Effects of developmental exposure to perfluorooctanoic acid (PFOA) on long bone morphology and bone cell differentiation.

Perfluorooctanoic acid (PFOA) is a ubiquitous and persistent environmental chemical, which has been used extensively due to its stability and surface tension-lowering properties. Toxicological effects include induction of neonatal mortality and reproductive toxicity. In this study, pregnant C57BL/6 mice were exposed orally to 0.3mg PFOA/kg/day throughout pregnancy, and female offspring were studied at the age of 13 or 17months. Morphometrical and biomechanical properties of femurs and tibias were analyzed with micro-computed tomography and 3-point bending, and bone PFOA concentrations were determined by mass spectrometry. The effects of PFOA on bone cell differentiation were studied in osteoclasts from C57BL/6 mice and in the MC3T3 pre-osteoblast cell line. PFOA exposed mice showed increased femoral periosteal area as well as decreased mineral density of tibias. Biomechanical properties of these bones were not affected. Bone PFOA concentrations were clearly elevated even at the age of 17months. In osteoblasts, low concentrations of PFOA increased osteocalcin (OCN) expression and calcium secretion, but at PFOA concentrations of 100µM and above osteocalcin (OCN) expression and calcium secretion were decreased. The number of osteoclasts was increased at all PFOA concentrations tested and resorption activity dose-dependently increased from 0.1-1.0µM, but decreased at higher concentrations. The results show that PFOA accumulates in bone and is present in bones until the old age. PFOA has the potential to influence bone turnover over a long period of time. Therefore bone is a target tissue for PFOA, and altered bone geometry and mineral density seem to persist throughout the life of the animal.

Programming of metabolic effects in C57BL/6JxFVB mice by in utero and lactational exposure to perfluorooctanoic acid.

Perfluorooctanoic acid (PFOA) is known to cause developmental toxicity and is a suggested endocrine disrupting compound (EDC). Early life exposure to EDCs has been implicated in programming of the developing organism for chronic diseases later in life. Here we study perinatal metabolic programming by PFOA using an experimental design relevant for human exposure. C57BL/6JxFVB hybrid mice were exposed during gestation and lactation via maternal feed to seven low doses of PFOA at and below the NOAEL used for current risk assessment (3-3000 µg/kg body weight/day). After weaning, offspring were followed for 23-25 weeks without further exposure. Offspring showed a dose-dependent decrease in body weight from postnatal day 4 to adulthood. Growth under high fat diet in the last 4-6 weeks of follow-up was increased in male and decreased in female offspring. Both sexes showed increased liver weights, hepatic foci of cellular alterations and nuclear dysmorphology. In females, reductions in perigonadal and perirenal fat pad weights, serum triglycerides and cholesterol were also observed. Endocrine parameters, such as glucose tolerance, serum insulin and leptin, were not affected. In conclusion, our study with perinatal exposure to PFOA in mice produced metabolic effects in adult offspring. This is most likely due to disrupted programming of metabolic homeostasis, but the assayed endpoints did not provide a mechanistic explanation. The BMDL of the programming effects in our study is below the current point of departure used for calculation of the tolerable daily intake.

Dose-dependent toxicological effects in rats following a 90-day dietary exposure to PCB-156 include retinoid disruption.

The toxicity of PCB-156 (2,3,3',4,4',5-hexachlorobiphenyl) was investigated in rats following subchronic dietary exposure. Groups of 10 male and female Sprague-Dawley rats were administered PCB-156 in the diet at 0, 0.01, 0.1, 1 or 10 ppm for 90 days. Dose-dependent increases were detected for the liver, lung and kidney weights, as well as for the liver EROD, PROD and UDPGT enzyme activities and liver uroporphyrin concentration. Dose-dependent decreases were observed in final body weight, body weight gain, and thymus weight. Apolar retinoid concentrations were decreased in the liver and lungs and increased in the kidneys. Histopathological examination of the liver, thyroid, and thymus showed mild to moderate dose-related changes. A LOAEL of 0.01 ppm was established, based on reduced apolar liver retinoid concentration. Benchmark dose-modelling corroborated the sensitivity of liver retinoid endpoints. The lower confidence limits (BMDL) for a 5% decrease in apolar liver retinoid concentrations were 0.0009 and 0.0007 ppm, respectively, in males and females, corresponding to a daily dose of 0.06 µg PCB-156 per kg body weight. Organizing dose-response data for the individual hepatic endpoints along the PCB-156 dosing scale revealed a sequence of events compatible with a causal link between depletion of apolar retinoids and the other liver biochemistry and pathology findings. Taken together, data suggest that the retinoid endpoints should be further evaluated for a causal relationship to PCB-induced liver toxicity and that retinoid system endpoints are identified and characterized to support health risk assessment in the emerging research fields of endocrine disruption and mixture toxicology.

