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Biomedical subjects

Jouko Tuomisto

Publications and source records attributed to Jouko Tuomisto.

At least 19 recordsLinked to original sources
PubMed2006

The 2005 World Health Organization reevaluation of human and Mammalian toxic equivalency factors for dioxins and dioxin-like compounds.

In June 2005, a World Health Organization (WHO)-International Programme on Chemical Safety expert meeting was held in Geneva during which the toxic equivalency factors (TEFs) for dioxin-like compounds, including some polychlorinated biphenyls (PCBs), were reevaluated. For this reevaluation process, the refined TEF database recently published by Haws et al. (2006, Toxicol. Sci. 89, 4-30) was used as a starting point. Decisions about a TEF value were made based on a combination of unweighted relative effect potency (REP) distributions from this database, expert judgment, and point estimates. Previous TEFs were assigned in increments of 0.01, 0.05, 0.1, etc., but for this reevaluation, it was decided to use half order of magnitude increments on a logarithmic scale of 0.03, 0.1, 0.3, etc. Changes were decided by the expert panel for 2,3,4,7,8-pentachlorodibenzofuran (PeCDF) (TEF = 0.3), 1,2,3,7,8-pentachlorodibenzofuran (PeCDF) (TEF = 0.03), octachlorodibenzo-p-dioxin and octachlorodibenzofuran (TEFs = 0.0003), 3,4,4',5-tetrachlorbiphenyl (PCB 81) (TEF = 0.0003), 3,3',4,4',5,5'-hexachlorobiphenyl (PCB 169) (TEF = 0.03), and a single TEF value (0.00003) for all relevant mono-ortho-substituted PCBs. Additivity, an important prerequisite of the TEF concept was again confirmed by results from recent in vivo mixture studies. Some experimental evidence shows that non-dioxin-like aryl hydrocarbon receptor agonists/antagonists are able to impact the overall toxic potency of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds, and this needs to be investigated further. Certain individual and groups of compounds were identified for possible future inclusion in the TEF concept, including 3,4,4'-TCB (PCB 37), polybrominated dibenzo-p-dioxins and dibenzofurans, mixed polyhalogenated dibenzo-p-dioxins and dibenzofurans, polyhalogenated naphthalenes, and polybrominated biphenyls. Concern was expressed about direct application of the TEF/total toxic equivalency (TEQ) approach to abiotic matrices, such as soil, sediment, etc., for direct application in human risk assessment. This is problematic as the present TEF scheme and TEQ methodology are primarily intended for estimating exposure and risks via oral ingestion (e.g., by dietary intake). A number of future approaches to determine alternative or additional TEFs were also identified. These included the use of a probabilistic methodology to determine TEFs that better describe the associated levels of uncertainty and "systemic" TEFs for blood and adipose tissue and TEQ for body burden.

Animals↗
PubMed2006

Assessment by c-Fos immunostaining of changes in brain neural activity induced by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and leptin in rats.

The environmental toxicant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) causes multiple effects in laboratory animals. One of these is a wasting syndrome (a dramatic loss of body weight over 2-5 weeks) whose mechanism is still largely unknown. We exploited the over 1000 times difference in TCDD sensitivity between Long-Evans (Turku/AB); (L-E) and Han/Wistar (Kuopio); (H/W) rats to reveal brain areas that might be activated by a single dose of TCDD (50 microg/kg) given 24 hr previously. Leptin (1.3 mg/kg intraperitoneally 2 hr before tissue harvest) was used as a reference compound, as its neural pathway for decreasing food intake in the control of energy homeostasis is fairly well known. Serial sections of the brains were immunostained with an antibody for the activity marker c-Fos, and selected areas -- primarily in the hypothalamus -- were analysed with a computer-assisted microscope. Given alone, TCDD did not elicit any major alterations in c-Fos protein levels in the hypothalamic nuclei at the early time-point studied (24 hr after administration), neither in pooled data nor in individual strains. The control substance leptin proved that the method is valid as it increased the number of c-Fos-immunopositive cells in the hypothalamic ventromedial and arcuate nuclei. Although the present findings are not suggestive of a primary role for the hypothalamus in the wasting syndrome, a time-course study covering also the feeding-active dark hours is warranted for their verification.

