The aryl hydrocarbon receptor (AhR) is a key regulator of the transcriptional expression for the cytochrome P450 1 (CYP1) genes. CYP1A2 is one of the major CYP1 enzymes that catalyse 2-hydroxylation of estrogen, a hormone that plays a critical role in the etiology of breast cancer. In this study, we investigated whether two common polymorphisms in these two genes, CYP1A2*1F and AhR Lys554Arg, were associated with breast cancer risk in 1090 cases and 1183 controls, a subset of the population-based case-control study, the Shanghai Breast Cancer Study. Caffeine tests were performed in vivo in a subset of 236 study subjects to investigate the relationship of these two polymorphisms with CYP1A2 activity. For the AhR gene, the A (Lys) allele was associated with a decreased risk of breast cancer. Using the genotype GG as reference, odds ratios of 0.82 [95% confidence interval (CI)=0.69-0.99] for the AG genotype and 0.76 (95% CI=0.58-1.01) for the AA genotype (P for trend=0.018) were obtained. However, no association was observed between CYP1A2 genotypes and breast cancer risk, although the CYP1A2*1F polymorphism was found to be related to CYP1A2 activity. The geometric mean values for the caffeine metabolites ratio were 2.90, 2.30, and 1.95 for CC, AC, and AA genotypes, respectively (P for trend=0.024). In conclusion, the results from our study suggest that the AhR Lys554Arg polymorphism may be a genetic susceptibility factor for breast cancer, whereas CYP1A2*1F, which is a potentially functional single nucleotide polymorphism, may not be related to breast cancer risk.

Among the different mechanisms proposed to explain the cancer-protecting effect of dietary flavonoids, substrate-like interactions with cytochrome P450 CYP1 enzymes have recently been explored. In the present study, the metabolism of the flavonoids chrysin, baicalein, scutellarein, sinensetin and genkwanin by recombinant CYP1A1, CYP1B1 and CYP1A2 enzymes, as well as their antiproliferative activity in MDA-MB-468 human breast adenocarcinoma and MCF-10A normal breast cell lines, were investigated. Baicalein and 6-hydroxyluteolin were the only conversion products of chrysin and scutellarein metabolism by CYP1 family enzymes, respectively, while baicalein itself was not metabolized further. Sinensetin and genkwanin produced a greater number of metabolites and were shown to inhibit strongly in vitro proliferation of MDA-MB-468 cells at submicromolar and micromolar concentrations, respectively, without essentially affecting the viability of MCF-10A cells. Cotreatment of the CYP1 family inhibitor acacetin reversed the antiproliferative activity noticed for the two flavones in MDA-MB-468 cells to 13 and 14 microM respectively. In contrast chrysin, baicalein and scutellarein inhibited proliferation of MDA-MB-468 cells to a lesser extent than sinensetin and genkwanin. The metabolism of genkwanin to apigenin and of chrysin to baicalein was favored by CYP1B1 and CYP1A1, respectively. Taken together the data suggests that CYP1 family enzymes enhance the antiproliferative activity of dietary flavonoids in breast cancer cells, through bioconversion to more active products.

Sediment contaminated with polycyclic aromatic hydrocarbons (PAHs) from a Superfund site on the Elizabeth River (ER) in Portsmouth, VA, is teratogenic to embryonic killifish (Fundulus heteroclitus) from reference sites. However, embryos born to a population of ER killifish are resistant to PAH-induced teratogenicity. Mechanisms underlying the resistance are unclear; however, ER killifish are refractory to induction of metabolic enzyme cytochrome P4501A (CYP1A), at the level of mRNA, protein and activity. The contaminated ER sediment comprises a complex mixture of PAHs with different mechanisms of toxicity. While many are inducers of metabolic enzymes involved in both phase I and phase II of biotransformation, some PAHs can also inhibit phase I enzymatic activity. Previous research has shown that co-exposure to PAHs with different modes of action can result in synergistic embryotoxicity (Billiard, S.M., Meyer, J.N.D., Wassenberg, M., Hodson, P.V., Di Giulio, R.T., 2008. Nonadditive effects of PAHs on early vertebrate development: mechanisms and implications for risk assessment. Toxicological Sciences 105, 5-23). Two of the abundant PAHs at the ER are fluoranthene (FL), a CYP1A inhibitor, and benzo[a]pyrene (BaP), a CYP1A inducer. Based on the ER resistant phenotype and the PAH mixture in the ER sediment, we hypothesized that the inhibition of CYP1A activity affects the teratogenicity of PAHs through a biotransformation-mediated mechanism. To examine this hypothesis, we compared the responses of killifish embryos born to parents from the ER and from a reference site (King's Creek (KC), VA) after a water-borne exposure to BaP (0-400 microg/L) in the presence or absence of FL (0-500 microg/L). Embryos were dosed from 24 to 120 h post-fertilization (hpf) and were analyzed for induction of CYP1 enzymatic activity as measured by the ethoxyresorufin-O-deethylase (EROD) assay, cardiac deformities, and BaP metabolic profile. KC embryos showed significant induction of CYP1 protein activity at all BaP concentrations examined. Co-exposure to 500 microg/L of FL significantly decreased CYP1 activity and increased cardiac deformities. ER embryos showed no change in CYP1 activity or cardiac deformities for any treatment. Significantly greater concentrations of BaP and BaP 9,10-dihydrodiol were recovered from ER embryos compared to those from KC. Co-exposure with FL did not significantly alter the amount of BaP or the metabolites recovered in either population. These findings suggest that the teratogenicity observed by co-exposure to BaP and FL cannot fully be explained by alteration in BaP metabolism. This study also indicates that the metabolic adaptation observed in the ER killifish cannot be explained simply by the refractory CYP1 phenotype.

