Four triazole fungicides used in agricultural or pharmaceutical applications were examined for hepatotoxic effects in mouse liver. Besides organ weight, histopathology, and cytochrome P450 (CYP) enzyme induction, DNA microarrays were used to generate gene expression profiles and hypotheses on potential mechanisms of action for this class of chemicals. Adult male CD-1 mice were exposed daily for 14 days to fluconazole, myclobutanil, propiconazole, or triadimefon at three dose levels by oral gavage. Doses were based on previous studies that resulted in liver hypertrophy or hepatotoxicity. All four triazoles caused hepatocyte hypertrophy, and all except triadimefon increased relative liver/body weight ratios at the middle and high dose levels. CYP enzyme activities were also induced by all four triazoles at the middle and high doses as measured by the dealkylations of four alkoxyresorufins, although some differences in substrate specificity were observed. Consistent with this common histopathology and biochemistry, several CYP and xenobiotic metabolizing enzyme (XME) genes were differentially expressed in response to all four (Cyp2d26 and Cyp3a11), or three of the four (Cyp2c40, Cyp2c55, Ces2, Slco1a4) triazoles. Differential expression of numerous other CYP and XME genes discriminated between the various triazoles, consistent with differences in CYP enzyme activities, and indicative of possible differences in mechanisms of hepatotoxicity or dose response. Multiple isoforms of Cyp1a, 2b, 2c, 3a, and other CYP and XME genes regulated by the nuclear receptors constitutive androstane receptor (CAR) and pregnane X receptor (PXR) were differentially expressed following triazole exposure. Based on these results, we expanded on our original hypothesis that triazole hepatotoxicity was mediated by CYP induction, to include additional XME genes, many of which are modulated by CAR and PXR.

Four triazole fungicides were studied using toxicogenomic techniques to identify potential mechanisms of action. Adult male Sprague-Dawley rats were dosed for 14 days by gavage with fluconazole, myclobutanil, propiconazole, or triadimefon. Following exposure, serum was collected for hormone measurements, and liver and testes were collected for histology, enzyme biochemistry, or gene expression profiling. Body and testis weights were unaffected, but liver weights were significantly increased by all four triazoles, and hepatocytes exhibited centrilobular hypertrophy. Myclobutanil exposure increased serum testosterone and decreased sperm motility, but no treatment-related testis histopathology was observed. We hypothesized that gene expression profiles would identify potential mechanisms of toxicity and used DNA microarrays and quantitative real-time PCR (qPCR) to generate profiles. Triazole fungicides are designed to inhibit fungal cytochrome P450 (CYP) 51 enzyme but can also modulate the expression and function of mammalian CYP genes and enzymes. Triazoles affected the expression of numerous CYP genes in rat liver and testis, including multiple Cyp2c and Cyp3a isoforms as well as other xenobiotic metabolizing enzyme (XME) and transporter genes. For some genes, such as Ces2 and Udpgtr2, all four triazoles had similar effects on expression, suggesting possible common mechanisms of action. Many of these CYP, XME and transporter genes are regulated by xeno-sensing nuclear receptors, and hierarchical clustering of CAR/PXR-regulated genes demonstrated the similarities of toxicogenomic responses in liver between all four triazoles and in testis between myclobutanil and triadimefon. Triazoles also affected expression of multiple genes involved in steroid hormone metabolism in the two tissues. Thus, gene expression profiles helped identify possible toxicological mechanisms of the triazole fungicides.