Animals↗
PubMed2005

Aryl hydrocarbon receptor regulates distinct dioxin-dependent and dioxin-independent gene batteries.

Conventional biochemical and molecular techniques identified previously several genes whose expression is regulated by the aryl hydrocarbon receptor (AHR). We sought to map the complete spectrum of AHR-dependent genes in male adult liver using expression arrays to contrast mRNA profiles in Ahr-null mice (Ahr(-/-)) with those in mice with wild-type AHR (Ahr(+)(/)(+)). Transcript profiles were determined both in untreated mice and in mice treated 19 h earlier with 1000 microg/kg 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Expression of 456 ProbeSets was significantly altered by TCDD in an AHR-dependent manner, including members of the classic AHRE-I gene battery, such as Cyp1a1, Cyp1a2, Cyp1b1, and Nqo1. In the absence of exogenous ligand, AHR status alone affected expression of 392 ProbeSets, suggesting that the AHR has multiple functions in normal physiology. In Ahr(-/-) mice, only 32 ProbeSets exhibited responses to TCDD, indicating that the AHR is required for virtually all transcriptional responses to dioxin exposure in liver. The flavin-containing monooxygenases, Fmo2 and Fmo3, considered previously to be uninducible, were highly induced by TCDD in an AHR-dependent manner. The estrogen receptor alpha as well as two estrogen-receptor-related genes (alpha and gamma) exhibit AHR-dependent expression, thereby extending cross-talk opportunities between the intensively studied AHR and estrogen receptor pathways. p53 binding sites are over-represented in genes down-regulated by TCDD, suggesting that TCDD inhibits p53 transcriptional activity. Overall, our study identifies a wide range of genes that depend on the AHR, either for constitutive expression or for response to TCDD.

Animals↗
PubMed2005

Toxicological implications of polymorphisms in receptors for xenobiotic chemicals: the case of the aryl hydrocarbon receptor.

Mechanistic toxicology has predominantly been focused on adverse effects that are caused by reactive metabolites or by reactive oxygen species. However, many important xenobiotics exert their toxicity, not by generating reactive products, but rather by altering expression of specific genes. In particular, some environmental contaminants target nuclear receptors that function as regulators of transcription. For example, binding of xenobiotic chemicals to steroid receptors is a principle mechanism of endocrine disruption. The aryl hydrocarbon receptor (AHR) mediates toxicity of dioxin-like compounds. In mice, a polymorphism in the AHR ligand-binding domain reduces binding affinity by about 10-fold in the DBA/2 strain compared with the C57BL/6 strain; consequently, dose-response curves for numerous biochemical and toxic effects are shifted about one log to the right in DBA/2 mice. In the Han/Wistar (Kuopio) (H/W) rat strain, a polymorphism causes a deletion of 38 or 43 amino acids from the AHR transactivation domain. This deletion is associated with a greater than 1000-fold resistance to lethality from 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Genes in the conventional AH gene battery (e.g. CYP1A1, CYP1A2, CYP1B1, ALDH3A1, NQO1 and UGT1A1) remain responsive to TCDD in H/W rats despite the large deletion. However, the deletion may selectively alter the receptor's ability to dysregulate specific genes that are key to dioxin toxicity. We are identifying these genes using an expression array approach in dioxin-sensitive vs. dioxin-resistant rat strains and lines. Polymorphisms exist in the human AH receptor, but thus far they have not been shown to have any substantial effect on human responses to AHR-ligands.

Animals↗
PubMed2005

Does mechanistic understanding help in risk assessment--the example of dioxins.

