Protein kinase C and CYPlAl induction in rainbow trout (Oncorhynchus mykiss) hepatocyte culture

1. The role of protein kinase C (PKC) in B-naphthoflavone (BNF) induction of CYP1A1 in rainbow trout hepatocytes was investigated.2. Primary cultures of rainbow trout hepatocytes treated with BNF for 24 hr showed an increase in microsomal 7-ethyoxyresorufm-O-deethylase (EROD) activity compared to cells treated with vehicle (DMSO) only.3. Increases in EROD activities were proportional to increased concentrations of BNF from 1 to 10 nM reaching a plateau at higher concentrations (20–100 nM) of BNF.4. Western blot analysis using specific antibody (LM4b) against CYP1A1 showed that changes in microsomal CYP1A1 protein paralleled that of EROD activity.5. The induction of EROD activity by BNF required both protein and RNA synthesis since the process was blocked by both cycloheximide and actinomycin D.6. Pretreatment of hepatocytes with 12-O-tetradecanoyl-phorbol-13-acetate (TPA) led to a dose dependent suppression of BNF-induced EROD activity and CYP1A1 content. TPA alone had no effect on hepatic EROD activity and CYP1A1 protein level.7. Pretreatment with sn-1,2 didecanoylglycerol, a PKC activator, had no effect on BNF-induced EROD activity in these cells.8. Pretreatment of cells with staurosporine, a PKC inhibitor, effectively blocked BNF-induced EROD activity.9. PKC may play a role in the induction of CYP1A1 gene expression in fish liver by BNF.     

Development of a monoclonal antibody for ELISA of CYP1A in primary cultures of rainbow trout Oncorhynchus mykiss hepatocytes

Induction of cytochrome P4501A CYP1A in cultured cells can be used to determine the induction potencies of xenobiotics or complex environmental samples. This report describes the development of an enzyme linked immunosorbent assay ELISA for measurement of CYP1A expression in primary cultures of rainbow trout Oncorhynchus mykiss hepatocytes. Juvenile rainbow trout were injected with naphthoflavone BNF 25 mg kg-1 body weight to induce the synthesis of CYP1A. The CYP1A isoenzyme was purified, characterized by immunological cross reactivity and N terminal sequencing and used to prepare a monoclonal antibody in Balb C mice. The specificity of the antibody for CYP1A was proved by Western blotting of samples from control and BNF injected fish. Two ELISA methods, a direct and a competitive one, were evaluated, with both methods being of comparable sensitivity. Rainbow trout hepatocytes, maintained as monolayers in serum free, chemically defined medium, were exposed to naphthoflavone, and the induction response was measured both by 7 ethoxyresorufin O deethylase EROD activity and the direct ELISA method. Comparison between EROD activity and immunodetectable CYP1A protein can provide information on the catalytic efficiency of CYP1A.     

Development of a monoclonal antibody for ELISA of CYP1A in primary cultures of rainbow trout Oncorhynchus mykiss hepatocytes

Induction of cytochrome P4501A CYP1A in cultured cells can be used to determine the induction potencies of xenobiotics or complex environmental samples. This report describes the development of an enzyme linked immunosorbent assay ELISA for measurement of CYP1A expression in primary cultures of rainbow trout Oncorhynchus mykiss hepatocytes. Juvenile rainbow trout were injected with naphthoflavone BNF 25 mg kg-1 body weight to induce the synthesis of CYP1A. The CYP1A isoenzyme was purified, characterized by immunological cross reactivity and N terminal sequencing and used to prepare a monoclonal antibody in Balb C mice. The specificity of the antibody for CYP1A was proved by Western blotting of samples from control and BNF injected fish. Two ELISA methods, a direct and a competitive one, were evaluated, with both methods being of comparable sensitivity. Rainbow trout hepatocytes, maintained as monolayers in serum free, chemically defined medium, were exposed to naphthoflavone, and the induction response was measured both by 7 ethoxyresorufin O deethylase EROD activity and the direct ELISA method. Comparison between EROD activity and immunodetectable CYP1A protein can provide information on the catalytic efficiency of CYP1A.     

