Transcriptional activation of the human Cu/Zn superoxide dismutase gene by 2,3,7,8-tetrachlorodibenzo-p-dioxin through the xenobiotic-responsive element

Cu/Zn superoxide dismutase (SOD1) catalyzes the dismutation of superoxide radicals produced during biological oxidations and environmental stress. Here we have investigated the effect of the most toxic dioxin, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), on the promoter of the Cu/Zn superoxide dismutase (SOD1) gene in HepG2 and HeLa cells using the chloramphenicol acetyltransferase gene as a reporter. The SOD1 promoter was activated 4- to 5-fold by TCDD treatment, in a concentration-dependent manner. In addition, the level of SOD1 mRNA and the enzymatic activity of the SOD1 protein were also enhanced on exposure of the cells to TCDD. Functional analysis of the regulatory region of the SOD1 gene by deletion and point mutation, and the use of a heterologous promoter system, showed that the SOD1 gene was transactivated by TCDD via the xenobiotic-responsive element (XRE). Gel mobility shift assays also confirmed the induction and the inducible binding of a receptor-ligand complex to XRE. Yeast cells that overexpress hSOD1 appeared to be more resistant to TCDD than the wild type. These results demonstrate that SOD1 is induced by TCDD via the XRE. The induced SOD1 may accelerate the neutralization of the superoxide anion and thus reduce the oxidative damage associated with dioxin toxicity.     

2,3,7,8-tetrachlorodibenzo-p-dioxin induces transcriptional activity of the human polymorphic hs1,2 enhancer of the 3'Igh regulatory region

2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is an environmental toxicant known to inhibit Ab secretion and Ig expression. Inhibition of Ig expression may be partially mediated through repression of the 3'Igh regulatory region (3'IghRR). TCDD inhibits mouse 3'IghRR activation and induces aryl hydrocarbon receptor binding to dioxin response elements within the 3'IghRR enhancers hs1,2 and hs4. The human hs1,2 enhancer (hu-hs1,2) is polymorphic as the result of the presence of one to four invariant sequences (ISs), which have been correlated with several autoimmune diseases. The IS also contains a dioxin response element core motif. Therefore, the objective was to determine whether hu-hs1,2 activity is sensitive to TCDD. Using a mouse B cell line (CH12.LX), we compared the effects of TCDD on mouse hs1,2 versus hu-hs1,2 activity. TCDD inhibited mouse hs1,2 similarly to the mouse 3'IghRR. In contrast, hu-hs1,2 was activated by TCDD, and antagonist studies supported an aryl hydrocarbon receptor-dependent activation, which was replicated in a human B cell line (IM-9). Absence of Pax5 binding sites is a major difference between the human and mouse hs1,2 sequence. Insertion of the high-affinity Pax5 site in hu-hs1,2 markedly blunted reporter activity but did not alter TCDD's effect (i.e., no shift from activation to inhibition). Additionally, deletional analysis demonstrated a significant IS contribution to hu-hs1,2 basal activity, but TCDD-induced activity was not strictly IS number dependent. Taken together, our results suggest that hu-hs1,2 is a significant target of TCDD and support species differences in hs1,2 regulation. Therefore, sensitivity of hu-hs1,2 to chemical-induced modulation may influence the occurrence and/or severity of human diseases associated with hu-hs1,2.     

Aryl hydrocarbon receptor-dependent induction of apoptosis by 2,3,7,8-tetrachlorodibenzo-p-dioxin in cerebellar granule cells from mouse