Risk assessment is based on scientific information, in part on "regulatory toxicology", i.e., studies following protocols accepted by national or international authorities, and in part on fundamental scientific information clarifying the mechanisms of toxicity and giving a better possibility to evaluate also the findings of routine safety studies. Both are needed, and increased biological understanding increases the possibilities of handling the data in a rational way. In addition, risk assessment seems to include some built-in assumptions that are not necessarily scientific at all. This review attempts to highlight the distortions that are possible if we follow certain rules in a blinkered way not taking into consideration all aspects of the risk. The highly controversial risk assessment of dioxins is used to exemplify the difficulties of excessively straightforward risk analysis process.

Animals↗
PubMed2005

Interference by 2,3,7,8-tetrachlorodibenzo-p-dioxin with cultured mouse submandibular gland branching morphogenesis involves reduced epidermal growth factor receptor signaling.

Toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) to mouse embryonic teeth, sharing features of early development with salivary glands in common, involves enhanced apoptosis and depends on the expression of epidermal growth factor (EGF) receptor. EGF receptor signaling, on the other hand, is essential for salivary gland branching morphogenesis. To see if TCDD impairs salivary gland morphogenesis and if the impairment is associated with EGF receptor signaling, we cultured mouse (NMRI) E13 submandibular glands with TCDD or TCDD in combination with EGF or fibronectin (FN), both previously found to enhance branching morphogenesis. Explants were examined stereo-microscopically and processed to paraffin sections. TCDD exposure impaired epithelial branching and cleft formation, resulting in enlarged buds. The glands were smaller than normal. EGF and FN alone concentration-dependently stimulated or inhibited branching morphogenesis but when co-administered with TCDD, failed to compensate for its effect. TCDD induced cytochrome P4501A1 expression in the glandular epithelium, indicating activation of the aryl hydrocarbon receptor. TCDD somewhat increased epithelial apoptosis as observed by terminal deoxynucleotidyl transferase (TdT)-mediated nick end-labeling method but the increase could not be correlated with morphological changes. The frequency of proliferating cells was not altered. Corresponding to the reduced cleft sites in TCDD-exposed explants, FN immunoreactivity in the epithelium was reduced. The results show that TCDD, comparably with EGF and FN at morphogenesis-inhibiting concentrations, impaired salivary gland branching morphogenesis in vitro. Together with the failure of EGF and FN at morphogenesis-stimulating concentrations to compensate for the effect of TCDD this implies that TCDD toxicity to developing salivary gland involves reduced EGF receptor signaling.

Animals↗
PubMed2005

Bone resorption by aryl hydrocarbon receptor-expressing osteoclasts is not disturbed by TCDD in short-term cultures.

Polychlorinated dibenzo-p-dioxins (PCDDs) are highly toxic environmental contaminants, and 2,3,7,8-tetrachlorobenzo-p-dioxin (TCDD) is the most potent dioxin. Dioxins bind specifically to the cytosolic aryl hydrocarbon receptor (AHR), which is a ligand-activated transcription factor, and a majority of toxic effects of dioxins are mediated via AHR. We have recently demonstrated that TCDD disrupts bone modeling and decreases bone mechanical strength, and that partial resistance to these effects is related to an altered transactivation domain in AHR structure. In order to better understand the effects of dioxins on bone, we studied the presence and precise localization of AHR and also the number and activity of osteoclasts after TCDD treatments. Total RNA was extracted from mixed bone cell population cultures and expression of AHR mRNA was studied using RT-PCR. Bone cells expressed a considerable amount of AHR mRNA. To see which bone cells express AHR, immunostainings were performed in primary rat bone cell cultures, pure human osteoclast cultures and histological sections from AHR knockout and wild type bones. Immunostaining revealed a strong expression of AHR both in osteoclasts and osteoblasts with an especially prominent stain in bone resorbing osteoclasts. Effects of dioxin on primary bone cells were evaluated after TCDD treatment in the pit formation assay. The activity of osteoclasts was not affected measured as the percentage of active osteoclasts and the actual area of resorbed bone. These data indicate that even though TCDD-treated bones show decreased mechanical strength and size, this is not a direct result from increased osteoclastic bone resorption.

Animals↗
PubMed2005

Altered retinoid metabolism in female Long-Evans and Han/Wistar rats following long-term 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-treatment.

