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Background. The expansion of the territory of human habitation leads to inevitable interference in the natural range of distribution of one or another species of animals, some of which may be dangerous for human life. Scorpions—the Arachnida class and order Scorpiones—can be considered as such typical representatives. Scorpions of the Buthidae family pose a particular danger to humans. However, LD50has not yet been defined for many species of this family, in particular, new representatives of the genus Leiurus. Leiurus macroctenusis a newly described species of scorpion distributed in Oman, and the toxicity of its venom is still unknown. Estimating the LD50of the venom is the first and most important step in creating the antivenom and understanding the medical significance of the researched animal species. The purpose of this study was to determine the lethal dose (LD100), the maximum tolerated dose (LD0), and the average lethal dose (LD50) in rats when using Leiurus macroctenusscorpion venom. Methods and Results. 15 sexually mature scorpions were used in the study, which were kept in the same conditions and milked by a common method (electric milking). For the study, 60 male rats were used, which were injected intramuscularly with 0.5?ml of venom solution with a gradual increase in the dose (5 groups, 10 rats in each), and 10 rats were injected intramuscularly with physiological solution as control group. LD calculations were done using probit analysis method in the modification of the method by V.B. Prozorovsky. The LD0of Leiurus macroctenusscorpion venom under the conditions of intramuscular injection was 0.02?mg/kg, LD100was 0.13?mg/kg, and LD50was 0.08?±?0.01?mg/kg. Conclusions. The analysis of scientific publications and other sources of information gives reason to believe that Leiurus macroctenushas one of the highest values of LD50not only among scorpions but also among all arthropods in the world. All these point to the significant clinical importance of this species of scorpion and require further research that will concern the toxic effect of its venom on various organ systems. Determining the LD50 of the venom for new scorpion species is crucial for creating effective antivenoms and understanding the medical implications of envenomation by this species.

Phytotoxic compounds isolated and identified from different plants have the ability to use as plant-based herbicides. Phytotoxic chemicals may be essential to weed management and environmental protection in order to reduce the indiscriminate use of synthetic pesticides. It has been reported that Elaeocarpus floribundusplant possesses phytotoxic compounds. The leaf extracts of this species demonstrated significant growth inhibition against the tested plants (dicot plant lettuce and plant monocot timothy) and inhibition was dose- and species-dependent pattern. Two phytotoxic compounds were separated using different purifications methods and identified as compounds 1and 2. All phytotoxic compounds displayed potent growth limitation against the tested species (cress). The compound concentrations needed for the inhibition of 50% growth (IC50value) of tested species ranged from 1.06 to 8.53?µM (micromolar). Findings of this research suggest that these compounds might be responsible for the phytotoxicity of Elaeocarpus floribundusplant. The results of this study may be helpful for the development of natural herbicide to control weeds.

Recent studies on mice genetically modified at the Ahrlocus and fed on high-fat diet have revealed a novel physiological role for the AHR in energy balance. Globally impaired function of the receptor counteracts the development of obesity by increasing energy expenditure, which appears to occur mostly in the skeletal muscle and brown adipose tissue. On the other hand, global and tissue-specific loss of AHR signaling can have opposite effects on liver fat content and their impact on insulin sensitivity is also context-dependent. As tryptophan metabolites are key AHR activators, these findings suggest that the AHR may act as a protein sensor enabling adequate protein intake from low-protein diets by allowing calorie overfeeding without resultant obesity.

Although high-throughput techniques such as microarrays and RNA-seq are powerful methods for monitoring mRNA levels and alternative splicing, it remains important to validate a subset of the results using alternate technologies. In this paper, the authors perform a systematic evaluation of two medium-throughput platforms for measuring mRNA abundance. The results provide useful guidance to researchers considering alternative methods for validating high-throughput mRNA expression data.