This study was undertaken to examine the effects of the triazole antifungal agent fluconazole on the expression of hepatic cytochrome P450 (Cyp) genes and the activities of Cyp enzymes in male Sprague–Dawley rats and male CD-1 mice. Alkoxyresorufin O-dealkylation (AROD) methods were used as measures of Cyp enzyme activities. Western analyses identified specific Cyp isoforms. Quantitative real-time reverse-transcription polymerase chain reaction (quantitative real time-RT-PCR) assays were used to quantitate the mRNA expression of specific Cyp genes induced by this conazole. Rats and mice were administered fluconazole 2, 25, or 50mg/kgbw/d by gavage daily for 14 days. In rats, fluconazole treatment (50mg/kgbw/d) significantly induced pentoxyresorufin O-dealkylation (PROD), benzyloxyresorufin O-dealkylation (BROD), and ethoxyresorufin O-dealkylation (EROD) hepatic microsomal activities. Fluconazole treatment significantly increased rat hepatic mRNA expression of CYP2B1 and CYP3A23/3A1 with dose-related responses. The highest dose of fluconazole gave a 128-fold induction of CYP2B1 and a 4.6-fold induction of CYP3A23/3A1 mRNA. CYP3A2 mRNA levels were also overexpressed 5.6–7.2-fold depending on dose. Western immunoblots of rat hepatic microsomal proteins identified Cyp isoforms: CYP1A1, CYP1A2, CYP2B1/2, CYP3A23/3A1, and Cyp3A2 with increased levels of CYP2B1/2 and CYP3A23/3A1 proteins. In mice, fluconazole induced BROD, PROD, EROD, and methoxyresorufin O-dealkylation hepatic microsomal activities after treatment with 25 and 50mg/kgbw/d. Fluconazole increased mouse hepatic mRNA expression of Cyp2b10 (1.9-fold) and Cyp3a11 (2.6-fold) in the 50mg/kgbw/d treatment group. In summary, these results indicated that fluconazole, a triazole-containing conazole, clearly induced CYP2B and CYP3A families of isoforms in rat liver and Cyp2b and Cyp3a families of isoforms in mouse liver.

As part of its mixtures program, the Agency for Toxic Substances and Disease Registry (ATSDR) supports in vitro and limited in vivo toxicity testing to further our understanding of the toxicity and health effects of chemical mixtures. There are increasing concerns that environmental chemicals adversely affect the health of humans and wildlife. These concerns have been augmented by the realization that exposure to chemicals often occurs to mixtures of these chemicals that may exhibit complex synergistic or antagonistic interactions. To address such concerns, we have conducted two studies with techniques that are being used increasingly in experimental toxicology. In the first study, six organochlorine pesticides (4,4 -DDT, 4,4 -DDD, 4,4 -DDE, aldrin, dieldrin, or endrin) were selected from the ATSDR Comprehensive Environmental Response, Compensation and Liability Act of 1980 (or Superfund) priority list and tested for their ability to modulate transcriptional activation of an estrogen-responsive reporter gene in transfected HeLa cells. In these assays, HeLa cells cotransfected with an expression vector encoding estrogen receptor and an estrogen-responsive chloramphenicol acetyltransferase (CAT) reporter plasmid were dosed with and without selected environmental chemicals either individually or in defined combinations. Estradiol consistently elicited 10- to 23-fold dose-dependent inductions in this assay. By contrast, all six of the organochlorine pesticides showed no detectable dose-related response when tested either individually or in binary combinations. Thus, these chemicals as binary mixtures do not exhibit any additional estrogenicity at the levels tested in these assays. In the second study, arsenic [As(V)], cadmium [Cd(II)], chromium [Cr(III, VI)], and lead [Pb(II)] were tested in a commercially developed assay system, CAT-Tox (L), to identify metal-responsive promoters and to determine whether the pattern of gene expression changed with a mixture of these metals. This assay employs a battery of recombinant HepG2 cell lines to test the transcriptional activation capacity of xenobiotics in any of 13 different signal-transduction pathways. Singly, As(V), Cd(II), Cr(III, VI), and Pb(II) produced complex induction profiles in these assays. However, no evidence of synergistic activity was detected with a mixture of Cd(II), Cr(III), and Pb(II). These results have shown metal activation of gene expression through several previously unreported signal-transduction pathways and thus suggest new directions for future studies into their biochemical mechanisms of toxicity. In conclusion, the (italic)in vitro(/italic) methods used in these studies provide insights into complex interactions that occur in cellular systems and could be used to identify biomarkers of exposure to other environmental chemical mixtures.

