Weak Aryl Hydrocarbon Receptor Agonist Research Articles

Tryptophan depletion sensitizes the AHR pathway by increasing AHR expression and GCN2/LAT1-mediated kynurenine uptake, and potentiates induction of regulatory T lymphocytes

BackgroundIndoleamine 2,3-dioxygenase 1 (IDO1) and tryptophan-dioxygenase (TDO) are enzymes catabolizing the essential amino acid tryptophan into kynurenine. Expression of these enzymes is frequently observed in advanced-stage cancers and is associated...

Exposure to retene, fluoranthene, and their binary mixture causes distinct transcriptomic and apical outcomes in rainbow trout (Oncorhynchus mykiss) yolk sac alevins.

Polycyclic aromatic hydrocarbons (PAHs) are widely spread environmental contaminants which affect developing organisms. It is known that improper activation of the aryl hydrocarbon receptor (AhR) by some PAHs contributes to toxicity, while other PAHs can disrupt cellular membrane function. The exact downstream mechanisms of AhR activation remain unresolved, especially with regard to cardiotoxicity. By exposing newly hatched rainbow trout alevins (Oncorhynchus mykiss) semi-statically to retene (32µg l-1; AhR agonist), fluoranthene (50µg l-1; weak AhR agonist and CYP1a inhibitor) and their binary mixture for 1, 3, 7 and 14 days, we aimed to uncover novel mechanisms of cardiotoxicity using a targeted microarray approach. At the end of the exposure, standard length, yolk area, blue sac disease (BSD) index and PAH body burden were measured, while the hearts were prepared for microarray analysis. Each exposure produced a unique toxicity profile. We observed that retene and the mixture, but not fluoranthene, significantly reduced growth by Day 14 compared to the control, while exposure to the mixture increased the BSD-index significantly from Day 3 onward. Body burden profiles were PAH-specific and correlated well with the exposure-specific upregulations of genes encoding for phase I and II enzymes. Exposure to the mixture over-represented pathways related to growth, amino acid and xenobiotic metabolism and oxidative stress responses. Alevins exposed to the individual PAHs displayed over-represented pathways involved in receptor signaling: retene downregulated genes with a role in G-protein signaling, while fluoranthene upregulated those involved in GABA signaling. Furthermore, exposure to retene and fluoranthene altered the expression of genes encoding for proteins involved in calcium- and potassium ion channels, which suggests affected heart structure and function. This study provides deeper understanding of the complexity of PAH toxicity and the necessity of investigating PAHs as mixtures and not as individual components.

5-Aminosalicylic Acid, A Weak Agonist for Aryl Hydrocarbon Receptor That Induces Splenic Regulatory T Cells

Introduction: 5-Aminosalicylic acid (5-ASA) is widely used as a key drug in inflammatory bowel disease. It has been recently reported that 5-ASA induces CD4 + Foxp3 + regulatory T cells (Tregs) in the colon via the aryl hydrocarbon receptor (AhR), a ligand-activated transcription factor that regulates inflammation. However, the role of 5-ASA as an AhR agonist that induces Tregs in the spleen remains unknown. Methods: In the present study, we investigated these themes using an AhR-mediated transactivation assay and flow cytometry analysis. The experiments were conducted by using DR-EcoScreen cells and C57BL/6 mice. Results: The DR-EcoScreen cell-based transactivation assay revealed that 5-ASA acted as a weak AhR agonist at concentrations of ≥300 μM (1.31–1.45-fold), and that a typical AhR agonist, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), activated AhR at a concentration of 0.1 nM (22.8-fold). In addition, the treatment of mouse splenic cells with 300 μM 5-ASA in a primary culture assay significantly induced CD4+CD25 + Foxp3 + Tregs (control vs. 5-ASA: 9.0% vs. 12.65%, p < 0.05), while 0.1 nM TCDD also showed significant induction of Tregs (control vs. TCDD: 9.0% vs. 14.1%, p < 0.05). Interestingly, this induction was eliminated by co-treatment with an AhR antagonist, CH-223191. Discussion: These results suggest that 5-ASA is a weak agonist of AhR and thereby induces Tregs in spleen cells. Our findings may provide useful insights into the mechanism by which 5-ASA regulates inflammation.

Exposure to Heptachlorodibenzo-p-dioxin (HpCDD) Regulates microRNA Expression in Human Lung Fibroblasts.