This study investigated the effects of long-term low-dose 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure on retinoid, thyroid hormone, and vitamin D homeostasis in Long-Evans and Han/Wistar rats using a tumor promotion exposure protocol. Female rats (ten/group) were partially hepatectomized, initiated with nitrosodiethylamine (NDEA), and given TCDD once per week by sc injection for 20 weeks at calculated daily doses of 0, 1, 10, 100, or 1000 ng/kg bw/day. Groups of nonhepatectomized/uninitiated rats (five/group) were identically maintained. After 20 weeks, the rats were killed, and apolar retinoid levels were determined in the liver and kidneys. No consistent differences were seen between partially hepatectomized/initiated and nonhepatectomized/uninitiated animals with respect to apolar retinoid levels or hepatic TCDD concentration. Further analyses of polar and apolar retinoid levels in liver, plasma, and kidney, as well as free thyroxine (FT4) and vitamin D (25-OH-D(3)) concentrations were carried out in partially hepatectomized/inititated animals. In Long-Evans rats, TCDD exposure dose-dependently decreased hepatic retinyl ester concentrations at doses of 1-100 ng/kg bw/day. Likewise, hepatic all-trans-retinoic acid (all-trans-RA) concentration was decreased 39 and 54% at 10 and 100 ng/kg bw/day respectively, whereas 9-cis-4-oxo-13,14-dihydro-retinoic acid (9-cis-4-oxo-13,14-dihydro-RA), a recently discovered retinoic acid metabolite, was decreased approximately 60% in the liver at 1 ng/kg bw/day. TCDD dose-dependently increased plasma retinol and kidney retinol concentrations, whereas all-trans-RA concentration was also increased in the plasma and kidney at 10 and 100 ng/kg bw/day. Plasma 9-cis-4-oxo-13,14-dihydro-RA was decreased to below detection limits from doses of 1 ng/kg bw/day TCDD. A qualitatively similar pattern of retinoid disruption was observed in the Han/Wistar rat strain following TCDD exposure. FT4 was decreased to a similar extent in both strains, whereas 25-OH-D(3) was decreased only at 100 ng/kg bw/day in Long-Evans rats. Together these results show that TCDD disrupts both retinoid storage and metabolism of retinoic acid and retinoic acid metabolites in liver, kidney, and plasma from doses as low as 1 ng/kg bw/day. Furthermore, 9-cis-4-oxo-13,14-dihydro-RA was identified as a novel and sensitive indicator of TCDD exposure, in a resistant and sensitive rat strain, thereby extending the database of low-dose TCDD effects.

Animals↗
PubMed2005

Effects of in utero and lactational TCDD exposure on bone development in differentially sensitive rat lines.

2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is a notorious model compound of highly toxic environmental pollutants, polychlorinated dibenzo-p-dioxins (PCDDs). Their toxic effects are mediated via cytosolic aryl hydrocarbon receptor (AHR). We studied the effects of several dose levels of TCDD on developing rat bone after maternal exposure at different times of gestation and lactation in three differentially sensitive rat lines. Rat lines A, B, and C differ in their sensitivity to TCDD due to mutated AHR (Ahr(hw)) in line A and another TCDD-resistance allele (B(hw)) in line B. Line C rats have no resistance alleles. Offspring were analyzed for bone mineral density and geometry by peripheral quantitative computed tomography (pQCT) and for bone biomechanics by three-point bending at mid-diaphysis of tibia and femur and by axial loading at femoral neck. TCDD treatment resulted in bone defects, mainly in offspring of the most sensitive line C at a maternal dose of 1 microg/kg. They included decreased bone length, cross-sectional area of cortex, and bone mineral density. Mechanical testing revealed significantly reduced bending breaking force and stiffness of tibia, femur, and femoral neck. The effects were exposure time-dependent, and earlier exposure caused more severe defects. Gestational exposure alone was not sufficient, but lactational exposure was required to cause the bone defects. Most of the defects were recovered at the age of 1 year. The results indicate that dioxins affect developing bone by interfering with bone growth and mechanical strength and that the effects are mainly reversible. The dioxin-resistance alleles, Ahr(hw) and B(hw) increase the resistance to these defects.