Toxic metals occur naturally at low concentrations throughout the environment, but are found in higher concentrations at many of the hazardous waste sites on the EPA Superfund list. As part of the Agency for Toxic Substances and Disease Registry (ATSDR) mandate to evaluate the toxicity of metals and mixtures, we chose four of the high-priority metal pollutants from ATSDR's HAZDAT list, including arsenic, cadmium, chromium, and lead, to test in a commercially developed assay system, CAT-Tox(L) (Xenometrix). This assay employs a battery of recombinant HepG2 cell lines to test the transcriptional activation capacity of xenobiotics in any of 13 different signal transduction pathways. Our specific aims were to identify metal-responsive promoters and determine whether the pattern of gene expression changed with a mixture of metals. Humic acid was used in all assays as a carrier to help solubilize the metals and, in all cases, the cells were exposed to the humic acid–metal mixture for 48 h. Humic acid alone, at 50–100 μM, showed moderate activation of the XRE promoter, but little other notable activity. As(V), at doses of 50–250 μM, produced a complex profile of activity showing significant dose-dependent induction of the hMTIIA, GST Ya, HSP70, FOS, XRE, NFκBRE, GADD153, p53RE, and CRE promoters. Pb(II) showed dose-related induction of the GST Ya, XRE, hMTIIA, GRP78, and CYP IA1 promoters at doses in the range of 12–100 μM. Cd(II), at 1.25–15 μM, yielded significant dose-dependent induction of hMTIIA, XRE, CYP IA1, GST Ya, HSP70, NFκBRE, and FOS. Whereas Cr(III) yielded small, though significant inductions of the CRE, FOS, GADD153, and XRE promoters only at the highest dose (750 μM), Cr(VI) produced significant dose-related inductions of the p53RE, FOS, NFκBRE, XRE, GADD45, HSP70, and CRE promoters at much lower doses, in the range of 5–10 μM. Assays testing serial dilutions of a mixture comprising 7.5 μM Cd(II), 750 μM Cr(III), and 100 μM Pb(II) (the combination of metals most frequently found at National Priority List sites) showed significant dose-dependent induction of the hMTIIA promoter, but failed to show dose-related induction of any other promoter and showed no evidence of synergistic activation of gene expression by the metals in this mixture. Our results thus show metal activation of gene expression through several previously unreported signal transduction pathways, including As(V) induction of GST Ya, FOS, XRE, NFkBRE, GADD153, p53RE, and CRE; Pb(II) induction of GST Ya, XRE, Cyp IA1, and GADD153; Cd(II) induction of NFkBRE, Cyp IA1, XRE, and GST Ya; and Cr(VI) induction of p53RE, XRE, GADD45, HSP70, and CRE promoters, and thus suggest new insights into the biochemical mechanisms of toxicity and carcinogenicity of metals. It is also an important finding that no evidence of synergistic activity was detected with the mixture of Cd(II), Cr(III), and Pb(II) tested in these assays.

There have been increasing concerns that environmental chemicals may adversely affect the health of humans and wildlife by acting as endocrine modulators. These concerns have been augmented by the realization that human exposure occurs not just to single chemical agents, but typically to mixtures of chemicals that could exhibit estrogenic activity qualitatively and/or quantitatively different from that of individual components. To address these concerns, we have evaluated the ability of six organochlorine pesticides (4,4′-DDT, 4,4′-DDD, 4,4′-DDE, aldrin, dieldrin, or endrin, all classified high priority by ATSDR) to modulate transcriptional activation of an estrogen-responsive reporter gene in transfected HeLa cells. In these assays, HeLa cells cotransfected with an expression vector encoding estrogen receptor and an estrogen-responsive chloramphenicol acetyltransferase (CAT) reporter plasmid were exposed to these pesticides individually and in defined combinations. While estradiol consistently elicited 10- to 23-fold dose-dependent inductions in these assays, the six organochlorine pesticides showed no detectable dose-related response when tested individually. When tested in binary combinations, the pesticide mixtures showed no additional estrogenicity. Thus, the pesticides tested, singly or as mixtures, showed virtually no evidence of estrogenicity.

