Steven R. Frame

Immunotoxicity of perfluorooctanoic acid and perfluorooctane sulfonate and the role of peroxisome proliferator-activated receptor alpha.

Perfluorooctanoic acid (PFOA) and perfluorooctane sulfonate (PFOS) are environmentally widespread and persistent chemicals with multiple toxicities reported in experimental animals and humans. These compounds can trigger biological activity by activating the alpha isotype of peroxisome proliferator-activated receptors (PPARs), ligand-activated transcription factors that regulate gene expression; however, some biological effects may occur independently of the receptor. Activation of the peroxisome proliferator-activated receptor alpha (PPARα) modulates lipid and glucose homeostasis, cell proliferation and differentiation, and inflammation. Reported immunomodulation in experimental animals exposed to PFOA and PFOS has included altered inflammatory responses, production of cytokines and other proteins, reduced lymphoid organ weights, and altered antibody synthesis. Mounting experimental animal evidence suggests PPARα independence of some immune effects. This evidence originates primarily from studies with PPARα knockout models exposed to PFOA that demonstrate hepatic peroxisome proliferation, reduced lymphoid organ weights, and altered antibody synthesis. As human PPARα expression is significantly less than that of rodents, potential PPARα independence indicates that future research must explore mechanisms of action of these compounds, including PPARα -dependent and -independent pathways. This multiauthored review contains brief descriptions of current and recently published work exploring immunomodulation by PFOA and PFOS, as well as a short overview of other PPARα ligands of therapeutic and environmental interest.

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)

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.

Ninety-Day Inhalation Toxicity Study With A Vapor Grown Carbon Nanofiber in Rats

A subchronic inhalation toxicity study of inhaled vapor grown carbon nanofibers (CNF) (VGCF-H) was conducted in male and female Sprague Dawley rats. The CNF test sample was composed of > 99.5% carbon with virtually no catalyst metals; Brunauer, Emmett, and Teller (BET) surface area measurements of 13.8 m2/g; and mean lengths and diameters of 5.8 µm and 158 nm, respectively.Four groups of rats per sex were exposed nose-only, 6 h/day, for 5 days/week to target concentrations of 0, 0.50, 2.5, or 25 mg/m3 VGCF-H over a 90-day period and evaluated 1 day later. Assessments included conventional clinical and histopathological methods, bronchoalveolar lavage fluid (BALF) analysis, and cell proliferation (CP) studies of the terminal bronchiole (TB), alveolar duct (AD), and subpleural regions of the respiratory tract. In addition, groups of 0 and 25 mg/m3 exposed rats were evaluated at 3 months postexposure (PE). Aerosol exposures of rats to 0.54 (4.9 f/cc), 2.5 (56 f/cc), and 25 (252 f/cc) mg/m(3) of VGCF-H CNFs produced concentration-related small, detectable accumulation of extrapulmonary fibers with no adverse tissue effects. At the two highest concentrations, inflammation of the TB and AD regions of the respiratory tract was noted wherein fiber-laden alveolar macrophages had accumulated. This finding was characterized by minimal infiltrates of inflammatory cells in rats exposed to 2.5mg/m(3) CNF, inflammation along with some thickening of interstitial walls, and hypertrophy/hyperplasia of type II epithelial cells, graded as slight for the 25mg/m(3) concentration. At 3 months PE, the inflammation in the high dose was reduced. No adverse effects were observed at 0.54mg/m(3). BALF and CP endpoint increases versus controls were noted at 25mg/m(3) VGCF-H but not different from control values at 0.54 or 2.5mg/m(3). After 90 days PE, BALF biomarkers were still increased at 25mg/m(3), indicating that the inflammatory response was not fully resolved. Greater than 90% of CNF-exposed, BALF-recovered alveolar macrophages from the 25 and 2.5mg/m(3) exposure groups contained nanofibers (> 60% for 0.5mg/m(3)). A nonspecific inflammatory response was also noted in the nasal passages. The no-observed-adverse-effect level for VGCF-H nanofibers was considered to be 0.54mg/m(3) (4.9 fibers/cc) for male and female rats, based on the minimal inflammation in the terminal bronchiole and alveolar duct areas of the lungs at 2.5mg/m(3) exposures. It is noteworthy that the histopathology observations at the 2.5mg/m(3) exposure level did not correlate with the CP or BALF data at that exposure concentration. In addition, the results with CNF are compared with published findings of 90-day inhalation studies in rats with carbon nanotubes, and hypotheses are presented for potency differences based on CNT physicochemical characteristics. Finally, the (lack of) relevance of CNF for the high aspect ratio nanomaterials/fiber paradigm is discussed.

Evaluation of the Immune System in Rats and Mice Administered Linear Ammonium Perfluorooctanoate

Repeated high doses of ammonium perfluorooctanoate (APFO) have been reported to affect immune system function in mice. To examine dose-response characteristics in both rats and mice, male CD rats and CD-1 mice were dosed by oral gavage with 0.3-30 mg/kg/day of linear APFO for 29 days. Anti-sheep red blood cell (SRBC) IgM levels, clinical signs, body weights, selected hematology, and lipid parameters, liver weights, spleen, and thymus weights and cell number, selected histopathology, and serum corticosterone concentrations were evaluated. In rats, linear APFO had no effect on production of anti-SRBC antibodies. Ten and 30 mg/kg/day resulted in systemic toxicity as evidenced by decreases in body weight gain to 74 and 37%, and increases in serum corticosterone levels to 135 and 196% of control, respectively. In mice dosed with 10 and 30 mg/kg/day, marked systemic toxicity and stress were observed, as evidenced by a loss in body weight of 3.8 and 6.6 g, respectively (despite a tripling of liver weight), approximately 230% increase in serum corticosterone, and increases in absolute numbers of peripheral blood neutrophils and monocytes with an accompanying decrease in absolute lymphocyte numbers. Immune-related findings at 10 and 30 mg/kg/day that likely represent secondary responses to the systemic toxicity and stress observed at these doses include: decreased IgM antibody production at 10 (20% suppression) and 30 mg/kg/day (28% suppression); decreased spleen and thymus weights and cell numbers; microscopic depletion/atrophy of lymphoid tissue at 10 (thymus) and 30 mg/kg/day (spleen). In summary, no immune-related changes occurred in rats, even at doses causing systemic toxicity. In mice, immune-related changes occurred only at doses causing significant and profound systemic toxicity and stress.

