Neurotoxic kynurenine metabolism is increased in the dorsal hippocampus and drives distinct depressive behaviors during inflammation.

The kynurenine pathway of tryptophan metabolism has an important role in mediating the behavioral effects of inflammation, which has implications in understanding neuropsychiatric comorbidity and for the development of novel therapies. Inhibition of the rate-limiting enzyme, indoleamine 2,3-dioxygenase (IDO), prevents the development of many of these inflammation-induced preclinical behaviors. However, dysregulation in the balance of downstream metabolism, where neuroactive kynurenines are generated, is hypothesized to be a functionally important pathogenic feature of inflammation-induced depression. Here we utilized two novel transgenic mouse strains to directly test the hypothesis that neurotoxic kynurenine metabolism causes depressive-like behavior following peripheral immune activation. Wild-type (WT) or kynurenine 3-monooxygenase (KMO)-deficient (KMO-/-) mice were administered either lipopolysaccharide (LPS, 0.5 mg kg-1) or saline intraperitoneally. Depressive-like behavior was measured across multiple domains 24 h after immune challenge. LPS precipitated a robust depressive-like phenotype, but KMO-/- mice were specifically protected from LPS-induced immobility in the tail suspension test (TST) and reduced spontaneous alternations in the Y-maze. Direct administration of 3-hydroxykynurenine, the metabolic product of KMO, caused a dose-dependent increase in depressive-like behaviors. Mice with targeted deletion of 3-hydroxyanthranilic acid dioxygenase (HAAO), the enzyme that generates quinolinic acid, were similarly challenged with LPS. Similar to KMO-/- mice, LPS failed to increase immobility during the TST. Whereas kynurenine metabolism was generally increased in behaviorally salient brain regions, a distinct shift toward KMO-dependent kynurenine metabolism occurred in the dorsal hippocampus in response to LPS. Together, these results demonstrate that KMO is a pivotal mediator of hippocampal-dependent depressive-like behaviors induced by peripheral LPS challenge.

Lipopolysaccharide-induced depressive-like behavior is mediated by indoleamine 2,3-dioxygenase activation in mice.

Although elevated activity of the tryptophan-degrading enzyme indoleamine 2,3-dioxygenase (IDO) has been proposed to mediate comorbid depression in inflammatory disorders, its causative role has never been tested. We report that peripheral administration of lipopolysaccharide (LPS) activates IDO and culminates in a distinct depressive-like behavioral syndrome, measured by increased duration of immobility in both the forced-swim and tail suspension tests. Blockade of IDO activation either indirectly with the anti-inflammatory tetracycline derivative minocycline, that attenuates LPS-induced expression of proinflammatory cytokines, or directly with the IDO antagonist 1-methyltryptophan (1-MT), prevents development of depressive-like behavior. Both minocycline and 1-MT normalize the kynurenine/tryptophan ratio in the plasma and brain of LPS-treated mice without changing the LPS-induced increase in turnover of brain serotonin. Administration of L-kynurenine, a metabolite of tryptophan that is generated by IDO, to naive mice dose dependently induces depressive-like behavior. These results implicate IDO as a critical molecular mediator of inflammation-induced depressive-like behavior, probably through the catabolism of tryptophan along the kynurenine pathway.

MUC1 expression in human prostate cancer cell lines and primary tumors.