2,3,7,8 Tetrachlorodibenzo-p-dioxin induction of cytochrome P4501A in cultured rat and human hepatocytes

We report here a novel observation that 2,3,7,8-tetracholorodibenzo-p-dioxin (TCDD) induced predominantly cytochrome P4501A1 (CYP1A1) in rat hepatocytes and predominantly CYP1A2 in human hepatocytes. As part of our research program to evaluate species-differences in response to CYP inducers, we studied the effects of TCDD on CYP1A activity, protein, and gene expression in primary cultures of rat and human hepatocytes. TCDD was found to induce CYP1A activity, measured as ethoxyresorufin-O-deethylase (EROD) activity, in both rat and human hepatocytes. TCDD induction of EROD activity in human hepatocytes (2-5 fold of concurrent solvent control), was significantly lower than that found in rat hepatocytes ( 20-fold of concurrent solvent control). Two structural analogs of TCDD, 2,3,7,8-tetrachlorodibenzofuran (TCDF) and 6-nitro-1,3,8-trichlorodibenzofuran (6-NCDF), were also evaluated. As observed for TCDD, human hepatocytes consistently showed a lower response than rat hepatocytes. As most TCDD-related effects are believed to be mediated via binding of the TCDD-Ah receptor (AhR) complex to DNA, nuclear AhR levels were measured in rat and human hepatocytes after TCDD treatment. We found that the nuclear AhR levels in TCDD-treated rat hepatocytes were approximately 4 times higher than found in TCDD-treated human hepatocytes. However, the estimated binding affinity of [3H]TCDD to nuclear AhR from rat hepatocytes was similar. The species difference in response to TCDD was further evaluated by analysis of CYP1A1 and CYP1A2 mRNA levels using Northern analysis, and P4501A1 and 1A2 protein levels using Western immunoblotting. Results showed that, at both gene expression and protein levels, TCDD induced predominantly CYP1A1 in rat hepatocytes and CYP1A2 in human hepatocytes.     

Modulation of Ah receptor and CYP1A1 expression by alpha-naphthoflavone in rainbow trout hepatocytes

The objective of this study was to evaluate whether alpha-naphthoflavone (ANF) modulates aryl hydrocarbon receptor (AhR) signaling in rainbow trout (Oncorhynchus mykiss). AhR and cytochrome P450 1A1 (CYP1A1) protein and mRNA content were used as indictors of AhR signaling. Primary culture of rainbow trout hepatocytes were exposed to different concentrations of ANF (10(-9)-10(-5) M), while beta-naphthoflavone (BNF 10(-10)-10(-6) M) and a combination of ANF and BNF were used to elucidate the impact of ANF on AhR signaling. ANF increased AhR and CYP1A1 protein expression in a concentration-related manner; the maximal induction was about 50% that of BNF. Despite the differences in protein content between ANF and BNF stimulation, the maximal AhR and CYP1A1 mRNA abundance seen with the high concentrations of ANF and BNF were similar. ANF significantly decreased ( approximately 50%) BNF-induced AhR protein expression (only at 10(-9) M), but not CYP1A1 protein and gene expression. In addition, ANF at a sub-maximal concentration (10(-7) M) did not affect BNF-induced AhR protein content, but increased the sensitivity of hepatocytes to BNF-mediated CYP1A1 protein expression. Taken together, the mode of action of ANF appears similar to BNF, including modulation of AhR expression and activation of AhR-mediated signaling in rainbow trout hepatocytes. Overall, ANF is not only a partial AhR agonist, but may also modify BNF-mediated AhR signaling in trout hepatocytes.     

