The effects of a vitamin D-deficient diet on chronic cadmium exposure in rats.

Itai-itai disease (IID) of humans is one of the most severe forms of chronic cadmium (Cd) intoxication. Itai-itai disease occurs mainly in post-menopausal women and is characterized by osteoporosis with osteomalacia, renal tubular disorder, and renal anemia. Some researchers insist the major cause of IID is not Cd, but rather malnutrition, especially hypovitaminosis D. We administrated a low concentration of Cd chloride intravenously to ovariectomized female rats that were fed a vitamin D-deficient diet or a normal diet for fifty weeks. The vitamin D-deficient diet decreased serum concentration of vitamin D, but it did not affect the metabolism of the kidney or bone. Cadmium treatment alone induced a decrease in serum concentration of vitamin D, as well as renal dysfunction, renal anemia, and abnormal bone metabolism. Osteoporosis with osteomalacia, tubular nephropathy, fibrous osteodystrophy, and bone marrow hyperplasia occurred following Cd treatment. In rats treated with Cd and administered a vitamin D-deficient diet, the toxic effects of Cd on kidney, bone, and hematopoiesis were enhanced in comparison to rats treated with Cd and a normal diet. The present experiment demonstrated that hypovitaminosis D did not evoke morphologic features of IID in humans but did enhance Cd-induced toxicity in the rat model of this disease.

Acute and subchronic toxicity and genotoxicity of SE5-OH, an equol-rich product produced by Lactococcus garvieae.

The consumption of soy-based products is associated with a number of health benefits and much of these benefits are proposed to be due to the soy isoflavones daidzein, genistein, glycitein, their glycosides, and equol, an isoflavone naturally produced from daidzein. Equol is a naturally bacterially-derived metabolite of daidzein and is produced by bacteria in the gut of those humans capable of hosting the particular organism. To allow all humans to enjoy the health benefits of equol, a new functional food ingredient has been developed that relies on bacterial conversion of daidzein to equol under strictly controlled conditions. This new food substance, termed SE5-OH, has been studied extensively for its acute and subchronic toxicity in Sprague-Dawley rats, as well as for its potential genotoxicity. The oral LD(50) is >4,000 mg/kg. In a 91-day, subchronic study, the no-observed-adverse-effect-level (NOAEL) was 2,000 mg/kg/day, the highest dose tested. SE5-OH was negative in Salmonella typhimurium tester strains TA98, TA100, TA1535 and TA1537 and in Escherichia coli tester strain WP2uvrA with and without metabolic activation. SE5-OH was negative for chromosome aberrations in Chinese hamster lung cells up to 3,000 microg/ml with and without metabolic activation and did not induce increases in micronucleated polychromatic erythrocytes taken from Sprague-Dawley rats administered (via gavage) up to 4,000 mg/kg SE5-OH twice daily for two consecutive days.

Effect of di(2-ethylhexyl) phthalate (DEHP) on genital organs from juvenile common marmosets: I. Morphological and biochemical investigation in 65-week toxicity study.

Recent studies demonstrated that preadolescent male rats are more sensitive to testicular damage from exposure to DEHP than adults. Male and female marmosets were treated daily with 0, 100, 500, or 2500 mg/kg DEHP by oral gavage for 65 wk from weaning (3 mo of age) to sexual maturity (18 mo). No treatment-related changes were observed in male organ weights, and no microscopic changes were found in male gonads or secondary sex organs. Sperm head counts, zinc levels, glutathione levels, and testicular enzyme activities were comparable between groups. Electron microscopic examination revealed no treatment-related abnormalities in Leydig, Sertoli, or spermatogenic cells. Histochemical examination of the testis after 3beta-hydroxysteroid dehydrogenase (3beta-HSD) staining did not reveal any alterations in steroid synthesis in the Leydig cells. Thus, although marmoset monkeys were treated with 2500 mg/kg DEHP, throughout the pre- and periadolescent period, no histological changes were noted in the testes. For females, increased ovarian and uterine weights and elevated blood estradiol level were observed in higher dosage groups, 500 and 2500 mg/kg. These increased weights were associated with the presence of large corpus luteum, a common finding in older female marmosets. Although an effect on the female ovary cannot be completely ruled out, no abnormal histological changes were observed in the ovaries or uteri in comparison to controls. No increases in hepatic peroxisomal enzyme activities were noted in treated groups; isolated hepatic enzyme activities (P-450 contents, testosterone 6beta-hydroxylase, and lauric acid omega-1omega-hydroxylase activities) were increased in males and/or females of either the mid- or high-dose groups, but no consistent dose-related trend was observed.