AZD9668: pharmacological characterization of a novel oral inhibitor of neutrophil elastase.

N-{[5-(methanesulfonyl)pyridin-2-yl]methyl}-6-methyl-5-(1-methyl-1H-pyrazol-5-yl)-2-oxo-1-[3-(trifluoromethyl)phenyl]-1,2-dihydropyridine-3-carboxamide (AZD9668) is a novel, oral inhibitor of neutrophil elastase (NE), an enzyme implicated in the signs, symptoms, and disease progression in NE-driven respiratory diseases such as bronchiectasis and chronic obstructive pulmonary disease via its role in the inflammatory process, mucus overproduction, and lung tissue damage. In vitro and in vivo experiments were done to evaluate the binding kinetics, potency, and selectivity of AZD9668, its effects in whole-blood and cell-based assays, and its efficacy in models of lung inflammation and damage. In contrast to earlier NE inhibitors, the interaction between AZD9668 and NE was rapidly reversible. AZD9668 was also highly selective for NE over other neutrophil-derived serine proteases. In cell-based assays, AZD9668 inhibited plasma NE activity in zymosan-stimulated whole blood. In isolated human polymorphonuclear cells, AZD9668 inhibited NE activity on the surface of stimulated cells and in the supernatant of primed, stimulated cells. AZD9668 showed good crossover potency to NE from other species. Oral administration of AZD9668 to mice or rats prevented human NE-induced lung injury, measured by lung hemorrhage, and an increase in matrix protein degradation products in bronchoalveolar lavage (BAL) fluid. In an acute smoke model, AZD9668 reduced the inflammatory response to cigarette smoke as indicated by a reduction in BAL neutrophils and interleukin-1ß. Finally, AZD9668 prevented airspace enlargement and small airway wall remodeling in guinea pigs in response to chronic tobacco smoke exposure whether dosed therapeutically or prophylactically. In summary, AZD9668 has the potential to reduce lung inflammation and the associated structural and functional changes in human diseases.

2,3,7,8-Tetrachlorodibenzo-p-dioxin kills immature thymocytes by Ca2+-mediated endonuclease activation.

Suspensions of thymocytes from young rats were incubated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), which resulted in a sustained increase in cytosolic free Ca2+ concentration followed by DNA fragmentation and loss of cell viability. Both the Ca2+ increase and DNA fragmentation were prevented in cells treated with the inhibitor of protein synthesis, cycloheximide, and DNA fragmentation and cell killing were not detected when cells were incubated in a "Ca2+-free" medium or pretreated with high concentrations of the calcium probe, quin-2 tetraacetoxymethyl ester. These results indicate that TCDD can kill immature thymocytes by initiating a suicide process similar to that previously described for glucocorticoid hormones.

Absence of capsule reveals glycan-mediated binding and recognition of salivary mucin MUC7 by Streptococcus pneumoniae.

Salivary proteins modulate bacterial colonization in the oral cavity and interact with systemic pathogens that pass through the oropharynx. An interesting example is the opportunistic respiratory pathogen Streptococcus pneumoniae that normally resides in the nasopharynx, but belongs to the greater Mitis group of streptococci, most of which colonize the oral cavity. Streptococcus pneumoniae also expresses a serine-rich repeat (SRR) adhesin, PsrP, which is a homologue to oral Mitis group SRR adhesins, such as Hsa of Streptococcus gordonii and SrpA of Streptococcus sanguinis. As the latter bind to salivary glycoproteins through recognition of terminal sialic acids, we wanted to determine whether S. pneumoniae also binds to salivary proteins through possibly the same mechanism. We found that only a capsule-free mutant of S. pneumoniae TIGR4 binds to salivary proteins, most prominently to mucin MUC7, but that this binding was not mediated through PsrP or recognition of sialic acid. We also found, however, that PsrP is involved in agglutination of human red blood cells (RBCs). After removal of PsrP, an additional previously masked lectin-like adhesin activity mediating agglutination of sialidase-treated RBCs becomes revealed. Using a custom-spotted glycoprotein and neoglycoprotein dot blot array, we identify candidate glycan motifs recognized by PsrP and by the putative S. pneumoniae adhesin that could perhaps be responsible for pneumococcal binding to salivary MUC7 and glycoproteins on RBCs.