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 Bowmans glands. Hamsters did not have demonstrable nasal cavity microscopic changes. Chronic exposure to MMA vapour did not cause tumours in either rats or hamsters.

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:CDr/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.

Toxicological evaluation of sodium perfluorohexanoate.

Sodium perfluorohexanoate [NaPFHx, F(CF(2))(5)CO(2)Na, CAS#2923-26-4] was evaluated in acute, 90-day subchronic, one-generation reproduction, developmental and in vitro genetic toxicity studies. In the subchronic/one-generation reproduction study, four groups of young adult male and female Crl:CD(SD) rats were administered NaPFHx daily for approximately 90 days by gavage at dosages of 0, 20, 100, or 500 mg/kg. Selected groups of rats were evaluated after 1- and 3-month recovery periods. Rats selected for reproductive evaluations were dosed for approximately 70 days prior to cohabitation, through gestation and lactation, for a total of about 4 months. The subchronic toxicity no observed adverse effect level (NOAEL) was 20mg/(kg day), based on nasal lesions observed at 100 and 500 mg/(kg day). No effects were observed for neurobehavioral endpoints. NaPFHx was a moderate inducer of hepatic peroxisomal beta-oxidation with a no observed effect level (NOEL) of 20 (male rats) and 100mg/(kg day) (female rats). Elevated hepatic beta-oxidation levels were observed following 1-month recovery in male and female rats at 500 mg/(kg day). No NaPFHx-related effects were observed on any reproductive parameters. The P(1) adult rat NOAEL was 20mg/(kg day), based on reduced body weight parameters, whereas the NOAEL for reproductive toxicity was 100 mg/(kg day), based on effects limited to reduced F(1) pup weights. In the developmental study, female rats were dosed via gavage on gestation day (GD) 6-20 with the same doses of NaPFHx administered in the subchronic study. The maternal and developmental toxicity NOAEL was 100 mg/(kg day), based on maternal and fetal body weight effects at 500 mg/(kg day). NaPFHx is therefore concluded not to present a reproductive or developmental hazard. NaPFHx genotoxicity studies showed no mutations in the bacterial reverse mutation (Ames) assay or chromosome aberrations in human lymphocytes treated with NaPFHx in vitro. The lowest NOAEL from all of the studies was 20mg/(kg day) in the subchronic study based on nasal lesions. Benchmark doses (BMDL10) for nasal lesions were 13 and 21 mg/(kg day) for male and female rats, respectively. The relevance of the nasal lesions to humans is not known.

Pulmonary exposures to Sepiolite nanoclay particulates in rats: Resolution following multinucleate giant cell formation

Sepiolite is a magnesium silicate-containing nanoclay mineral and is utilized as a nanofiller for nanocomposite applications. We postulated that lung exposures to Sepiolite clay samples could produce sustained effects. Accordingly, the pulmonary and extrapulmonary systemic impacts in rats of intratracheally instilled Sepiolite nanoclay samples were compared with quartz or ultrafine (uf) titanium dioxide particle-types at doses of 1mg/kg or 5mg/kg. All particulates were well characterized, and dedicated groups were evaluated by bronchoalveolar lavage, lung cell proliferation, macrophage functional assays and full body histopathology at selected times postexposure (pe). Bronchoalveolar lavage results demonstrated that quartz particles produced persistent, dose-dependent lung inflammatory responses measured from 24h through 3 months pe. Exposures to uf TiO(2) particles or Sepiolite samples produced transient neutrophilic responses at 24-h pe; however, unlike the other particle-types, Sepiolite exposures produced macrophage-agglomerates or multinucleate giant cells at 1 week, 5 weeks and 3 months pe. In vitro alveolar macrophage functional studies demonstrated that mononuclear cells recovered from quartz but not Sepiolite or uf TiO(2)-exposed rats were deficient in their chemotactic capacities. Moreover, lung parenchymal cell proliferation rates were increased in rats exposed to quartz but not Sepiolite or uf TiO(2) particles. Histopathological evaluation of lung tissues revealed that pulmonary exposures to Sepiolite nanoclay or quartz samples produced inflammation in centriacinar regions at 24-h pe but the effects decreased in severity over time for Sepiolite and increased for quartz-exposed rats. The quartz-induced lesions were progressive and were characterized at 3 months by acinar foamy alveolar macrophage accumulation and septal thickening due to inflammation, alveolar Type II cell hyperplasia and collagen deposition. In the Sepiolite nanoclay group, the finding of multinucleated giant cell accumulation associated with minor collagen deposition in acinar regions was rarely observed. Exposures to ultrafine TiO(2) produced minimal effects characterized by the occurrence of phagocytic macrophages in alveolar ducts. Full body histopathology studies were conducted at 24h and 3 months post particle exposures. Histopathological evaluations revealed minor particle accumulations in some mediastinal or thoracic lymph nodes. However, it is noteworthy that no extrapulmonary target organ effects were observed in any of the particle-exposed groups at 3 months postexposure.

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)