Inhibitory effects of Delta(9)-tetrahydrocannabinol (Delta(9)-THC), cannabidiol (CBD), and cannabinol (CBN), the three major constituents in marijuana, on catalytic activities of human cytochrome P450 (CYP) 1 enzymes were investigated. These cannabinoids inhibited 7-ethoxyresorufin O-deethylase activity of recombinant CYP1A1, CYP1A2, and CYP1B1 in a competitive manner. CBD most potently inhibited the CYP1A1 activity; the apparent K(i) value (0.155microM) was at least one-seventeenth of the values for other CYP1 isoforms. On the other hand, CBN more effectively decreased the activity of CYP1A2 and CYP1B1 (K(i)=0.0790 and 0.148microM, respectively) compared with CYP1A1 (K(i)=0.541microM). Delta(9)-THC less potently inhibited the CYP1 activity than CBD and CBN, and showed low selectivity against the CYP1 inhibition (K(i)=2.47-7.54microM). The preincubation of CBD resulted in a time- and concentration-dependent decrease in catalytic activity of all the recombinant CYP1 enzymes and human liver microsomes. Similarly, the preincubation of Delta(9)-THC or CBN caused a time- and concentration-dependent inhibition of recombinant CYP1A1. The inactivation of CYP1A1 by CBD indicated the highest k(inact)/K(I) value (540l/mmol/min) among the CYP1 enzyme sources tested. The inactivation of recombinant CYP1A1 and human liver microsomes by CBD required NADPH, was not influenced by dialysis and by glutathione, N-acetylcysteine, and superoxide dismutase as trapping agents. These results indicated that CBD and CBN showed CYP1 isoform-selective direct inhibition and that CBD was characterized as a potent mechanism-based inhibitor of human CYP1 enzymes, especially CYP1A1.

OBJECTIVE

To investigate the expression of P450 enzyme genes by using end-stage liver disease samples and trimmed normal Chinese donor livers.

METHODS

The end-stage liver disease samples [n = 93, including hepatocellular carcinoma (HCC), peri-HCC tissue, hepatitis B virus cirrhosis, alcoholic cirrhosis, and severe cirrhosis] and trimmed normal Chinese donor livers (n = 35) from The Institute of Organ Transplantation in Beijing, China. Total RNA was extracted, purified, and subjected to real-time RT-PCR analysis.

RESULTS

For cytochrome P450 enzymes 1 (CYP1) family, the expression of CYP1A2 was decreased 90% in HCC, 80% in alcoholic cirrhosis, and 65% in severe cirrhosis. For CYP2 family, the expression of CAR was decreased 50% in HCC, but increased 50% in peri-HCC tissues. Similar decreases (about 50%) of CYP2B6, CYP2C9, CYP2C19, CYP2D6 and CYP2E1 were observed in HCC, as compared to peri-HCC tissues and normal livers. CYP2C19 were decreased in all end-stage liver diseases and CYP2E1 also decreased in alcoholic cirrhosis and severe cirrhosis. For CYP3 family, the expression of PXR was decreased 60% in HCC, together with decreases in CYP3A4, CYP3A5, and CYP3A7. In contrast, the expression of CYP3A7 was slightly increased in HBV cirrhosis. The expression of CYP4A11 was decreased 85% in HCC, 7% in alcoholic cirrhosis and severe liver cirrhosis, along with decreases in PPARα. The 93 end-stage livers had much higher inter-individual variations in gene expression than 35 normal livers.

CONCLUSIONS

The expression of CYP enzyme genes and corresponding nuclear receptors was generally decreased in end-stage liver diseases, and significant differences in gene expression were evident between peri-HCC and HCC.