Subclinical hypervitaminosis A causes fragile bones in rats.

Excessive intake of vitamin A has been associated with an increased risk of hip fracture in humans. This finding has raised the question of whether long-term intake of relatively moderate doses ("subclinical" hypervitaminosis A) contributes to fracture risk. Although it has been known for more than half a century that toxic doses of vitamin A lead to spontaneous fractures in rats, the lowest intake that induces adverse effects is not known, and the result of exposure to excessive doses that do not cause general toxicity has been rarely investigated. In this study, mature female rats were fed a standard diet with 12 IU vitamin A/g pellet (control, C), or standard diet supplemented with either 120 IU ("10 x C") or 600 IU ("50 x C") vitamin A/g pellet for 12 weeks. Fifteen animals were included in each group. The supplemented diets correspond to a vitamin A intake of approximately 1800 IU/day and 9000 IU/day, respectively. The latter dose is about one third of that previously reported to cause skeletal lesions. At the end of the study, serum retinyl esters were elevated 4- (p < 0.01) and 20-fold (p < 0.001) and the total amount of liver retinoid had increased 3- (p < 0.001) and 7-fold (p < 0.001) in the 10 x C and 50 x C group, respectively. The animals showed no clinical signs of general toxicity, and there were no significant bone changes in the 10 x C group. However, in the 50 x C group, a characteristic thinning of the cortex (cortical area -6.5% [p < 0.001]) and reduction of the diameter of the long bones were evident (bone cross-sectional area -7.2% [p < 0.01] at the midshaft and -11.0% [p < 0.01] at the metaphysis), as measured by peripheral quantitative computed tomography. In agreement with these data and a decreased polar strength strain index (-14.0%, p < 0.01), the three-point bending breaking force of the femur was reduced by 10.3% (p < 0.01) in the 50 x C group. These data indicate that the negative skeletal effects appear at a subchronic vitamin A intake of somewhere between 10 and 50 times the standard diet. This level is considerably lower than previously reported. Our results suggest that long-term ingestion of modest excesses of vitamin A may contribute to fracture risk.

Clinical outcome in four children with metachromatic leukodystrophy treated by bone marrow transplantation.

Four children with metachromatic leukodystrophy (MLD) underwent allogeneic bone marrow transplantation between 1988 and 1993. No effect on the natural course of the disease was observed in two children with late infantile and juvenile MLD. They had moderate neurological symptoms at the time of BMT and were followed for 7 and 6 years, respectively. The third child with the juvenile form of MLD was mildly to moderately affected when transplanted. She had lost some gross motor functions as well as speech and mental abilities at follow-up 3 years later. The fourth case, diagnosed biochemically and presymptomatically as late infantile MLD, had a subtle gait disturbance when grafted at 18 months of age. Demyelination, not observed before BMT, was visualized 1 year later on MRI. This boy's condition has continued to deteriorate 2 years after transplantation. We have adopted recent recommendations that BMT should be considered only in presymptomatic children with late infantile MLD or early in the course of juvenile MLD. In such children, still longer follow-up periods are necessary to evaluate the benefit of BMT.