Benzo(ghi)perylene (BghiP) and 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (HpCDD) were elevated in serum from personnel deployed to sites with open burn pits. Here, we investigated the ability of BghiP and HpCDD to regulate microRNA (miRNA) expression through the aryl hydrocarbon receptor (AHR). Human lung fibroblasts (HLFs) were exposed to BghiP and HpCDD. AHR activity was measured by reporter assay and gene expression. Deployment related miRNA were measured by quantitative polymerase chain reaction. AHR expression was depleted using siRNA. BghiP displayed weak AHR agonist activity. HpCDD induced AHR activity in a dose-dependent manner. Let-7d-5p, miR-103-3p, miR-107, and miR-144-3p levels were significantly altered by HpCDD. AHR knockdown attenuated these effects. These studies reveal that miRNAs previously identified in sera from personnel deployed to sites with open burn pits are altered by HpCDD exposure in HLFs.

Editor's Highlight: Microbial-Derived 1,4-Dihydroxy-2-naphthoic Acid and Related Compounds as Aryl Hydrocarbon Receptor Agonists/Antagonists: Structure-Activity Relationships and Receptor Modeling.

1,4-Dihydroxy-2-naphthoic acid (1,4-DHNA) is a bacterial-derived metabolite that binds the aryl hydrocarbon receptor (AhR) and exhibits anti-inflammatory activity in the gut. The structure-dependent AhR activity of hydroxyl/carboxy-substituted naphthoic acids (NAs) was determined in young adult mouse colonic (YAMC) cells and human Caco2 colon cancer cells using CYP1A1/CYP1B1 mRNAs as Ah-responsive genes. Compounds used in this study include 1,4-, 3,5-, and 3,7-DHNA, 1,4-dimethoxy-2-naphthoic acid (1,4-DMNA), 1- and 4-hydroxy-2-naphthoic acid (1-HNA, 4-HNA), 1- and 2-naphthoic acid (1-NA, 2-NA), and 1- and 2-naphthol (1-NOH, 2-NOH). 1,4-DHNA was the most potent compound among hydroxyl/carboxy naphthalene derivatives, and the fold induction response for CYP1A1 and CYP1B1 was similar to that observed for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in YAMC and Caco2 cells. 1- and 4-HNA were less potent than 1,4-DHNA but induced maximal (TCDD-like) response for CYP1B1 (both cell lines) and CYP1A1 (Caco2 cells). With the exception of 1- and 2-NA, all compounds significantly induced Cyp1b1 in YAMC cells and these responses were not observed in AhR-deficient YAMC cells generated using CRISPR/Cas9 technology. In addition, we also observed that 1- and 2-NOH (and 1,4-DHNA) were weak AhR agonists, and 1- and 2-NOH also exhibited partial AhR antagonist activity. Structure-activity relationship studies for CYP1A1 but not CYP1B1 were similar in both cell lines, and CYP1A1 induction required one or both 1,4-dihydroxy substituents and activity was significantly enhanced by the 2-carboxyl group. We also used computational analysis to show that 1,4-DHNA and TCDD share similar interactions within the AhR binding pocket and differ primarily due to the negatively charged group of 1,4-DHNA.

Embryonic cardiotoxicity of weak aryl hydrocarbon receptor agonists and CYP1A inhibitor fluoranthene in the Atlantic killifish (Fundulus heteroclitus)

High affinity aryl hydrocarbon receptor (AHR) ligands, such as certain polychlorinated biphenyls and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), cause severe cardiac teratogenesis in fish embryos. Moderately strong AHR agonists, for example benzo[a]pyrene and β-naphthoflavone, are capable of causing similar cardiotoxic effects, particularly when coupled with cytochrome P450 1A (CYP1A) inhibitors (e.g., fluoranthene (FL). Additionally, some weaker AHR agonists (carbaryl, 2-methylindole, 3-methylindole, and phenanthrene) are known to also cause cardiotoxicity in zebrafish (Danio rerio) embryos when coupled with FL; however, the cardiotoxic effects were not mediated specifically by AHR stimulation. This study was performed to determine if binary exposure to weak AHR agonists and FL were also capable of causing cardiotoxicity in Atlantic killifish Fundulus heteroclitus embryos. Binary exposures were performed in both naïve and PAH-adapted killifish embryos to examine resistance to weak agonists and FL binary exposures. Weak agonists used in this study included the following: carbaryl, phenanthrene, 2-methylindole, 3-methylindole, indigo, and indirubin. Carbaryl, indigo, and indirubin induced the highest CYP1 activity levels in naïve killifish embryos, but no significant CYP1 induction was observed in the PAH-adapted killifish.Embryos were coexposed to subteratogenic levels of each agonist and 500μg/L FL to assess if binary administration could cause cardiotoxicity. Indigo and indirubin coupled with FL caused cardiac teratogenesis in naïve killifish, but coexposures did not produce cardiac chamber abnormalities in the PAH-adapted population. Knockdown of AHR2 in naïve killifish embryos did not prevent cardiac teratogenesis. The data suggest a unique mechanism of cardiotoxicity that is not driven by AHR2 activation.