Induction of cytochrome P450 1A and DNA damage in isolated rainbow trout (Oncorhynchus mykiss) hepatocytes by 2,3,7,8 tetrachlorodibenzo-p-dioxin

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on hepatocytes isolated from immature rainbow trout (Oncorhynchus mykiss) by collagenase perfusion were investigated with respect to induction of cytochrome P450 1A (CYP1A) enzyme activities and protein contents as well as DNA damage. Exposure of primary rainbow trout hepatocytes to TCDD resulted in increased CYP1A contents, as determined by immunoblotting, enhanced activities of 7-ethoxyresorufin-O-deethylase (EROD) and increased DNA damage as determined by the comet assay. By means of electron microscopy, no symptoms of cytotoxicity could be observed except for slight increases of lysosomal components and the smooth endoplasmic reticulum. Whereas CYP1A contents constantly increased over the duration of the entire experiment, EROD activities remained constant from day 3 of exposure to 1 nM TCDD; maximum induction of CYP1A activities was reached with 0.1 nM TCDD after 5 days. DNA damage increased in a time- and dose-dependent fashion until day 3. After 5 days, DNA damage was less pronounced, and the number of damaged nuclei declined in all TCDD concentrations. Since TCDD has been shown to not directly react with DNA, metabolism of TCDD or TCDD-induced changes in other metabolic pathways are suspected to result in the production of DNA-reactive (endogenous) substances.     

Induction of cytochrome P450 1A1 and conjugating enzymes in rainbow trout (Oncorhynchus mykiss) liver: A time course study

1. The effects of i.p. injections of isosafrole (ISF) or β-naphthoflavone (β-NF) on the cytochrome P450 (CYP) 1A1 system and conjugating enzymes were investigated in livers from juvenile rainbow trout in a time course study employing catalytic, immunochemical and cDNA probes.2. β-NF treatment resulted in a rapid rise in CYP1A1 mRNA followed by accumulation of P450 1A1 protein and P450 1A1 mediated enzyme activity measured as ethoxyresorufin-O-deethylase (EROD) activity.3. ISF treatment resulted in a comparatively weak induction of CYP1A1 mRNA and P450 1A1 protein levels whilst EROD activity was markedly induced; thus when expressed on the basis of immunoquantified P450 1A1 protein, the specific EROD activity was signficantly higher in ISF than β-NF treated fish.4. In vitro inhibition studies revealed that ISF inhibited EROD activity to a far lesser extent than β-NF.5. Conjugation enzymes represented by phenol UDP-glucuronosyltransferase and glutathione S-transferase (GST) activities, were induced by β-NF, whereas ISF treatment had no effect on these enzyme activities.6. Immunoblotting using antibodies raised against rat GST7-7 showed that a Pi class trout GST enzyme was induced by β-NF treatment.     

Induction of cytochrome P450 1A and DNA damage in isolated rainbow trout (Oncorhynchus mykiss) hepatocytes by 2,3,7,8 tetrachlorodibenzo-p-dioxin

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on hepatocytes isolated from immature rainbow trout (Oncorhynchus mykiss) by collagenase perfusion were investigated with respect to induction of cytochrome P450 1A (CYP1A) enzyme activities and protein contents as well as DNA damage. Exposure of primary rainbow trout hepatocytes to TCDD resulted in increased CYP1A contents, as determined by immunoblotting, enhanced activities of 7-ethoxyresorufin-O-deethylase (EROD) and increased DNA damage as determined by the comet assay. By means of electron microscopy, no symptoms of cytotoxicity could be observed except for slight increases of lysosomal components and the smooth endoplasmic reticulum. Whereas CYP1A contents constantly increased over the duration of the entire experiment, EROD activities remained constant from day 3 of exposure to 1 nM TCDD; maximum induction of CYP1A activities was reached with 0.1 nM TCDD after 5 days. DNA damage increased in a time- and dose-dependent fashion until day 3. After 5 days, DNA damage was less pronounced, and the number of damaged nuclei declined in all TCDD concentrations. Since TCDD has been shown to not directly react with DNA, metabolism of TCDD or TCDD-induced changes in other metabolic pathways are suspected to result in the production of DNA-reactive (endogenous) substances.     