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a prototypical environmental contaminant with neurotoxic properties that alters neurodevelopment and behavior. TCDD is a ligand of the aryl hydrocarbon receptor (AhR), which is a key signaling molecule to fully understand the toxic and carcinogenic properties of dioxin. Much effort is underway to unravel the molecular mechanisms and the signaling pathways involved in TCDD-induced neurotoxicity, and to define its molecular targets in neurons. We have used cerebellar granule cells (CGC) from wild-type (AhR+/+) and AhR-null (AhR-/-) mice to characterize the cell death that takes place in neurons after TCDD toxicity. TCDD induced cell death in CGC cultures from wild-type mice with an EC(50) of 127±21 nM. On the contrary, when CGC neurons from AhR-null mice were treated with TCDD no significant cell death was observed. The role of AhR in TCDD-induced death was further assessed by using the antagonists resveratrol and α-naphtoflavone, which readily protected against TCDD toxicity in AhR+/+ CGC cultures. AhR+/+ CGC cultures treated with TCDD showed nuclear fragmentation, DNA laddering, and increased caspase 3 activity, similarly to what was found by the use of staurosporine, a well-established inducer of apoptosis. Finally, the AhR pathway was active in CGC because TCDD could induce the expression of the target gene cytochrome P450 1A2 in AhR+/+ CGC cultures. All together these results support the hypothesis that TCDD toxicity in CGC neurons involves the AhR and that it takes place mainly through an apoptotic process. AhR could be then considered a novel target in neurotoxicity and neurodegeneration whose down-modulation could block certain xenobiotic-related adverse effects in CNS.     

Bioassay-based screening of microorganisms that degrade dioxin using substrate-immobilized microtubes

In the current study, we attempted to develop a method for bioassay-based screening of microorganisms that degrade dioxin. However, a crucial problem encountered was that the standard dioxin 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) added to bacterial medium immediately disappeared from the liquid phase due to its adsorption onto polypropylene (PP) tubes. Among other aromatic hydrocarbons, adsorption onto PP tubes was also observed in beta-naphthoflavone but not in benzo[a]pyrene. Adsorption of TCDD was observed not only onto PP tubes but also onto polystyrene, glass, and PP tubes with low affinity for DNA or protein. Silanization was not effective at preventing adsorption of TCDD. TCDD immobilized onto PP tubes was recovered by organic solvents, including ethanol, methanol, and dimethyl sulfoxide (DMSO). The elution efficiency of the immobilized TCDD by DMSO was approximately 85%. Based on these findings, screening of bacteria that degrade dioxin was attempted as follows. First, TCDD was immobilized onto PP tubes. Second, bacterial suspension was added to the tubes and incubated for biodegradation of TCDD. Third, remaining, immobilized TCDD was eluted by DMSO and subjected to a reporter bioassay to evaluate the level of TCDD. Using this method, we demonstrated successful screening of bacteria that have the potential for degradation of dioxin.     

In vitro effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on ovarian, pituitary, and pineal function in pigs

The aims of the study were: (1) to examine 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and/or prolactin (PRL) effects on in vitro secretion of progesterone (P₄) and estradiol (E₂) by luteinized granulosa and theca cells from porcine preovulatory follicles; and (2) to determine the effects of TCDD on PRL, luteinizing hormone (LH), and melatonin luteal phase in pigs. We found that TCDD itself did not affect progesterone secretion, but it abolished the stimulatory effect of PRL in the follicular cells. TCDD stimulated PRL secretion during the luteal phase and inhibited during the follicular phase. Moreover, TCDD increased luteinizing hormone secretion by pituitary cells during the follicular phase. In contrast to protein and steroid hormones, melatonin secretion in vitro was not affected by TCDD. In conclusion, it was found that the pituitary-ovarian axis in pigs is sensitive to TCDD, and the dioxin exhibited a profound ability to disrupt the ovarian actions of prolactin.     

