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.     

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.     

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 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 7-ethoxyresorufin-O-deethylase activity by planar chlorinated hydrocarbons and polycyclic aromatic hydrocarbons in cell lines from the rainbow trout pituitary

The induction of 7-ethoxyresorufin-o-deethylase (EROD) activity was examined in three rainbow trout pituitary cell lines: RTP-91E, RTP-91F and RTP-2. RTP-91E and RTP-91F were developed from the pituitary of a male and have epithelial-like and fibroblast-like morphologies, respectively. RTP-2, which was described previously, was developed from the pituitary of a female and has an epithelial-like shape. In all cell lines EROD activity was induced by 2,3,7,8- tetrachlorodibenzo-p-dioxin (TCDD). Immunoblotting with the polyclonal antibody, anti-trout CYP1A1(277-294)/KLH, confirmed induction of a 58-kDa polypeptide. Potential inhibitors of the aryl hydrocarbon receptor, geldanamycin and alpha-naphthoflavone, inhibited EROD induction by TCDD. Other compounds inducing EROD activity were 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF), 3,3',4,4',5-pentachlorobiphenyl (PCB 126), and 3-methylcholanthrene (3MC). When judged by the concentration eliciting 50% of the maximal response (EC50), induction was similar in RTP-2 and RTP-91E, and less effective in RTP-91F. Regardless of the cell line, the rank order from most to least potent inducer on the basis of EC50 value was TCDD> or =PCDD>TCDF>PCB 126>3MC. When induction potencies were expressed relative to TCDD, the values obtained with the pituitary cell lines were similar to previously published values derived with a rainbow trout liver cell line.     

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.     

Transitory metabolic disruption and cytotoxicity elicited by benzo[a]pyrene in two cell lines from rainbow trout liver

Two cell lines, RTL-W1 and R1, from rainbow trout liver were used to investigate the effects of benzo[A]pyrene (BaP). BaP induced a catalytic measure of CYP1A, 7-ethoxyresorufin-O-deethylase (EROD) activity, in the rainbow trout liver cell line RTL-W1 but not in R1. Geldanamycin inhibited EROD induction by BaP. Potential BaP metabolites, BaP-7,8-dihydrodiol (BDP) and 6,12-BaP quinone (BQ) also induced EROD activity in RTL-W1. Very low BaP concentrations slightly stimulated cell proliferation in both cell lines. Higher BaP concentrations caused cytotoxicity in RTL-W1 but not in R1. Cytotoxicity was detected in a cell viability assay with 5-carboxyfluorescein diacetate acetoxymethyl ester, and as a decline in cell number. In both cell lines, BaP exposure impaired the reduction of the redox dye, alamar Blue (AB). After BaP removal, AB reduction recovered. Similar results were observed with BQ. As AB monitors metabolic activity, this novel phenomenon was termed transitory metabolic disruption. This decline in AB readings that was caused by BaP was ameliorated in RTL-W1 by alpha-naphthoflavone and geldanamycin, which suggests a role for CYP1A, and in R1 by indomethacin, which suggests involvement of prostaglandin-H-synthase. The significance of the response to BaP that is detected with AB and whether other PAHs cause it will be interesting future questions.     

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.     

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.     

Inhibition of in vitro aflatoxin B1-DNA binding in rainbow trout by CYP1A inhibitors: α-naphthoflavone, β-naphthoflavone and trout CYP1A1 peptide antibody

Rainbow trout cytochrome P450 (CYP)1A detoxifies aflatoxin B₁ (AFB₁) to aflatoxin M₁ (AFM₁), whereas CYP2K1 activates AFB₁ to AFB₁-8,9-epoxide. We report that α-naphthoflavone (ANF) and β-naphthoflavone (BNF) both strongly inhibit CYP1A-mediated ethoxyresorufin O-deethylase (EROD) activity (K_i = 9.1 ± 0.8 and 7.6 ± 1.1 nM, respectively). These inhibitors (selective for mammalian CYP1A at low concentrations), as well as rabbit polyclonal antibody to a trout CYP1A1 peptide (residues 277–294), also strongly inhibited trout microsome-catalyzed AFB₁-DNA binding and lauric acid (ω-1) hydroxylation in vitro, reactions previously established to be CYP2K1-dependent. ANF at 0.5, 5, 50 and 500 μM inhibited liver microsome-catalyzed AFB₁-DNA binding by 22, 58, 84 and 91%, respectively, whereas BNF at the same concentrations inhibited 22, 74, 78 and 81%, respectively. The CYP1A1 peptide and CYP2K1 polyclonal antibodies (10 mg IgG/mg microsomal protein) inhibited AFB₁-DNA binding by 84 and 66%, respectively, compared with pre-immune IgG. Lauric acid (ω-1) hydroxylation was inhibited 61% by 5 μM ANF, 69% by 5 μM BNF and 100% by either antibody at 12 mg IgG/mg microsomal protein. These results demonstrate that mammalian CYP1A inhibitors also inhibit trout microsomal AFB₁-DNA binding and lauric acid (ω-1) hydroxylation, catalyzed primarily by CYP2K1. In the absence of evidence that trout CYP1A can catalyze AFB₁-DNA binding, the results suggest configuration similarities at, or near, the active sites for these two fish enzymes that result in antibody crossreaction and loss of the inhibitor specificity observed with mammalian CYP1A.     