Hepatic vitamin a depletion is a sensitive marker of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure in four rodent species.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD)-treated animals show altered retinoid homeostasis and exhibit signs of toxicity similar to those of vitamin A-deficient animals. In this study we established dose-response curves for sublethal oral doses of TCDD and hepatic vitamin A gain in four rodent species. This was done to evaluate any potential correlation between decreased hepatic vitamin A gain and other TCDD-induced effects, particularly depressed body weight gain and hepatic CYP1A induction. Young Hartley guinea pigs, Sprague-Dawley rats, C57BL/6 mice, and Golden Syrian hamsters were given single oral doses of TCDD at up to 2.5, 100, 1000, and 1000 microg/kg bw, respectively, and killed 28 days after treatment. Hepatic vitamin A gain was decreased 25% compared to controls at estimated doses of 0.1, 0.9, 1.1 and 3.6 microg/kg bw in guinea pigs, hamsters, rats, and mice, respectively. CYP1A induction and hepatic vitamin A gain were affected at similar dose levels and showed similar, but inverse dose-response curves in each of the four species, consistent with the hypothesis that altered vitamin A homeostasis is Ah-receptor mediated. In addition, there was an apparent correlation between the dose-response curves for decreased hepatic vitamin A gain and decreased body weight gain in all species. Taken together with the known importance of vitamin A in body weight regulation, this result was consistent with a contributing role for altered retinoid homeostasis in the wasting syndrome induced by TCDD.

Mobilization of vitamin A stores in rats after administration of 2,3, 7,8-tetrachlorodibenzo-p-dioxin: a kinetic analysis.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a highly toxic environmental contaminant that prevents the normal accumulation of vitamin A in liver and causes increased excretion of vitamin A. To determine what alterations in vitamin A metabolism occur first in response to TCDD treatment, we administered TCDD (7.0 microg/kg b.w. ) orally to rats that had received a nonperturbing (tracer) iv dose of [(3)H]vitamin A-labeled plasma (n = 3) or lymph (n = 3) 21 days earlier. Within a few days after TCDD administration, fraction of the injected radiolabel in plasma, which had been in a terminal slope when plotted on a semilog scale, increased and remained elevated until the experiment was terminated (day 42). At that time, liver vitamin A levels were 65% lower in TCDD-perturbed rats than in controls. Using model-based compartmental analysis and compartmental models developed previously for control rats (S. K. Kelley et al., 1998, Toxicol. Sci, 44:1-13), we determined the minimal changes needed to account for the perturbation in plasma [(3)H] tracer responses after TCDD administration. We determined that the effects of TCDD could be explained by adjusting the value of one fractional transfer coefficient corresponding to the mobilization of vitamin A from large, slowly turning-over pools. We speculate that this change corresponds to an increased fractional rate of retinyl ester hydrolysis, and that it precedes the TCDD-associated increased irreversible utilization and excretion of vitamin A.

Use of model-based compartmental analysis to study effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin on vitamin A kinetics in rats.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a highly toxic, widespread environmental contaminant that has dramatic adverse effects on the metabolism of vitamin A. We used model-based compartmental analysis to investigate sites and quantitative impacts of TCDD on vitamin A kinetics in rats given on oral loading dose of TCDD in oil (3.5 micrograms/kg) followed by weekly maintenance doses (0.7 microgram/kg) or oil only. [3H]Retinol in its plasma transport complex (experiment 1) of lymph containing chylomicrons labeled mainly with [3H]retinyl esters (experiment 2) were administered i.v., and tracer kinetics in plasma, liver, carcass, urine, and feces were measured for up to 42 days. TCDD treatment caused significant reductions in liver vitamin A levels and significant changes in tracer kinetics and tracer excretion. A four-compartment model was used to fit tracer data for experiment 1; for experiment 2, compartments were added to describe the metabolism of newly absorbed vitamin A. The compartmental models predict that TCDD caused a slight delay in plasma clearance (via an increased recycling to plasma), and in liver processing, of chylomicron-derived vitamin A. Models for both experiments predict that TCDD exposure did not affect the fractional uptake of plasma retinol from the rapidly turning-over extravascular pool, but it doubled the fractional transfer of recycled retinol from slowly turning-over pools of vitamin A to plasma. The residence time for vitamin A was reduced by 70% in TCDD-treated rats, transfer into urine and feces was tripled, and vitamin A utilization rates were significantly increased. Since our results do not indicate that retinol esterification is inhibited, we hypothesize that some of the significant effects of TCDD on vitamin A metabolism result from increased catabolism and mobilization of vitamin A from slowly turning-over pools (especially the liver).

Effect of 2,3,7,8-tetrachlorodibenzoy-p-dioxin on the hepatic 7-ethoxyresorufin O-deethylase activity in four rodent species.

