal

Mechanobullous disease was diagnosed in a male Belgian foal that had sloughed hooves at 30 hours and at 6 and 12 days of age. Histologic and electron microscopic studies disclosed that lesions were the result of separation of the basal epithelial cell layer from the lamina densa of the basement membrane zone along the lamina lucida. Results of immunofluorescence on tissue specimens were negative for immunoglobulin deposition. The breeding history of the foal's dam indicated that the foal was produced from breeding of the mare to its full sibling stallion. This same mare had produced a female foal, sired by a different stallion, which also had sloughed hooves during the first 2 weeks of life and had similar histologic and electron microscopic changes. This newly recognized disease of horses most closely resembles junctional-type epidermolysis bullosa described in human beings.