Specificity and cross-reactivity of monoclonal and polyclonal antibodies against cytochrome P-450E of the marine fish scup

Development and Applications of a Zebrafish (Danio rerio) CYP1A-Targeted Monoclonal Antibody (CRC4) with Reactivity across Vertebrate Taxa: Evidence for a Conserved CYP1A Epitope

CYP1A is a heme-thiolate enzyme associated with the cytochrome P4501A1 monooxygenase system and is inducible by a wide variety of xenobiotics and endogenous ligands that bind and activate the aryl hydrocarbon receptor (AHR). The AHR-CYP1A axis is important for detoxification of certain xenobiotics and for homeostatic balance of endogenous sex hormones, amine hormones, vitamins, fatty acids, and phospholipids. Herein, we generated and described applications of a zebrafish CYP1A-targeted monoclonal antibody (mAb CRC4) that fortuitously recognizes induced CYP1A across vertebrate taxa, including fish, chicken, mouse, rat, and human. We then demonstrated that mAb CRC4 targets a highly conserved epitope signature of vertebrate CYP1A. The unique complimentary determining region (CDR) sequences of heavy and light chains were determined, and these Ig sequences will allow for the expression of recombinant mAb CRC4, thus superseding the need for long-term hybridoma maintenance. This antibody works well for immunohistochemistry (IHC), as well as whole-mounted IHC in zebrafish embryos. Monoclonal antibody CRC4 may be particularly useful for studying the AHR-CYP1A axis in multiple vertebrate species and within the context of Oceans and Human Health research. By using archived samples, when possible, we actively promoted efforts to reduce, replace, and refine studies involving live animals.

Functional characterization of zebrafish cytochrome P450 1 family proteins expressed in yeast

BACKGROUND

Zebrafish express five cytochrome P450 1 genes: CYP1A, CYP1B1, CYP1C1, CYP1C2, inducible by aryl hydrocarbon receptor agonists, and CYP1D1, a constitutively expressed CYP1A-like gene. We examined substrate selectivity of CYP1s expressed in yeast.

METHODS

CYP1s were expressed in W(R) yeast, engineered to over-express P450 reductase, via pYES/DEST52 and via pYeDP60. Microsomal fractions from transformed yeast were examined for activity with fluorogenic substrates, benzo[a]pyrene and testosterone. Modeling and docking approaches were used to further evaluate sites of oxidation on benzo[a]pyrene and testosterone.

RESULTS

CYP1s expressed in yeast dealkylated ethoxy-, methoxy-, pentoxy- and benzoxy-resorufin (EROD, MROD, PROD, BROD). CYP1A and CYP1C2 had the highest rates of EROD activity, while PROD and BROD activities were low for all five CYP1s. The relative rates of resorufin dealkylation by CYP1C1, CYP1C2 and CYP1D1 expressed via pYeDP60 were highly similar to relative rates obtained with pYES/DEST52-expressed enzymes. CYP1C1 and CYP1C2 dealkylated substituted coumarins and ethoxy-fluorescein-ethylester, while CYP1D1 did not. The CYP1Cs and CYP1D1 co-expressed with epoxide hydrolase oxidized BaP with different rates and product profiles, and all three produced BaP-7,8,9,10-tetrol. The CYP1Cs but not CYP1D1 metabolized testosterone to 6β-OH-testosterone. However, CYP1D1 formed an unidentified testosterone metabolite better than the CYP1Cs. Testosterone and BaP docked to CYP homology models with poses consistent with differing product profiles.

CONCLUSIONS

Yeast-expressed zebrafish CYP1s will be useful in determining further functionality with endogenous and xenobiotic compounds.

GENERAL SIGNIFICANCE

Determining the roles of zebrafish CYP1s in physiology and toxicology depends on knowing the substrate selectivity of these enzymes.

Genotoxic bioactivation of constituents of a diesel exhaust particle extract by the human lung

The ability of the human lung to catalyze genotoxic bioactivation of constituents of diesel exhaust particle (DEP) extract (DEPE) and the identity of the lung enzymes involved in the bioactivation were investigated using human lung tissues obtained from surgical resections. Genotoxicity was determined by lung S9-catalyzed mutagenicity of DEPE constituents to Salmonella typhimurium TA98NR in the Ames test and by DEPE-induced pneumocyte DNA damage response as determined by γH2Ax expression in ex vivo tissues. S9 was prepared from lung explants treated ex vivo with either DEPE to induce pulmonary enzymes (DEPE-S9) or vehicle only (CON-S9). TA98NR served as the tester strain for the purpose of enhancing and minimizing the contribution of lung S9 and Salmonella, respectively, to DEPE bioactivation. DEPE-S9 was 2.2-fold more active than CON-S9 or rat liver S9 in DEPE bioactivation and the bioactivation was inhibited 58, 45, 22, and 16% by α-naphthoflavone, dicumarol, ketoconazole, and ticlopidine, respectively. Alveolar S9 was less active than bronchioalveolar S9 in DEPE bioactivation. DEPE and diesel exhaust particles (DEP) induced γ-pH2Ax expression in pulmonary cells. Pulmonary CYP1A1 and NQO1 were induced by DEPE treatment, with the constitutive and induced CYP1A1 distributed throughout all peripheral lung regions, whereas NQO1 was limited in distribution to bronchiolar epithelium. The results show that the human lung is highly active in catalyzing genotoxic bioactivation of diesel emission constituents and that CYP1A and NQO1 play major roles in the reaction. The findings underscore the usefulness of human lung tissues in studies of the pneumotoxicity potential of chemicals to humans.

Assessment of the sublethal toxicity of organochlorine pesticide endosulfan in juvenile common carp (Cyprinus carpio)

This study is aimed at evaluating the sublethal effects of endosulfan (EDS) in juvenile common carp (Cyprinus carpio). For this purpose, fish were exposed for 15 days to the technical EDS (95% pure) diluted in dimethyl sulfoxide (DMSO) 0.1% of the total volume in water solution in a semi-static system at sublethal concentration (1 μg/L). Subsequently, the liver somatic index (LSI) and factor condition (K) were determined. The total cytocrome P450 (CYP), CYP1A isoform, and the ethoxyresorufin-O-deethylase (EROD) activity were determined from the hepatic microsomal fraction as well as the activity of the oxidative stress enzyme system such as superoxide dismutase (SOD), catalase (CAT), glutathione-S-transferase (GST), glutathione peroxidase (GP(X)), glutathione reductase (GR), and glucose-6-phosphate dehydrogenase (G6PDH). Among the parameters assessed, EDS at the sublethal concentration in subchronic exposure caused significant changes in liver somatic indices as well as induction of the phase I biotransformation system and oxidative stress in juvenile common carp (Cyprinus carpio). Thus, it is seen that the use of biochemical biomarkers of environmental contamination in this study proved to be an extremely important tool for detecting the adverse effects of xenobiotics in the aquatic environment, even at low concentration.