Temporal and dose-related effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on hepatic 7-ethoxyresorufin O-deethylase (EROD) activity were investigated in young male Hartley guinea pigs, Sprague-Dawley rats, C57Bl/6 mice, DBA/2 mice and Golden Syrian hamsters. Animals were terminated 1, 7, 14, 28, 56 and 112 days after the administration of a single i.p. dose of TCDD. The maximal induction of EROD activity, at doses producing a similar toxic and limited lethal effect in all species/strains, was 42-, 18-, 7- and 3-fold in rats, DBA/2 mice, C57Bl/6 mice and guinea pigs, respectively. No treatment-related induction of EROD activity was observed in hamsters. Generally, maximal induction occurred 1-4 weeks after injection in all species. The guinea pig alone maintained the same magnitude of induction of EROD activity throughout the study. Observed toxic effects, i.e., lethality, loss of body weight gain, liver enlargement and thymic atrophy, did not correlate with the TCDD-induced hepatic EROD activity. The obtained results suggest that the fold induction of cytochrome P450 1A1 activity is not a critical event for the expression of the lethal effect of TCDD in rodents.

Change of bone tissue composition and impaired bone strength in rats exposed to 3,3',4,4',5-pentachlorobiphenyl (PCB126).

The aim of this study was to compare effects of estrogen depletion (ovariectomy) and exposure to 3,3',4,4',5-pentachlorobiphenyl (PCB126) on bone strength and bone tissue composition in the rat. Half of the rats were ovariectomized (n=20) and the remainder were sham-operated. Ten of the ovariectomized rats and ten of the sham operated were exposed to PCB126 (ip injections) for 3 months (total dose, 384 microgram/kg bodyweight), while those remaining received the vehicle. The humerus and femur were used for analysis of torsional strength and biochemical studies, respectively. Both sham-operated and ovariectomized animals showed a significantly shorter bone length, lower water content and a decreased torsional stiffness when exposed to PCB126. Sham-operated rats exposed to PCB126 had lower maximum torque when compared with sham operated controls. The PCB126-exposed rats also exhibited a significantly lower collagen concentration, but showed a higher pyridinoline concentration of cortical bone. PCB126 exposure decreased the hepatic level of vitamin A but increased vitamin A levels in serum and kidneys. Ovariectomy per se increased bone length and organic content and decreased the inorganic content significantly, but did not affect any of the tested biomechanical parameters. In conclusion, this study showed that the common environmental pollutant PCB126 impaired bone strength and altered bone composition. It is hypothesized that these effects might partly be explained by PCB-induced retinoid disturbances.

Marked alterations in retinoid homeostasis of Sprague-Dawley rats induced by a single i.p. dose of 10 micrograms/kg of 2,3,7,8-tetrachlorodibenzo-p-dioxin.

Interference of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in retinoid homeostasis was investigated in Sprague-Dawley rats with a low (dietary induced) retinoid status, that were fed a [3H]retinol-containing diet (37 MBq, 10,000 IU/kg diet) for 21 days to facilitate determination of retinoid concentrations in various tissues. The rats were exposed to a single i.p. dose of 10 micrograms TCDD/kg body weight in corn oil, or to corn oil at day 7 of [3H]retinol supplementation. TCDD induced significant reductions in retinol and retinyl ester concentrations and [3H] retinol-derived radioactivity in the liver, the lung, the intestine and the adrenals to 3-5%, 40-45%, 37%, and 56% of control values, respectively, at 14 days after exposure. In contrast, the retinoid concentrations and the amount of [3H]retinol-derived radioactivity in the kidney and serum of TCDD-treated rats was increased to 440% and 140% of corn oil-treated controls, respectively, at the termination time of the experiment. Analysis of the amount of serum retinol binding protein (RBP) by gel-permeation chromatography revealed an 150% increase in the free fraction of retinol-RBP, i.e., uncoupled to transthyretin (TTR), in serum of TCDD-treated rats. In addition, urinary excretion of [3H]retinol-derived radioactivity was significantly enhanced (to 140% of controls) by TCDD. These data indicate that TCDD induces an increased mobilization of retinoids from hepatic and extrahepatic storage sites into serum accompanied by an enhanced elimination via the kidney into the urine of rats.