Benzo[a]pyrene (BaP) is a prototypical polycyclic aromatic hydrocarbon (PAH) found in combustion processes. Cytochrome P450 1A1 and 1B1 enzymes (CYP1A1 and CYP1B1) can both detoxify PAHs and activate them to cancer-causing reactive intermediates. Following high dosage of oral BaP (125 mg/kg/day), ablation of the mouse Cyp1a1 gene causes immunosuppression and death within ∼28 days, whereas Cyp1(+/+) wild-type mice remain healthy for >12 months on this regimen. In this study, male Cyp1(+/+) wild-type, Cyp1a1(-/-) and Cyp1b1(-/-) single-knockout and Cyp1a1/1b1(-/-) double-knockout mice received a lower dose (12.5 mg/kg/day) of oral BaP. Tissues from 16 different organs-including proximal small intestine (PSI), liver and preputial gland duct (PGD)-were evaluated; microarray cDNA expression and >30 mRNA levels were measured. Cyp1a1(-/-) mice revealed markedly increased CYP1B1 mRNA levels in the PSI, and between 8 and 12 weeks developed unique PSI adenomas and adenocarcinomas. Cyp1a1/1b1(-/-) mice showed no PSI tumors but instead developed squamous cell carcinoma of the PGD. Cyp1(+/+) and Cyp1b1(-/-) mice remained healthy with no remarkable abnormalities in any tissue examined. PSI adenocarcinomas exhibited striking upregulation of the Xist gene, suggesting epigenetic silencing of specific genes on the Y-chromosome; the Rab30 oncogene was upregulated; the Nr0b2 tumor suppressor gene was downregulated; paradoxical overexpression of numerous immunoglobulin kappa- and heavy-chain variable genes was found-although the adenocarcinoma showed no immunohistochemical evidence of being lymphatic in origin. This oral BaP mouse paradigm represents an example of "gene-environment interactions" in which the same exposure of carcinogen results in altered target organ and tumor type, as a function of just 1 or 2 globally absent genes.

One of today's greatest challenges in environmental toxicology is to understand effects of mixture toxicity, commonly referred to as cocktail effects, in humans and in wildlife. Biomarker responses in fish are routinely used to assess exposure of anthropogenic chemicals in the aquatic environment. However, little is known about how cocktail effects affect these biomarker responses. For this reason, there is an obvious risk for misinterpretation of biomarker-data and this can have profound negative effects on stakeholder's decisions and actions, as well as on legislations and remediation-plans initiated in order to reduce exposure to certain chemicals. Besides, chemical safety-levels are traditionally based on experiences from lab-studies with single chemicals, which is unfortunate as a chemical can be more toxic when it is mixed with other chemicals, because of the cocktail effect. This review focuses on pharmacokinetic interactions between different classes of pollutants on detoxification mechanisms and how that affects two commonly used biomarkers in the aquatic environment: (1) induction of cytochrome P450 1A (CYP1A) that is mediated via activation of the arylhydrocarbon receptor (AhR), used to assess exposure to aromatic hydrocarbons; (2) induction of vitellogenin (VTG) that is mediated via activation of the estrogen receptor (ER), used to assess exposure to estrogenic chemicals. These responses can be either directly or indirectly affected by the presence of other classes of pollutants as a result of cocktail effects. For example, chemicals that inhibit the function of key metabolic enzymes and transporter pumps that are involved in elimination of AhR- and ER agonists, can result in bioaccumulation of aromatic hydrocarbons and estrogenic chemicals resulting in increased biomarker responses. This cocktail effect can lead to overestimation of the actual exposure pressure. On the contrary, induction of expression of key metabolic enzymes and transporter activities can result in increased elimination of AhR- and ER agonists that can lead to possible underestimation of the exposure. Another type of cocktail effect is inhibiting receptor cross-talk that may cause decreased biomarker responses that can also lead to underestimation of the actual exposure. To address the possible involvement of pharmacokinetic interactions including receptor cross-talks, we need to combine analyses on receptor signaling with studies on function of key biotransformation enzymes such as major catabolic CYP enzymes (e.g. CYP1-4) as well as efflux pumps (e.g. ATP-binding cassette transporter proteins). Besides, studies of inhibition of these enzymes and pumps activities pose a great potential to be used as future biomarkers as they are more clearly liked to adverse outcomes, compared to for example induction of CYP1A and VTG expression.

3-Methylindole (3 MI) is a selective pulmonary toxicant, and cytochrome P450 (P450) bioactivation of 3 MI, through hydroxylation, epoxidation, or dehydrogenation pathways, is a prerequisite for toxicity. CYP2F1 and CYP2F3 exclusively catalyze the dehydrogenation of 3 MI to 3-methyleneindolenine, without detectable formation of the hydroxylation or epoxidation products. It was not known whether 3 MI is simply an excellent dehydrogenation substrate for all P450 enzymes, or whether certain cytochrome P450s responsible for 3 MI bioactivation have unique active sites that only catalyze the dehydrogenation of the molecule, while other P450s would catalyze only the oxygenation of 3 MI. Therefore, the kinetics of product formation by the CYP2F1 and CYP2F3 enzymes were compared with other cytochrome P450 enzymes. The enzymes tested were CYP1A1, CYP1A2, CYP1B1, and CYP2E1. The CYP1A1 and CYP1A2 enzymes produced all three 3 MI metabolites: the dehydrogenation product, 3-methyleneindolenine (V(max)/K(m) = 4 and 22, respectively); the hydroxylation product, indole-3-carbinol (V(max)/K(m) = 42 and 100, respectively); and the epoxidation product, 3-methyloxindole (V(max)/K(m) = 4 and 72, respectively). These CYP1A enzymes catalyzed oxygenation of 3 MI at much faster rates than dehydrogenation. CYP1B1 produced indole-3-carbinol (V(max)/K(m) = 85) and 3-methyloxindole (V(max)/K(m) = 7), and CYP2E1 only produced 3-methyloxindole (V(max)/K(m) = 98), but neither enzyme catalyzed the formation of the dehydrogenated product. Six additional P450 enzymes that were tested formed none of the dehydrogenation product. The ability of the various CYP1 family enzymes to catalyze the formation of all three major 3 MI metabolites, along with the specific oxygenation by CYP2E1, illustrates that dehydrogenation of 3 MI is not a substrate-directed process, but that the members of the CYP2F family possess unique active sites that specifically catalyze only the dehydrogenation mechanism.