Structural features of cytochrome P450 1A associated with the absence of EROD activity in liver of the loricariid catfish Pterygoplichthys sp

The Amazon catfish genus Pterygoplichthys (Loricariidae, Siluriformes) is closely related to the loricariid genus Hypostomus, in which at least two species lack detectable ethoxyresorufin-O-deethylase (EROD) activity, typically catalyzed by cytochrome P450 1 (CYP1) enzymes. Pterygoplichthys sp. liver microsomes also lacked EROD, as well as activity with other substituted resorufins, but aryl hydrocarbon receptor agonists induced hepatic CYP1A mRNA and protein suggesting structural/functional differences in Pterygoplichthys CYP1s from those in other vertebrates. Comparing the sequences of CYP1As of Pterygoplichthys sp. and of two phylogenetically related siluriform species that do catalyze EROD (Ancistrus sp., Loricariidae and Corydoras sp., Callichthyidae) showed that these three proteins share amino acids at 17 positions that are not shared by any fish in a set of 24 other species. Pterygoplichthys and Ancistrus (the loricariids) have an additional 22 amino acid substitutions in common that are not shared by Corydoras or by other fish species. Pterygoplichthys has six exclusive amino acid substitutions. Molecular docking and dynamics simulations indicate that Pterygoplichthys CYP1A has a weak affinity for ER, which binds infrequently in a productive orientation, and in a less stable conformation than in CYP1As of species that catalyze EROD. ER also binds with the carbonyl moiety proximal to the heme iron. Pterygoplichthys CYP1A has amino acid substitutions that reduce the frequency of correctly oriented ER in the AS preventing the detection of EROD activity. The results indicate that loricariid CYP1As may have a peculiar substrate selectivity that differs from CYP1As of most vertebrate.

Effects of the dioxin-like PCB 126 on larval summer flounder (Paralichthys dentatus)

Little is known about the sensitivity of teleost post-embryonic developmental stages (larval and metamorphic) to dioxin-like compounds. Larval and metamorphosing summer flounder (Paralichthys dentatus) were exposed to the dioxin-like polychlorinated biphenyl congener PCB 126, to compare their sensitivity to other fish species early life stages, and to document effects on metamorphic development, including degree of eye migration and gastric maturation. Median lethal doses (LD 50s) ranged between 30 and 220 ng/g wet mass, indicating that pre- and early-metamorphic stages of summer flounder are equally sensitive to the embryos of some of the most vulnerable fish species tested. Consistent with the presence of a functional aryl hydrocarbon receptor pathway, dose-dependent induction of cytochrome P-4501A (CYP1A) at four days post-exposure was observed in liver, stomach, intestine, and kidney of metamorphosing larvae. Stage-dependent differences in the epithelial distribution of CYP1A immunoreactivity were observed in the developing stomach of fish exposed to relatively high PCB 126 doses. A single sublethal dose (15 ng/g) delayed metamorphic progress (determined by the degree of eye migration), and resulted in abnormally high levels of cell proliferation and abnormal gastric gland morphology in late metamorphic stages. These results suggest that the post-embryonic larval and metamorphic stages of summer flounder, and potentially other fish species with complex life histories, are vulnerable to the effects of dioxin-like compounds, including lethality, developmental delay, and malformations.

Catalytic and immunochemical detection of hepatic and extrahepatic microsomal cytochrome P450 1A1 (CYP1A1) in white-sided dolphin (Lagenorhynchus acutus)

We have characterized microsomal systems and measured the levels of microsomal cytochrome P450 1A1 (CYP1A1) and ethoxyresorufin-O-deethylase (EROD) activity in multiple internal organs of male and female white-sided dolphin (Lagenorhynchus acutus) from the northwest Atlantic Ocean. Internal organs were sampled within 24h of death, sometimes in a period of hours, collection times which are significantly less than usually seen for marine mammals. Tissue autolysis, as assessed by histological analysis of liver, was minimal to none in all individuals. Total P420 did not correlate with time from death to sampling, suggesting that it is a poor indicator of P450 degradation in cetacean tissues where perfusion is not practical. The total hepatic microsomal P450 content, cytochrome b5 content, and NADPH-cytochrome c (P450) reductase (CPR) activity averaged 0.29nmolmg(-1), 0.12nmolmg(-1), and 238nmolmg(-1)min(-1), respectively. Microsomal CPR activity in liver was higher than that in lung and kidney, and was higher than that reported in liver of most other cetacean species. Immunodetected CYP1A1 content was low in all organs, less than 3pmolesCYP1A equivalentsmg(-1). EROD activity ranged from 9 to 376pmolesmg(-1)min(-1) and was greater in liver than in other tissues. Hepatic microsomal EROD activity and CYP1A1 content did not correlate. However, hepatic EROD activity, but not CYP1A1 protein content, was well correlated with both total PCB and Sigmamono-ortho PCB concentrations in blubber. Length, as a proxy for age, did not correlate with hepatic EROD activity or CYP1A1 protein levels, and sex did not influence the relationship between EROD and contaminant concentrations. We cannot easily control for the extent of tissue degradation in cetacean studies nor do we have a complete history of these animals. Therefore, other factors such as degradation or hormonal state may have a role in the observed relationships. Yet, as in other mammals, hepatic tissues appear to be a major site of CYP1A1 expression and probably of biotransformation of CYP1A substrates in white-sided dolphin. The expression of an EROD catalyst in liver likely reflects induction by PCBs, but the P450 enzyme catalyzing hepatic EROD activity in these whales may not be CYP1A1.

Identification of mitochondrial cytochrome P450 induced in response to polycyclic aromatic hydrocarbons in the mummichog (Fundulus heteroclitus)

Increasing evidence suggests that polycyclic aromatic hydrocarbons (PAHs) such as benzo[a]pyrene (BaP) are localized to the mitochondria. Because the toxic effects of many PAHs are the result of metabolism by cytochrome P4501A (CYP1A), it is important to investigate whether active forms of these enzymes can be identified in the mitochondria. In this study, we identified mitochondrial P450s with a monoclonal antibody against scup (Stenotomus chrysops) CYP1A in the isolated mitochondrial fraction of the liver from adult male mummichog (Fundulus heteroclitus) livers. The size of the protein in the mitochondria was similar to that of microsomal CYP1A. Fish dosed with 10mg/kg BaP had increased EROD activity in the mitochondrial fraction compared to controls. In mummichog larvae dosed with 100 microg/L BaP and 100 microg/L benzo[k]fluoranthene, CYP1A protein levels as well as enzyme activity were elevated. However, fish from a PAH-polluted Superfund site (Elizabeth River, Portsmouth VA) showed recalcitrant mitochondrial CYP1A protein levels and enzyme activity in a similar manner to microsomal CYP1A.