Chronic cadmium treatment induces islet B cell injury in ovariectomized cynomolgus monkeys.

In an attempt to establish a primate model of chronic cadmium (Cd) toxicosis, we ovariectomized cynomolgus monkeys and treated with CdCl2 by repeated intravenous injections for 13 to 15 months. The animals showed an increase in blood glucose from Month 10 and a decrease in blood insulin at Month 11of the Cd-treatment. Histopathological examination of the Cd-treated animals revealed islet atrophy with reduction in islet number and vacuolation of the islet cells, whereas there was no remarkable change in the acinar cells of the exocrine pancreas. In histomorphometrical examination, insulin-positive areas in the islets were significantly decreased, accompanying a relative increase of glucagon-positive areas. Large amounts of Cd accumulated in the pancreas, and metallothionein (MT), a Cd binding protein, was localized in the islets of Cd-treated animals. The present study demonstrated that the chronic intravenous injection of Cd to cynomolgus monkeys induced the accumulation of the metal in the pancreas, degeneration of islet B cells and the diabetic clinical signs. Therefore the islet B cell is one of the major targets of the chronic Cd poisoning in monkeys.

Metabolite profiling and identification in human urine after single oral administration of DEHP.

Di(2-ethylhexyl)phthalate (DEHP) is known to be a reproductive toxicant in male rodents, and its primary or secondary metabolites seem to be causative agents. To identify and quantify urinary metabolites of DEHP in humans, urine samples collected from healthy male and female volunteers following oral administration of deuterium labeled DEHP (d(4)-DEHP) at 3mg/person were analyzed by a high performance liquid chromatograph/mass spectrometer (LC-MS), and the excretion behavior of orally taken DEHP was evaluated. Mono(2-ethylhexyl)phthalate (MEHP), OH-MEHP, oxo-MEHP, COOH-MEHP, and their glucuronides were identified as metabolites in the male and female urine. The ratios of the conjugate forms in the total urinary metabolites were remarkably high from immediately after administration (0 to 4-hr post-dose), which were approximately 69% to 86% (male) and 80% to 89% (female) until 36-hr post-dose. It was suggested that DEHP taken orally was promptly converted to MEHP and its oxidative metabolites such as OH-MEHP, oxo-MEHP, and COOH-MEHP, and most of these metabolites received the conjugation reaction and were excreted as glucuronides. Remarkable differences from rodents, in which most of these metabolites were excreted as free forms, were demonstrated.

Metabolism of di (2-ethylhexyl) phthalate (DEHP): comparative study in juvenile and fetal marmosets and rats.

We compared the metabolic profile of di (2-ethylhexyl) phthalate (DEHP) in juveniles and fetus between rats and marmosets. STUDY-I: (14)C-DEHP (100 and 2,500 mg/kg) was singly administered to juvenile and adult marmosets by gavage. C(max) of the radioactivity in juvenile marmosets was 6.45 and 31 µg eq./g, respectively. The radioactivity excreted mainly into feces; however, at least 10% of the radioactivity was absorbed even at 2,500 mg/kg. No abnormal accumulation was observed in the male reproductive organs. STUDY-II: (14)C-DEHP (100 mg/kg) was singly administered to juveniles of rat and marmoset. The plasma radioactivity in marmosets was about 5% to 9% of that in rats. Free forms of mono-2-ethylhexyl phthalate (MEHP) and its oxidized metabolites such as oxo-, OH-, and COOH-MEHP were detected as the main compositions in rat plasma. In marmosets, free form of MEHP was also detected as a major composition, but not for oxidized MEHP metabolites. In rats, oxidized MEHP metabolites were excreted into urine as unconjugated forms. MEHP and its oxidized metabolites were also detected in marmoset urine; however, they were mostly glucuronized. No specific accumulation of the radioactivity was noted in the testes of either species; however, the radioactivity concentration in the marmoset testes was much lower than that in rats. STUDY-III: (14)C-DEHP (100 mg/kg) was singly administered to dams on gestation day 130 for marmosets and day 20 for rats. In either species, no specific accumulation of radioactivity was noted in the testis of fetuses from the dams treated with (14)C-DEHP; however, the radioactivity in the rat testis was about 20-times higher than that in the marmoset. Major metabolite components in rat whole fetal tissue were free forms of MEHP, OH-MEHP, and oxo-MEHP. Free form of MEHP was also detected as only a peak in the marmoset fetal tissue.

Species differences in toxicokinetic parameters of glycidol after a single dose of glycidol or glycidol linoleate in rats and monkeys.