Ligand-Specific Transcriptional Mechanisms Underlie Aryl Hydrocarbon Receptor-Mediated Developmental Toxicity of Oxygenated PAHs.

Polycyclic aromatic hydrocarbons (PAHs) are priority environmental contaminants that exhibit mutagenic, carcinogenic, proinflammatory, and teratogenic properties. Oxygen-substituted PAHs (OPAHs) are formed during combustion processes and via phototoxidation and biological degradation of parent (unsubstituted) PAHs. Despite their prevalence both in contaminated industrial sites and in urban air, OPAH mechanisms of action in biological systems are relatively understudied. Like parent PAHs, OPAHs exert structure-dependent mutagenic activities and activation of the aryl hydrocarbon receptor (AHR) and cytochrome p450 metabolic pathway. Four-ring OPAHs 1,9-benz-10-anthrone (BEZO) and benz(a)anthracene-7,12-dione (7,12-B[a]AQ) cause morphological aberrations and induce markers of oxidative stress in developing zebrafish with similar potency, but only 7,12-B[a]AQ induces robust Cyp1a protein expression. We investigated the role of the AHR in mediating the toxicity of BEZO and 7,12-B[a]AQ, and found that knockdown of AHR2 rescued developmental effects caused by both compounds. Using RNA-seq and molecular docking, we identified transcriptional responses that precede developmental toxicity induced via differential interaction with AHR2. Redox-homeostasis genes were affected similarly by these OPAHs, while 7,12-B[a]AQ preferentially activated phase 1 metabolism and BEZO uniquely decreased visual system genes. Analysis of biological functions and upstream regulators suggests that BEZO is a weak AHR agonist, but interacts with other transcriptional regulators to cause developmental toxicity in an AHR-dependent manner. Identifying ligand-dependent AHR interactions and signaling pathways is essential for understanding toxicity of this class of environmentally relevant compounds.

Zebrafish cardiotoxicity: the effects of CYP1A inhibition and AHR2 knockdown following exposure to weak aryl hydrocarbon receptor agonists.

The aryl hydrocarbon receptor (AHR) is a ligand-activated transcription factor that mediates many of the toxic effects of dioxin-like compounds (DLCs) and some polycyclic aromatic hydrocarbons (PAHs). Strong AHR agonists, such as certain polychlorinated biphenyls and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), cause severe cardiac teratogenesis in fish embryos. Moderately strong AHR agonists, such as benzo[a]pyrene and β-naphthoflavone, have been shown to cause similar cardiotoxic effects when coupled with a cytochrome P450 1A (CYP1A) inhibitor, such as fluoranthene (FL). We sought to determine if weak AHR agonists, when combined with a CYP1A inhibitor (FL) or CYP1A morpholino gene knockdown, are capable of causing cardiac deformities similar to moderately strong AHR agonists (Wassenberg and Di Giulio Environ Health Perspect 112(17):1658-1664, 2004a; Wassenberg and Di Giulio Res 58(2-5):163-168, 2004b; Billiard et al. Toxicol Sci 92(2):526-536, 2006; Van Tiem and Di Giulio Toxicol Appl Pharmacol 254(3):280-287, 2011). The weak AHR agonists included the following: carbaryl, phenanthrene, 2-methylindole, 3-methylindole, indigo, and indirubin. Danio rerio (zebrafish) embryos were first exposed to weak AHR agonists at equimolar concentrations. The agonists were assessed for their relative potency as inducers of CYP1 enzyme activity, measured by the ethoxyresorufin-O-deethylase (EROD) assay, and cardiac deformities. Carbaryl, 2-methylindole, and 3-methylindole induced the highest CYP1A activity in zebrafish. Experiments were then conducted to determine the individual cardiotoxicity of each compound. Next, zebrafish were coexposed to each agonist (at concentrations below those determined to be cardiotoxic) and FL in combination to assess if CYP1A inhibition could induce cardiac deformities. Carbaryl, 2-methylindole, 3-methylindole, and phenanthrene significantly increased pericardial edema relative to controls when combined with FL. To further evaluate the interaction of the weak AHR agonists and CYP1A inhibition, a morpholino was used to knockdown CYP1A expression, and embryos were then exposed to each agonist individually. In embryos exposed to2-methylindole, CYP1A knockdown caused a similar level of pericardial edema to that caused by exposure to2-methylindole and FL.The results showed a complex pattern of cardiotoxic response to weak agonist inhibitor exposure and morpholino-knockdown. However, CYP1A knockdown in phenanthrene and 3-methylindole only moderately increased pericardial edema relative to coexposure to FL. AHR2 expression was also knocked down using a morpholino to determine its role in mediating the observed cardiac teratogenesis. Knockdown of AHR2 did not rescue the pericardial edema as previously observed with strong AHR agonists. While some of the cardiotoxicity observed may be attributed to the combination of weak AHR agonism and CYP1A inhibition, other weak AHR agonists appear to be causing cardiotoxicity through an AHR2-independent mechanism. The data show that CYP1A is protective of the cardiac toxicity associated with weak AHR agonists and that knockdown can generate pericardial edema, but these findings are also suggestive of differing mechanisms of cardiac toxicity among known AHR agonists.