Alleles↗
PubMed2005

Effect of TCDD on mRNA expression of genes encoding bHLH/PAS proteins in rat hypothalamus.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) brings about a wide variety of toxic and biochemical effects via an AH receptor (AHR)-mediated signalling pathway. Wasting syndrome and acute lethality are TCDD-induced endpoints showing a striking sensitivity difference between two rat strains, TCDD-sensitive Long-Evans (Turku/AB) (L-E) and TCDD-resistant Han/Wistar (Kuopio) (H/W). These rat strains were used to study hypothalamic effects of TCDD on expression of genes encoding AHR-regulated bHLH/PAS proteins potentially involved in molecular pathogenesis of the wasting syndrome. In addition, two well-established target genes of TCDD, CYP1A1 and CYP1A2 were also examined. Quantitative RT-PCR was used to measure mRNA levels in hypothalamus, which is a major center of food intake and body weight regulation. At both 6 and 96 h after a single dose of 50 microg/kg TCDD, significant elevations were found in mRNA levels of AHR repressor (AHRR), CYP1A1 and CYP1A2, but not those of AHR, ARNT or ARNT2. Likewise, TCDD (100 microg/kg) did not alter the expression of SIM1, implicated in the suppressive impact of TCDD on food intake, nor that of PER2, involved in regulation of circadian rhythms. Differences between H/W and L-E rats appeared in constitutive levels of AHR and ARNT and in TCDD-induced levels of CYP1A2, AHRR, AHR and ARNT, which all were about two- to four-fold lower in H/W rats. Thus, although the changes found do not account for the wasting syndrome, expression of all principal genes of the AHR-signalling pathway in rat hypothalamus make it a candidate target for TCDD.

Animals↗
PubMed2005

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and leptin on hypothalamic mRNA expression of factors participating in food intake regulation in a TCDD-sensitive and a TCDD-resistant rat strain.

An acutely toxic dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) leads to a drastically and permanently reduced feed intake and wasting by an unknown mechanism. We focused on the possible interference of TCDD with hypothalamic factors known to take part in the regulation of eating and metabolism, utilizing the over 1000-fold TCDD-sensitivity difference between Long-Evans (Turku/AB; L-E) and Han/Wistar (Kuopio) rats. The mRNA expression of 18 hypothalamic factors (including NPY, AgRP, and CART) was measured by quantitative RT-PCR at 6, 24 and 96 h after TCDD administration. The effects of TCDD were compared with those of leptin and with feed restriction employing a TCDD dose that elicited a severe reduction of feed intake in L-E rats. TCDD mainly modified expression of orexigenic factors causing an initial suppression followed by reversal to enhanced expression by 96 h. The latter was also seen in feed-restricted controls. In contrast, leptin altered both orexigenic and anorexigenic factor mRNAs in a more even manner and its effects were clustered at 6 h. The transient nature of feeding-promoting factor suppression does not strongly support a key role for this phenomenon in TCDD-induced wasting syndrome. However, the fact that TCDD mainly affected orexigenic factors and the temporal differences in response found between the rat strains warrant further research.

Animals↗
PubMed2005

Polychlorinated dibenzo-p-dioxins, dibenzofurans, and biphenyls in the general population in Finland.

We measured adipose tissue concentrations of polychlorinated dibenzo-p-dioxins, dibenzofurans (PCDD/Fs), and polychlorinated biphenyls (PCBs) in 420 general Finns living in southern Finland. The mean (median) concentrations of WHO(PCDD/F)-TEQ and WHO(PCB)-TEQ were 29.0 (24.1) and 20.7 (16.7) pg g-1 fat, respectively. The concentrations clearly correlated with age. Expressing the concentrations as a function of subject's ages revealed that the exposure of Finns has declined over the last 30 years. A downward gradient was found in the concentrations from the Baltic Sea coast to inland areas in Finland, and this was assessed to be due to consumption of the Baltic Sea fish, especially Baltic herring. Linear regression models for natural logarithm WHO(PCDD/F)-TEQ, natural logarithm WHO(PCB)-TEQ, and natural logarithm WHO(total)-TEQ, explained 70%, 69%, and 72% of the variability, respectively. Age, lactation, place of residence, and fish consumption frequencies were significant predictors in the models.