Flavin-containing monooxygenases (FMOs) are important in detoxication but generally are considered not to be inducible by xenobiotics. Our recent microarray studies revealed induction of FMO2 and FMO3 mRNAs by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in liver of mice with wild-type aryl hydrocarbon receptor (AHR) but not in Ahr-null mice. The aim of the present study was to delineate mechanisms of FMO regulation. In adult male mice, basal FMO3 mRNA is low but was induced 6-fold at 4 h and 6000-fold at 24 h. The ED50 was approximately 1 μg/kg for FMO2 and FMO3, similar to that for the classic AHR-regulated gene, Cyp1a1. In adult female mice basal FMO3 mRNA is high and was not induced at 4 h but was elevated 8-fold at 24 h. FMO5 mRNA was significantly down-regulated by TCDD in both male and female adult mice. Juvenile mice show no sex difference in response to TCDD; FMO3 was induced 4 to 6-fold by TCDD in both sexes. Chromatin immunoprecipitation demonstrated recruitment of AHR and aryl hydrocarbon nuclear translocator proteins to Fmo3regulatory regions, suggesting that induction by TCDD is a primary AHR-mediated event. Although FMO2 and FMO3 mRNAs were highly induced by TCDD in adult males, overall FMO catalytic activity increased only modestly. In contrast to the striking up-regulation of FMO2 and FMO3 in mouse liver, TCDD has little effect on FMO mRNA in rat liver. However, FMO2 and FMO3 mRNAs were highly induced in transgenic mice that express wild-type rat AHR, indicating that lack of induction in rat is not due to an incompetent AHR in this species.

Flavin-containing monooxygenases (FMOs) are important in detoxication but generally are considered not to be inducible by xenobiotics. Our recent microarray studies revealed induction of FMO2 and FMO3 mRNAs by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in liver of mice with wild-type aryl hydrocarbon receptor (AHR) but not in Ahr-null mice. The aim of the present study was to delineate mechanisms of FMO regulation. In adult male mice, basal FMO3 mRNA is low but was induced 6-fold at 4 h and 6000-fold at 24 h. The ED50 was approximately 1 µg/kg for FMO2 and FMO3, similar to that for the classic AHR-regulated gene, Cyp1a1. In adult female mice basal FMO3 mRNA is high and was not induced at 4 h but was elevated 8-fold at 24 h. FMO5 mRNA was significantly down-regulated by TCDD in both male and female adult mice. Juvenile mice show no sex difference in response to TCDD; FMO3 was induced 4 to 6-fold by TCDD in both sexes. Chromatin immunoprecipitation demonstrated recruitment of AHR and aryl hydrocarbon nuclear translocator proteins to Fmo3 regulatory regions, suggesting that induction by TCDD is a primary AHR-mediated event. Although FMO2 and FMO3 mRNAs were highly induced by TCDD in adult males, overall FMO catalytic activity increased only modestly. In contrast to the striking up-regulation of FMO2 and FMO3 in mouse liver, TCDD has little effect on FMO mRNA in rat liver. However, FMO2 and FMO3 mRNAs were highly induced in transgenic mice that express wild-type rat AHR, indicating that lack of induction in rat is not due to an incompetent AHR in this species.

The AHRlocus encodes the aryl hydrocarbon receptor (AHR), a transcriptional regulator of multiple drug-metabolizing enzymes and mediator of toxicity of dioxin-like chemicals. The Han/Wistar (Kuopio) rat strain (H/W) is remarkably resistant to lethal effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) because of a point mutation in the exon/intron 10 boundary in AHRgenomic structure that leads to use of 3 alternative cryptic splice sites, potentially creating 3 alternative transcripts and 2 protein products. The deletion variant (DV), which lacks 43 amino acids in the transactivation domain, has the highest intrinsic transactivation activity in vitro; amino acids 766 to 783 suppress transactivation function. However, DV expression levels in H/W rats in vivo are low in liver, lung, thymus, kidney, and testis; insertion variant mRNAs (IVs) are the dominant mRNA forms in H/W rats in which wild-type AHR mRNA is undetectable. In dioxin-sensitive rat strains and lines that are homozygous for wild-type AHRalleles, wild-type AHR mRNA is the most abundant transcript but some IV transcripts are detectable. TCDD treatment in vivo increases transcript levels for both the DV and IVs in H/W rats and increases wild-type transcript levels in dioxin-sensitive rats but does not alter which transcript forms are expressed. In silico modeling indicates that the DV mRNA has lost considerable secondary structure, whereas at the protein level, the transactivation domain of the IV in the dioxin-resistant H/W rat has greater α-helical content and a more hydrophobic terminus than wild-type AHR, which may produce a protein conformation that is less amenable to interaction with other regulatory proteins.