Combustion derived ultrafine particles induce cytochromeP-450 expression in specific lung compartments in the developing neonatal and adult rat

Vehicle exhaust is rich in polycyclic aromatic hydrocarbons (PAH) and can be a dominant contributor to ultrafine urban particulate matter (PM). Exposure to ultrafine PM is correlated with respiratory infections and asthmatic symptoms in young children. The lung undergoes substantial growth, alveolarization, and cellular maturation within the first years of life, which may be impacted by environmental pollutants such as PM. PAHs in PM can serve as ligands for the aryl hydrocarbon receptor (AhR) that induces expression of certain isozymes in the cytochrome P-450 superfamily, such as CYP1A1 and CYP1B1, localized in specific lung cell types. Although AhR activation and induction has been widely studied, its context within PM exposure and impact on the developing lung is poorly understood. In response, we have developed a replicable ultrafine premixed flame particle (PFP) generating system and used in vitro and in vivo models to define PM effects on AhR activation in the developing lung. We exposed 7-day neonatal and adult rats to a single 6-h PFP exposure and determined that PFPs cause significant parenchymal toxicity in neonates. PFPs contain weak AhR agonists that upregulate AhR-xenobiotic response element activity and expression and are capable inducers of CYP1A1 and CYP1B1 expression in both ages with different spatial and temporal patterns. Neonatal CYP1A1 expression was muted and delayed compared with adults, possibly because of differences in the enzyme maturation. We conclude that the inability of neonates to sufficiently adapt in response to PFP exposure may, in part, explain their susceptibility to PFP and urban ultrafine PM.

Low-level pyrene exposure causes cardiac toxicity in zebrafish (Danio rerio) embryos

It is widely accepted that the most abundant polycyclic aromatic hydrocarbons (PAHs) in weathered crude oils is cardiotoxic. Although PAHs toxic endpoints show strong correlation with the aryl hydrocarbon receptor (AhR), a ligand activated transcription factor, and is thought to be a potent inducer of cytochrome P4501A, the action mechanism of PAHs on vertebrate cardiovascular development and disease is unclear. Herein, we address the cardiac developmental effects of exposure to the weak AhR agonist pyrene on the early life-stages of zebrafish. Embryos were exposed to 0, 0.05, 0.5, 5, and 50nmol/L pyrene up to 72h post-fertilization (hpf). Pyrene-treated embryos showed dose-dependent heart abnormalities, such as pericardial edema and cardiac looping defects. Changes in AhR1a, AhR1b, AhR2, and Cyp1A expression were assessed by real-time RT-PCR. The results showed that low-level pyrene failed to alter these genes expression. However, the homeodomain transcription factor Nkx2.5, which plays an essential role in the development of the cardiovascular system, was down-regulated in a dose-dependent manner by pyrene exposure. The bone morphogenetic protein 2b (Bmp2b), which has been identified as the upstream gene of Nkx2.5, also was inhibited in a dose-dependent manner after treatment with pyrene. Taken together, these data indicated that embryonic exposure of zebrafish to low-level environmental pyrene disrupt normal cardiac development and alter expression of defective cardiac differentiation related genes.

Fundulus heteroclitus adapted to PAHs are cross-resistant to multiple insecticides