Adipose Tissue↗
PubMed2004

Dioxin-responsive AHRE-II gene battery: identification by phylogenetic footprinting.

We identified a set of genes that respond to dioxins through the recently discovered AHRE-II ("XRE-II") enhancer element. A total of 36 genes containing AHRE-II motifs conserved across human, mouse, and rat gene orthologs were identified by genome-wide transcription-factor binding-site searches and phylogenetic footprinting. Microarray experiments on liver from rats treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin revealed statistically significant changes in mRNA levels for 13 of these 36 genes after three hours and 15 genes after 19h. The set of responsive genes was functionally characterized by ontological analysis and found to be enriched in ion-channels and transporters. Our identification of 36 putatively AHRE-II-regulated genes highlights the regulatory versatility of the aryl hydrocarbon receptor (AHR) and the ability of the AHR and its dimerization partner, ARNT, to act both as a ligand-activated transcription-factor (on AHRE-I) and as a ligand-activated coactivator (on AHRE-II). Collectively, these results demonstrate that the AHRE-II induction mechanism is employed by multiple genes and provide the first categorization of the gene battery of a ligand-activated coactivator.

Animals↗
PubMed2004

Adult 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure and effects on male reproductive organs in three differentially TCDD-susceptible rat lines.

The contribution of genetic factors to adult male reproductive system toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was analyzed in three rat lines differentially resistant to TCDD acute lethality: line A, B, and C rats (selectively bred from TCDD-resistant Han/Wistar [Kuopio; H/W] and TCDD-sensitive Long-Evans [Turku/AB; L-E] rats). The resistance is linked to a mutated H/W-type aryl hydrocarbon receptor allele in line A and to an H/W-type unknown "B" allele in line B. Line C rats do not have resistance alleles. Mature male line A, B and C rats were given single oral doses up to 1000, 300, and 30 micrograms/kg TCDD, respectively. The dose-responses of TCDD effects on male reproductive organ weights, sperm numbers, and serum testosterone concentrations were analyzed 17 days after exposure. Serum testosterone concentrations were decreased by the highest doses of TCDD, and there were no major sensitivity differences among the rat lines. Correspondingly, the decrease in relative weight of ventral prostate and seminal vesicles was seen only after a dose of >/=100 micrograms/kg TCDD. Thus the effect was observed only in resistant lines A and B. The relative weights of testes and epididymides were not affected. Significant decrease in spermatogenesis was observed in each rat line, but the amount of decrease was reduced by resistance alleles. The highest TCDD dose decreased the daily sperm production by 37, 38, and 60% in line A, B, and C rats, respectively. Therefore, the resistance alleles appear to selectively modify the TCDD effects on the adult male reproductive system. The fact that the influence of resistance alleles on spermatogenesis is different from that on androgenic status indicates that the effect of TCDD on sperm numbers is not fully related to decreased serum testosterone.

Alleles↗
PubMed2004

Effects of epidermal growth factor receptor deficiency and 2,3,7,8-tetrachlorodibenzo-p-dioxin on fetal development in mice.

Dioxins are persistent environmental contaminants that cause multiple disorders in laboratory animals, including teratogenesis. In mice, the most important teratogenic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) are hydronephrosis and cleft palate. Aryl hydrocarbon receptor (AHR) mediates most of the TCDD-induced effects, but modulation of these effects by other factors such as epidermal growth factor receptor (EGFR) has been propounded. TCDD changes the expression of both EGF and its receptor EGFR, which may be one step in the pathway leading to cleft palate and hydronephrosis. In the present study, the importance of EGFR in TCDD-induced teratogenicity was evaluated. Heterozygous EGFR(+/-)-mice were mated and pregnant females exposed to 1.5-106.0 microg/kg TCDD on gestation day (GD) 10 and killed on GD 18. The fetuses were studied for cleft palate, hydronephrosis, and open eyes. There was no marked difference among the three genotypes in sensitivity to cleft palate or hydronephrosis, but in EGFR(-/-)-mice frequency of the open eye malformation decreased dose-dependently. In conclusion, EGFR signaling is not required for TCDD-induced cleft palate or hydronephrosis but TCDD appears to counteract the effect of EGFR deficiency on eye opening.