Because of rampant concern that estrogenic chemicals in the environment may be adversely affecting the health of humans and wildlife, reliable methods for detecting and characterizing estrogenic chemicals are needed. It is important that general agreement be reached on which tests to use and that these tests then be applied to the testing of both man-made and naturally occurring chemicals. As a step toward developing a comprehensive approach to screening chemicals for estrogenic activity, three assays for detecting estrogenicity were conducted on 10 chemicals with known or suspected estrogenic activity. The assays were 1) competitive binding with the mouse uterine estrogen receptor, 2) transcriptional activation in HeLa cells transfected with plasmids containing an estrogen receptor and a response element, and 3) the uterotropic assay in mice. The chemicals studied were 17 beta-estradiol, diethylstilbestrol, tamoxifen, 4-hydroxytamoxifen, methoxychlor, the methoxychlor metabolite 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE), endosulfan, nonylphenol, o,p'-DDT, and kepone. These studies were conducted to assess the utility of this three-assay combination in the routine screening of chemicals, or combinations of chemicals, for estrogenic activity. Results were consistent among the three assays with respect to what is known about the estrogenic activities of the chemicals tested and their requirements for metabolic activation. By providing information on three levels of hormonal activity (receptor binding, transcriptional activation, and an in vivo effect in an estrogen-responsive tissue), an informative profile of estrogenic activity is obtained with a reasonable investment of resources.

Numerous xenobiotics regulate cellular functions by altering transcription of target genes, Use of sensitive and specific biomarkers based on gene transcript levels may help clarify the shape of the dose-response curve in the low-dose region associated with human exposures to environmental concentrations of chemicals. We have quantified gene transcription induced by 2,3,7,8-tetrachlorodibenzo-p-dioxin in both animal models and humans with the use of Northern analysis and PCR-based methods, In addition, we describe a rapid and sensitive in vitro assay that we have used to screen chemicals and biological samples for their ability to alter gene transcription. Whereas some of the endpoints in our studies such as cytochrome P-450 1A1 are predictive indicators of exposure and dose, other gene responses such as growth factors are more complex and represent a critical event, progression, or adaptation to a pathological alteration. In conclusion, measurement of toxicant-induced gene transcription will contribute to the usefulness of biomarkers in addressing issues of human health and environmentally induced disease.

Gene transcription mediated by steroid hormones has become one of the most extensively characterized model systems for studying the regulation of gene expression in eukaryotic cells. However, specific details of gene regulation by steroid hormones are often complex and may be unique in specific cell types. Diverse regulatory mechanisms leading to either activation or repression of particular genes frequently involve interactions between steroid hormone receptors and other ubiquitous and/or cell-specific transcription factors that act on the complex promoter of the regulated gene. Interplay between steroid receptor-mediated and other signal transduction pathways may also be involved. In addition, recent novel results indicate that moderate variations in the intracellular concentration of pyridoxal 5'-phosphate (PLP), the biologically active form of vitamin B6, can have pronounced modulatory effects on steroid-induced gene expression. Specifically, elevation of intracellular PLP levels leads to decreased transcriptional responses to glucocorticoid, progesterone, androgen, or estrogen hormones. Conversely, cells in a vitamin B6-deficient state exhibit enhanced responsiveness to steroid hormones. One aspect of the mechanism by which these transcriptional modulatory effects of PLP occur has recently been shown to involve interruption of functional interactions between steroid hormone receptors and the nuclear transcription factor NF1. These findings--that the vitamin B6 nutritional status of cells modulates their capacity to respond to steroid hormones--impose an additional level of cell-specific control over steroid hormone regulation of gene expression and will serve as the focal point for this review.