Atlantic killifish (Fundulus heteroclitus) from the Atlantic Wood Superfund site on the Elizabeth River (ER), VA are dramatically resistant to the acute toxicity and teratogenesis caused by polycyclic aromatic hydrocarbons (PAHs). To understand the consequences of adaptation to chronic PAH pollution, we have attempted to further define the chemical tolerance associated with this resistance. An important component of the PAH adaptation of ER fish is the dramatic down-regulation of the aryl hydrocarbon receptor (AHR) pathway, resulting in decreased cytochrome p450 (CYP) 1 activity. Herein, we compared the susceptibility to several insecticides of ER fish to that of reference site (King's Creek; KC) fish; use of these chemicals as probes of the resistance will help to demonstrate if the contaminant adaptation exhibited by ER fish is broad or narrow and AHR-focused. We hypothesized that ER fish would be less susceptible to the organophosphate chlorpyrifos (activated by CYP) and more susceptible to the pyrethroid permethrin (detoxified by CYP). Comparison of acute toxicity in 5-day-old larvae supported this hypothesis for chlorpyrifos. As expected, chemical up-regulation of CYP by co-exposure to β-naphthoflavone (BNF) enhanced the susceptibility of KC but it did not affect ER larvae. Unexpectedly, ER larvae were much less susceptible to permethrin than KC larvae. However, co-exposure to BNF greatly decreased the susceptibility of KC larvae, indicating that metabolism of permethrin by CYP was protective. Additionally, fish from each population were compared for susceptibility to the carbamate carbaryl, an acute neurotoxicant and weak AHR agonist that induces teratogenesis similar to that caused by PAHs. ER embryos and larvae were less susceptible than KC fish. These results suggest that the adaptive phenotype of ER fish is multi-faceted and that aspects other than CYP response are likely to greatly affect their response to contaminants.

Molecular and developmental effects of exposure to pyrene in the early life-stages of Cyprinodon variegatus

Polycyclic aromatic hydrocarbons (PAHs) have been connected to developmental toxicity in the early life-stages of many species by their ability to bind to the aryl hydrocarbon receptor (AHR), which dimerizes with ARNT (AHR nuclear translocator) to induce transcription of genes such as CYP1A1. ARNT also dimerizes with HIF (hypoxia-inducible factor α) to induce transcription of genes such as VEGF (vascular endothelial growth factor), suggesting that PAHs may interfere with transcription of VEGF by competing for ARNT. Herein, we address the molecular and developmental effects of exposures to the weak AHR agonist pyrene on the early life-stages of the sheepshead minnow Cyprinodon variegatus. Embryos were exposed under flow-through conditions to 0, 20, 60, or 150 ppb pyrene up to 432 hours post-fertilization (hpf). RNA was extracted at 5 time points (12, 24, 48, 96, and 432 hpf) and changes in CYP1A1 and VEGF expression were assessed by real-time RT-PCR. Since few genes have been documented for the sheepshead minnow, we first cloned and sequenced CYP1A1, VEGF and internal standard 18S rRNA. Pyrene significantly induced the AHR-regulated gene, CYP1A1, in a time- and dose-dependent manner, while pyrene failed to alter the HIF-regulated gene, VEGF. However, VEGF was found to change during various stages of normal development in this study. Although a normal hatch time (5 dpf) was observed for all treatments, pyrene-treated embryos showed dose-dependent abnormalities such as severe dorsal body curvature, mild pericardial and yolk-sac edema, and increased mortality. Taken together, these data indicate that embryonic exposure of sheepshead minnows to pyrene disrupts normal development and alters expression of an AHR/ARNT-regulated gene. In addition, embryonic exposure to pyrene failed to provide evidence of possible AHR-HIF pathway cross-talk since developmental expression of VEGF was unaltered.

The environmental carcinogen benzo[a]pyrene induces expression of monocyte-chemoattractant protein-1 in vascular tissue: a possible role in atherogenesis

Exposure to carcinogenic polycyclic aromatic hydrocarbons (PAHs) has been implicated in the aetiology of atherosclerosis. Previously we showed that chronic exposure of ApoE−/− mice to the prototype PAH benzo[a]pyrene (B[a]P) causes enhanced progression of atherosclerosis, which was characterised by an increased inflammatory cell content in the atherosclerotic plaques. The aim of the present study was to evaluate the effect of B[a]P on vascular expression of monocyte-chemoattractant protein 1 (MCP-1), which is a crucial molecule promoting the recruitment of monocytes into atherosclerotic lesions. We hypothesised that B[a]P-induced expression of MCP-1 is mediated through aryl hydrocarbon receptor (AhR) activation. Initially we performed in vivo studies showing that acute treatment with B[a]P induces MCP-1 gene expression in aortic tissue of ApoE−/− mice. These observations could be confirmed by in vitro studies with human endothelial cells (RF24 cell line and primary HUVEC), showing a dose- and time-dependent increase in MCP-1 expression upon exposure to B[a]P. This was paralleled by an induction of cytochrome P450 1A1 and 1B1, indicating Ah receptor activation. No increased gene expression (MCP-1, CYP1A1 and 1B1) was found upon incubation with the structural isomer benzo[e]pyrene, which is a weak AhR agonist. Moreover, B[a]P-induced MCP-1 gene and protein expression was inhibited by co-treatment with the AhR antagonist α-naphthoflavone. In addition to its effect on basal gene expression, we showed that B[a]P significantly enhanced TNFα-induced expression of MCP-1. We were unable to block B[a]P-induced MCP-1 expression by antioxidant treatment. In contrast, we found that addition of N-acetylcysteine or vitamin C enhanced transcription of MCP-1 by B[a]P. In conclusion, our studies revealed potent vascular pro-inflammatory effects of B[a]P, as evidenced by AhR-mediated induction of MCP-1. These observations further contribute to the concept that induction of inflammation is a crucial process in PAH-enhanced atherogenesis.