The trascriptional activation of the human copper/zinc superoxide dismutase gene by 2,3,7,8-tetrachlorodibenzo-p-dioxin through two different regulator sites,the anitoxidant responsive element and xenobiotic responsive element

Cu/Zn superoxide dismutase (SOD1) catalyzes the dismutation of superoxide radicals produced during biological oxidations and environmental stress. The most toxic dioxin, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), induces SOD1 in human liver cells. Deletion analyses showed that the promoter region between -400 and -239 was responsible for the induction, in which two different characteristic regulatory elements, the antioxidant responsive element (ARE) and xenobiotic responsive element (XRE), are located. When the cells transfected with the plasmid containing those two cis-elements, the transactivation of SOD1 promoter was about 4-fold by TCDD, whereas mutation either on the ARE or XRE elevated the promoter activity by about 2-fold. Functional analyses of these two elements by deletion, mutation in the natural context, heterologous promoter assay, and gel mobility shift assay supported the notion that the activation of the SOD1 promoter was induced by TCDD through these two regulatory elements ARE and XRE. These results alongside our previous data indicate that the induction of SOD1 in response to TCDD is mediated by either Nrf2 protein or Ah receptor protein through ARE and XRE, respectively. These results also imply that the SOD1 can be induced by dioxin either in combination with or independently of these two regulatory elements to effectively defend cells from oxidative stress.     

Dictyostelium differentiation-inducing factor-3 activates glycogen synthase kinase-3beta and degrades cyclin D1 in mammalian cells

In search of chemical substances applicable for the treatment of cancer and other proliferative disorders, we studied the signal transduction of Dictyostelium differentiation-inducing factors (DIFs) in mammalian cells mainly using HeLa cells. Although DIF-1 and DIF-3 both strongly inhibited cell proliferation by inducing G(0)/G(1) arrest, DIF-3 was more effective than DIF-1. DIF-3 suppressed cyclin D1 expression at both mRNA and protein levels, whereas the overexpression of cyclin D1 overrode DIF-3-induced cell cycle arrest. The DIF-3-induced decrease in the amount of cyclin D1 protein preceded the reduction in the level of cyclin D1 mRNA. The decrease in cyclin D1 protein seemed to be caused by accelerated proteolysis, since it was abrogated by N-acetyl-Leu-Leu-norleucinal, a proteasome inhibitor. DIF-3-induced degradation of cyclin D1 was also prevented by treatment with lithium chloride, an inhibitor of glycogen synthase kinase-3beta (GSK-3beta), suggesting that DIF-3 induced cyclin D1 proteolysis through the activation of GSK-3beta. Indeed, DIF-3 dephosphorylated Ser(9) and phosphorylated tyrosine on GSK-3beta, and it stimulated GSK-3beta activity in an in vitro kinase assay. Moreover, DIF-3 was revealed to induce the nuclear translocation of GSK-3beta by immunofluorescent microscopy and immunoblotting of subcellular protein fractions. These results suggested that DIF-3 activates GSK-3beta to accelerate the proteolysis of cyclin D1 and that this mechanism is involved in the DIF-3-induced G(0)/G(1) arrest in mammalian cells.     

Primary culture of chicken hepatocytes as an in vitro model for determining the influence of dioxin

An easy method for primary culture of chicken hepatocytes was developed to study the influence of dioxin on birds. Chicken hepatocytes could maintain gene expression and protein secretion of albumin for a long period in serum-free medium with free atmosphere exchange at 37 degrees C. Moreover, the cells showed a sensitive response to 2, 3, 7, 8-tetrachlorodibenzo-p-dioxin (TCDD) by monitoring the expression of P450 1A, theta GST (theta-GST) and albumin genes.     

The aryl hydrocarbon receptor (AhR) tyrosine 9, a residue that is essential for AhR DNA binding activity, is not a phosphoresidue but augments AhR phosphorylation