This chapter describes the protein-blotting procedures for evaluating the interactions of steroids receptors with DNA. Selective binding of steroid hormone receptors to hypoxia response element (HRE)-containing DNA fragments has been demonstrated by a variety of techniques for the study of DNA–protein interaction, including DNA–cellulose competitive binding, nitrocellulose filter binding, gel retardation, sucrose gradient shift, DNA footprinting (nuclease protection), and methylation interference assays, in addition to Southwestern blotting. Each of these techniques has its own set of advantages and limitations. Southwestern blotting, unlike nuclease protection or methylation interference studies, does not require the prior purification of the DNA-binding protein and can be used to study DNA–protein interactions in crude cellular extracts or in partially purified protein preparations at any stage of purification. Southwestern blotting offers further advantages in that once a protein extract has been electrophoretically separated and finally immobilized on a nitrocellulose filter, proteins of interest can potentially be characterized by a number of criteria, including relative mobility on the sodium dodecyl sulfate (SDS)-polyacrylamide gel, isoelectric point on two-dimensional gels, DNA-binding activity, ligand binding, or immunoreactivity, if antibodies for the protein are available.

Sucrose density gradient shift assays were adapted to permit determination of the affinity of interaction between human glucocorticoid receptors (GR) and DNA under conditions of DNA excess. Saturation analyses were performed to ascertain dissociation constants for the interaction of activated human GR with each of five DNA fragments. Centrifugation of GR-DNA complexes on sucrose gradients under nearly isotonic salt conditions revealed similar affinities with dissociation constants in the range of 2-16 nM for GR interaction with DNA fragments containing glucocorticoid response elements (GREs) exhibiting partial dyad symmetry. By contrast, GR exhibited virtually no affinity for non-GRE-containing DNA or for DNA containing only GRE half-sites. Additionally, GR showed evidence of multiple-site interaction with a DNA fragment containing two partially symmetric GREs, but interacted at only one site of an MMTV LTR DNA fragment containing a single partially symmetric GRE along with a cluster of three half-GREs. Together these data indicate that under physiologically relevant conditions, glucocorticoid receptors have high selectivity and affinity only for DNA containing specific partially symmetric GREs and further suggest that this high affinity for such DNA sites may be sufficient to account for the selective regulation of gene expression observed in glucocorticoid-responsive cells.

Sucrose density gradient shift assays were used to study the interactions of human glucocorticoid receptors (GR) with small DNA fragments either containing or lacking glucocorticoid response element (GRE) DNA consensus sequences. When crude cytoplasmic extracts containing [3H]triamcinolone acetonide [( 3H]TA) labeled GR were incubated with unlabeled DNA under conditions of DNA excess, a GRE-containing DNA fragment obtained from the 5' long terminal repeat of mouse mammary tumor virus (MMTV LTR) formed a stable 12-16S complex with activated, but not nonactivated, [3H]TA receptor. By contrast, if the cytosols were treated with calf thymus DNA-cellulose to deplete non-GR-DNA-binding proteins prior to heat activation, a smaller 7-10S complex was formed with the MMTV LTR DNA fragment. When similar experiments were conducted under conditions of large receptor excess, using 3' [32P]-MMTV LTR DNA, the trace quantity of DNA formed a stable 10-14S complex with DNA-cellulose pretreated cytosols or with untreated cytosols in the presence of excess Escherichia coli competitor DNA. If trace quantities of the 3' [32P]-MMTV LTR DNA were incubated with untreated crude cytosols, much larger complexes were formed, indicating the association of other cytosolic proteins with the MMTV LTR DNA fragment. Activated [3H]TA receptor from DNA-cellulose pretreated cytosols also interacted with two similarly sized fragments from pBR322 DNA, but with lower apparent affinities in the order MMTV LTR DNA fragment much greater than pBR322 fragment containing a single GRE DNA consensus sequence greater than non-GRE-containing pBR322 fragment.(ABSTRACT TRUNCATED AT 250 WORDS)

