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Jouko Tuomisto

Publications and source records attributed to Jouko Tuomisto.

At least 19 recordsLinked to original sources

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↗

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↗

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↗

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↗

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↗

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↗

Soft-tissue sarcoma and dioxin: A case-control study.

Soft-tissue sarcoma has been proposed to be a candidate for a dioxin-induced cancer. However, previous epidemiologic studies have suffered from poor exposure data and mixed exposures. We studied the association between sarcoma risk and individually estimated dioxin exposure in a general population exposed to relatively low levels of dioxin via food. A multicenter prospective case-control study was conducted in 4 university hospitals and 12 other hospitals in southern Finland. Participants included 110 patients with soft-tissue sarcoma (cases) and 227 area- and age-matched controls. Controls were patients operated for appendicitis. Individual dioxin concentrations were analyzed from subcutaneous fat samples by gas chromatography-mass spectrometry. The average (range) dioxin concentration was 33.4 (4.4-145.5) ng/kg (toxic equivalencies in fat according to WHO). No increased risk associated with increased dioxin concentration was observed. In contrast, the highest risk of sarcoma was found at low levels of dioxin. Odds ratios for different quintiles as compared with the lowest quintile of dioxins (median, 11.5 ng/kg) varied from 0.43 (95% CI = 0.18-1.05) to 0.65 (95% CI = 0.22-1.95). The result was little affected by studied confounders and the findings were similar for different sarcoma subtypes, age groups and study areas. The results imply that dioxin does not increase the risk of soft-tissue sarcoma at the present population levels.

Age Factors↗

Primary structure and inducibility by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) of aryl hydrocarbon receptor repressor in a TCDD-sensitive and a TCDD-resistant rat strain.

The aryl hydrocarbon receptor repressor (AHRR) is a negative regulator of AH receptor (AHR), which mediates most of the toxic and biochemical effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). AHR has been shown to be the major reason for the exceptionally wide (ca. 1000-fold) sensitivity difference in acute toxicity of TCDD between two rat strains, sensitive Long-Evans (Turku/AB) (L-E) and resistant Han/Wistar (Kuopio) (H/W), but there is another, currently unknown contributing factor involved. In the present study, we examined AHRR structure and expression in these rat strains to find out whether AHRR could be this auxiliary factor. Molecular cloning of AHRR coding region showed that consistent with AHRR proteins in other species, the N-terminal end of rat AHRR is highly conserved, but PAS B and Q-rich domains are severely truncated or lacking. Identical structures were recorded in both strains. Next, the time-, dose-, and tissue-dependent expression of AHRR was determined using quantitative real-time RT-PCR. In liver, AHRR expression was very low in untreated rats, but it increased rapidly after TCDD exposure (100microg/kg). Testis exhibited the highest constitutive expression of AHRR, whereas kidney, spleen, and heart showed the highest induction of AHRR in response to TCDD treatment. Again, no marked differences were found between H/W and L-E rats, implying that AHRR is not the auxiliary contributing factor to the strain difference in TCDD sensitivity. However, simultaneous measurement of CYP1A1 mRNA reinforced the view that AHRR is an important determinant of tissue-specific responsiveness to TCDD.

Amino Acid Sequence↗

Is the precautionary principle used to cover up ignorance?

The precautionary principle is rapidly spreading in risk management in spite of vague understanding of its consequences. Some caveats are presented in this commentary, and some principles proposed for improved risk assessment/risk management procedures. Improvement is especially needed in such cases where the risks of different management options must be compared.

Administrative Personnel↗

Developmental dental aberrations after the dioxin accident in Seveso.

Children's developing teeth may be sensitive to environmental dioxins, and in animal studies developing teeth are one of the most sensitive targets of toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Twenty-five years after the dioxin accident in Seveso, Italy, 48 subjects from the contaminated areas (zones A and B) and in patches lightly contaminated (zone R) were recruited for the examination of dental and oral aberrations. Subjects were randomly invited from those exposed in their childhood and for whom frozen serum samples were available. The subjects were frequency matched with 65 subjects from the surrounding non-ABR zone for age, sex, and education. Concentrations of TCDD in previously analyzed plasma samples (zone ABR subjects only) ranged from 23 to 26,000 ng/kg in serum lipid. Ninety-three percent (25 of 27) of the subjects who had developmental enamel defects had been < 5 years of age at the time of the accident. The prevalence of defects in this age group was 42% (15 of 36) in zone ABR subjects and 26% (10 of 39) in zone non-ABR subjects, correlating with serum TCDD levels (p = 0.016). Hypodontia was seen in 12.5% (6 of 48) and 4.6% (3 of 65) of the zone ABR and non-ABR subjects, respectively, also correlating with serum TCDD level (p = 0.05). In conclusion, developmental dental aberrations were associated with childhood exposure to TCDD. In contrast, dental caries and periodontal disease, both infectious in nature, and oral pigmentation and salivary flow rate were not related to the exposure. The results support our hypothesis that dioxins can interfere with human organogenesis.