The AHR locus encodes the aryl hydrocarbon receptor (AHR), a transcriptional regulator of multiple drug-metabolizing enzymes and mediator of toxicity of dioxin-like chemicals. The Han/Wistar (Kuopio) rat strain (H/W) is remarkably resistant to lethal effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) because of a point mutation in the exon/intron 10 boundary in AHR genomic structure that leads to use of 3 alternative cryptic splice sites, potentially creating 3 alternative transcripts and 2 protein products. The deletion variant (DV), which lacks 43 amino acids in the transactivation domain, has the highest intrinsic transactivation activity in vitro; amino acids 766 to 783 suppress transactivation function. However, DV expression levels in H/W rats in vivo are low in liver, lung, thymus, kidney, and testis; insertion variant mRNAs (IVs) are the dominant mRNA forms in H/W rats in which wild-type AHR mRNA is undetectable. In dioxin-sensitive rat strains and lines that are homozygous for wild-type AHR alleles, wild-type AHR mRNA is the most abundant transcript but some IV transcripts are detectable. TCDD treatment in vivo increases transcript levels for both the DV and IVs in H/W rats and increases wild-type transcript levels in dioxin-sensitive rats but does not alter which transcript forms are expressed. In silico modeling indicates that the DV mRNA has lost considerable secondary structure, whereas at the protein level, the transactivation domain of the IV in the dioxin-resistant H/W rat has greater α-helical content and a more hydrophobic terminus than wild-type AHR, which may produce a protein conformation that is less amenable to interaction with other regulatory proteins.

One characteristic feature of acute 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) toxicity is dramatic interspecies and interstrain variability in sensitivity. This complicates dioxin risk assessment for humans. However, this variability also provides a means of characterizing mechanisms of dioxin toxicity. Long-Evans (Turku/AB) rats are orders of magnitude more susceptible to TCDD lethality than Han/Wistar (Kuopio) rats, and this difference constitutes a very useful model for identifying mechanisms of dioxin toxicity. We adopted a proteomic approach to identify the differential effects of TCDD exposure on liver protein expression in Han/Wistar rats as compared with Long-Evans rats. This allows determination of which, if any, protein markers are indicative of differences in dioxin susceptibility and/or responsible for conferring resistance. Differential protein expression in total liver protein was assessed using two-dimensional gel electrophoresis, computerized gel image analysis, in-gel digestion, and mass spectrometry. We observed significant changes in the abundance of several proteins, which fall into three general classes: (i) TCDD-independent and exclusively strain-specific (e.g.isoforms of the protein-disulfide isomerase A3, regucalcin, and agmatine ureohydrolase); (ii) strain-independent and only dependent on TCDD exposure (e.g.aldehyde dehydrogenase 3A1 and rat selenium-binding protein 2); (iii) dependent on both TCDD exposure and strain (e.g.oxidative stress-related proteins, apoptosis-inducing factor, and MAWD-binding protein). By integrating transcriptomic (microarray) data and genomic data (computational search of regulatory elements), we found that protein expression levels were mainly controlled at the level of transcription. These results reveal, for the first time, a subset of hepatic proteins that are differentially regulated in response to TCDD in a strain-specific manner. Some of these differential responses may play a role in establishing the major differences in TCDD response between these two strains of rats. As such, our work is expected to lead to new insights into the mechanism of TCDD toxicity and resistance.

One characteristic feature of acute 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) toxicity is dramatic interspecies and interstrain variability in sensitivity. This complicates dioxin risk assessment for humans. However, this variability also provides a means of characterizing mechanisms of dioxin toxicity. Long-Evans (Turku/AB) rats are orders of magnitude more susceptible to TCDD lethality than Han/Wistar (Kuopio) rats, and this difference constitutes a very useful model for identifying mechanisms of dioxin toxicity. We adopted a proteomic approach to identify the differential effects of TCDD exposure on liver protein expression in Han/Wistar rats as compared with Long-Evans rats. This allows determination of which, if any, protein markers are indicative of differences in dioxin susceptibility and/or responsible for conferring resistance. Differential protein expression in total liver protein was assessed using two-dimensional gel electrophoresis, computerized gel image analysis, in-gel digestion, and mass spectrometry. We observed significant changes in the abundance of several proteins, which fall into three general classes: (i) TCDD-independent and exclusively strain-specific (e.g. isoforms of the protein-disulfide isomerase A3, regucalcin, and agmatine ureohydrolase); (ii) strain-independent and only dependent on TCDD exposure (e.g. aldehyde dehydrogenase 3A1 and rat selenium-binding protein 2); (iii) dependent on both TCDD exposure and strain (e.g. oxidative stress-related proteins, apoptosis-inducing factor, and MAWD-binding protein). By integrating transcriptomic (microarray) data and genomic data (computational search of regulatory elements), we found that protein expression levels were mainly controlled at the level of transcription. These results reveal, for the first time, a subset of hepatic proteins that are differentially regulated in response to TCDD in a strain-specific manner. Some of these differential responses may play a role in establishing the major differences in TCDD response between these two strains of rats. As such, our work is expected to lead to new insights into the mechanism of TCDD toxicity and resistance.