The Strongylocentrotus purpuratus cyclophilin1 gene (Sp-cyp1) is expressed exclusively in skeletogenic mesenchyme cells of the embryo, beginning in the micromere lineage of the early blastula stage and continuing after gastrulation during the syncytial deposition of the skeleton. This gene encodes a protein which is a member of the peptidyl-prolyl cis-trans isomerase (PPIase) family. Sp-cyp1 is among the differentiation genes activated in the skeletogenic territory as a terminal function of the endomesodermal gene regulatory network. Network perturbation analysis had predicted the skeletogenic regulators Ets1 and Deadringer (Dri) to be its driver inputs. Here, we show that a 218-bp cis-regulatory DNA fragment recapitulates skeletogenic Sp-cyp1 expression; that elimination of either Ets1 or Dri inputs severely depresses the activity of expression constructs containing this DNA fragment; and that Ets1 and Dri target sites within the 218 bp fragment are required for normal expression. This indicates that the predicted inputs are direct. Other studies indicate that the same inputs are evidently necessary for expression of several other skeletogenic differentiation genes, and these genes probably constitute a skeletogenic gene battery, defined by its Ets plus Dri regulatory inputs.

The cytochrome P4501 gene family consists of two members, CYP1A1 and CYP1A2, that are induced by halogenated hydrocarbons and polycyclic aromatic hydrocarbons. The human CYP1 promoters and 5'-flanking sequences were cloned into luciferase expression vectors to develop cell lines that stably express luciferase activity in response to CYP1 gene induction. Plasmids were initially tested in transient transfection assays. Transient transfections resulted in high-level expression of luciferase by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) from both the CYP1 expression vectors, pLUC1A1 and pLUC1A2. In dose-response experiments, 10 nM TCDD caused a maximal induction of pLUC1A2-directed luciferase activity that was 10-fold over control. Maximal pLUC1A1-directed luciferase activity was 65-fold over control in cells treated with 10 nM TCDD. Stable integration of CYP1-luciferase-neo plasmids, pL1A1N and pL1A2N, into the human hepatoma cell line, HepG2, was achieved by selection with G418. G418-resistant colonies were isolated for both pL1A1N and pL1A2N plasmids. The pL1A2N transfectants showed basal-level luciferase activity, but were nonresponsive to treatment with 10 nM TCDD. These results are in contrast to the observed induction of pLUC1A2-mediated luciferase expression in transient transfection experiments. Stable integration of the human CYP1A2 gene sequences appears to silence the transcriptional activation by TCDD. The pL1A1N transfectants showed inducible luciferase activity and one cell line, referred to as 101L, was used to establish dose-response relationships for TCDD and various polycyclic aromatic hydrocarbons. Maximal induction occurred after treatment with 100 nM TCDD, 10 microM 3-methylcholanthrene, 50 microM benz[a]anthracene, and 50 microM benzo[a]pyrene. These studies illustrate the use of the CYP1A1-luciferase cell line for the study of structure-activity relationships.

The tryptophan photooxidation product 6-formylindolo[3,2-b]carbazole (FICZ) has been proposed as a physiological ligand for the mammalian aryl hydrocarbon receptor (AHR), which it binds with high-affinity, inducing expression of cytochrome P450 1A1 (CYP1A1). We investigated whether the response to FICZ is evolutionarily conserved in vertebrates by measuring FICZ binding to two zebrafish AHRs (AHR1B and AHR2) and its ability to induce zebrafish CYP1 genes (CYP1A, CYP1B1, CYP1C1, CYP1C2, and CYP1D1) in vivo. Exposure of zebrafish embryos (48 h-post-fertilization; hpf) to 10 nM FICZ for 6h caused strong induction of CYP1A mRNA and a statistically significant but modest induction of CYP1B1 and CYP1C1. Neither CYP1C2 nor CYP1D1 expression was induced by FICZ under the conditions of dose, time or developmental stage examined here. CYP1A induction was significantly greater after 6 h than after 12 h of exposure to FICZ, suggesting a rapid degradation of inducer. The 6-h EC(50) values for induction of CYP1A and CYP1B1 by FICZ were 0.6 and 0.5 nM compared to 72-h EC(50) values of 2.3 and 2.7 nM for PCB126, indicating that in zebrafish embryos FICZ is a more potent inducer than PCB126. FICZ at 10 nM was able to completely displace binding of 2,3,7,8-tetrachloro-1,6[3H]-dibenzo-p-dioxin to in vitro-expressed zebrafish AHR2 and AHR1B. Inhibition of AHR2 translation in zebrafish embryos by an AHR2-specific morpholino antisense oligonucleotide decreased the induction of CYP1A and CYP1B1 by FICZ and by PCB126. Together, these results demonstrate that FICZ is a potent AHR agonist in zebrafish, inducing expression of multiple CYP1 genes largely through AHR2. Evolutionary conservation of the response to FICZ is consistent with a possible role as an endogenous signaling molecule acting through the AHR.