Glycidol fatty acid esters (GEs) have been identified as contaminants in refined edible oils. Although the possible release of glycidol (G) from GEs is a concern, little is known about the conversion of GEs to G in the human body. This study addressed the toxicokinetics of glycidol linoleate (GL) and G in male Crl:CD(SD) rats and cynomolgus monkeys. Equimolar amounts of GL (341 mg/kg) or G (75 mg/kg) were administered by gavage to each animal. G was found in both species after the G and GL administration, while plasma GL concentrations were below the lower limit of quantification (5 ng/ml) in both species. In rats, the administration of GL or G produced similar concentration-time profiles for G. In monkeys, the C(max) and AUC values after GL administration were significantly lower than those after G administration. The oral bioavailability of G in monkeys (34.3%) was remarkably lower than that in rats (68.8%) at 75 mg/kg G administration. In addition, plasma G concentrations after oral administration at three lower doses of GL or G were measured in both species. In monkeys, G was detected only at the highest dose of G. In contrast, the rats exhibited similar plasma G concentration-time profiles after GL or G administration with significantly higher G levels than those in monkeys. In conclusion, these results indicate that there are remarkable species differences in the toxicokinetics of GEs and G between rodents and primates, findings that should be considered when assessing the human risk of GEs.

Induction of peroxisome proliferator-activated receptor alpha (PPARalpha)-related enzymes by di(2-ethylhexyl) phthalate (DEHP) treatment in mice and rats, but not marmosets.

To clarify species differences in the induction of peroxisome proliferator-activated receptor alpha (PPARalpha)-related enzymes by di(2-ethylhexyl)phthalate (DEHP) exposure, we investigated the inductions of PPARalpha and its target genes (mitochondrial medium-chain acyl-CoA dehydrogenase (MCAD) and peroxisomal keto-acyl-CoA thiolase (PT) in liver from mice (CD-1), rats (Sprague-Dawley), and marmosets (Callithrix jacchus) exposed to DEHP. Male mice and rats were treated with 0, 1.25 and 2.5 mmol/kg DEHP for 2 weeks, and marmosets with 0, 0.25, 1.25 and 6.25 mmol/kg DEHP for 15 months by gavage. Hepatic mono(2-ethylhexyl)phthalate (MEHP) levels were significantly higher in mice and rats than in marmosets. The constitutive expression of hepatic PPARalpha was 5-7 times greater in rats and mice than in marmosets, but DEHP treatment did not induce PPARalpha-mRNA in all animals. The treatment-induced PT expression detected either by anti-PT antibody or PT-mRNA levels in the liver only from mice and rats, and the induction of the mRNA was greater in the latter than in the former. Thus, DEHP used in this experiment influenced the peroxisomal enzymes in mice and rats, but did not affect the mitochondrial enzymes in any animals or the peroxisomal enzymes in marmosets. These results suggest that there are species differences in the induction of PPARalpha-related enzymes, especially in peroxisomal enzymes by DEHP treatment, and their underlying mechanism may in part reside in the different constitutive levels of PPARalpha and different forming levels of MEHP.

Species differences in the metabolism of di(2-ethylhexyl) phthalate (DEHP) in several organs of mice, rats, and marmosets.

To clarify species differences in the metabolism of di(2-ethylhexyl) phthalate (DEHP) we measured the activity of four DEHP-metabolizing enzymes (lipase, UDP-glucuronyltransferase (UGT), alcohol dehydrogenase (ADH), and aldehyde dehydrogenase (ALDH)) in several organs (the liver, lungs, kidneys, and small intestine) of mice (CD-1), rats (Sprague-Dawley), and marmosets (Callithrix jacchus). Lipase activity, measured by the rate of formation of mono(2-ethylhexyl) phthalate (MEHP) from DEHP, differed by 27- to 357-fold among species; the activity was highest in the small intestines of mice and lowest in the lungs of marmosets. This might be because of the significant differences between Vmax/Km values of lipase for DEHP among the species. UGT activity for MEHP in the liver microsomes was highest in mice, followed by rats and marmosets. These differences, however, were only marginal compared with those for lipase activity. ADH and ALDH activity also differed among species; the activity of the former in the livers of marmosets was 1.6-3.9 times greater than in those of rats or mice; the activity of the latter was higher in rats and marmosets (2-14 times) than in mice. These results were quite different from those for lipase or UGT activity. Because MEHP is considered to be the more potent ligand to peroxisome proliferator-activated receptor alpha involved in different toxic processes, a possibly major difference in MEHP-formation capacity could be also considered on extrapolation from rodents to humans.