Up-regulation of hepatic ABCC2, ABCG2, CYP1A1 and GST in multixenobiotic-resistant killifish (Fundulus heteroclitus) from the Sydney Tar Ponds, Nova Scotia, Canada

Cellular defence against accumulation of toxic xenobiotics includes metabolism by phase I and II enzymes and export of toxicants and their metabolites via ATP-binding cassette (ABC) transporters. Liver gene expression of representatives of these three protein groups was examined in a population of multixenobiotic-resistant killifish (Fundulus heteroclitus) from the Sydney Tar Ponds, Nova Scotia, Canada. The Tar Ponds are heavily polluted with polycyclic aromatic hydrocarbons, polychlorinated biphenyls and heavy metals. The relationship among ABC transporters ABCB1, ABCB11, ABCC2, ABCG2, phase I enzyme cytochrome P4501A1 (CYP1A1) and phase II enzyme glutathione-S-transferase (GST-mu) was investigated by quantifying hepatic transcript abundance. In Tar Pond killifish, hepatic mRNA expression levels of ABCC2, ABCG2, CYP1A1 and GST-mu were elevated compared to reference sites, suggesting that hydrophobic contaminants undergo phase I and II metabolism and are then excreted into the bile of these fish. Hepatic ABCB1 and ABCB11 mRNA were not up-regulated in Tar Pond fish compared to two reference sites, indicating that these two proteins are not involved in conferring multixenobiotic resistance to Tar Pond killifish. The results suggest instead that liver up-regulation of phase I and II enzymes and complementary ABC transporters ABCC2 and ABCG2 may confer contaminant resistance to Tar Pond fish.

Tissue specific induction of cytochrome P450 (CYP) 1A1 and 1B1 in rat liver and lung following in vitro (tissue slice) and in vivo exposure to benzo(a)pyrene

Cytochrome P-450s (CYPs) detoxify a wide variety of xenobiotics and environmental contaminants, but can also bioactivate carcinogenic polycyclic aromatic hydrocarbons, such as benzo(a)pyrene (BaP), to DNA-reactive species. The primary CYPs involved in the metabolism and bioactivation of BaP are CYP1A1 and CYP1B1. Furthermore, BaP can induce expression of CYP1A1 and CYP1B1 via the aryl hydrocarbon receptor. Induction of CYP1A1 and CYP1B1 by BaP in target (lung) and non-target (liver) tissues was investigated utilizing precision-cut rat liver and lung slices exposed to BaP in vitro. Tissue slices were also prepared from rats pretreated in vivo with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) to induce expression of CYP1A1 and CYP1B1. In addition, in vivo exposure studies were performed with BaP to characterize and validate the use of the in vitro tissue slice model. In vitro exposure of liver and lung slices to BaP resulted in a concentration-dependent increase in CYP1A1 and CYP1B1 mRNA and protein levels, which correlated directly with the exposure-related increase in BaP-DNA adduct levels observed previously in the tissue slices [Harrigan, J.A., Vezina, C.M., McGarrigle, B.P., Ersing, N., Box, H.C., Maccubbin, A.E., Olson, J.R., 2004. DNA adduct formation in precision-cut rat liver and lung slices exposed to benzo(a)pyrene. Toxicological Sciences 77, 307-314]. Pretreatment of animals in vivo with TCDD produced a marked induction of CYP1A1 and CYP1B1 expression in the tissue slices, which was similar to the levels of CYP1A1 and CYP1B1 mRNA achieved in liver and lung following in vivo treatment with BaP. Following in vitro exposure to BaP, the levels of CYP1A1 were greater in the lung than the liver, while following all exposures (in vitro and in vivo), the levels of CYP1B1 mRNA were greater in lung tissue compared to liver. The higher expression of CYP1A1 and CYP1B1 in the lung was associated with higher levels of BaP-DNA adducts in the lung slices (Harrigan et al.'s work) and together, these results may contribute to the tissue specificity of BaP-mediated carcinogenesis.

Evidence for resistance to benzo[a]pyrene and 3,4,3'4'-tetrachlorobiphenyl in a chronically polluted Fundulus heteroclitus population

Halogenated aromatic hydrocarbons (HAHs) and polynuclear aromatic hydrocarbons (PAHs) are major environmental contaminants. Fish species that are chronically exposed to these compounds can develop resistance to their toxic effects. In all fish species studied to date, toxicant resistance has been accompanied by decreased inducibility of the xenobiotic metabolizing enzyme, cytochrome P450 1A (CYPIA). CYP1A induction is mediated through the Aryl Hydrocarbon Receptor (AHR). Although these compounds mediate their effects through this pathway, there have been resistant populations in which one chemical class cannot induce CYPIA expression (HAHs) while the other (PAHs) can. Resistance to PAHs was examined in a HAH-resistant population of Fundulus heteroclitus collected from a site contaminated with both compound classes (Newark Bay, NJ). Fish were injected intraperitoneally with the HAH 3,4,3',4'-tetrachlorobiphenyl (PCB77), benzo[a]pyrene (B[a]P, a PAH) or vehicle and sacrificed after 2 (B[a]P) or 5 days (PCB77, vehicle). We found no significant increase in CYP1A mRNA levels in resistant Newark Bay F. heteroclitus treated with either B[a]P or PCB77, while there was a 3.9 fold (PCB77) and 4.2 fold (B[a]P) increase in CYP1A mRNA in Flax fish relative to controls. AHR labeling studies revealed significantly (P < 0.05) lower levels of hepatic AHR in Newark fish (1,770 +/- 1,693.2 DPM) relative to Flax fish (6,082.5 +/- 1,709.9 DPM). Overall, these data suggest Newark F. heteroclitus are resistant to both PAHs and HAHs at the level of CYP1A mRNA, which might be mediated, in part, though lower expression of AHR. We are currently studying the promoter sequence to determine its role in chemical resistance.

Biochemical indicators of contaminant exposure in spotted pigfish (Orthopristis ruber) caught at three bays of Rio de Janeiro coast

The initial sampling in the Marine Monitoring Program (MOMAM), coordinated by the Ministry of Marine Affairs (IEAPM), was performed along the southeast coast of Brazil. Orthopristis ruber samples were collected at Guanabara, Sepetiba and Ilha Grande Bays. Microsomal CYP1A levels and cytosolic cholinesterase (ChE), catalase (CAT) and glutathione S-transferase (GST) activities were measured in the liver of these fish according to established procedures. CAT activity and CYP1A content were significantly higher (P < or = 0.05) in fish caught at Guanabara Bay, which might be due to higher levels of peroxisome proliferators and Ah receptor agonists, respectively, at this site compared to the other sites. Also, lower GST activity was observed in fish from this site, which may possibly be related to the presence of oxidative-stress inducing compounds.