Chlorinated hydrocarbons (CHCs) are environmental contaminants that bioaccumulate and hence are detected in human tissues. Epidemiological evidence suggests that the increased incidence of a variety of human cancers, such as lymphoma, leukemia and liver and breast cancers, might be attributed to exposure to these agents. The ability of CHCs to disrupt estrogen homeostasis is hypothesized to be responsible for their biological effects. The present study examined the effect of CHCs on the expression of cytochrome P450 (CYP)1A1, CYP1A2 and CYP1B1 mRNAs and the consequent 2- and 4-hydroxylation of 17beta-estradiol (E(2)) in female Sprague-Dawley rats. Animals were administered a single dose of the LD(50) of 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD) (25 microg/kg), 2, 4-dichlorophenoxyacetic acid (2,4-D) (375 mg/kg) and dieldrin (DED) (38 mg/kg) by gavage. Seventy-two hours after treatment, increased expression of CYP1A1, CYP1A2 and CYP1B1 was observed in the liver, kidney and mammary tissue. Since CYP1A and CYP1B1 are the major enzymes catalyzing 2- and 4-hydroxylation of E(2), respectively, the effect of these CHCs on the metabolism of E(2) was investigated in rat tissues. Formation of 2- and 4-catechol estrogens was increased in a tissue-specific manner in response to treatment. TCDD was the most potent inducer for CYP1 enzyme mRNA and for the 2- and 4-hydroxylation of E(2). 2,4-D and DED induced similar responses, but less than that of TCDD. These results suggest that induction of CYP1 family enzymes and consequent increases in estrogen metabolism by CHCs in target tissues may be factors contributing to the biological effects associated with exposure to these agents.

trans-Resveratrol (3,5,4'-trihydroxy-trans-stilbene) has been reported to confer chemoprotection against 7,12-dimethylbenz[a]anthracene (DMBA)-induced carcinogenicity in a murine model. A potential mechanism for this effect by trans-resveratrol is inhibition of DMBA-bioactivating cytochrome P450 (CYP) enzymes such as CYP1B1, CYP1A1, and CYP1A2. In the present study, we examined in detail the in vitro inhibitory effects of trans-resveratrol on these three human CYP enzymes. trans-Resveratrol decreased 7-ethoxyresorufin O-dealkylation activity catalyzed by human recombinant CYP1B1, CYP1A1, and CYP1A2 in a concentration-dependent manner and by a mixed type of inhibition. This direct inhibition was enzyme-selective, as judged by the differences in the apparent K(i) values (0.8 +/- 0.1 microM, 1.2 +/- 0.1 microM, and 15.5 +/- 1.1 microM for CYP1B1, CYP1A1, and CYP1A2, respectively). Preincubating recombinant CYP1A2 or human liver microsomes with trans-resveratrol and NADPH prior to the initiation of substrate oxidation resulted in a time- and concentration-dependent decrease in catalytic activity. The inactivation of liver microsomal CYP1A2 by trans-resveratrol required NADPH, was not reversible by dialysis, and was not affected by the trapping agents glutathione, N-acetylcysteine, catalase, or superoxide dismutase, but was attenuated by a CYP1A2 substrate, imipramine. Analysis of a panel of individual human liver microsomes showed intersample differences in the response to the in vitro inactivation by trans-resveratrol. In contrast to CYP1A2, CYP1B1 was not subject to inactivation by this compound and the reduction in CYP1A1 activity was time- but not concentration-dependent. In summary, trans-resveratrol differentially inhibited human CYP1 enzymes and this occurred by two distinct mechanisms: direct inhibition (mainly CYP1B1 and CYP1A1) and mechanism-based inactivation (CYP1A2).

Human cytochrome P450 (CYP)1B1 is a major enzyme for carcinogenic estrogen metabolism and involved in the metabolic activation of procarcinogens of the polycyclic aromatic hydrocarbons (PAHs). CYP1B1 is known to be expressed at a high frequency in various human cancers, but not in normal tissues. It also plays an important role in the metabolism of various anti-cancer drugs. These findings suggest inhibition of CYP1B1 as a new oncological therapeutic strategy. Several natural and synthetic compounds have been studied in an effort to find the isoform-specific inhibitors of the CYP1 subfamily. A survey of the inhibitors of CYP1B1 and other related inhibitors of the CYP1 subfamily is provided in this review.

