John C. O'Connor

The toxicology of perfluorooctanoate.

ABSTRACT PFOA is a peroxisome proliferator (PPAR agonist) and exerts morphological and biochemical effects characteristic of PPAR agonists. These effects include increased β-oxidation of fatty acids, increases in several cytochrome P-450 (CYP450)-mediated reactions, and inhibition of the secretion of very low-density lipoproteins and cholesterol from the liver. These effects on lipid metabolism and transport result in a reduction of cholesterol and triglycerides in serum and an accumulation of lipids in the liver. The triad of tumors observed (liver, Leydig cell, and pancreatic acinar-cell) is typical of many PPAR agonists and is believed to involve nongenotoxic mechanisms. The hepatocellular tumors observed in rats are likely to have been the result of the activation of the peroxisome proliferator activated receptor α (PPARα). The tumors observed in the testis (Leydig-cell) have been hypothesized to be associated with an increased level of serum estradiol in concert with testicular growth factors. The mechanism responsible for the acinarcell tumors of the pancreas in rats remains the subject of active investigation. The mechanism resulting in the hepatocellular tumors in rats (PPARα activation) is not likely to be relevant to humans. Similarly, the proposed mechanism for Leydig-cell tumor formation is of questionable relevance to humans. Acinar tumors of the pancreas are rare in humans, and the relevance of the these tumors, as found in rats, to humans is uncertain. Epidemiological investigations and medical surveillance of occupationally exposed workers have not found consistent associations between PFOA exposure and adverse health effects.

Effects of Dietary 17β-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.

Evaluation of Tier I screening approaches for detecting endocrine-active compounds (EACs).

In 1996, Congress passed legislation requiring the U.S. Environmental Protection Agency (EPA) to implement screening/testing strategies for endocrine-active compounds (EACs). In response, EPA convened the Endocrine Disruptor Screening and Testing Advisory Committee (EDSTAC) to advise the agency on a strategy to screen and test xenobiotics for endocrine disruption. EDSTAC completed their charter in 1998 by recommending a tiered screening and testing scheme to evaluate compounds for their potential to act as agonists or antagonists to the estrogen or androgen receptors, steroid biosynthesis inhibitors, or their ability to alter thyroid function. For Tier I, the EDSTAC-recommended screening battery comprised eight different assays, but EDSTAC also proposed two alternative batteries that were deemed worthy of further evaluation. The challenge currently confronting EPA is to choose among the Tier I screening options and then to standardize protocols, validate the assays, and determine the criteria for judging a compound as positive or negative in the battery. The purpose of the current review is to: (1) provide an overview of the three EDSTAC options, (2) evaluate the data currently available for the individual assays of the three EDSTAC options and discuss the strengths and limitations of each, and (3) provide a final recommendation for a Tier I screen based on the experiences of the authors who have used all of the individual assays under consideration by EDSTAC. The goal of this report is not to provide an exhaustive historical review of each assay, but rather to summarize some of the more relevant data from available published reports as it relates to current proposed study designs for those particular assays. Based on the current data, a Tier I screening battery consisting of in vitro receptor binding assays, a 3-day uterotrophic assay, and a 15-day intact male assay are recommended as the preferred approach on which future validation efforts should be focused. This screening approach is a mode-of-action screen that will identify specific types of endocrine activity. Because it utilizes many endpoints from the same test animals (i.e., it integrates), it is the most cost-effective and efficient option in terms of animal usage. The mode-of-action screening approach advances scientific understanding and is preferred over other options based on apical tests, as these essentially are reproductive effects screens that are not necessarily specific for endocrine activity. Because Tier II tests include the critical apical endpoints used in the pubertal models, a mode-of-action approach provides complementary rather than redundant data. By identifying the potential mode of action, critical endpoints can be included in Tier II studies that will be used to define dose-response curves and no observed adverse effect levels (NOAELs)/no observed effect levels (NOELs) for the compound.

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 endpoints 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 24h 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 α2 adrenergic receptors. Ligands to the D2 receptor, but not the α2 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.

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)

90-day oral gavage toxicity study of 8-2 fluorotelomer alcohol in rats.

8-2 fluorotelomer alcohol is a fluorinated chemical intermediate used to manufacture specialty polymers and surfactants. The potential subchronic toxicity and the reversibility of the effects of this chemical were evaluated following approximately 90 days of oral gavage dosing to Crl:CD®(SD)IGS BR rats. A complete toxicological profile, including neurobehavioral assessments and hepatic β-oxidation, were conducted at selected intervals and a group of rats was included for a 90-day postdosing recovery period. Dose levels tested were 0 (control), 1, 5, 25, and 125 mg/kg. No test-substance-related mortality occurred at any dose level. Rats at 125 mg/kg developed striated teeth, such that these animals were switched to ground chow at 77 days. No treatment-related alterations in body weight, food consumption, neurobehavioral parameters, or hematology/clinical chemistry were found. Hepatic β-oxidation was increased in males at 125 mg/kg and in females at 25 and 125 mg/kg. In both males and females, plasma fluorine levels were increased at 125 mg/kg and urinary fluorine was elevated at ≥5 mg/kg. Degeneration/disorganization of enamel organ ameloblast cells was observed at 125 mg/kg in males, but not females. Liver weight increases accompanied by focal hepatic necrosis were observed at both 25 and 125 mg/kg, and chronic progressive nephrotoxicity occurred in female rats at 125 mg/kg. With the exception of hepatocellular necrosis in males at 125 mg/kg and the increased incidence and severity of chronic progressive nephropathy in females at 125 mg/kg, all other changes showed evidence of reversibility. The no-observed-adverse-effect level was 5 mg/kg.