3 ′-Methoxy-4 ′-nitroflavone, a reported aryl hydrocarbon receptor antagonist, enhances Cyp1a1 transcription by a dioxin responsive element-dependent mechanism

The aryl hydrocarbon receptor (AhR) is a ligand-activated transcription factor, regulating expression of a group of specific genes including cytochrome P450 1A1 (Cyp1a1). Stably transfected luciferase with dioxin responsive elements (DRE) in its promoter region has been commonly used as a reporter gene to study the mechanism of AhR signaling and compare potencies of TCDD and related compounds. However, how these two genes might respond to structurally diverse AhR ligands was unknown. This study investigates their expression in the same cells in response to TCDD, the most potent agonist, and 3 ′M4 ′NF, a reported potent antagonist. Our data suggest that these two compounds appear to play different roles in regulating these genes. While TCDD enhanced transcription of both genes, 3 ′M4 ′NF induced the endogenous Cyp1a1, but not the reporter gene. Mechanistic studies indicated that the increase in induction of CYP1A1 protein by 3 ′M4 ′NF was mediated by AhR-dependent transcriptional activation. Further analysis of the Cyp1a1 promoter sequence did not reveal any 3 ′M4 ′NF-specific responsive elements other than DREs. Rather, the interaction between the 3 ′M4 ′NF-bound receptor complex and DREs was confirmed by the observation that a single nucleotide mutation in DRE core sequences obliterated AhR enhancer activity in response to both TCDD and 3 ′M4 ′NF. Together these data suggest that 3 ′M4 ′NF, a weak AhR agonist, activates the AhR to recognize and interact with the same DREs as TCDD. However, depending on its concentration as well as the promoter context of a particular gene, the ability of 3 ′M4 ′NF to act as an AhR antagonist or agonist may appear different for various genes.

Aryl hydrocarbon receptor-mediated activity of mutagenic polycyclic aromatic hydrocarbons determined using in vitro reporter gene assay

Activation of aryl hydrocarbon receptor (AhR) by 30 polycyclic aromatic hydrocarbons (PAHs) was determined in the chemical-activated luciferase expression (CALUX) assay, using two exposure times (6 and 24 h), in order to reflect the metabolization of PAHs. AhR-inducing potencies of PAHs were expressed as induction equivalency factors (IEFs) relative to benzo[ a]pyrene and 2,3,7,8-tetrachlorodibenzo- p-dioxin (TCDD). In 24 h exposure assay, the highest IEFs were found for benzo[ k]fluoranthene, dibenzo[ a, h]anthracene and dibenzo[ a, k]fluoranthene (approximately three orders of magnitude lower than TCDD) followed by dibenzo[ a, j]anthracene, benzo[ j]fluoranthene, indeno[1,2,3- cd]pyrene, and naphtho[2,3- a]pyrene. The 6 h exposure to PAHs led to a significantly higher AhR-mediated activity than the 24 h exposure (generally by two orders of magnitude), probably due to the high rate of PAH metabolism. The strongest AhR inducers showed IEFs approaching that of TCDD. Several PAHs, including some strong mutagens, such as dibenzo[ a, l]pyrene, cyclopenta[ cd]pyrene, and benzo[ a]perylene, elicited only partial agonist activity. Calculation of IEFs based on EC25 values and/or 6 h exposure data is suggested as an alternative approach to estimation of toxic potencies of PAHs with high metabolic rates and/or the weak AhR agonists. The IEFs, together with the recently reported relative mutagenic potencies of PAHs [Mutat. Res. 371 (1996) 123; Mutat. Res. 446 (1999) 1] were combined with data on concentrations of PAHs in extracts of model environmental samples (river sediments) to calculate AhR-mediated induction equivalents and mutagenic equivalents. The highest AhR-mediated induction equivalents were found for benzo[ k]fluoranthene and benzo[ j]fluoranthene, followed by indeno[1,2,3- cd]pyrene, dibenzo[ a, h]anthracene, benzo[ a]pyrene, dibenzo[ a, j]anthracene, chrysene, and benzo[ b]fluoranthene. High mutagenic equivalents in the river sediments were found for benzo[ a]pyrene, dibenzo[ a, e]pyrene, and naphtho[2,3- a]pyrene and to a lesser extent also for benzo[ a]anthracene, benzo[ b]fluoranthene, indeno[1,2,3- cd]pyrene, benzo[ j]fluoranthene, dibenzo[ a, e]fluoranthene and dibenzo[ a, i]pyrene. These data illustrate that AhR-mediated activity of PAHs, including the highly mutagenic compounds, occurring in the environment but not routinely monitored, could significantly contribute to their adverse effects.