MUC1 expression was evaluated in normal prostate epithelial cells (PrEC), and prostate cancer cell lines in response to dihydrotestosterone (DHT), interferon-gamma (IFN-gamma) and tumor necrosis factor-alpha (TNF-alpha) treatment. Expression of MUC1 core protein was stimulated in PrEC and PC-3 cells after cytokine treatment, but was highly and constitutively expressed by DU-145 cells. MUC1 was not expressed by LNCaP, C4-2 or C4-2B cells under any condition. DHT alone or in combination with cytokines had no effect on MUC1 expression in any cell line tested. Using antibodies capable of detecting all isoforms of MUC1 core protein independent of their glycosylation state, immunohistochemical staining of tissue microarrays containing both nontumor and tumor tissue revealed that only 17% of tumor tissues and 41% of nontumor tissues stained positively for MUC1. Staining patterns in tumor tissue varied from focal apical staining to diffuse cytoplasmic staining. Neither the presence of MUC1 core protein nor its subcellular distribution correlated with Gleason grade. These data indicate that MUC1 is a poor marker of prostate cancer progression. Furthermore, IFN-gamma and TNF-alpha strongly induce MUC1 expression in both normal prostate epithelia and certain prostate tumor cell lines and may exacerbate pathologies associated with MUC1-positive prostate cancers.

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.

Role of prolactin in chloro-S-triazine rat mammary tumorigenesis.

Chloro-S-triazine herbicides [cyanazine (CZ), atrazine (AZ), simazine (SZ)] increase mammary tumors in Crl:CD BR rats but not in F-344 rats or in mice. A nongenotoxic mechanism was investigated since the chloro-S-triazines are negative in short-term tests for genotoxicity. An in vivo battery was used to assess the chloro-S-triazines for estrogenic activity or for their ability to increase prolactin (PRL) levels, both of which play important roles in enhancing mammary gland tumorigenesis in rodents. Ovariectomized (OVX) female rats were treated with AZ, CZ, SZ, or three CZ metabolites for 4 days via intraperitoneal injection. The pattern of responses between the chloro-S-triazines and four controls (estradiol, estriol, haloperidol, reserpine) was compared. For the 6 end-points examined, the responses from rats treated with AZ, CZ, SZ, and the metabolites of CZ most closely matched the responses from the reserpine-treated rats (a PRL rather than estrogenic mechanism). In addition, AZ, CZ, and SZ were tested in several other in vitro models (estrogen/biogenic amine receptor competition assays and a yeast-expressed human estrogen receptor transcription assay) as well as an in vivo 24 h time-course experiment to characterize the CZ-induced increases in PRL levels. AZ, CZ, and SZ are not estrogen receptor (ER) activating compounds based on yeast transactivation and receptor competition data. CZ and AZ demonstrated marginal competition (at mM levels) to the D and alpha2 adrenergic receptors. Ligands to the D2 receptor, but not the alpha2 adrenergic receptor, are known to induce mammary tumors. CZ was also found to produce elevated PRL levels in a time-course similar to that seen with reserpine and haloperidol. Overall, the pattern of responses obtained with the chloro-S-triazines most closely matched the responses observed for reserpine. Taken together, these data suggest chloro-S-triazine-induced mammary tumors in rats are mediated through a PRL mechanism, which is thought to be of low relevance to humans.

Chronic toxicity and oncogenicity bioassay in rats with the chloro-s-triazine herbicide cyanazine.

Cyanazine is a member of the chloro-s-triazine class of herbicides. Other triazine herbicides have been shown to induce mammary-gland tumors in rats, although the response is unique to the Sprague-Dawley strain. Cyanazine is nongenotoxic. The present study was conducted to evaluate the chronic toxicity and oncogenic potential of cyanazine. Groups of 62 male and female rats were fed diets containing cyanazine at concentrations of 1, 5, 25, or 50 ppm for up to 2 yr. Mean body weight and body weight gain of male and female rats of the 25- and 50-ppm groups were significantly reduced over the course of the study. Food consumption and food efficiency were also reduced in these groups. Survival was not adversely affected in the treatment groups compared to controls. A significant increase in the incidence of masses of the inguinal region was noted among female rats of the 50-ppm group. These masses were correlated with a significant increase in the incidence of female rats with mammary-gland adenocarcinomas and carcinosarcomas. The incidence of rats with malignant mammary-gland tumors was elevated in the 5-, 25-, and 50-ppm groups, although the incidence within the 5-ppm group was within historical controls. There were no other toxicologically significant observations with respect to ophthalmological, clinical laboratory, or pathological evaluations. Under the conditions of this study, the no-observed-adverse-effect level was 5 ppm. Research into the mechanism of action suggests these mammary tumors are mediated through a prolactin mechanism that is thought to be of low relevance to humans.