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 μg/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 α as well as two estrogen-receptor-related genes (α and γ) 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.

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 µg/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 α as well as two estrogen-receptor-related genes (α and γ) 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.

In this study we investigated the effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the p53 response to DNA damaging agents. Pre-treatment of rats with TCDD attenuated the p53 liver response to diethylnitrosamine (DEN) and reduced levels of p53 and Ser15 phosphorylated p53. In addition, there were more slowly migrating p53 species, forming a ladder, which suggests an increased ubiquination of p53 in TCDD-pre-treated rats. Terminal deoxynucleotidyl transferase-mediated X-dUTP nick-end labelling analysis indicated decreased apoptosis rates in the livers of these rats. Studies on aryl hydrocarbon receptor (AhR) knockout mice and their wild-type littermates confirmed this effect in AhR +/+ but not in AhR −/− mice, indicating that this effect may be AhR-mediated. Quantitative RT-PCR analysis revealed no increased mRNA levels in TCDD-treated rats, but immunohistological studies indicated that TCDD modulated Mdm2 protein levels, and in particular, increased nuclear levels in rat hepatocytes in situ. In vitro studies employing HepG2 cells confirmed the in vivo data. Thus, TCDD increased basal levels of Mdm2 protein, but not mRNA, and attenuated the p53 response to a variety of genotoxic and cytotoxic agents. The increase in Mdm2 protein levels was accompanied by rapid and highly sensitive phosphorylation of Mdm2 at Ser166, which has been associated to active Mdm2. In summary, TCDD is a potent inhibitor of p53 that may influence the liver's ability to handle genotoxic agents in a safe way, and may play a role in TCDD-induced carcinogenesis.

Most toxic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) are mediated by the aryl hydrocarbon receptor (AHR). A single, acute dose of TCDD can alter its own receptor levels thus complicating evaluation of dose–response relationships for AHR-mediated events. Since environmental exposure to dioxins is typically of a repeated low-dose nature, we examined the effect of such exposure on AHR expression. Three rat strains differing greatly in their sensitivity to acute TCDD lethality, Long–Evans (Turku AB) (L-E) (LD50 ∼10 μg/kg); Sprague Dawley (SD) (LD50 ∼50 μg/kg); and Han/Wistar (Kuopio) (H/W) (LD50 > 9600 μg/kg), were administered TCDD intragastrically, biweekly for 22 weeks producing doses equivalent to 0, 10, 30, and 100 ng/kg/day. Changes in hepatic AHR levels were quantitated at the protein level by radioligand binding and immunoblotting and at the mRNA level by RT–PCR. Cytosolic AHR protein was elevated at 10 or 30 ng/kg/day TCDD in SD and L-E rats; AHR mRNA was also elevated at these doses, suggesting a pretranslational mechanism. There was no apparent relationship between TCDD-induced AHR regulation and strain sensitivity to TCDD. Overall, “subchronic” TCDD did not greatly perturb AHR expression. The maintenance of relatively constant receptor levels in the face of persistent agonist stimulation is in contrast to the sustained depletion of AHR by TCDD observed in cell culture and to the fluctuations in AHR observed hours to days following acute TCDD exposure in vivo.Changes in AHR levels may affect dose–response relationships; the effect of TCDD on its own receptor at environmentally relevant dosing schemes is therefore important to risk assessment.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) brings about a wide spectrum of toxic and biochemical changes, most of which are mediated by the AH receptor (AHR). Recent cloning of the AHR from the two most TCDD-resistant laboratory animals, Han/Wistar (Kuopio) rats and hamsters, suggested a critical role for the C-terminal transactivation domain structure in TCDD sensitivity. Here we cloned the AHR from the most TCDD-susceptible species, guinea pig. The N-terminus of its AHR was highly similar to that in the resistant animals. However, the C-terminal Q-rich subdomain was only about half the size of this subunit in the hamster AHR. There was a distinct correlation across published mammalian species between the number of glutamine residues in the Q-rich subdomain and sensitivity to the acute lethality of TCDD. The closest homolog of the Guinea pig receptor turned out to be the human AHR, which may be relevant for dioxin risk assessment.