Constitutive and TCDD-induced expression of Ah receptor-responsive genes in the pituitary.

The 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related substances cause a wide variety of pathological alterations, with the most severe being progressive anorexia and body weight loss. These features suggest a possible involvement of the nervous system and endocrine organs, including the pituitary gland. TCDD-related toxicity is considered mainly to be mediated by the aryl hydrocarbon receptor (AHR) protein, which binds TCDD, and heterodimerizes with its partner protein, the aryl hydrocarbon receptor nuclear translocator (ARNT), and binds to xenobiotica responsive elements (XREs) in the promoter regions of biotransformation genes as well as genes involved in growth, differentiation and cellular homeostasis. In the present study, we have investigated the expression of AHR responsive genes in the pituitary of untreated and TCDD treated 129/SV/C57BL/6 mice in vivo and in pituitary cells in vitro. After TCDD or beta-naphthoflavone (beta NF) treatment, the relative levels of cytochrome P4501A1 (CYP1A1) mRNA and protein were dramatically increased in pituitary cells. The AHR repressor (AHRR) mRNA level was induced 7-13-fold by TCDD and beta NF. Furthermore, the expression of the adrenocorticotrophic hormone (ACTH) precursor, the proopiomelanocortin (POMC) gene, was investigated. A three-fold increase in POMC mRNA was observed in the pituitary of TCDD treated mice. POMC mRNA level was also increased in the pituitary cell line AtT-20 after TCDD treatment. The proteins encoded by POMC translational products, ACTH and beta-endorphin, were found with immunocytochemistry staining to be increased in AtT-20 cells after TCDD exposure. The presence of several XRE sequences in the promoter region and in the first intron of the human POMC gene suggest that the up-regulation of POMC expression in the pituitary may play a role in the endocrine alterations induced by TCDD. All together, the results point to the pituitary gland being a direct target for TCDD.

Synthesis and Localization of Pancreatic Secretory Proteins in Pancreatic Acinar-like Metaplasia in the Distal Part of the Oesophagus.

BACKGROUND: Pancreatic acinar-like metaplasia has previously been described in the gastric mucosa and in the distal part of the oesophagus. The resemblance to pancreatic acinar cells prompted us to study the possible occurrence of secretory pancreatic proteins in these cells. METHODS: Seven specimens obtained from the distal oesophagus at gastroscopy where routine microscopy showed pancreatic acinar-like metaplasia were selected for this study. Sections were subjected to immunohistochemical detection of trypsinogen, pancreatic elastase, procarboxypeptidase B and pancreatic secretory trypsin inhibitor using specific antisera. An alkaline-phosphatase-conjugated oligodeoxynucleotide probe, complementary to the transcript for trypsinogen 2 (anionic) was used for in situ hybridization. RESULTS: Cells with pancreatic acinar-like metaplasia were immunoreactive to all pancreatic secretory proteins studied. In situ hybridization showed the presence of trypsinogen 2 mRNA in pancreatic acinar-like metaplasia. The pancreatic proteins were not seen in other cells in the distal oesophagus. CONCLUSION: Pancreatic acinar- like metaplasia is common in the distal oesophagus and pancreatic secretory proteins, including trypsininogen 2, are produced in the oesophageal metaplastic acinar cells. The biological significance of this finding has yet not been thoroughly studied.

Effects of TCDD on vitamin A status and liver microsomal enzyme activities in a TCDD-susceptible and a TCDD-resistant rat strain.