Cytochrome P450 (P450) monooxygenases are capable of catalyzing metabolism of various endogenous and exogenous compounds, such as bile acids, fatty acids, retinoids, steroids, drugs and other xenobiotics. The enzymes, belonging to CYP1, CYP2 and CYP3 families are primarily involved in the metabolism of drugs and xenobiotics. P450-mediated defense mechanism protects organisms from the potentially toxic effects of xenobiotics to which they are exposed. The adaptive transcriptional induction of P450s by xenobiotics is mediated by aromatic hydrocarbon receptor of Per-ARNT-Sim family, and nuclear hormone receptors, including pregnane X receptor, constitutive androstane receptor and glucocorticoid receptor. In addition to the receptor-mediated induction, endogenous factors (developmental, sex or hormonal factors) can also modulate P450 expression. Steroid hormones are biologically active compounds, controlling many physiological processes via endocrine signaling pathways and contributing to the transcriptional regulation of drug metabolizing P450s. Any change in P450 activities influences the rate of activation or inactivation of drugs. Exposure to xenobiotics (drugs, environmental pollutants) can exert changes in endocrine function both directly as hormone agonists/antagonists or indirectly altering the rates of hormone metabolism and consequently the circulating levels of hormones. Modulation of P450 expression by xenobiotics can affect the subsequent metabolism of not only foreign chemicals, but also steroid hormones. Perturbation in hormone metabolism leads to the imbalance in sexual and reproductive development, and in glucose, lipid and salt/water homeostasis. The purpose of this review is to highlight the interplay between drug-metabolizing P450s and steroid hormones as well as the interactions of xenosensor with steroid signaling pathways.

Cytochrome P450 epoxidation of linoleic acid produces biologically active metabolites which have been associated with many pathological conditions that often lead to acute renal failure. In the present study, we evaluated the ability of specific cytochrome P450s to produce linoleic acid monoepoxides. We then tested the cytotoxic properties of linoleic acid, linoleic acid monoepoxides, and corresponding diols in a rabbit renal proximal tubule model. CYP1A2, CYP2E1, CYP2J2, CYP2J3, CYP2J5, and CYP2J9 metabolized linoleic acid at rates comparable to arachidonic acid and produced linoleic acid monoepoxides as major products. Cytotoxicity studies showed that linoleic acid, linoleic acid monoepoxides, and corresponding diols are toxic at pathologically relevant concentrations (100-500 microM). Concentration-dependent studies showed that linoleic acid and linoleic acid monoepoxides are the most toxic and induce mitochondrial dysfunction prior to cell death. Cytoprotectants known to block cell death associated with mitochondrial dysfunction and oxidative stress did not prevent cell death induced by linoleic acid and linoleic acid monoepoxides. This study shows that P450s in the CYP1 and CYP2 gene families metabolize linoleic acid to linoleic acid monoepoxides and that the monoepoxides, as well as linoleic acid, disrupt mitochondrial function without causing oxidative stress.

Dioxin (2,3,7,8-tetrachlorodibenzo-p-dioxin) induces cleft palate and hydronephrosis in mice, when exposed in utero; these effects are mediated by the aryl hydrocarbon receptor. The Cyp1a1, Cyp1a2, and Cyp1b1 genes are up-regulated by the aryl hydrocarbon receptor. To elucidate their roles in dioxin-induced teratogenesis, we compared Cyp1a1(-/-), Cyp1a2(-/-), and Cyp1b1(-/-) knock-out mice with Cyp1(+/+) wild-type mice. Dioxin was administered (25 microg/kg, gavage) on gestational day 10, and embryos were examined on gestational day 18. The incidence of cleft palate and hydronephrosis was not significantly different in fetuses from Cyp1a1(-/-), Cyp1b1(-/-), and Cyp1(+/+) wild-type mice. To fetuses carried by Cyp1a2(-/-) dams, however, this dose of dioxin was lethal; this effect was absolutely dependent on the maternal Cyp1a2 genotype and independent of the embryonic Cyp1a2 genotype. Dioxin levels were highest in adipose tissue, mammary gland, and circulating blood of Cyp1a2(-/-) mothers, compared with that in the Cyp1(+/+) mothers, who showed highest dioxin levels in liver. More dioxin reached the embryos from Cyp1a2(-/-) dams, compared with that from Cyp1(+/+) dams. Fetuses from Cyp1a2(-/-) dams exhibited a approximately 6-fold increased sensitivity to cleft palate, hydronephrosis, and lethality. Using the humanized hCYP1A1_1A2 transgenic mouse (expressing the human CYP1A1 and CYP1A2 genes in the absence of mouse Cyp1a2 gene), the teratogenic effects of dioxin reverted to the wild-type phenotype. These data indicate that maternal mouse hepatic CYP1A2, by sequestering dioxin and thus altering the pharmacokinetics, protects the embryos from toxicity and birth defects; substitution of the human CYP1A2 trans-gene provides the same protection. In contrast, neither CYP1A1 nor CYP1B1 appears to play a role in dioxin-mediated teratogenesis.