Species-specific responses of constitutively active receptor (CAR)-CYP2B coupling: lack of CYP2B inducer-responsive nuclear translocation of CAR in marine teleost, scup (Stenotomus chrysops)

The mammalian constitutively active receptor (CAR) is a novel ligand-activated transcription factor that participates in controlling the expression of cytochrome P450 2B (CYP2B) genes in response to pharmaceutical agents (phenobarbital) and halogenated aromatic hydrocarbons (ortho-substituted PCBs). The occurrence and physiological function of this protein are as yet unknown in marine animals, where there has been a paradoxical lack of induction by PB-type chemicals. One approach to understanding CAR function is to study the evolutionary history of processes such as CAR-CYP2B coupling. In this study, CAR function was evaluated in a representative teleost fish (scup, Stenotomus chrysops). Treatment of scup with 1,4-bis[2-(3,5-dichloropyridyloxy)]benzene (TCPOBOP), which is one of the most potent CYP2B inducers in mouse, caused no increase in hepatic alkoxyresorufin O-dealkylase activity nor in immunodetectable CYP2B-like protein levels. Western blot analyses of scup livers using anti-human CAR antisera revealed the occurrence of a putative CAR homologue in nuclear and cytoplasmic fractions, but no nuclear accumulation of CAR following TCPOBOP treatment, which is a first step regulating the transcriptional activation of CYP2B genes in mouse. Immunohistochemical study also showed no translocation of CAR into nucleus in the hepatocytes of TCPOBOP-treated scup. These results suggest that there may be species-specific differences in CAR activation or CAR-CYP2B coupling signaling transduction in fish from those in mouse.

Catalytic and immunochemical properties of hepatic cytochrome P450 1A in three avian species treated with beta-naphthoflavone or isosafrole

Induction of cytochrome P450 1A (CYP1A) can be used as a biomarker of exposure to planar halogenated aromatic hydrocarbons (PHAHs). Our objective was to characterize the induction of CYP1A activity and protein in three avian species following in vivo treatment with beta-naphthoflavone (BNF) and/or isosafrole. Alkoxyresorufin-O-dealkylase (alk-ROD) activities of hepatic microsomes from Herring Gulls (Larus argentatus) (HGs), Double-crested Cormorants (Phalacrocorax auritus) (DCCs) and chickens (Gallus domesticus) were measured using ethoxy-, methoxy-, pentoxy- and benzyloxy-resorufin, in the presence and absence of the inhibitors ellipticine or furafylline. Immunoreactivity of microsomal proteins with antibodies to several CYP1A proteins was investigated. CYP1A protein and alk-ROD activities of HGs and DCCs, but not chickens, were induced by isosafrole. Ellipticine was a potent and non-selective inhibitor of alk-ROD activity in all three species, while furafylline inhibition of alk-ROD activities varied among species and treatments. In all three species, BNF induced a protein immunoreactive with monoclonal antibody to CYP1A1 from the marine fish Stenotomus chrysops (scup), but a CYP1A2-like protein was not detected in avian microsomes probed with polyclonal antibodies to mouse CYP1A2. Variations in responses among avian species indicate that CYP1A proteins and substrate specificities should be characterized for each species used in PHAH biomonitoring programs.

Measurement of cytochrome P4501A induction in dab (Limanda limanda) and other teleosts with species-specific cDNA probes: isolation and characterisation of dab cDNA and its use in expression studies with beta-naphthoflavone-treated fish

Induction of cytochrome P4501A (CYP1A) in fish is an important biomarker in marine monitoring programmes but a number of factors complicate interpretation of data based on catalytic activity. To provide additional analytical tools, we have cloned and sequenced entire (dab) and partial cDNAs (flounder, turbot, sand eel) from several fish species. A detailed analysis comparing the new sequences to those on the database (13 sequences) is presented and identifies an invariant, teleost-specific sequence (195-IVVSVANVICGMCFGRRYDH-214) which might be the basis for production of a species cross-reactive antibody. Northern and slot blots of fish RNA (sand eel, plaice, turbot, flounder and dab) showed extensive cross-species hybridisation with each of the cDNAs (sand eel, plaice, turbot, flounder and dab). The exception was turbot RNA, which only gave adequate hybridisation when the turbot probe was used. Attempts to normalise the hybridisation data to GAPDH mRNA were not satisfactory since there were significant species differences in expression of this gene and expression was suppressed (20-40%) by beta-naphthoflavone treatment. The CYP1A probes indicated induction levels relative to untreated dab of: plaice (five-fold); turbot (12-fold); flounder (12-fold); and dab (10-fold). The study demonstrates the relative ease with which species-specific molecular probes can be generated and used.

Acquired resistance to Ah receptor agonists in a population of Atlantic killifish (Fundulus heteroclitus) inhabiting a marine superfund site: in vivo and in vitro studies on the inducibility of xenobiotic metabolizing enzymes

New Bedford Harbor (NBH), MA, is a federal Superfund site that is heavily contaminated with polychlorinated biphenyls (PCBs) and other halogenated aromatic hydrocarbons (HAHs), including some potent aryl hydrocarbon receptor (AhR) agonists. A population of Atlantic killifish (Fundulus heteroclitus) continues to inhabit this site, despite accumulating extraordinarily high concentrations of PCBs (272 microg/g dry weight). To determine if NBH killifish have developed resistance to HAHs that act through the AhR, we examined the inducibility of cytochrome P4501A1 (CYP1A1), UDP glucuronosyl transferase (UGT), and glutathione S-transferase (GST) in fish from NBH and a reference site, Scorton Creek (SC, Cape Cod, MA; PCB concentrations 0.177 microg/g dry weight). 2,3,7,8-Tetrachlorodibenzofuran (TCDF) induced CYP1A1 mRNA, protein, and activity in SC fish in all tissues examined (liver, heart, gut, gill, kidney, spleen, and gonad). In contrast, NBH fish expressed low levels of CYP1A1 and showed no induction of CYP1A1 mRNA, protein, or activity by TCDF, or induction that was lower in magnitude or required higher doses of inducer. p-Nitrophenol UGT activity was not induced by TCDF in either population, while GST activity with 1-chloro-2,4-dinitrobenzene as substrate was induced only in NBH fish in one experiment. Inducibility of CYP1A1 by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or beta-naphthoflavone (BNF) was measured in primary hepatocyte cultures prepared from SC and NBH fish. TCDD induced CYP1A1 activity (ethoxyresorufin O-deethylase) to the same degree in hepatocytes from both populations, demonstrating the functionality of the AhR signaling pathway in NBH fish. However, hepatocytes from NBH fish were 14-fold less sensitive to TCDD than were those from SC fish. The nonhalogenated AhR agonist BNF also induced CYP1A1 in cells from both populations, although with only a 3-fold difference in sensitivity (NBH < SC). These results indicate that chronic exposure to high levels of HAHs has led to a reduction in the sensitivity of NBH killifish to AhR agonists. The resistance is systemic and pretranslational, and exhibits compound-specific differences in magnitude. These findings suggest an alteration in the AhR signal transduction pathway in NBH fish.