The interference with tooth development by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was studied in dioxin-resistant Han/Wistar rats. Lactating dams were given a single dose of 50 or 1000 μg TCDD/kg body wt 1 day after delivery and the pup heads were analyzed radiographically or histologically at postnatal days 9 and/or 22. Of 19 animals studied histologically, 10 lacked one or more third molars, which were at the bud stage at the start of the experiment. A higher proportion of pups exposed to the higher dose (9/13) lacked third molars than those exposed to the lower dose (1/6) (27/52 and 2/24 teeth missing, respectively). Missing upper third molars (19/38) were more frequent than were lower (10/38). The development of the third molars present was retarded. The root tips of the more advanced first and second molars were prematurely closed and root formation was arrested, but eruption was not affected. Dentinogenesis of the continuously erupting lower incisor teeth was preeruptively arrested because of pulpal cell death. All the teeth of the control rat pups developed normally. In contrast to the control pups, none of the 11 experimental pups examined radiographically (6 exposed to the higher dose and 5 to the lower) showed mineralization of their third molar cusps. The results show that the effects of TCDD on rat tooth development depend on not only the dose but also the tooth type and developmental stage. Inasmuch as early tooth development is under the control of inductive interactions between the epithelium and the mesenchyme, the interference by TCDD with tooth morphogenesis with the consequent arrest of development is likely to involve epithelial–mesenchymal signaling.

Hamsters and Han/Wistar (Kuopio; H/W) rats show peculiarly selective responsiveness to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). They are extremely resistant to its acute lethality but sensitive to, e.g., enzyme induction. The biological effects of TCDD are mediated by the AH receptor (AHR). Recent studies on H/W rat AHR discovered a remodelled transactivation domain which appears to be critical for the TCDD resistance of these animals. Here, molecular cloning and sequencing of hamster AHR reveals another type of restructured transactivation domain. In hamsters, the functionally pivotal Q-rich region is substantially expanded and enriched in glutamine compared with all other AHRs cloned to date. By contrast, the amino-terminal end is highly conserved, which is in agreement with the H/W rat AHR. Because of the additional material in the transactivation domain, hamster AHR protein is larger than that in rats or mice, but the pattern of AHR mRNA expression in tissues is similar.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD),11Some of these results were presented at the 37th Annual Meeting of the Society of Toxicology, held in Seattle, Washington, March 1–5, 1998 (abstract 326).22Abbreviations used: AHR, aryl hydrocarbon receptor;Ahr,AHR gene; “B,” an unknown dioxin resistance gene; EROD, ethoxyresorufin-O-deethylase; H/W, Han/Wistar; hw, H/W type; L-E, Long–Evans; TCDD, 2,3,7,8-tetrachlorodibenzo-p-dioxin; TNT, Tris–NaCl–Tween 20 buffer; wt, wild typethe most toxic congener of dioxins, exhibits wide sensitivity differences between a sensitive Long–Evans (L-E) rat and a resistant Han/Wistar (H/W) rat. The sensitivity is determined probably by two autosomal genes and it is highly end point dependent. The difference is more than 1000-fold for acute toxicity and negligible for CYP1A1 induction. The rat strains were recently shown to have differences in the size of AH receptor (AHR), which mediates most effects of TCDD. In the present study, the rat strains were crossed and the resistant alleles of genes determining TCDD sensitivity were segregated to new rat lines. Selection was based on AHR phenotype determined by Western blot and resistance to TCDD lethality. Two genes determining resistance were found: theAhrand a novel gene designated “B.” In homozygous rats, the H/W typeAhrhwallele prevented TCDD lethality up to 2000 μg/kg or more, and the H/W type “Bhw” allele also increased resistance to TCDD lethality but to a lesser extent. Heterozygous rats were only slightly more resistant to acute lethality than the respective sensitive homozygous rats. CYP1A1 induction was similar irrespective of theAhrand “B” genotypes, but a substantial increase in serum bilirubin seen after low doses in sensitive rats occurred only after large doses in “Bhw/hw” and not at all inAhrhw/hwrats. In conclusion, theAhrhwallele is a major determinant of the exceptional resistance of H/W rats to TCDD lethality. There is also an additional gene, whose function remains to be characterized, conferring limited resistance to TCDD toxicity. These two H/W rat-derived alleles are separately expressed in the new rat lines created.