In this work we have investigated a system of long-term primary cultures of adult human hepatocytes which, in contrast to those previously described, has the advantage of requiring neither the use of additive cells as in co-cultures, nor of matrix component preparations like Matrigel or collagen sandwich. This system has been used previously for long-term cultures of hepatocytes from young baboon, and some modifications have been introduced here to take into account the specificity of adult human hepatocytes. In this system, hepatocytes are plated at confluence on collagen-coated dishes and cultured in a serum-free medium consisting of Williams'E supplemented with hormones and growth factors. Proteins secreted specifically by the liver, including albumin, alpha-1 antitrypsin, plasminogen, fibrinogen, lipoproteins ApoA1 and ApoB100, have been quantified in the extracellular medium as a function of time, either by immunoblot or ELISA. In addition, the expression and inducibility of CYP proteins of the CYP1, CYP2 and CYP3 families in response to their prototypical inducers including 2,3,7,8-tetrachlorodibenzo(p)dioxin and rifampicin, have been evaluated by immunoblot analysis of microsomes or cell lysates. Moreover, the oxidative metabolism of cyclosporin A, a monoxygenase activity depending on CYP3A4, has been monitored directly on the cultured cells by HPLC analysis of extracellular medium. Our results show that, under these culture conditions, adult human hepatocytes retain these phenotypical characteristics for at least 35 days. This system meets the requirements for use as a model for screening CYP protein inducers.

Previous reports have proposed a cross-talk between the nuclear factor erythroid-2 p45-related factor-2 (Nrf2)/antioxidant response element (ARE) and the aryl hydrocarbon receptor (AhR)/xenobiotic response element (XRE) signaling pathways. Therefore, the aim of the current study was to examine the level of phase I, phase II drug metabolizing enzymes (DMEs), and phase III transporters and their related transcription factors in the Nrf2 knockout model. Our results showed that phase II DMEs that are under the control of Nrf2 typified by NAD(P)H: quinone oxidoreductase 1 (Nqo1), and glutathione S-transferase (Gst) were significantly lower at the mRNA, protein, and catalytic activity levels in the livers of Nrf2 knockout mice compared to wild type. Furthermore, phase I cytochrome P450s (CYPs), Cyp1, and Cyp2b10 at mRNA, protein, and catalytic activity levels were significantly lower in the livers of Nrf2 knockout mice. Interestingly, our results showed that the transcription factors AhR, constitutive androstane receptor (CAR), and pregnane X receptor (PXR) at mRNA, and protein expression levels were significantly lower in the livers of Nrf2 knockout mice compared to wild type. Importantly, phase III drug transporters mRNA levels of the multiple drug resistance associated proteins (Mrp2 and Mrp3), and solute carrier organic anion transporters (Slco1a6 and Slco2b1) were significantly lower in the liver of Nrf2 knockout mice. Co-activators, Ncoa1, Ncoa2, and Ncoa3 mRNA levels were not altered while co-repressors, Ncor1 and Ncor2 were significantly lower in the livers of Nrf2 knockout mice. In conclusion, knockout of Nrf2 causes disruption to the coordination of phase I, phase II drug DMEs, and phase III drug transporters through altering the transcription factors controlling them.

CYP1 is a trans acting regulatory locus modulating both iso 1- and iso 2-cytochrome c synthesis. Genetical analysis of various mutated alleles has allowed us to identify the gene product as a positive regulatory element. The region of the target sequence of the CYP1 product on the iso 2-cytochrome c structural gene was located by molecular and genetic analysis of two cis acting mutations located at the CYP3 locus: CYP3-36 and CYP3-4, which have been shown to arise from the integration of TY1 elements near the promoter site. Determination of the amount of iso 2-cytochrome c synthesized by strains bearing various genetic constructions, in which the cis acting mutations were associated with different alleles of the CYP1 trans acting locus, showed that TY1 inserted into CYP3-36 extinguishes the activation function due to a mutated overproducer allele CYP1-18, while CYP3-4 amplifies this function. This result identifies at least a part of the target sequence of the CYP1 product within the region separating the two TY1 insertions. To clone the CYP1 gene, we took advantage of the iso 2-cytochrome c overproducer phenotype of the mutated allele CYP1-18, which confers a Lactate+ phenotype on an iso 1-cytochrome c-deficient strain. Such a phenotype allowed the isolation of a recombinant plasmid YEpJFM1 carrying the mutated allele, able to complement on lactate medium a lactate- recipient strain. The identity of the YEpJFM1 sequence with the chromosomal gene was confirmed by homologous recombination at the CYP1 locus.