A novel 4 S [3H]β-naphthoflavone-binding protein in liver cytosol of female Sprague‒Dawley rats treated with aryl hydrocarbon receptor agonists

β-Naphthoflavone (β-NF) is a widely used inducer of phase-I and phase-II enzymes controlled by aryl hydrocarbon receptor (AhR). Studies of competitive binding with 3H-labelled 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 3-methylcholanthrene (3-MC) and benzo[a]pyrene (B[a]P) have shown that β-NF is a high-affinity ligand for AhR and also for polycyclic aromatic hydrocarbon (PAH)-binding protein, both soluble proteins of rat liver in 8 S and 4 S fractions, respectively, of sucrose gradients. This study examined binding of [3H]β-NF to liver cytosolic proteins of female Sprague-Dawley rats. Treatment of rats with β-NF, 3-MC, TCDD or α-naphthoflavone (α-NF) increased the specific [3H]β-NF binding to liver cytosol up to 125-fold that of vehicle (corn oil)-treated rats (< 100 fmol/mg of protein). Sucrose gradients revealed a large 4 S and a small 8 S peak of radioactivity from [3H]β-NF binding to cytosols of β-NF-, 3-MC-, TCDD- or α-NF-treated rats. Whereas co-incubation with the unlabelled β-NF eliminated both peaks, co-incubation with 2,3,7,8-tetrachlorodibenzofuran (TCDF) eliminated only the 8 S peak. The sucrose density gradient from [3H]TCDD binding to cytosol of β-NF- or TCDD-treated rats yielded a small 4 S and a larger 8 S peak; only the latter was abolished by co-incubation with TCDF. Thus, the patterns of sedimentation, distribution and elimination of radioactivity from the 8 S fraction of the liver cytosols from β-NF-, 3-MC-, TCDD- or α-NF-treated rats were characteristic for the AhR, whereas those from the 4 S fraction appeared specific for [3H]β-NF binding. The data indicate that potent AhR agonists, TCDD, 3-MC and β-NF, and to a lesser extent α-NF, a weak AhR agonist, induce a 4 S [3H]β-NF-binding protein in liver cytosol of female rats. α-NF, β-NF and 3-MC were effective competitors (80-85% inhibition) of the [3H]β-NF-specific binding to the β-NF-, 3 MC- or TCDD-induced 4 S protein, whereas several PAHs including B[a]P and benzo[e]pyrene were only weak competitors. The increased [3H]β-NF binding was not associated with glycine N-methyltransferase activity. Hence, the 4 S [3H]β-NF-binding protein described herein differs from the constitutive 4 S PAH-binding protein of rat liver cytosols in the inducibility by β-NF and 3-MC, ligand-binding characteristics, and lack of glycine N-methyltransferase activity. Gel filtration on Sephacryl of liver cytosols from β-NF-treated rats indicated a molecular mass of ≈ 42 kDa for [3H]β-NF-bound protein and suggested that it was derived from a large mass component that before the radioligand binding was eluted with the void volume of the gel and sedimented in a 7 S fraction of the sucrose gradient. The [3H]β-NF binding activity was not eluted with glutathione S-transferase Ya, aldehyde-3-dehydrogenase or DT-diaphorase [NAD(P)H: quinone oxidoreductase] activities, which are AhR-controlled and β-NF-inducible. Further studies are needed to determine the identity and function of this novel protein which may be involved either directly or indirectly (as a carrier protein) in xenobiotic metabolism in vivo.

A novel 4 S [3H]β-naphthoflavone-binding protein in liver cytosol of female Sprague–Dawley rats treated with aryl hydrocarbon receptor agonists