Animals↗
PubMed2004

Pattern of male reproductive system effects after in utero and lactational 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure in three differentially TCDD-sensitive rat lines.

Male reproductive effects induced by in utero and lactational exposure to TCDD were analyzed in three rat lines that are differently sensitive to TCDD. Rats from lines A, B, and C were selectively bred from TCDD-resistant Han/Wistar (Kuopio, H/W) and TCDD-sensitive Long-Evans (Turku/AB, L-E) rats and exhibited very different LD50 values for TCDD: >10,000, 830, and 40 microg/kg in males, respectively. The resistance in line A rats was linked to a mutated H/W-type aryl hydrocarbon receptor (Ahr(hw)) and in line B rats to a H/W-type unknown allele B (B(hw)). Line C rats had no resistance alleles. Influence of the resistance alleles on developmentally induced male reproductive effects of TCDD was studied by exposing pregnant females to TCDD (0.03, 0.1, 0.3, or 1 microg/kg) on gestation day (GD) 15. Male progeny were sacrificed on postnatal day (PND) 70. Next, the dams were given 1 microg/kg TCDD on GD 15 and male progeny were sacrificed on PND 14, 21, 28, 35, or 49. Serum testosterone concentration, male sex organ weights, and testicular and cauda epididymal sperm numbers were analyzed; the most sensitive end point was decreased sperm numbers. The dose of 1 microg/kg TCDD reduced daily sperm production by 9.3, 25, and 36%, and cauda epididymal sperm reserves by 18, 42, and 49% in rat lines A, B, and C when measured on PND 70, respectively. The most consistent and significant effect was decreased weight of prostate lobes. The growth of the male reproductive organs was not markedly affected by the resistance alleles Ahr(hw) and B(hw). In contrast, the effects on sperm parameters appeared to be slightly modified by the resistance alleles. Thus, the intraspecies genetic differences in C-terminal transactivation domain of AHR appear to modify the sensitivity to only certain dioxin-induced male reproductive effects.

Animals↗
PubMed2004

Postnatal development of resistance to short-term high-dose toxic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin in TCDD-resistant and -semiresistant rats.

Despite great interspecies differences in adult 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) sensitivity, the toxic potency of TCDD is similar across species in fetal mortality. Han/Wistar (Kuopio; H/W) rats are exceptionally resistant to acute toxicity of TCDD, but show sensitivity to embryotoxicity and teratogenicity. The resistance of adult H/W rats to acute TCDD toxicity is based on a point mutation in the transactivation domain of the aryl hydrocarbon receptor (AHR) and to an unknown gene "B". This study investigated the time course of postnatal development of resistance to TCDD and the significance of genotypic variation in resistance development. H/W, line A (a new line with the H/W-type mutated AHR), and line B rats (a line with normal AHR but moderately resistant because of gene "B") were exposed to a single dose of TCDD 2-56 days after birth. H/W and line A rats received 1000 microg/kg; male and female B rats received 200 and 100 microg/kg, respectively. Survival was monitored for 42 days. Interestingly, although TCDD ceased growth and weight gain in all TCDD groups, the younger dosed animals did not seem to reach the body weight of the older dosed animals even in 100 days. The survival results after 42 days showed that line A rats are fairly resistant to TCDD immediately after birth, and their full TCDD resistance develops during the first week of life. The moderate resistance of line B rats develops approximately at the time of weaning. This difference in the time course of resistance development suggests that there are basic differences in pathways mediating resistance in lines A and B rats.

Alleles↗