In vitro metabolism of polychlorinated biphenyl congeners by beluga whale (Delphinapterus leucas) and pilot whale (Globicephala melas) and relationship to cytochrome P450 expression

We measured rates of oxidative metabolism of two tetrachlorobiphenyl (TCB) congeners by hepatic microsomes of two marine mammal species, beluga whale and pilot whale, as related to content of selected cytochrome P450 (CYP) forms. Beluga liver microsomes oxidized 3,3',4,4'-TCB at rates averaging 21 and 5 pmol/min per mg for males and females, respectively, while pilot whale samples oxidized this congener at 0.3 pmol/min per mg or less. However, rates of 3,3',4,4'-TCB metabolism correlated with immunodetected CYP1A1 protein content in liver microsomes of both species. The CYP1A inhibitor alpha-naphthoflavone inhibited 3,3',4,4'-TCB metabolism by 40% in beluga, supporting a role for a cetacean CYP1A as a catalyst of this activity. Major metabolites of 3,3',4,4'-TCB generated by beluga liver microsomes were 4-OH-3,3',4',5-TCB and 5-OH-3,3',4,4'-TCB (98% of total), similar to metabolites formed by other species CYP1A1, and suggesting a 4,5-epoxide-TCB intermediate. Liver microsomes of both species metabolized 2,2',5,5'-TCB at rates of 0.2-1.5 pmol/min per mg. Both species also expressed microsomal proteins cross-reactive with antibodies raised against some mammalian CYP2Bs (rabbit; dog), but not others (rat; scup). Whether CYP2B homologues occur and function in cetaceans is uncertain. This study demonstrates that PCBs are metabolized to aqueous-soluble products by cetacean liver enzymes, and that in beluga, rates of metabolism of 3,3',4,4'-TCB are substantially greater than those of 2,2',5,5'-TCB. These directly measured rates generally support the view that PCB metabolism plays a role in shaping the distribution patterns of PCB residues found in cetacean tissue.

Differential expression of two CYP1A genes in rainbow trout (Oncorhynchys mykiss)

Differential expression of two rainbow trout CYP1A genes was measured in vivo and in vitro in response to treatment with the model CYP1A inducers beta-naphthoflavone (BNF), 3-methylcholanthrene (3-MC), isosafrole (ISF), and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD, only in vitro). Originally described by Berndtson and Chen (Arch. Biochem. Biophys. 310, 187-195, 1994) as CYP1A1 and CYP1A2, these genes were renamed CYP1A3 and CYP1A1, respectively, by the P450 nomenclature committee. A significant, differential, inducer-dependent induction of the two CYP1A mRNAs, as measured by RNase protection assay, was observed in vivo. CYP1A3 and CYP1A1 mRNA levels in liver were significantly induced 50- and 18-fold, respectively, following ip injection with BNF. Conversely, CYP1A3 and CYP1A1 mRNA levels were significantly induced 5- and 66-fold, respectively, following ip injection with 3-MC. Isosafrole had no significant effect on in vivo induction of CYP1A mRNA levels. In primary cultures of hepatocytes, BNF, 3-MC, ISF, as well as TCDD all significantly induced CYP1A3 and CYP1A1 mRNA levels compared to controls. The differential induction of the two CYP1A genes was not as evident in vitro as in vivo. In addition, reanalysis and sequence comparison of the these two trout CYP1A genes with the first trout CYP1A cDNA described by Heilmann et al. (DNA 7, 379-387, 1988) indicate that the Heilmann cDNA is a hybrid of the two trout genes. The 5' portion of the cDNA sequence (212 bp) was determined by sequencing of a genomic clone and is 100% identical to the trout CYP1A3 gene. The majority of the cDNA sequence (2377 bp), however, was sequenced from a partial cDNA clone and is 99.2% identical to trout CYP1A1. Although the nomenclature of these two trout CYP1A genes is undergoing revision, these results demonstrate a differential, inducer-dependent response to model mammalian CYP1A inducers.

Cytochrome P4501A (CYP1A) in teleostean fishes. A review of immunohistochemical studies

Cytochrome P4501A monooxygenase has an important function in the biotransformation of many xenobiotics, including polynuclear aromatic hydrocarbons, and planar organochlorine compounds. The metabolism can lead to detoxification or activation to reactive intermediates. Exposure of fish leads to a receptor-mediated induction of CYP1A gene expression. The induction response can be quantitatively analysed by means of molecular techniques (RT-PCR, Northern Blotting), immunochemical approaches (ELISA, Western Blotting), and enzymatic methods (7-ethoxyresorufin-O-deethylase, EROD) at the catalytical level. Immunohistochemical studies have provided qualitative information on cell and tissue distribution of CYP1A in teleost fish. The liver is the major organ of CYP1A activity in fish, but the enzyme is additionally expressed in numerous extrahepatic organs, including kidney, alimentary canal, heart, gills, olfactory system, gonads, brain and endocrine tissues. In many tissues, the vascular endothelia show a strong CYP1A immunoreactivity. As indicated from immunohistochemical studies with fish embryos and larvae, the typical cell and tissue distribution of CYP1A is established early during fish ontogeny.