Abstract: Reduced gluconeogenesis due to decreased activity of key gluconeogenic enzymes in liver, together with feed refusal, has been suggested to play an important role in 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced lethality in rats. This study was carried out to further analyse the toxicological significance of reduced gluconeogenesis by comparing dose-responses and time-courses of effects of TCDD on the activity of phosphoenolpyruvate carboxykinase (PEPCK) in liver, liver glycogen concentration as well as plasma concentrations of glucose and amino acids in both genders of TCDD-sensitive Long-Evans (L-E) rats and TCDD-resistant Han/Wistar (H/W) rats. A dose-dependent decrease in PEPCK activity was observed in H/W rats, but in L-E rats the activity was not decreased. However, TCDD impaired the strong increase in liver PEPCK activity observed in pair-fed controls of the L-E strain. Liver glycogen concentrations were severely decreased in L-E rats and moderately in H/W rats. This effect seems to be secondary to reduced feed intake, since a similar decrease was seen in pair-fed controls. Decreases in plasma glucose concentrations were also more profound in L-E rats than in H/W rats, but pair-fed controls were generally less affected. Circulating concentrations of amino acids were markedly increased in TCDD-treated L-E rats, which is likely to reflect increased mobilization of amino acids and their decreased metabolism in liver. Reduction of liver PEPCK activity cannot account for the sensitivity difference of these two strains of rats in terms of mortality. Nevertheless, the response of both strains of TCDD-treated rats regarding gluconeogenesis is different from that seen in pair-fed controls and suggesting that impairment of this pathway contributes to the development of the wasting syndrome.

Long–Evans rats (strain Turku AB; L–E) are at least 1000-fold more sensitive (LD50about 10 μg/kg) to the acute lethal effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) than are Han/Wistar (Kuopio; H/W) rats (LD50> 9600 μg/kg). The AH receptor (AHR) is believed to mediate the toxic effects of TCDD and related halogenated aromatic hydrocarbons. We compared the AHRs of L–E and H/W rats to determine if there were any structural or functional receptor differences that might be related to the dramatic difference in the sensitivity of these two strains to the lethal effects of TCDD. Cytosols from liver and lung of the sensitive L–E rats contained about twofold higher levels of specific binding sites for [3H]TCDD than occurred in H/W rats; theKdfor binding of [3H]TCDD to AHR in hepatic cytosols was similar between the two strains. Addition of the oxyanions, molybdate or tungstate (20 mM), had little effect upon ligand binding to AHR in hepatic cytosols from L–E rats whereas in cytosols from H/W rats these agents substantially diminished or totally abolished TCDD binding. The AHR in H/W cytosols also lost ligand-binding function when NaCl (20 to 400 mM) was added to the buffer whereas, in cytosols from L–E rats, the addition of 400 mM NaCl caused the receptor complex to shift from 9S to 6S during velocity sedimentation but did not destroy ligand binding function. AHR from hepatic cytosol of both the L–E and H/W rats could be transformed to the DNA-binding state in the presence of TCDD or other dioxin congeners as assessed by gel mobility shift assays. The most dramatic difference in AHR properties between L–E and H/W rats is molecular mass. Immunoblotting of cytosolic proteins revealed that the AHR in L–E rats has an apparent mass of ≈106 kDa, similar to the mass of the receptor previously reported in several other common laboratory rat strains. In contrast, the mass of the AHR in H/W rats is ≈98 kDa, significantly smaller than the mass of receptor reported in any other rat strains. F1offspring of a cross between L–E and H/W rats expressed both the 106- and the 98-kDa protein. There was no apparent difference in the mass of the AHR nuclear translocator protein (ARNT) between the two strains, but the hepatic concentration of ARNT was about three times as high in L–E as in H/W rats. It will be interesting to find out how the altered structure of the AHR in H/W rats is related to their remarkable resistance to the lethal effects of TCDD.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is the most potent dioxin. There are exceptionally wide inter- and intraspecies differences in sensitivity to TCDD toxicity with Han/Wistar (H/W) (Kuopio) rats being the most resistant mammals tested. A peculiar feature of H/W rats is that despite their unresponsiveness to the acute lethality of TCDD, their sensitivity to other biological impacts of TCDD (e.g., CYP1A1 induction) is preserved. The biological effects of TCDD are mediated by the aryl hydrocarbon receptor (AhR). We recently found that the AhR of H/W rats (about 98 kDa) is smaller than the receptor in other rat strains (106 kDa). In the present study, molecular cloning and sequencing of the H/W rat AhR revealed that the reason for its smaller size is a deletion/insertion-type change at the 3′ end of exon 10 in the receptor cDNA. This change emanates from a single point mutation at the first nucleotide of intron 10, resulting in altered mRNA splicing. At the protein level, the mutation leads to a total loss of either 43 or 38 amino acids (with altered sequence for the last seven amino acids in the latter case) toward the carboxyl-terminal end in the trans-activation domain of the AhR. H/W rats also harbor a point mutation in exon 10 that will cause a Val-to-Ala substitution in codon 497, but this occurs in a variable region of the AhR. These findings suggest that there is a relatively small region in the AhR trans-activation domain that may be capable of providing selectivity to its function.