Key Lessons from Performance of the U.S. EPA Endocrine Disruptor Screening Program (EDSP) Tier 1 Male and Female Pubertal Assays

The male and female pubertal assays, which are included in the U.S. Environmental Protection Agencys (EPA) Endocrine Disruptor Screening Program (EDSP) Tier 1 battery, can detect endocrine-active compounds operating by various modes of action. This article uses the collective experience of three laboratories to provide information on pubertal assay conduct, interlaboratory reproducibility, endpoint redundancy, and data interpretation. The various criteria used to select the maximum tolerated dose are described. A comparison of historical control data across laboratories confirmed reasonably good interlaboratory reproducibility. With a reliance on apical endpoints, interpretation of pubertal assay effects as specifically endocrine-mediated or secondary to other systemic effects can be problematic and mode of action may be difficult to discern. Across 21–23 data sets, relative liver weight, a nonspecific endocrine endpoint, was the most commonly affected endpoint in male and female assays. For endocrine endpoints, patterns of effects were generally seen; rarely was an endocrine-sensitive endpoint affected in isolation. In males, most frequently missed EPA-established performance criteria included mean weights for kidney and thyroid, and the coefficient of variation for age and body weight at preputial separation, seminal vesicle weight, and final body weight. In females, the frequently missed EPA-established performance criteria included mean adrenal weight and mean age at vaginal opening. To ensure specificity for endocrine effects, the pubertal assays should be interpreted using a weight-of-evidence approach as part of the entire EDSP battery. Based on the frequency with which certain performance criteria were missed, an EPA review of these criteria is warranted.

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.

Two-day inhalation toxicity study of methyl iodide in the rat

The effects of inhaled methyl iodide (MeI) on clinical pathology parameters, glutathione (GSH) tissue levels, serum thyroid hormone and inorganic iodide concentrations, S-methylcysteine hemoglobin concentrations, and liver UDP-glucuronyltransferase activity were studied in the rat. Male rats were exposed by whole-body inhalation to 0, 25, or 100 ppm MeI, 6 h/day for up to 2 days. Serum cholesterol concentrations (both high-density lipoprotein [HDL] and low-density lipoprotein [LDL] fractions) were increased and triglycerides were decreased at both exposure levels. Serum thyroid-stimulating hormone (TSH) concentrations were increased at 25 and 100 ppm, and serum triiodothyronine (T3) and thyroxine (T4) concentrations were decreased at 100 ppm. There was no change in either reverse triiodothyronine (rT3) or UDP-glucuronyltransferase activity at either exposure level. A dose- and time-dependent reduction in GSH levels in blood, kidney, liver, and nasal tissue was observed, with the greatest reduction in nasal tissue (olfactory and respiratory epithelium). MeI exposure also resulted in a substantial dose- and time-dependent increase in both serum inorganic iodide and red blood cell S-methylcysteine hemoglobin adducts. These results indicate that following inhalation exposure, MeI is rapidly metabolized in blood and tissue of rats, resulting in methylation products and release of inorganic iodide.

Results of the negative control chemical allyl alcohol in the 15-day intact adult male rat screening assay for endocrine activity.

Development, standardization, and validation of methods to assess the potential of chemicals to disrupt hormonal homeostasis have been the focus of considerable research efforts over the past 10 years. As part of our validation effort, we evaluated the specificity of the 15-day intact adult male rat assay, using a negative control chemical, allyl alcohol, a known hepatotoxicant that was not expected to induce endocrine effects. Male rats were dosed for 15 days via oral gavage with 0, 10, 30, 40, or 50 mg/kg/day allyl alcohol. The endpoints evaluated included final body and organ weights, serum hormone concentrations, and a limited histopathology assessment. No mortality or adverse clinical signs were observed. Mean final body weight for rats in the 50-mg/kg/day dose group was decreased to 90% of control. Mean relative liver weights were increased at 40 and 50 mg/kg/day (115% and 117% of control, respectively). Serum testosterone and DHT concentrations were statistically significantly decreased at 50 mg/kg/day (72% of control). Serum prolactin concentrations were statistically significantly decreased at 40 mg/kg/day (58% of control), but not at 50 mg/kg/day. There were no effects on the other endpoints evaluated. Consistent with previous guidance for interpreting the 15-day intact adult male rat assay, histological and weight changes of target organs were given a higher weight-of-evidence than changes in serum hormone concentrations alone. Therefore, with only minimal changes in serum hormone concentrations and no effects on organ weights or microscopic alterations, the results of allyl alcohol in the 15-day intact adult male rat assay were considered negative and consistent with the predicted results.