Time- and concentration-dependent induction of CYP1A1 and CYP1A2 in precision-cut rat liver slices incubated in dynamic organ culture in the presence of 2,3,7,8-tetrachlorodibenzo-p-dioxin

In a previous 24-h study, precision-cut rat liver slices were validated as a useful in vitro model for assessing the dose-related induction of CYP1A1 and CYP1A2 in rat liver following exposure to 2, 3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Further assessment of the utility of this model was accomplished by initially exposing rat liver slices to medium containing TCDD (0.01 nM) for 24 h and incubating the slices up to an additional 72 h in TCDD-free medium. The slices remained viable throughout the incubation period with an intracellular potassium content varying from 45.2 +/- 2.3 micromol/g at 48 h to 50.0 +/- 1.6 micromol/g at 72 h. In TCDD-exposed slices, CYP1A1 protein and its respective enzymatic activity, the O-deethylation of ethoxyresorufin (EROD), significantly increased with time over the 96-h incubation period, with EROD activity increasing from 63.6 +/- 14.2 at 24 h to 905 +/- 291 pmol/mg/min at 96 h. Under identical incubation conditions, but in the absence of TCDD, the EROD activity for the control liver slices ranged from 14. 3 +/- 4.3 to 44.9 +/- 11.9 pmol/min/mg. Conversely, the level of CYP1A2 protein and its respective activity (acetanilide hydroxylation) transiently decreased from 24 to 96 h with no significant differences observed between the control (0 nM TCDD) and treatment group (0.01 nM TCDD). The concentration-effect relationship at 96 h was characterized by incubating rat liver slices for the initial 24 h in medium containing TCDD at concentrations ranging from 0.1 pM to 10 nM. Induction of CYP1A1 protein and EROD activity was observed for all treatment groups with the 10 nM TCDD treatment group displaying greater than 100-fold induction compared to control (0 nM TCDD). Immunohistochemical localization of CYP1A1 protein within liver slices supported the time- and concentration-dependent induction of EROD activity by TCDD. The induction of CYP1A1 was initially observed to be centrilobular, with increased expression due to both elevated CYP1A1 within cells and the recruitment of additional cells expressing CYP1A1 throughout the entire liver slice. Additionally, the immunohistochemical analysis of the liver slices demonstrated the conservation of tissue architecture following up to 96 h of incubation in dynamic organ culture and provided further evidence for maintenance of tissue viability. In comparison to CYP1A1, the induction of CYP1A2 at 96 h was a less sensitive response, with significant induction of CYP1A2 protein and its respective activity occurring at a medium concentration of 0.1 nM TCDD (686 pg/g liver). In general, increasing the incubation period from 24 to 96 h markedly increased TCDD-induced expression of CYP1A1 and minimally enhanced CYP1A2 expression. Moreover, extending the incubation period to 96 h resulted in in vitro induction profiles for CYP1A1 and CYP1A2 that were qualitatively and quantitatively similar to that previously observed following in vivo exposure to TCDD (Drahushuk et al., Toxicol. Appl. Pharmacol. 140, 393-403, 1996).

Immunochemical approaches to studies of CYP1A localization and induction by xenobiotics in fish

There is an increasing understanding that polynuclear aromatic hydrocarbons (PAHs) and organochlorine compounds (like polychlorinated biphenyls (PCBs), certain pesticides and dioxins) in the aquatic environment may lead to physiological and pathological effects such as immunological disturbances, effects on reproduction and development, and even neoplasms. Exposure to pollutants may have consequences at all levels in the biological organization, from the cellular level over effects on the individual organism, population, to the entire ecosystem. The cytochrome P450 system (CYP or P450) has an essential function in the biotransformation of endogenous and exogenous compounds. The fact that many different environmental pollutants induce de novo synthesis of cytochrome P450 1A (CYP1A) proteins in fish, gives these enzymes an interesting position in aquatic toxicology. Many investigations concerning the CYP1A system in fish have been performed over the last two decades, demonstrating its usefulness as a biomarker for aquatic pollution. A general overview of the biochemical and toxicological aspects concerning the cytochrome P450 system will be given here, followed by a more detailed description of CYP1A induction responses in fish. Ecotoxicological consequences of CYP1A induction and the use of immunochemical techniques for CYP1A detection as a biomarker in environmental monitoring will be discussed.

Effects of triphenyltin and other organotins on hepatic monooxygenase system in fish

The interaction of the organotin fungicide triphenyltin chloride (TPT) with fish microsomal monooxygenase systems has been studied in vitro and in vivo in the marine fish scup (Stenotomus chrysops). In vitro incubation of fish liver microsomes with TPT resulted in the conversion of about 40% of the native total spectral P450 to P420. In addition, a strong concentration-related inhibition of ethoxyresorufin O-deethylase (EROD) activity was observed, with a complete loss at 1.0 mM TPT. Pentoxyresorufin-O-dealkylase (PROD) activity was inhibited only at the highest concentration tested. This suggests either some specificity for the EROD catalyst CYP1A1, or a loss of reductant NADPH cytochrome c reductase as the cause. Further in vitro incubations showed that NADPH, but not NADH, cytochrome c reductase was strongly inhibited at 100 microM TPT and higher. To further investigate this effect, fish were injected with single doses of 5, 25 and 50 microM TPT (1.9, 9.6 and 19.3 mg kg-1 TPT), and 24 and 48 h later, hepatic microsomes were analyzed for total P450 content, EROD activity, NAD(P)H cytochrome c reductase, and the content of three CYP forms. EROD activity tended to be decreased in TPT-treated scup, with the response being stronger after 48 than 24 h. No significant conversion of spectrally determined P450 to cytochrome P420 was found, and cytochrome b5 was not affected. However, both NAD(P)H cytochrome c reductases were significantly inhibited at all concentrations. Immunoblot analysis showed reduction of CYP1A1 content at all doses, being significant at 25 mM after 48 h, but no decrease in CYP3A-like protein, the dominant catalyst of testosterone 6 beta-hydroxylation, nor CYP2B-like protein, the major contributor to indicates significant effects of TPT at high concentrations on fish hepatic CYP1A1 protein, EROD activity and the reductases. TPT seems to act more specifically on CYP1A1 than on other CYP forms. These findings combined with those of our previous studies (Brüschweiler BJ, Würgler FE, Fent K. Environ Toxicol Chem 1996;15:827-735; Fent K, Bucheli TD. Aquat Toxicol 1994;28:107-126; Fent K, Stegeman JJ. Aquat Toxicol 1991;20:159-168; Fent K, Stegeman JJ. Aquat Toxicol 1993;24:219-240) indicate a general degenerative effect of organotins on the fish microsomal monooxygenase system, although some differences are seen between the organotins, and between species. We conclude that these effects of organotins have consequences for use of CYP1A as a biomarker and endocrine disruption.