The effect of monooxygenase inducing agents on the incorporation of [35S]methionine into hepatic microsomal protein of rainbow trout (Salmo gairdneri)

Treatment of rainbow trout (Salmo gairdneri) with 150 mg/kg BNF resulted in an increase in hepatic microsomal monooxygenase activity as assessed by ECOD and EROD when compared to those activities in corn oil-pretreated animals. Administration of 100 mg/kg 2,4,5,2',4',5'-hexachlorobiphenyl (6-CB) to trout had no significant effect on these catalytic activities or on BeND. The amount of radioactivity in hepatic microsomes at 24, 48 or 72 hr following the administration of 75 muCi of [35S]methionine was consistently higher in animals pretreated with BNF than in those treated with corn oil or 6-CB. Autoradiography/fluorography of electrophoretograms demonstrated the appearance of at least three radiolabeled bands in the 50,000-60,000 mol. wt range in solubilized microsomes from BNF-treated fish which were not present in microsomes from control animals or fish treated with 6-CB. These data indicate that the stimulation of hepatic microsomal catalytic activities observed following the administration of 3-MC-type agents to rainbow trout is due, at least in part, to induction of enzyme(s) rather than activation of existing enzyme(s). These results further support the observation that fish appear to be non-responsive to phenobarbital-type inducing agents.     

Biochemical and molecular biological analysis of different responses to 2,3,7,8-tetrachlorodibenzo-p-dioxin in chick embryo heart and liver

We studied the mechanism of toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in the chick embryo, which is an organism highly sensitive to TCDD. TCDD was injected into egg yolks prior to embryogenesis, and eggs were incubated for 12 or 18 days. In TCDD-exposed embryos, we observed increased heart wet weight and change in the color of the liver, with abnormal fatty vesicle formation. To determine whether these effects were mediated by the aryl hydrocarbon receptor (AhR), we examined expression levels of AhR, CYP1A4, and CYP1A5. AhR was expressed continuously in the heart and liver during embryogenesis, whereas induction of CYP1A4 and CYP1A5 by TCDD was detected only in the liver. In situ hybridization study of tissue sections revealed induction of CYP1A4 in the abnormal liver tissue in which color change was not observed. To determine whether these different responses to TCDD depended on the cell type, primary cultures of chick hepatocytes and cardiac myocytes were established and 7-ethoxyresorufin-O-deethylase (EROD) activity was measured. Induction of EROD activity following exposure to TCDD was detected in hepatocytes but not in cardiac myocytes. Although the heart is a principal target organ for TCDD toxicity and AhR is expressed throughout embryogenesis, induction of CYP1A was not observed in the chick heart. Thus, we conclude that defects in the heart induced by exposure to TCDD occur via a different pathway than that occurring in the 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.     

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.     

Down regulation of CYP 1A1 by glucocorticoids in trout hepatocytes in vitro

Summary Short-term culture of rainbow trout (Onchorhynchus mykiss) hepatocytes was used to examine the effect of dexamethasone (DEX) on microsomal CYP 1A1 protein content and 7-ethoxyresorufin-O-deethylase (EROD) activity in vitro. Hepatocytes prepared by controlled collagenase digestion and plated at a density of 0.25 × 10⁶ cells/cm² in plastic culture dishes precoated with trout skin extract (7.6 μg skin protein/cm²) to facilitate cell attachment were maintained at 16° C. Cells were treated with DEX (10⁻⁹ to 10⁻⁷ M) or vehicle (dimethyl sulfoxide, DMSO) at 24 h. Microsomal CYP 1A1 protein content and EROD activities were measured at 72 h. Both CYP 1A1 protein as measured by Western blots using CYP 1A1 specific anti-sera and EROD activity were significantly lower in DEX (10⁻⁸ to 10⁻⁷ M)-treated hepatocytes compared to untreated (control) or DMSO-treated cells. The effect was dose dependent in that a gradual decrease of CYP 1A1 protein and EROD activities were seen with increasing doses of DEX (10⁻⁸ to 10⁻⁷ M). DEX at 10⁻⁹ M was ineffective. Concomitant addition of 10⁻⁶ M RU486, a type II specific glucocorticoid receptor antagonist, to hepatocytes treated with 10⁻⁷ M DEX abolished the DEX effect. RU486 at 10⁻⁸ M was ineffective. Spironolactone (10⁻⁸ to 10⁻⁶ M), a type I specific glucocorticoid receptor antagonist, did not counteract the DEX effect. RU486 or spironolactone (10⁻⁶ M) alone had no effect on CYP 1A1 under similar conditions. DEX thus down regulates CYP 1A1 in fish cultured hepatocytes and this regulation is mediated through the type II glucocorticoid receptor(s).