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.

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 17 beta-estradiol on serum hormone concentrations and estrous cycle in female Crl:CD BR rats: effects on parental and first generation rats.

The recently passed Food Quality Protection Act of 1996 requires the U.S. EPA to implement screening strategies for endocrine active compounds (EACs) within the next 2 years. Interpreting results from screening tests is complicated by the absence of traditional dietary rodent bioassay data with model estrogenic compounds such as 17 beta-estradiol. Thus, a 90-day/one-generation reproduction study with 17 beta-estradiol was designed to: (1) provide such baseline data; (2) set dose levels for multigeneration reproduction and combined chronic toxicity/oncogenicity studies; and (3) evaluate various mechanistic/biochemical endpoints for inclusion in these follow-up studies. The current article describes the effects of dietary administration of 0, 0.05, 2.5, 10, and 50 ppm 17 beta-estradiol on the serum hormone concentrations and estrous cyclicity of female Crl:CD BR rats and evaluates a sampling strategy for measuring serum hormone levels in cycling female rats. Serum hormones were measured at three time points during a 90-day dietary exposure (1 week, 28 days, and 90 days) and in the F1 generation rats on postnatal day 98. Over the course of the 90-day feeding study for the P1 generation and from postnatal days 21 to 98 for the F1 generation, the estrous cycle was monitored daily in 10 rats/group. In P1 generation rats, dietary administration of 2.5, 10, and 50 ppm 17 beta-estradiol produced a dose-dependent increase in serum estradiol (E2) concentrations at all time points. In contrast, administration of 0.05, 2.5, 10, and 50 ppm 17 beta-estradiol produced a dose-dependent decrease in serum progesterone (P4) concentrations on test day 90, which correlated with an absence of corpora lutea and ovarian atrophy. At 10 and 50 ppm 17 beta-estradiol, serum luteinizing hormone (LH) concentrations were consistently decreased at all time points and were decreased at 2.5 ppm on test day 90. Serum prolactin (PRL) concentrations were increased at 50 ppm 17 beta-estradiol on test day 90. Serum follicle stimulating hormone (FSH) concentrations were either similar to the control levels or minimally changed at all time points. No F1 generation rats were produced at 10 or 50 ppm 17 beta-estradiol. In F1 generation rats, serum E2 concentrations were increased and P4 concentrations were decreased at a dietary concentration of 2.5 ppm 17 beta-estradiol, while serum concentrations of LH, FSH, and PRL were similar to the control. Dietary administration of 17 beta-estradiol at concentrations of 2.5 (both generations) and 10 and 50 ppm (P1 generation only) produced marked effects on the estrous cycle: decreased number of cycles, increased mean cycle length, and decreased number of normally cycling rats. The estrous cyclicity of rats fed 2.5 ppm 17 beta-estradiol appeared more severely affected in rats of the F1 generation than in rats of the P1 generation. Whether this increase in severity is related to an in utero exposure and/or greater mean daily intake of 17 beta-estradiol in the F1 generation rats in the postnatal period is unclear. Another goal of this study was to evaluate whether a single time point sampling strategy using cycling female rats could be used to detect compound-related changes in serum hormone concentrations. In evaluating a sampling strategy for measuring serum hormone levels, it appears that detection of compound-related alterations in serum hormone concentrations can be best detected by sampling during diestrus. Since the stage of the cycle dramatically influences hormone concentrations, large sample sizes (n = 50) are needed if serum hormone measurements are not matched with the stage of the cycle. The data indicate that this strategy of measuring serum hormone concentrations has utility in detecting compound-related effects within the confines of a traditional guideline study (subchronic, chronic, or multigenerational reproduction study).