Effects of non-ortho-substituted polychlorinated biphenyls (congeners 77 and 126) on cytochrome p4501a and conjugation activities in rainbow trout (Oncorhynchus mykiss)

Immature rainbow trout (Oncorhynchus mykiss) in two separate experiments received a single intraperitoneal injection of 0.1, 1 and 5 mg/kg of either 3,3′,4,4′-tetra- or 3,3′,4,4′,5-pentachlorobiphenyl (IUPAC congeners 77 and 126, respectively). The experiments were run at water temperatures of 6 °C and 4 °C. Fish were killed 6 days after the injection. Biotransformation enzyme activities and cytochrome P4501A (CYP1A) amount and occurrence in different tissues were assayed. Congeners 77 and 126 strongly induced 7-ethoxyresorufin O-deethylase (EROD) and benzo(α)pyrene hydroxylase (AHH) activities in liver and kidney of rainbow trout. The induction of these cytochrome P4501A dependent monooxygenases was dose-related especially with congener 77 in the kidney. However, in the liver the highest dose of both congeners and in kidney the highest dose of congener 126 did not increase the catalytic monooxygenase activities as much as would have been expected based on the responses obtained with the lower doses. This may be because the monooxygenase activities already had attained their maximal induction capacity at 1 mg/kg dose of each congener. The PCB residues in liver were also determined and found to be highest after 5 mg/kg injections (610 μg/kg wet weight with congener 77 and 220 μg/kg with congener 126). When cytochrome P4501A protein content was measured, the induction of cytochrome P4501A was still on the increase even in those cases where catalytic activity failed to show any further induction. Immunohistochemical samples from liver, kidney and intestine showed cytochrome P4501A staining which strongly correlated with cytochrome P4501A in microsomes. Such observations suggest that the amount and occurrence of P4501A in the tissues can express the induction even when catalytic activities seem to be suppressed. With respect to enzymes mediating conjugation reactions, hepatic and renal UDP-glucuronosyltransferase (UDP-GT) activities showed elevated levels especially with the 1 and 5 mg/kg doses of both congeners. Glutathione S-transferase (GST) activities did not show such a clear trend. Congeners 77 and 126 preferentially affected the P4501A enzymes but to some extent also conjugation activities.     

Expression of HSP70 and CYP1A protein in ovary and liver of juvenile rainbow trout exposed to beta-naphthoflavone

Cytochrome P4501A (CYP1A) and the 70-kDa stress protein (HSP70) were determined using Western blotting in the ovary and liver of juvenile female rainbow trout (Oncorhynchus mykiss) exposed for 4 days to beta-naphthoflavone (betaNF) following a single intraperitoneal injection. Ovarian CYP1A protein was observed in both control and betaNF-exposed fish, indicating constitutive and inducible expression of CYP1A in immature trout ovaries. CYP1A protein levels determined using densitometry were 14- and 46-fold greater in betaNF-exposed trout compared to controls in the liver and ovary, respectively. Hepatic microsomal ethoxyresorufin O-deethylase (EROD) activity, a specific catalytic marker of CYP1A, was also induced 38-fold above controls following betaNF exposure. Hepatic HSP70 protein expression was significantly higher in whole cell homogenates, but not in cytosolic fractions, collected from betaNF-exposed fish in comparison to control fish. There was no difference in ovarian HSP70 levels determined in whole cell homogenates between control and betaNF-exposed fish. The observation that unlike liver, ovarian HSP70 expression remained unchanged following induction of CYP1A protein may be related to the sensitivity of the teleost ovary to environmental toxicants that act as aryl hydrocarbon receptor agonists.     

2,3,7,8-Tetrachlorodibenzo-p-dioxin alters melatonin metabolism in fish hepatocytes