beta-Naphthoflavone (beta-NF) is a widely used inducer of phase-I and phase-II enzymes controlled by aryl hydrocarbon receptor (AhR). Studies of competitive binding with (3)H-labelled 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD), 3-methylcholanthrene (3-MC) and benzo[a]pyrene (B[a]P) have shown that beta-NF is a high-affinity ligand for AhR and also for polycyclic aromatic hydrocarbon (PAH)-binding protein, both soluble proteins of rat liver in 8 S and 4 S fractions, respectively, of sucrose gradients. This study examined binding of [(3)H]beta-NF to liver cytosolic proteins of female Sprague-Dawley rats. Treatment of rats with beta-NF, 3-MC, TCDD or alpha-naphthoflavone (alpha-NF) increased the specific [(3)H]beta-NF binding to liver cytosol up to 125-fold that of vehicle (corn oil)-treated rats (<100 fmol/mg of protein). Sucrose gradients revealed a large 4 S and a small 8 S peak of radioactivity from [(3)H]beta-NF binding to cytosols of beta-NF-, 3-MC-, TCDD- or alpha-NF-treated rats. Whereas co-incubation with the unlabelled beta-NF eliminated both peaks, co-incubation with 2,3, 7,8-tetrachlorodibenzofuran (TCDF) eliminated only the 8 S peak. The sucrose density gradient from [(3)H]TCDD binding to cytosol of beta-NF- or TCDD-treated rats yielded a small 4 S and a larger 8 S peak; only the latter was abolished by co-incubation with TCDF. Thus, the patterns of sedimentation, distribution and elimination of radioactivity from the 8 S fraction of the liver cytosols from beta-NF-, 3-MC-, TCDD- or alpha-NF-treated rats were characteristic for the AhR, whereas those from the 4 S fraction appeared specific for [(3)H]beta-NF binding. The data indicate that potent AhR agonists, TCDD, 3-MC and beta-NF, and to a lesser extent alpha-NF, a weak AhR agonist, induce a 4 S [(3)H]beta-NF-binding protein in liver cytosol of female rats. alpha-NF, beta-NF and 3-MC were effective competitors (80-85% inhibition) of the [(3)H]beta-NF-specific binding to the beta-NF-, 3 MC- or TCDD-induced 4 S protein, whereas several PAHs including B[a]P and benzo[e]pyrene were only weak competitors. The increased [(3)H]beta-NF binding was not associated with glycine N-methyltransferase activity. Hence, the 4 S [(3)H]beta-NF-binding protein described herein differs from the constitutive 4 S PAH-binding protein of rat liver cytosols in the inducibility by beta-NF and 3-MC, ligand-binding characteristics, and lack of glycine N-methyltransferase activity. Gel filtration on Sephacryl of liver cytosols from beta-NF-treated rats indicated a molecular mass of approximately 42 kDa for [(3)H]beta-NF-bound protein and suggested that it was derived from a large mass component that before the radioligand binding was eluted with the void volume of the gel and sedimented in a 7 S fraction of the sucrose gradient. The [(3)H]beta-NF binding activity was not eluted with glutathione S-transferase Ya, aldehyde-3-dehydrogenase or DT-diaphorase [NAD(P)H: quinone oxidoreductase] activities, which are AhR-controlled and beta-NF-inducible. Further studies are needed to determine the identity and function of this novel protein which may be involved either directly or indirectly (as a carrier protein) in xenobiotic metabolism in vivo.

Differential in vivo effects of alpha-naphthoflavone and beta-naphthoflavone on CYP1A1 and CYP2E1 in rat liver, lung, heart, and kidney.

Male Sprague-Dawley rats were treated intraperitoneally with corn oil, the aryl hydrocarbon receptor (AHR) agonist beta-naphthoflavone (betaNF), or the relatively weak AHR agonist alpha-naphthoflavone (alphaNF). Animals treated with betaNF experienced a significant loss (12%) of total body mass over 5 days and a dramatic elevation of CYP1A1 mRNA in all of the organs studied. Treatment with alphaNF had no significant effect on body mass after 5 days and caused only minor increases of liver, kidney, and heart CYP1A1 mRNA. In contrast, lung CYP1A1 mRNA was increased by alphaNF treatment to levels comparable to that seen with betaNF treatment. CYP2E1 mRNA levels were also elevated in liver, lung, kidney, and heart in response to betaNF treatment, whereas alphaNF was without effect. Large increases of CYP1Al-dependent 7-ethoxyresorufin O-deethylation (EROD) activity occurred with microsomes prepared from the tissues of betaNF-treated animals. Comparatively small changes were associated with alphaNF treatment, with the exception of lung, where EROD activity was increased to approximately 60% of that with betaNF treatment. CYP2E1-dependent p-nitrophenol hydroxylase (PNP) activity was also increased by betaNF treatment in microsomes prepared from kidney (3.1-fold), whereas alphaNF was without effect. In contrast, alphaNF or betaNF treatment caused significant decreases of lung microsomal PNP (72% and 27% of corn oil control, respectively) and 7-pentoxyresorufin O-deethylation (48% and 17% of corn oil control, respectively) activities, indicating that PNP activity may be catalyzed by P450 isoforms other than CYP2E1 in rat lung. We conclude that betaNF and alphaNF have differential effects on the expression and catalytic activity of CYP1A1 and CYP2E1, depending upon the organ studied. These changes most likely occur as a result of the direct actions of these compounds as AHR agonists, in addition to secondary effects associated with AHR-mediated toxicity.