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.

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.

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.

Evaluation of the primary humoral immune response following exposure of male rats to 17beta-estradiol or flutamide for 15 days.

There is a concern that certain industrial chemicals found in the environment may mimic or antagonize endogenous hormones and adversely affect the endocrine as well as the immune system. The objective of this study was to determine if exposure of Crl:CD (SD)BR male rats to 17beta-estradiol (17beta-E2), an estrogen receptor agonist, or flutamide (FLUT), an androgen receptor antagonist, would significantly alter the primary IgM humoral immune response to sheep red blood cells (SRBC). This study was conducted in the context of a male in vivo Tier I battery designed to identify endocrine-active compounds (EACs). The Tier I male battery consists of organ weights coupled with a comprehensive hormonal assessment. Rats were dosed by the intraperitoneal route for 15 days with vehicle or 0.001, 0.0025, 0.0075, or 0.050 mg/kg/day 17beta-E2 or 0.25, 1, 5, or 20 mg/kg/day FLUT. Six days prior to termination, selected rats were injected intravenously with SRBC for assessment of humoral immune function. Spleen cell number and spleen and thymus weights were obtained. Serum was analyzed for anti-SRBC IgM antibody by using an enzyme-linked immunosorbent assay. At 0.050 mg/kg/day 17beta-E2, mean final body and absolute thymus weights were significantly decreased to 84 and 65% of control, respectively. 17beta-E2 did not significantly alter spleen weight, spleen cell number, or the primary IgM humoral immune response to SRBC. The no-observed-adverse-effect level (NOAEL) for immune system alteration was 0.050 mg/kg/day 17beta-E2 since the decrease in absolute thymus weight was judged to be secondary to the decrements in body weight. In the Tier I male battery, responses to 17beta-E2 included decreased absolute testis and epididymis weights, decreased relative accessory sex gland unit weights, hormonal alterations (decreased serum testosterone (T), dihydrotestosterone (DHT), and luteinizing hormone (LH), and increased serum prolactin and E2 levels). The lowest-observed-adverse-effect level (LOAEL) for the reproductive indices was 0.001 mg/kg/day 17beta-E2 based on the hormonal alterations seen at this level; no NOAEL was established. Exposure to FLUT did not significantly alter mean final body, spleen, or absolute thymus weights, spleen cell number, or the primary IgM humoral immune response to SRBC. A significant increase (118% of control) in relative thymus weight was observed at 20 mg/kg/day FLUT. The NOAEL for immune system alteration was 5 mg/kg/day FLUT based on the increased relative thymus weights that were judged to be compound-related. In the Tier I male battery, responses to FLUT included decreased absolute epididymis and relative accessory sex gland unit weights and hormonal alterations (increased serum T, DHT, E2, and LH, and decreased follicle stimulating hormone levels). The LOAEL for the reproductive indices was 0.25 mg/kg/day FLUT based on the hormonal alterations seen at this level; no NOAEL was established. Based on these data, the reproductive and not the immune system appears to be the primary target organ of toxicity in young adult male rats treated with either 17beta-E2 or FLUT.

Ex vivo and in vitro testis and ovary explants: utility for identifying steroid biosynthesis inhibitors and comparison to a Tier I screening battery.