Pineal hormone melatonin is an important regulator of endocrine and circadian rhythms in vertebrates. Since liver is assumed to be the major organ in the metabolism of this indole hormone, we investigated the effect of the known Ah-receptor agonist, 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD) on melatonin metabolism in fish hepatocytes as well as the in vitro effect of melatonin on trout hepatic microsomal cytochrome P4501A (CYP1A) catalyst. Primary cell cultures of rainbow trout hepatocytes were exposed to [3H]melatonin (1 nM to 1 microM) alone and in combination with TCDD (50 pM) at 15 degrees C for 24 or 48 h. Analysis of melatonin and its metabolites in the culture medium and hepatocytes by HPLC revealed that about 96% of the added [3H]melatonin was metabolised after 24 h in both control and TCDD treated cultures. 3H-radioactivity was found mainly in the culture medium and less than 5% of the total 3H-radioactivity retained inside hepatocytes. Of the HPLC separated metabolites, one coeluted with 6-hydroxymelatonin and one unknown metabolite eluted after 6-hydroxymelatonin. In addition, two other metabolites were more water-soluble than 6-hydroxymelatonin and were considered to be conjugated products. Treatment of the hepatocytes with TCDD increased the amount of the major oxidated product, 6-hydroxymelatonin, about 2.5-fold after 24 h and 1.2-fold after 48 h exposure, respectively when compared with the control cultures. Whereas the amount of the unknown metabolite eluting after 6-hydroxymelatonin decreased about 1.3-fold after 24 h and 1.2-fold after 48 h exposure, respectively. Melatonin alone did not affect P4501A associated EROD-activity or CYP1AmRNA levels in the primary hepatocyte cultures. TCDD-treatment increased EROD-activity 3 to 5-fold and respective CYP1AmRNA content 6 to 14-fold, when compared with the control or melatonin-treated cultures. Furthermore, melatonin competitively inhibited EROD-activity in liver microsomes with a Ki value of 62.06+/-3.78 microM. The results show that TCDD alters metabolic degradation of melatonin in hepatocytes and suggest that P4501A may be an important P450 isoenzyme involved in oxidative metabolism of melatonin in fish liver.     

Temporal kinetics and concentration-response relationships for induction of CYP1A, CYP2B, and CYP3A in primary cultures of beagle dog hepatocytes

Compared to other species, little information is available on the xenobiotic-induced regulation of cytochrome P450 enzymes in the beagle dog. Dogs are widely used in the pharmaceutical industry for many study types, including those that will impact decisions on compound progression. The purpose of this study was (1) to determine the temporal kinetics of drug-induced changes in canine CYP1A, CYP2B, and CYP3A mRNA and enzymatic activity, and (2) to characterize concentration-response relationships for CYP1A2, CYP2B11, and CYP3A12 using primary cultures of canine hepatocytes treated with beta-naphthoflavone (BNF), phenobarbital (PB), and rifampin (RIF), respectively. CYP1A1 and CYP1A2 mRNA exhibited maximal expression (12,700-fold and 206-fold, respectively) after 36 h of treatment with BNF. PB treatment, but not RIF treatment, caused maximal induction of CYP2B11 mRNA (149-fold) after 48 h of treatment. CYP3A12 and CYP3A26 mRNA levels were increased maximally after 72 h of treatment with PB and RIF (CYP3A12, 35-fold and 18-fold, and CYP3A26, 72-fold and 22-fold with PB and RIF treatment, respectively). Concentration-response relationships for BNF induced 7-ethoxyresorufin O-dealkylation (EROD) (EC(50) = 7.8 +/- 4.2 microM), PB induced 7-benzyloxyresorufin O-dealkylation (BROD) (EC(50) = 123 +/- 30 microM), and PB and RIF induced testosterone 6beta-hydroxylation (EC(50) = 132 +/- 28 microM and 0.98 +/- 0.16 microM) resembled the relationship for human CYP induction compared to that of rodent. Interestingly, RIF had no effect on CYP2B11 expression, which represents a species difference overlooked in previous investigations. Overall, the induction of dog CYP1A, CYP2B, and CYP3A exhibits characteristics that are intermediate to those of rodent and human.     