To investigate the relationship between vitamin A status and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) lethality, the influence of TCDD on tissue and serum vitamin A levels was determined in the most TCDD-susceptible (Long-Evans) and the most TCDD-resistant (Han/Wistar) rat strains. The TCDD LD50 values of these two strains differ by a factor of more than 300. Groups of three rats per strain were used in a dose-response study (given single ip doses of 0, 4, 40, 400, 800 or 1600 micrograms TCDD/kg body weight and killed on day 11) and in a time-course experiment (given single ip doses of 0, 4 and, in the case of Han/Wistar rats only, 1600 micrograms TCDD/kg body weight, and killed on days 4, 11, 23, 50 and 76). The strains showed similar response over the 76-day study with respect to vitamin A levels in the liver, kidneys, testicles and serum after exposure to a sublethal dose of TCDD (4 micrograms/kg body weight). In contrast, TCDD doses lethal to the Long-Evans strain only (40-1600 micrograms/kg, day 11) markedly increased kidney and serum vitamin A levels in Han/Wistar rats, while they were practically without effect in Long-Evans rats. Hepatic cytochrome P-450 concentration, and the activities of 7-ethoxyresorufin O-deethylase, ethylmorphine N-demethylase, and uridine diphosphate glucuronosyltransferase (towards p-nitrophenol) were affected by the TCDD doses in much the same manner in both strains. These findings show that the correlations between TCDD lethality and changes in vitamin A status found among species of laboratory animals do not hold for Long-Evans and Han/Wistar strains of rat.

Effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin on the lymphatic absorption of a single oral dose of [3H]retinol and on the intestinal retinol esterification in the rat.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) alters the turnover of vitamin A in the body and inhibits the normal hepatic accumulation of dietary vitamin A. Vitamin A is absorbed in the small intestine, where it is incorporated into chylomicrons as retinyl esters for release into the lymph and further distributed via blood to the liver for storage. The aim of the present study was to investigate if the decreased hepatic vitamin A levels in TCDD-exposed rats could be due to impaired intestinal absorption of vitamin A via lymph. Male Sprague-Dawley rats were given a single oral dose of TCDD (10 microg/kg). Five days after administration, the main intestinal lymph duct of the rats was cannulated. After a 24-h recovery from surgery, the rats were each given a single dose of [3H]retinol in corn oil via gavage and the lymph was collected for 24 h. The cumulative radiolabel recovered in the intestinal lymph was significantly lower in TCDD-treated than in control rats during the first 6 h of absorption. However, no significant differences in radiolabel recovered in lymph were seen when looking at the entire 24-h collection period. In the intestinal mucosa, retinol esterification catalyzed by the enzyme lecithin:retinol acyl transferase (LRAT) or acyl coenzyme A (CoA):retinol transferase (ARAT) was not statistically different between the groups. However, mucosal retinyl palmitate levels were significantly increased in TCDD-treated rats. In conclusion, a small and transient reduction was found of the uptake of vitamin A into the lymph of TCDD-treated rats. It is obvious that this finding cannot explain the TCDD-induced decrease in hepatic vitamin A levels in the rat. Rather, a combination of inhibited retinol esterification in hepatic stellate cells, increased release of endogenous vitamin A, and increased hepatic catabolism of retinoids could explain the effect of TCDD on liver retinoid levels.

Effect of 2,3,7,8-tetrachlorodibenzo-P-dioxin (TCDD) on the hepatic stellate cell population in the rat.

TCDD inhibits the normal accumulation of vitamin A in the hepatic stellate cells, which constitute the main storage site for vitamin A. In this study we investigated if the reduced capacity of stellate cells to store vitamin A could be due to cell transformation or cytotoxicity. Livers from rats exposed to TCDD were immunohistochemically stained for markers of normal and transformed stellate cells. The results show that the TCDD-induced inhibition of hepatic vitamin A accumulation is neither due to a reduction in the number of stellate cells nor to transformation of the cells.

Effect on tissue vitamin A levels in the rat following subchronic exposure to four individual PCB congeners (IUPAC 77, 118, 126, and 153).

The present study was carried out to investigate the effect on tissue vitamin A levels in rats exposed to 3,3',4,4'-tetraCB (CB-77), 2,3',4,4',5-pentaCB (CB-118), 3,3',4,4',5-pentaCB (CB-126), and 2,2',4,4',5,5'-hexaCB (CB-153). The obtained results show that hepatic vitamin A levels are reduced both in male and female rats following dietary exposure to individual PCB congeners for 13 weeks. However, there are pronounced potency differences between congeners. Compared to TCDD, the hepatic vitamin A reducing potencies of CB-126, CB-77 and CB-153, are 0.05, 0.0001 and 0.00001, respectively, in male rats. Compared to male rats, female rats are equally sensitive to hepatic vitamin A reduction both by TCDD and dioxinlike CBs. Effects on renal and pulmonary vitamin A levels vary between CBs and between sexes.