Accidents, Occupational↗

Identification of novel splice variants of ARNT and ARNT2 in the rat.

Most of the biochemical and toxic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) are mediated by the bHLH/PAS protein AH receptor (AHR). For regulation of gene activities, AHR dimerizes with another member of the bHLH/PAS protein family, AHR nuclear translocator (ARNT). A substrain of Wistar rats, Han/Wistar (Kuopio) (H/W), is about 1000-fold more resistant to the acute lethality of TCDD than other strains, exemplified by Long-Evans (Turku/AB) (L-E); the LD50 values for these two strains are >9600 and 10-20 microg/kg, respectively. Previous studies have demonstrated that the major reason for the exceptional TCDD resistance of H/W rats lies in their AHR, which is remodeled at its C-terminal transactivation domain, but there appears to be another contributing gene product. The present study set out to compare the primary structure of ARNT and the closely related ARNT2 proteins in H/W and L-E rats by cDNA cloning. To our surprise, we found several isoforms of these proteins only one of which has previously been reported in rats. All of the isoforms appeared to arise from alternative splicing. For ARNT, isoforms with deletions at exon 5, 3(') end of exon 6 or 5(') end of exon 11, or with an insertion at 5(') end of exon 20 were discovered. There was also interindividual variation in the number of glutamine-encoding codons at 5(') end of exon 16. The most exciting new variant was revealed for ARNT2, because the insertion found at 5(') end of exon 19 disrupts the functionally critical transactivation domain in the protein, implying a dominant negative role for this isoform. The relative expression levels of the variants did not differ in the two rat strains, nor did TCDD modify the ratios, suggesting that the variants do not contribute to TCDD resistance. However, the regulation of ARNT and ARNT2 activities may be more intricate than previously assumed.

Alternative Splicing↗

Dose-response analysis of short-term effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin in three differentially susceptible rat lines.

Line A, B, and C rats were selectively bred from TCDD-resistant Han/Wistar (Kuopio; H/W) and TCDD-sensitive Long-Evans (Turku/AB; L-E) rats. Line A rats are the most resistant to TCDD acute lethality followed by line B and line C rats. The resistance in line A rats is associated with a mutated H/W-type aryl hydrocarbon receptor (Ahr) allele (Ahr(hw)) and in line B rats the resistance is associated with an allele of an unknown gene B (B(hw)), while line C rats are almost as sensitive to TCDD as L-E rats. The dose-responses of characteristic short-term effects (day 8 postexposure) of TCDD were used to evaluate the efficacy (magnitude of effect) and potency relationships between these lines. Line A rats showed similar efficacies as line C (line A:line C efficacy ratio more than 0.7) for thymus weight, EROD activity, and incisor tooth defects. In contrast, efficacies in line A were decreased (efficacy ratios 0.19-0.37) for body weight change, serum bilirubin, and FFA levels, and serum ASAT activity. For most endpoints the efficacies in line B rats seem to be lower than in line C rats. The potencies were close to each other in line A and B rats, but somewhat lower than in line C rats. The results support our previous concept of two different AHR-mediated signaling pathways leading to dioxin type I and type II endpoints. Rats with the Ahr(hw/hw) genotype show a markedly decreased efficacy for type II endpoints, but B(hw) allele had only a minor effect on efficacies for most endpoints. Both H/W-type resistance alleles also decreased the potency of TCDD. However, the potency differences in short-term toxicity seem not to explain, at least alone, the differences seen in acute lethality among the rat lines.

Alleles↗

2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced accumulation of biliverdin and hepatic peliosis in rats.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a widespread, persistent, and highly toxic environmental pollutant. The most TCDD-sensitive and the most TCDD-resistant rat strains (Long-Evans [Turku/AB] and Han/Wistar [Kuopio], respectively) were crossbred to separate the alleles of two genes (Ahrand an unidentified gene "B") mediating resistance against TCDD toxicity. During crossbreeding, a new type of toxicity in livers of both sexes was detected, characterized macroscopically by intense dark green to black color and swelling that appeared most frequently after a large dose (300 micro g/kg or more as a single intragastric dose) and a follow-up period of more than three weeks. Therefore, studies were undertaken to identify the causative pigment chemically and to examine the hepatotoxicity histologically. The pigment fractions were separated by thin layer chromatography and then analyzed by HPLC and electrospray mass spectrometry. The pigment was found to consist of biliverdin and several biliverdin-related compounds. In liver histopathology carried out on male rats, progressive sinusoidal distension and hepatic peliosis with membrane-bound cysts were seen. The clinical manifestations of pigment accumulation were recorded most often in intermediately resistant rat lines such as line B (homozygous for the gene B), but never occurred in rats expressing only the Han/Wistar (Kuopio)-type Ah receptor with an altered transactivation domain structure.

Animals↗