Testis and ovary explants have been proposed as in vitro screens for identifying potential inhibitors of steroid biosynthesis. The goals of the current study were to optimize the conditions of the two assays, to characterize these assays using several compounds with well-defined endocrine activity, and to compare the responses from the explant assays with an in vivo male battery currently undergoing validation using the Crl:CD BR rat in order to evaluate their utility as test systems for screening unknown compounds for possible steroid biosynthesis inhibition activity. There were two components to the testis/ovary assays: ex vivo and in vitro. The ex vivo component used testes/ovaries from animals dosed with the test compounds in vivo, and the in vitro component used testes/ovaries from control animals. For the testis assays, decapsulated testis explants (50 mg) were placed into glass scintillation vials, +/-1.0 IU/ml hCG for 3 h in a shaking water bath (34 degrees C). Following the incubation period, medium was removed, centrifuged, and frozen until assayed for hormone concentrations. A similar procedure was used for the ovary explant assay except that each ovary was incubated separately. The testis explants were evaluated using the following compounds: ketoconazole (KETO), a testosterone biosynthesis inhibitor; aminoglutethimide (AG) (only in vitro) and anastrozole (ANA), aromatase inhibitors; finasteride (FIN), a 5alpha-reductase inhibitor; 17beta-estradiol (17beta-E2), an estrogen receptor agonist; flutamide (FLUT), an androgen receptor antagonist; ICI-182,780 (ICI), an estrogen receptor antagonist; haloperidol (HALO), a D2 receptor antagonist; and reserpine (RES), a dopamine depletor. In the ovary assay, AG (only in vitro), ANA, ICI, and HALO (only in vitro) were evaluated. Addition of fetal calf serum to the medium allowed measurement of estradiol (E2) in the testis assay, but production was not inhibited by ANA or AG. In the ovary explant assay, only AG was identified as inhibiting E2 production in vitro. Hence, both the testis and ovary explant assays appear to have limited utility for detecting aromatase inhibitors. Screening of these nine diverse endocrine-active compounds resulted in all of them being identified as altering the endocrine system when assessed by ex vivo and in vitro testis explants. Using only the in vitro assessment with the criteria of steroid biosynthesis inhibition, four of nine compounds were correctly identified in the testis explant assay (17beta-E2, KETO, FLUT, and HALO). The predictability of both the in vitro and ex vivo ovary assay was 50%, suggesting a 50% false positive or negative rate with unknown compounds. However, of the seven compounds assessed to date (17beta-E2, ICI, ANA, KETO, FLUT, HALO, and RES), all were correctly identified using an in vivo male battery, which also has the capability to detect other endocrine activities. Therefore, the testis and ovary explant assay would not be necessary if one were using an in vivo male battery, since this screen would identify steroid biosynthesis inhibitors and would also identify several other endocrine activities. Because of the difficulties in assessing cytotoxicity and the high false positive/negative rates, the ovary and testis explant assays are not useful as routine screening procedures for detecting steroid biosynthesis inhibitors; however, they may have utility in confirming in vivo findings.

Development of a Tier I screening battery for detecting endocrine-active compounds (EACs).

One of the components of our research program is development of a mode-of-action screening battery to detect several different types of endocrine-active compounds (EACs). Our working hypothesis is that a comprehensive short-term in vivo/in vitro battery can be developed to identify endocrine toxicants using a collection of endpoints. The goals of this battery are that it be quick, cost effective, and predictive. The purpose of this battery is to identify potential EACs and to assess their potency in order to prioritize compounds for further study. Two in vivo screens (intact male and ovariectomized female rats) are being evaluated for their ability to detect several different types of endocrine activity. To validate this screen, 15 compounds with known endocrine activities are being used to evaluate a collection of different endpoints for their variability, stability over time, predictiveness, and dose dependency. These positive controls were chosen because they can modulate development, reproduction, or cancer. The advantage of an in vivo screen is that it utilizes a metabolically and physiologically intact system. The male in vivo battery will be used to assess several different types of endocrine activity, primarily by using a comprehensive hormonal battery. The female in vivo battery will be used to identify compounds which are either estrogenic/antiestrogenic or can alter the prolactin pathway. The in vitro portion of the screening battery consists of a yeast transactivation system (YTS). The YTS is being evaluated for its ability to identify compounds which are agonists or antagonists to the estrogen, androgen, or progesterone receptors. The expression of mammalian receptors in yeast allows for assessment of steroid-dependent transcriptional activators. The value of this system is that it can be used as a routine screen for compounds that interact with steroid receptors. Alterations in ligand binding to these receptors can be correlated with alterations in development via masculinization of females and/or feminization of males, decreases in reproductive success, or modulation of cancer incidence from in vivo tests. The in vivo and in vitro screens are designed to be run in parallel with built-in redundancy in order to reduce the probability of false-negative/ positive responses.