Cytochromes P-4501A, P-4503A and P-4502B in liver and heart of Mugil capito treated with CYP1A inducers

Hepatic microsomes of Aroclor 1254-treated Mugil capito showed a single protein band detected in immunoblot with monoclonal antibody 1-12-3 to teleost (scup) CYP1A. The hepatic CYP1A like protein was induced with dose dependency after exposure of the fish to β-naphthoflavone (BNF) as well as to Aroclor 1254. The induced mullet hepatic CYP1A protein was confined to a distinct fraction obtained by DE-52 anion exchange chromatography, and its relative content in that fraction increased in fish that were treated with higher doses of inducer. EROD (7-ethoxyresorufin O-deethylase) activity in hepatic microsomes from mullet treated with various doses of BNF correlated significantly (r(2)=0.81502, P<0.01) with CYP1A content. Treatment of the mullet with low dose of Aroclor 1254 (25 mg/kg) induced only traces of CYP1A in liver microsomes (5.1±4.8 mg/kg). However, in mullet treated with the high dose of Aroclor 1254 (100 mg/kg) there was a dramatic induction in CYP1A content (408±275 pmol/mg) and this hemoprotein comprised about 83% of the total P-450 content of liver microsomes. The total level of P-450, although induced in the liver tissue, was not induced in heart tissue of Aroclor 1254 treated mullet. On the other hand, P-4501A was induced in treated mullet to a level that comprised almost all of the cardiac P-450 content. EROD activity in the heart tissue of induced mullet was characterized by low V(max) and high K(m) values (K(m)=2.35 mM, V(max)=39.5 pmol/min per mg) compared to the values recorded for the enzyme from the liver (K(m)=1.0 mM, V(max)=288.0 pmol/min per mg). Cardiac CYP1A with low catalytic activity and repression of CYP-types other then CYP1A in heart of CYP1A induced fish may be part of a mechanism aimed to preserve crucial levels of electron donors and molecular oxygen in cardiac muscle of fish exposed to CYP1A inducers.

Aryl hydrocarbon receptor function in early vertebrates: inducibility of cytochrome P450 1A in agnathan and elasmobranch fish

The mammalian aryl hydrocarbon receptor (AHR) is a ligand-activated transcription factor that controls the expression of cytochrome P450 1A (CYP1A) genes in response to halogenated aromatic hydrocarbons such as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). The natural ligand and normal physiologic function of this protein are as yet unknown. One approach to understanding AHR function and significance is to determine the evolutionary history of this receptor and of processes such as CYP1A induction that are controlled by the AHR in mammals. In these studies, AHR function was evaluated in representative cartilaginous fish (little skate, Raja erinacea) and jawless fish (sea lamprey, Petromyzon marinus and Atlantic hagfish, Myxine glutinosa), using CYP1A induction as a model AHR-dependent response. Treatment of skate with beta-naphthoflavone (BNF) caused an 8-fold increase in hepatic ethoxyresorufin O-deethylase (EROD) activity as well as a 37-fold increase in the content of immunodetectable CYP1A protein. Evidence of CYP1A inducibility was also obtained for another cartilaginous fish, the smooth dogfish Mustelus canis. In contrast, hepatic EROD activity was not detected in untreated lamprey nor in lamprey treated with 3,3'4,4'-tetrachlorobiphenyl (TCB), a potent AHR agonist in teleosts. A possible CYP1A homolog was detected in lamprey hepatic microsomes by one of three antibodies to teleost CYP1A, but expression of this protein was not altered by TCB treatment. CYP1A protein and catalytic activity were measurable in hagfish, but neither was induced after treatment with TCB. These results suggest that the AHR-CYP1A signal transduction pathway is highly conserved in gnathostomes, but that there may be fundamental differences in AHR signaling or AHR-CYP1A coupling in agnathan fish. Agnathan fish such as hagfish and lamprey may be interesting model species for examining possible ancestral AHR functions not related to CYP1A regulation.

Cytochromes P450 in liver of the turtle Chrysemys picta picta and the induction and partial purification of CYP1A-like proteins

Cytochromes P450 (CYP) in hepatic microsomes from the turtle Chrysemys picta picta and their response to inducers were examined. Freshly caught turtles had one protein (59 kDa) detected in western blot with monoclonal antibody 1-12-3 to scup CYP1A. That same band and a second band were detected with polyclonal anti-mouse Cyp1a1. Polyclonal anti-scup P450B (putative CYP2B) recognized three bands and anti-scup P450A (putative CYP3A), one band. TCB (3,3',4,4'-tetrachlorobiphenyl) at 5 mg kg-1 injected once induced EROD activity 3-fold. Repeated high-dose injections of TCB, 2,3,3',4,4'-pentachlorobiphenyl, Aroclor 1254 or beta-naphthoflavone induced CYP1A 20-fold and P450B-related proteins 2-3-fold. Rates of ethoxy- (EROD) methoxy- (MROD) and pentoxyresorufin O-dealkylases and benzo[a]pyrene (B[a]P) hydroxylase (AHH) were induced by these treatments, and were correlated with putative CYP1A content. Phenobarbital slightly elevated only MROD activity. Ethoxycoumarin (EC) O-deethylase rates were high, 1.6-2.2 nmol min-1 mg-1 in control and treated turtles, suggesting that EC is not a turtle CYP1A substrate. Highly induced EROD rates were 0.06 nmol min-1 mg-1, while AHH rates exceeded 4 nmol min-1 mg-1, suggesting that C. picta picta CYP1A may prefer PAH substrates. Induction of AHH was reflected in the formation of metabolites 3-OH-, 9-OH- and 7-OH-BP and BP-7,8-dihydrodiol (DHD). BP-4,5-DHD was not detected. Chromatographic procedures resolved the 59 kDa putative CYP1A from the second protein recognized by anti-Cyp1a1. The 59-kDa protein was also specifically and highly immunopurified by Mab 1-12-3. Thus, several CYP including two CYP1A-related proteins are expressed in turtle liver. Multiple CYP1A genes in reptiles may provide an insight into the origin of divergence in the CYP1A subfamily. Induction of a CYP1A may be a useful indicator of exposure to Ah receptor agonists in turtles.

A fish hepatoma cell line (PLHC-1) as a tool to study cytotoxicity and CYP1A induction properties of cellulose and wood chip extracts