Glucocorticoids, members of the highly conserved steroid hormone family in evolution, exert numerous physiological effects on the developmental and adaptational processes of eukaryotic organisms. In general, free circulating glucocorticoids released from the adrenal cortex in response to adrenocorticotropic hormone (ACTH) from the pituitary enter target cells by a passive diffusion process conferred by the high lipid solubility common to all steroids. Although there have been some reports on membrane effects of steroid hormones, actions of steroid hormones appear to be largely mediated by their intracellular receptors. These receptors act much like ligand-dependent transcription factors that regulate gene expression. The magnitude of steroid hormone responses, therefore, is determined not only by the hormone concentration but also by cellular levels of functional receptor proteins. Proposed models for the structure of the glucocorticoid receptor (GR) have the common feature that the receptor exists as an oligomeric protein complex that consists of one or more subunits complexed with non-steroid-binding proteins such as the heat shock protein 90 (hsp90). Dissociation of the oligomeric complex takes place following binding of the hormone and permits translocation of the steroid-receptor complex into the nucleus where it associates with enhancer-like glucocorticoid response elements (GREs) in the genome. This could either induce the expression of normally silent genes or change the transcription of constitutively expressed housekeeping genes (such as the GR gene itself) by up- or down-regulation. Thus to fully understand the mechanism underlying glucocorticoid action, the study of GR autoregulation becomes an imperative issue.

A computer search of the pBR322 DNA sequence identified five sites matching reported glucocorticoid regulatory element (GRE) DNA consensus sequences and three related sites. A pBR322 DNA fragment containing one GRE site was shown to bind immobilized HeLa S3 cell glucocorticoid receptor and to compete for receptor binding in a competitive binding assay. Conversely, a pBR322 DNA fragment devoid of GRE sites showed barely detectable interaction with glucocorticoid receptor in either of these assays. These results demonstrate the importance of GRE consensus sequences in glucocorticoid receptor interactions with DNA, and further identify a cause for high background binding observed when pBR322 DNA is used as a negative control in studies of glucocorticoid receptor-DNA interactions.

To exert their effects, glucocorticoid receptor complexes interact selectively with DNA sequences known as glucocorticoid regulatory elements. We have studied the interaction between human glucocorticoid receptors and mouse mammary tumor virus (MMTV) DNA by means of a procedure that permits analysis after immobilization of the receptor on nitrocellulose. Proteins from crude cytosolic or nuclear extracts were electrophoresed on NaDodSO4/PAGE gels, soaked in a urea buffer to remove NaDodSO4, transferred to nitrocellulose, and probed with nick-translated MMTV [32P]DNA in a 5% nonfat dry milk buffer, which minimizes nonselective DNA-protein interactions. We present evidence that MMTV [32P]DNA interacts selectively with the glucocorticoid receptor. These data include comigration of [3H]dexamethasone mesylate-labeled band and bound MMTV [32P]DNA on gel electrophoresis systems; localization of DNA-binding activity in the cytosol of cells incubated with steroid at 0 degrees C and in the nucleus and cytosol of cells incubated at 37 degrees C; binding of the MMTV DNA to highly purified receptor; and absence of MMTV DNA binding activity in extracts from cells whose receptor has been down-regulated. Furthermore, glucocorticoid receptors analyzed under these conditions exhibit selective binding to DNA fragments that contain glucocorticoid regulatory elements.

Glucocorticoids negatively regulate expression of the human proopiomelanocortin (POMC) gene. It has been postulated that this effect may be modulated by a direct interaction of the glucocorticoid receptor (GR) with DNA in the vicinity of the POMC promoter. In order to investigate interactions of GR with POMC DNA, DNA-cellulose competitive binding assays have been performed using isolated fragments of cloned POMC DNA to compete with calf thymus DNA-cellulose for binding of triamcinolone acetonide affinity-labelled GR prepared from HeLa S/sub 3/ cells. In these assays, two fragments isolated from the 5' flanking sequences of POMC DNA (Fragment 3,-1765 to -677 and Fragment 4, -676 to +125 with respect to the mRNA cap site) have competed favorably, with Fragment 3 consistently competing more strongly than Fragment 4. Additional studies have been conducted utilizing a newly developed South-western Blot procedure in which specific /sup 32/P-labelled DNA fragments are allowed to bind to dexamethasone mesylate labelled GR immobilized on nitrocellulose filters. Results from these studies have also shown preferential binding by POMC DNA fragments 3 and 4. DNA footprinting and gene transfer experiments are now being conducted to further characterize the nature of GR interaction with POMC DNA.