Weak estrogenic activity from continuous-release pellets.

In the process of evaluating a proprietary compound for weak estrogenic activity, two different types of dosing regimens were used, repeated daily dosing (three times/d) and continuous-release pellets. In studies using the proprietary compound, rats that were dosed via intraperitoneal injection showed no estrogenic responses, while those receiving the test compound via continuous-release pellets displayed several estrogenic responses. Because of the conflicting results, the control pellets were evaluated for estrogenic activity in the same battery of tests using the same number of pellets. In studies using only the control pellets, several estrogenic responses were observed including increased uterine weight, uterine stromal cell proliferation, estrous conversion, uterine progesterone receptor content, and decreased uterine estrogen receptor content. Animals receiving no pellet implant showed no estrogenic responses. In addition, a methylene chloride/DMSO extract of the control pellets promoted expression of a reporter gene controlled by the estrogen receptor and demonstrated competition with 17 beta-estradiol for binding to the human estrogen receptor. It is concluded that component(s) of the control pellets possess weak estrogenic activity.

An in vivo battery for identifying endocrine modulators that are estrogenic or dopamine regulators.

We have combined several endpoints into a single 5-day in vivo screening procedure to identify estrogenic compounds and dopaminergic modulators, both of which play important roles in enhancing mammary tumorigenesis in rodents. The endpoints evaluated as markers of estrogenicity included increases in uterine fluid and vaginal cornification incidence, serum prolactin levels, uterine weight, uterine epithelial cell height, uterine stromal cell proliferation, and uterine progesterone receptor (PR) number and decreases in uterine estrogen receptor (ER) number. The endpoints evaluated for changes in dopamine regulation included increases in prolactin and decreases in growth hormone levels. The estrogen agonist estradiol (E2) and estriol (E3), the mixed estrogen agonist/ antagonist tamoxifen (TAM), the full antiestrogen ICI-182, 780 (ICI),and the dopamine modulators haloperidol (HAL) and reserpine (RES) were tested using a three-time/day (8-hr intervals) intraperitoneal dosing regimen in sexually mature ovariectomized female Crl:CD BR rats. All compounds were evaluated over a range of concentrations. This in vivo battery was used to evaluate the effects of different classes of endocrine modulators on the selected endpoints. For example, the estrogen receptor agonists E2 and E3 display a unique profile based on changes in the uterotrophic endpoints (estrus conversion, uterine fluid imbibition, increases in uterine weight, and uterine endometrial cell proliferation) where full and partial agonists can be distinguished by the magnitude of these responses. Both the estrogen receptor antagonist ICI and the dopamine modulators HAL and RES lack these uterotrophic responses. Dopamine modulators can be distinguished from estrogen receptor agonists by the profile of increased prolactin levels with no uterotrophic changes. Estrogen receptor antagonists can be distinguished from agonists by comparing their effects on ER, PR, and uterotrophic responses. For instance, the full estrogen receptor antagonist ICI decreased ER (to almost 0) and PR levels, but has no uterotrophic effects, while TAM decreases ER (to almost 0) and increases PR with uterotrophic effects. The most useful endpoints for distinguishing estrogen agonists and dopamine modulators were uterine fluid imbibition, uterine weight, uterine stromal cell proliferation, and serum prolactin levels. In order to distinguish an estrogen agonist from an antagonist, other endpoints, such as receptor levels, are necessary. The advantage of an in vivo screen is that it utilizes a metabolically and physiologically defined system which is especially important with highly integrative system such as the endocrine system. This battery can be used as a screening tool to identify potential endocrine modulators as well as to identify mode of action following adverse findings in toxicology studies. Last, additional endpoints may be added to identify other classes of endocrine modulators.