We have previously shown that the wasting syndrome in response to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) administration is associated with a specific increase in free tryptophan (unbound to albumin) in rats. The present series of experiments was undertaken to characterize how the binding of tryptophan to albumin is altered by TCDD and to find the underlying cause of the changes. TCDD administered to Long-Evans rats proved to diminish the maximal binding capacity (Bmax) of albumin for tryptophan by ca. 60% without any marked change in the binding affinity. Of candidate mediating factors, neither TCDD nor bilirubin affected the binding equilibrium of tryptophan with albumin in vitro. However, a mixture of free fatty acids greatly increased the proportion of free tryptophan at physiologically relevant concentrations. Similarly, the free fatty acid mixture added to plasma in vitro decreased only Bmax of albumin in a manner similar to the effect of TCDD administered in vivo. Extraction of lipid-soluble substances from the plasma with ether was effective in reversing the increase in free tryptophan in the plasma of TCDD-treated rats while dialysis of water-soluble substances was not. Ether extraction also resulted in a decrease in free fatty acids. We conclude that disturbances in lipid metabolism may be involved in the pathogenesis of TCDD-induced alterations in tryptophan binding to albumin in vivo.

We have previously reported that in rats 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) lethality is associated (although not necessarily causally) with changes in brain serotonin (5-HT) metabolism. In the present study, we have examined whether this holds for other species by comparing the effect of TCDD in the most TCDD-susceptible and the most TCDD-resistant species, guinea pigs and hamsters, respectively. Body weight gain of guinea pigs exposed to TCDD (0.3–2.7 μg/kg) diminished dose dependently, while the effect was marginal in hamsters (900–4600 μg/kg). Brain 5-hydroxyindoleacetic acid (the main metabolite of brain 5-HT), brain tryptophan (the precursor amino acid of 5-HT), and plasma free and total tryptophan were not affected at any dose in guinea pigs. In contrast, 4 days after exposure, the levels of plasma free and total tryptophan were consistently increased in hamsters. These, as well as brain tryptophan, were still elevated 10 days after exposure. TCDD did not affect plasma glucose level in either species. Liver glycogen was decreased in a dose-dependent manner in TCDD-treated guinea pigs as well as in their pair-fed controls on day 10. There was no change in liver glycogen in hamsters. The activity of the gluconeogenic enzyme, phosphoenolpyruvate carboxykinase was only depressed in hamsters by all doses of TCDD. We conclude that changes in tryptophan metabolism or in carbohydrate homeostasis cannot explain the wide interspecies differences in susceptibility to the acute lethality of TCDD, although they may correlate with some aspects of its toxicity in certain species.

Risk evaluation of complex environmental mixtures of polychlorinated dibenzo-p-dioxins and related halogenated aromatic hydrocarbons (polychlorinated dibenzofurans, azo- and azoxybenzenes, naphthalenes and some of the biphenyls) is currently carried out by measuring the concentration of each congener in the mixture and then multiplying every figure by its specific constant, toxic equivalency factor (TEF). All congeners are thought to produce highly similar effects albeit at different doses, and the TEFs are believed to represent the potencies of the congeners relative to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), considered the most toxic derivative of this class of environmental contaminants. Here we compared the acute toxicities of TCDD, 1,2,3,7,8-penta-, 1,2,3,4,7,8-hexa- and 1,2,3,4,6,7,8-heptachloro-dibenzo-p-dioxin in the most TCDD-susceptible (Long-Evans Turku AB; L-E) and the most TCDD-resistant (Han/Wistar Kuopio; H/W) rat strain. While L-E rats exhibited the expected rank order of sensitivities to the four dioxins, the higher chlorinated dioxins were more toxic than TCDD (in terms of acute lethality) to H/W rats, with the hexachlorodioxin showing the greatest potency. Even if the doses were adjusted according to the LD50 values, both biochemical and morphological effects elicited by the dioxins turned out to depend, often critically, on strain, congener or the interaction of these two determinants. These findings demonstrate that the dioxins have distinct profiles of acute toxicities and underscore the importance of response and test organism in defining the TEFs.