The COX6 gene encodes subunit VI of cytochrome c oxidase. Previously, this gene and its mRNAs were characterized, and its expression has been shown to be subject to glucose repression/derepression. In this study we have examined the effects of heme and the HAP1 (CYP1) and HAP2 genes on the expression of COX6. By quantitating COX6 RNA levels and assaying beta-galactosidase activity in yeast cells carrying COX6-lacZ fusion genes, we have found that COX6 is regulated positively by heme and HAP2, but is unaffected by HAP1. Through 5' deletion analysis we have also found that the effects of heme and HAP2 on COX6 are mediated by sequences between 135 and 590 base pairs upstream of its initiation codon. These findings identify COX6 as the fourth respiratory protein gene that is known to be regulated positively by heme and HAP2. The other three, CYC1, COX4, and COX5a, encode iso-1-cytochrome c, cytochrome c oxidase subunit IV, and an isolog, Va, of cytochrome c oxidase subunit V, respectively. Thus, it appears that the biogenesis of two interacting proteins, cytochrome c and cytochrome c oxidase, in the mitochondrial respiratory chain, are under the control of common factors.

A series of trans-stilbene derivatives containing a 3,5-dimethoxyphenyl moiety were prepared through a new efficient solution phase synthetic pathway, and their inhibitory activities were evaluated on human cytochrome P450s (CYP) 1A1, 1A2, and 1B1 to find a potent and selective CYP1B1 inhibitor. We found that a substituent at the 2-position of the stilbene skeleton plays a very important role in discriminating between CYP1As and CYP1B1. Among the compounds tested, the most selective and potent CYP1B1 inhibitor was 2,3',4,5'-tetramethoxystilbene. Compound 7j, 2-[2-(3,5-dimethoxy-phenyl)vinyl]thiophene, showed greater inhibitory activities but had a lower selectivity toward all of the CYP1s tested.

The ontogeny of the first four families of cytochromes P450 (P450s) (i.e., Cyp1-Cyp4) can affect the biotransformation of drugs and dietary chemicals in liver, resulting in unique pharmacological reactions in children. Because genome-scale investigations have identified many novel P450 isoforms, it is critical to perform a systematic characterization of these P450s during liver development. In this study, livers were collected from C57BL/6 mice 2 days before birth and at various postnatal ages (0-45 days of age). The mRNA levels for 75 P450 isoforms (Cyp1-Cyp4) were quantified with branched DNA assays and reverse transcription-polymerase chain reaction assays. More than half of the mouse P450s are conserved in humans, but there are more isoforms in mice. The P450 mRNA levels increased after birth in mouse liver, forming four distinct ontogenic patterns. The majority of P450s form a total of eight genomic clusters, namely, Cyp1a1 and Cyp1a2 genes on chromosome 9 (cluster 1), Cyp2a, Cyp2b, Cyp2f, Cyp2g, and Cyp2t genes on chromosome 7 (cluster 2), Cyp2c genes on chromosome 19 (cluster 3), Cyp2d genes on chromosome 15 (cluster 4), Cyp2j genes on chromosome 4 (cluster 5), Cyp3a genes on chromosome 5 (cluster 6), Cyp4a, Cyp4b, and Cyp4x genes on chromosome 4 (cluster 7), and Cyp4f genes on chromosome 17 (cluster 8). Some P450 isoforms within the same genomic cluster showed similar ontogenic patterns. In conclusion, the present study revealed four patterns of ontogeny for P450s in liver and showed that many P450s within a genomic cluster exhibited similar ontogenic patterns, which suggests that some P450s within a cluster are likely regulated by a common pathway during liver development.

Several cytochrome P450 (CYP) enzymes are expressed in the human lung, where they participate in metabolic inactivation and activation of numerous exogenous and endogenous compounds. In this study, the expression pattern of all known xenobiotic-metabolizing CYP genes was characterized in the human alveolar type II cell-derived A549 adenocarcinoma cell line using qualitative reverse transcriptase/polymerase chain reaction (RT-PCR). In addition, the mechanisms of induction by chemicals of members in the CYP1 and CYP3A subfamilies were assessed by quantitative RT-PCR. The expression of messenger RNAs (mRNAs) of CYPs 1A1, 1B1, 2B6, 2C, 2E1, 3A5, and 3A7 was detected in the A549 cells. The amounts of mRNAs of CYPs 1A2, 2A6, 2A7, 2A13, 2F1, 3A4, and 4B1 were below the limit of detection. 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) induced CYP1A1 and CYP1B1 mRNAs 56-fold and 2.5-fold, respectively. CYP3A5 was induced 8-fold by dexamethasone and 11-fold by phenobarbital. CYP3A4 was not induced by any of the typical CYP3A4 inducers used. The tyrosine kinase inhibitor genistein and the protein kinase C inhibitor staurosporine blocked TCDD-elicited induction of CYP1A1, but they did not affect CYP1B1 induction. Protein phosphatase inhibitors okadaic acid and calyculin A enhanced TCDD-induction of CYP1B1 slightly, but had negligible effects on CYP1A1 induction. These results suggest that CYP1A1 and CYP1B1 are differentially regulated in human pulmonary epithelial cells and give the first indication of the induction of CYP3A5 by glucocorticoids in human lung cells. These results establish that having retained several characteristics of human lung epithelial cell CYP expression, the A549 lung cell line is a valuable model for mechanistic studies on induction of the pulmonary CYP system.