We delineate a mechanism by which dioxin (2,3,7,8-tetrachlorodibenzo-p-dioxin or TCDD)-mediated formation of the aryl hydrocarbon receptor (AhR) DNA binding complex is disrupted by a single mutation at the conserved AhR tyrosine 9. Replacement of tyrosine 9 with the structurally conservative phenylalanine (AhRY9F) abolished binding to dioxin response element (DRE) D, E, and A and abrogated DRE-driven gene induction mediated by the AhR with no effect on TCDD binding, TCDD-induced nuclear localization, or ARNT heterodimerization. The speculated role for phosphorylation at tyrosine 9 was also examined. Anti-phosphotyrosine immunoblotting could not detect a major difference between the AhRY9F mutant and wild-type AhR, but a basic isoelectric point shift was detected by two-dimensional gel electrophoresis of AhRY9F. However, an antibody raised to recognize only phosphorylated tyrosine 9 (anti-AhRpY9) confirmed that AhR tyrosine 9 is not a phosphorylated residue required for DRE binding. Kinase assays using synthetic peptides corresponding to the wild-type and mutant AhR residues 1-23 demonstrated that a tyrosine at position 9 is important for substrate recognition at serine(s)/threonine(s) within this sequence by purified protein kinase C (PKC). Also, compared with AhRY9F, immunopurified full-length wild-type receptor was more rapidly phosphorylated by PKC. Furthermore, co-treatment of AhR-deficient cells that expressed AhRY9F and a DRE-driven luciferase construct with phorbol 12-myristate 13-acetate and TCDD resulted in a 30% increase in luciferase activity compared with AhRY9F treated with TCDD alone. Overall, AhR tyrosine 9, which is not a phosphorylated residue itself but is required for DNA binding, appears to play a crucial role in AhR activity by permitting proper phosphorylation of the AhR.     

Expression of phase I and phase II genes in mouse embryonic stem cells cultured in the presence of 2,3,7,8-tetrachlorodibenzo-para-dioxin

Embryonic stem (ES) cells have features that resemble the pluripotent cells of peri-implantation embryos and have been used as an in vitro model to assess the effects of test substances on these stages of development. Here, for the first time, we report on the effects of the xenobiotic 2,3,7,8-tetrachlorodibenzo-para-dioxin (TCDD) on mouse ES cells cultured with TCDD at concentrations ranging from 0.0001 to 100 nM for 15 min to 48 h. TCDD effects were determined by analysing the induction of Cyp1A1, Cyp1A2, Cyp1B1 (phase I) and Nqo1, Gsta1, Ugt1a6 (phase II) genes. Cyp1A1 was the phase I gene most rapidly induced (4 h at 1 nM); Cyp1B1 was induced at 48 h (1 nM), whereas Cyp1A2 expression was not affected. TCDD did not alter phase II gene expression, which remained at basal levels throughout the 48 h of culture. We studied more accurately the expression of Cyp1A1, the earliest gene to respond to the presence of TCDD. We found that: 1) Cyp1A1 gene induction is dependent on the duration of exposure (precisely it is first induced after 3 h of culture at 1 nM, the minimum effective-dose); 2) Cyp1A1 induction requires the continuous presence of TCDD, being interrupted 4 h after removal of the xenobiotic; and 3) induced expression of CYP1A1 protein is dependent on TCDD concentration, the higher the concentration the earlier the production of the enzyme. Furthermore, after 48 h of treatment, TCDD did not promote either apoptosis or changes to the differentiation status of the ES cells. These results are the first important step to investigate the effects of dioxin on the very early stages of mammalian development.     

A dioxin sensitive gene, mammalian WAPL, is implicated in spermatogenesis

2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is an endocrine disruptor that produces a variety of toxic effects. We have isolated a mouse homolog of the hWAPL gene, termed mouse WAPL (mWAPL), as a target of TCDD by cDNA representational difference analysis from mouse embryonic stem cells. A statistically significant increase in mWAPL expression was observed at 0.1 microM TCDD in AhR-/- mouse embryonic fibroblast cells. Interestingly, at 1 microM TCDD, mWAPL mRNA levels decreased in AhR+/+ cells, but further increased in AhR-/- cells. hWAPL and mWAPL were highly expressed only in testes among normal tissue samples, and we observed mWAPL localization in the synaptonemal complex of testicular chromosomes. In addition, mouse testes decreased the expression of mWAPL mRNA after a single intraperitoneal injection of TCDD. Thus, mammalian WAPL such as hWAPL and mWAPL may be involved in spermatogenesis and be target genes mediating the reproductive toxicity induced by TCDD.