Long-term regulation of body weight and food intake were studied after rats were subjected to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), which causes hypophagia and body weight loss, and to ventromedial hypothalamic lesion, which causes hyperphagia, metabolic changes and obesity. These two factors appeared to have an interaction, as ventromedial hypothalamic lesion initially aggravated the effects of TCDD on body weight and food intake. This was seen in both TCDD-resistant and TCDD-susceptible rat strains. In contrast, if TCDD was given several weeks before the lesion and body weight had stabilized to a low level, no aggravation was seen, but TCDD completely blocked the effects of ventromedial hypothalamic lesion. Thus, TCDD seems to affect the same regulation chain that is involved in the lesioning of the ventromedial hypothalamus. TCDD might serve as a tool in studying different mechanisms of long-term food intake and body weight regulation.

Abstract: We compared the effects of 2,3,7,8-tetra (TCDD), 1,2,3,7,8-penta (PeCDD), 1,2,3,4,7,8-hexa (HxCDD) and 1,2,3,4,6,7,8-heptachlorodibenzo-p-dioxin (HpCDD) on brain serotonin metabolism, plasma tryptophan and liver tryptophan pyrrolase activity in two rat strains, TCDD-sensitive Long-Evans (Turku AB; L-E) and TCDD-resistant Han/Wistar (Kuopio; H/W). Previously it was shown that L-E rats exhibit the expected rank order of potency for CDDs in terms of acute toxicity with TCDD being the most potent, followed by PeCDD, HxCDD and HpCDD. In contrast, to H/W rats HxCDD was the most toxic and TCDD the least toxic of these congeners. In the present study, the CDDs decreased body weight in L-E rats in the following order of potency: TCDD>PeCDD>HxCDD>HpCDD. The same rank order was recorded for elevations in brain tryptophan and plasma free tryptophan concentrations as well as for inhibition of the main hepatic tryptophan metabolizing enzyme, tryptophan pyrrolase. By contrast, in H/W rats HxCDD was the most effective congener in producing loss of body weight, followed by HpCDD, PeCDD and TCDD. This was also true of changes in tryptophan homeostasis. These findings imply that in TCDD-susceptible L-E and TCDD-resistant H/W rats the potency of dioxin congeners in inducing acute toxicity highly correlates with their ability to disrupt tryptophan homeostasis. However, there may not be a direct causal relationship between body weight loss and altered tryptophan homeostasis, because the magnitudes of these two phenomena were not consistently parallel across the dioxin congeners tested.

A set of experiments was carried out in order to approach the complex nature of L. monocytogenes infections from different aspects. Experiment 1 showed that Listeria are able to gain admission to body by numerous ways and both subcutaneous and oral entry can lead to fatal septicemia. It also gave slight support to the theory of direct neural transmission of Listeria to the brain and indicated the possibility that intestinal absorption after oral exposition at least partly occurs via lymphatic vessels. No inflammatory reaction could be caused to mice by ocular flushing with Listeria suspension.

Target Tissue Morphology and Serum Biochemistry following 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) Exposure in a TCDD-Susceptible and a TCDD-Resistant Rat Strain. POHJANVIRTA, R., KULJU, T., MORSELT, A. F. W., TUOMINEN, R., JUVONEN, R., ROZMAN, K.,MÄNNISTÖ, P., COLLAN, Y., SAINIO, E.-L., AND TUOMISTO, J. (1989). Fundam. Appl. Toxicol. 12, 698–712. The mode of action of the highly toxic environmental contaminant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is unknown. It was recently discovered that two strains of rat, Long-Evans (L-E) and Han/Wistar (H/W), differ widely in susceptibility to TCDD. Employing this strain divergence as a probe, the present study set out to assess the role of various biochemical and morphological effects in TCDD lethality. In the main experiment, the rats were treated once ip with 0, 5, 50, or (H/W) 500 μg/kg TCDD and killed 1 to 16 days postexposure. Several target organs were evaluated by light microscopy and a number of serum lipid and carbohydrate parameters as well as a few major regulatory hormones were analyzed. The results demonstrated that most alterations caused by TCDD were essentially similar in both strains. TCDD reduced circulating thyroxine to a slightly greater extent and more permanently in the sensitive L-E strain. Moreover, a highly significant interaction on thyroid-stimulating hormone was found among strain, dose. and time. Serum concentrations of corticosterone and free fatty acids were increased only in the L-E rats given 50 μg/kg TCDD, i.e., at an apparent LDl00 dose level for this strain. Yet, the most striking interstrain difference was seen in the liver which was distinctly affected after Day 4 in L-E rats given 50 μg/kg TCDD but only marginally affected in rats from any H/W group. The lesion, while showing no necrotic cell changes, was suggestive of plasma membrane damage, possibly reflecting the production of free radicals. The relation of the findings to possible mechanisms of TCDD action is discussed.