Preferential inducibility of CYP1A1 and CYP1A2 by TCDD: differential regulation in primary human hepatocytes versus transformed human cells

Cytochrome P4501A1 (CYP1A1) induction, a marker of aryl hydrocarbon (Ah) receptor activation, has been associated with carcinogenicity of the environmental agent 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Consistently, we show that TCDD treatment led to induction of CYP1A1 in responsive human cancer cell lines including HepG2, LS174T, and MCF-7, as determined by Western blotting and CYP1A form-selective R-warfarin 6- and 8-hydroxylation. TCDD, however, preferably induced CYP1A2, not CYP1A1, in primary human hepatocytes. Such CYP1A form-preferred induction at the protein level was apparently uncorrelated with non-preferred mRNA induction in any cells studied. Moreover, while both genes were up-regulated by TCDD in primary hepatocytes and HepG2 cells, the induction of CYP1A1 and CYP1A2 at the mRNA level was distinguishable, indicated by the marked differences in activation kinetics and the response to the protein synthesis inhibitors, anisomycin and cycloheximide. Furthermore, formation of total benzo(a)pyrene (BaP)-DNA adducts was not altered following BaP exposure in TCDD-treated primary hepatocytes, whereas significantly elevated, in a CYP1A1-dependent manner, in the treated HepG2 cells. Taken together, our findings, demonstrating the complexities of TCDD-associated human Ah receptor function and differential regulations of CYP 1A enzymes, suggest clearly the need for caution when extrapolating data obtained in cell-based models.     

Induction of cytochrome P4501A by highly purified hexachlorobenzene in primary cultures of ring-necked pheasant and Japanese quail embryo hepatocytes

Primary cultures of ring-necked pheasant (Phasianus colchicus) and Japanese quail (Coturnix japonica) embryo hepatocytes were used to compare the potencies of highly purified hexachlorobenzne (HCB-P), reagent-grade HCB (RG-HCB) and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) as inducers of ethoxyresorufin O-deethylase (EROD) activity, cytochrome P4501A (CYP1A4) messenger ribonucleic acid (mRNA) and CYP1A5 mRNA. HCB-P, RG-HCB and TCDD all induced EROD activity and up-regulated CYP1A4 and CYP1A5 mRNA. Induction was not caused by contamination of HCB with polychlorinated dibenzo-p-dioxins, dibenzofurans or biphenyls. Based upon a comparison of the EC(50) and EC(threshold) values for EROD and CYP1A4/5 concentration-response curves, the potency of HCB relative to TCDD was 0.001 in ring-necked pheasant and 0.01 in Japanese quail embryo hepatocytes. Differences in species sensitivity to HCB were found to be mainly dictated by differences in species sensitivity to TCDD rather than differences in the absolute potency of HCB. Consequently, ring-necked pheasant and Japanese quail embryo hepatocytes were found to be equally sensitive to HCB exposure. Species sensitivity comparisons were also made with chicken (Gallus gallus domesticus) and revealed that chicken embryo hepatocytes were less responsive to EROD induction (lower maximal response) by HCB compared to the embryo hepatocytes of pheasant and quail.     

Estrogen-mediated suppression of cytochrome P4501A (CYP1A) expression in rainbow trout hepatocytes: role of estrogen receptor.

Hepatic CYP1A expression in fish can be modulated by the female sex hormone, 17beta-estradiol (E2), however neither the mechanism of E2 suppression of CYP1A nor the capacity for hormonal regulation to overcome CYP1A induction by xenobiotics are known. The present study investigates for the first time in fish if the estrogen receptor (ER) is involved in the suppressive action of E2 on CYP1A gene expression. The study further examines, if the E2 effect is able to overcome xenobiotic induction of CYP1A. As experimental model, in vitro cultures of rainbow trout, Oncorhynchus mykiss, hepatocytes were used. The effect of E2 on CYP1A was assessed by measuring the CYP1A-associated 7-ethoxyresorufin-O-deethylase (EROD) enzyme activity, and CYP1A mRNA contents. E2 at non-cytotoxic concentrations caused a significant time- and concentration-dependent decline of basal but not of induced hepatic EROD activities. The inhibitory action of E2 on basal CYP1A was also evident at the mRNA level. The presence of the ER antagonist tamoxifen abolished the inhibitory action of E2 on CYP1A expression. The results from these in vitro experiments provide evidence (a) that the ER is involved in the suppressive action of E2 on CYP1A, and (b) that E2 inhibitory action does not overcome xenobiotic induction of CYP1A.