Cytotoxicity and CYP1A induction properties of celluloses and wood chips were studied with a teleost liver cell line, PLHC-1. Cells were exposed to acetone extracts of celluloses produced using new bleaching techniques (elemental chlorine free, ECF; totally chlorine free, TCF) in two sulphate mills or without any bleaching (unbleached, UB) in a sulphite mill. In another set of exposures, celluloses (ECF and TCF bleached) and wood chips (from pine and birch) were collected from a sulphate mill, extracted with acetone, and the extracts used to treat the cells. After exposure, O-deethylation of 7-ethoxyresorufin (EROD, a measure of cytochrome P4501A (CYP1A) catalytic activity), and total protein content, a measure of cytotoxicity, were assayed. The presence of the CYP1A protein in the exposed cells was assessed by immunoblotting. The cellulose and wood chip extracts were able to cause both cytotoxicity and EROD induction in the PLHC-1 cells. In the exposures conducted with the material from three different mills, the celluloses made of birch were more cytotoxic and more potent inducers of EROD activity than were the celluloses of pine. Further, UB celluloses increased EROD activity and caused cytotoxicity at lower doses than material bleached with modern bleaching techniques. In the exposures made with material from one single mill, there were no clear trends between the celluloses made of pine or birch. Wood chips of pine, however, were more cytotoxic than wood chips of birch. Especially with pine wood chips, cytotoxicity interfered with the induction of EROD activity, thus complicating the evaluation of CYP1A induction. CYP1A protein content was not detected in cells exposed to extracts of celluloses or wood chips, possibly due to low amounts of protein available for the assay. Wood and pulp processing, like bleaching, may change the chemical composition of the raw material in a way that reduces the potency for biological effects of the final product, cellulose. This could explain why both UB celluloses and wood chips were more potent in the cells than ECF or TCF bleached celluloses. In this study the PLHC-1 cell line showed its potential for use in evaluating the biological activity existing in pulp and paper mill products and raw materials. The identity and source of the compounds that were able to affect the PLHC-1 cell line remain to be determined.

Arachidonic acid metabolism in the marine fish Stenotomus chrysops (Scup) and the effects of cytochrome P450 1A inducers

Cytochrome P450-mediated arachidonic acid (AA) metabolism was investigated in the marine fish scup, Stenotomus chrysops. Liver microsomes incubated with AA and NADPH produced epoxyeicosatrienoic acids (EETs) and their hydration products (dihydroxyeicosatrienoic acids, DHETs), midchain conjugated dienols (midchain HETEs), and C16-through C20-alcohols of AA (omega-terminal HETEs), all identified by HPLC and GC/MS. Gravid females had 4-fold lower AA metabolism rates than males but identical metabolite profiles. The 5,6-EET (inferred from stable metabolites) was most abundant (47% of total EETs) followed by 14,15-, 11,12-, and 8,9-EET (27, 13, and 13%, respectively). The 12-HETE represented 25% of total HETEs followed in abundance by 16-, 15-, 11-, 19-, 20-, 8-, and 9-HETE. Antibodies against scup CYP1A and a scup CYP2B-like protein inhibited liver microsomal AA metabolism by 30 and 46%, respectively. GC/MS analysis revealed EETs and DHETs as endogenous constituents in scup liver; the predominant EETs were 8,9- and 14,15-EET, followed by a lesser amount of 11,12-EET. Chiral analysis showed a preference for the S,R-enantiomers of endogenous 8,9-, 11,12-, and 14,15-EET (optical purities 80, 64, and 64%, respectively). Treatment of scup with the CYP1A inducer benzo(a)pyrene (BP) increased liver microsomal formation of EETs and HETEs by 2.7-fold in spring and 1.7-fold in summer. BP treatment did not affect microsomal EET regioselectivity, but shifted hydroxylation in favor of 19-HETE and induced 17-HETE formation. 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) treatment in summer did not induce liver microsomal AA metabolism rates, yet BP and TCDD both increased endogenous EET content of liver (5- and 3-fold, respectively), with a shift to 14,15-EET. BP treatment increased the selectivity for the S,R-enantiomers of endogenous 8,9-, 11,12-, and 14,15-EET (optical purities 91, 84, and 83%, respectively). Kidney, gill, and heart microsomes all metabolized AA, at rates 10- to 30-fold less than liver microsomes. Similar amounts of endogenous 8,9- and 14,15-EET and less 11,12-EET were detected in heart and kidney, and there was a strong enantioselectivity for 8(R),9(S)-EET in heart (optical purity 78%) but not in kidney. BP treatment did not alter the total EET content in these organs but did shift the regiochemical profile in heart to favor 14,15-EET. Thus, scup liver and extrahepatic organs metabolize AA via multiple cytochrome P450 (CYP) forms to eicosanoids in vitro and in vivo. BP or TCDD induced endogenous AA metabolism in liver, altering EET regioselectivity and, with BP, stereoselectivity. While AhR agonists alter metabolism of AA in early diverging vertebrates expressing both CYP1A and AhR, the magnitude of effects may depend upon the type of inducer.

Xenobiotics and xenoestrogens in fish: modulation of cytochrome P450 and carcinogenesis

As is the case with mammals, an ever-increasing number of cytochromes P450 (CYPs) are being characterized from fish. The focus of work on fish CYPs has been primarily on environmental induction of CYP1A by pollutants such as the polycyclic aromatic hydrocarbons, polychlorinated biphenyls, dioxins and dibenzofurans. This response has been the basis for a sensitive biomonitoring tool of ecosystem health for a number of years. Studies have documented a correlation between CYP1A induction, pollutant levels and tumor incidence, especially in bottom-dwelling species. The rainbow trout has been utilized as a tumor model to document the role of CYP1A modulation in the inhibition or promotion of cancer. Fish are also very responsive to the class of chemicals known as xenoestrogens. Recent evidence is presented documenting the modulation of CYPs by xenoestrogens and their potential role as modulators of the tumor response. In this paper, we summarize the current knowledge concerning the occurrence of CYPs in fish and focus on the role of CYP1A induction in environmental monitoring of various genotoxic carcinogens and in the modulation of cancer in the trout model. Finally, the important class of aquatic pollutants known as xenoestrogens have now been shown to modulate CYP levels perhaps leading to alterations in tumor response or other adverse effects.

Ascites, premature emergence, increased gonadal cell apoptosis, and cytochrome P4501A induction in pink salmon larvae continuously exposed to oil-contaminated gravel during development

Development of pink salmon (Oncorhynchus gorbuscha) incubating in gravel contaminated with weathered Prudhoe Bay crude oil was retarded at concentrations as low as 55.2 μg oil/g gravel. Larvae exposed to various levels of oil contamination were sampled 4 weeks before emergence, at emergence, and 13 days after emergence for histopathology (quantitative and semiquantitative) and cytochrome P4501A (CYP1A) induction (using immunohistochemical staining). A subset of postemergent fish was not fed. Hydrocarbon analysis by gas chromatography and mass spectroscopy revealed that tissue uptake of polynuclear aromatic hydrocarbons (PAH) was mediated by oil's dissolution in water, with significant biological effects when the peak total PAH concentration in water was as low as 4.4 μg/L. Oil-related effects included induction of CYP1A, development of ascites, and increased mortality. Several oil-related changes were indicative of premature emergence. Compared with control fish, for example, exposed fish of the same age and emerging on the same day had greater amounts of yolk and hepatocellular glycogen, increased apoptosis of gonadal cells and midventral skin cells, and less food in the gastrointestinal tract. Histological features were similar within groups of larvae sampled 4 weeks before and 13 days after emergence, and oil-induced changes were not affected by feeding during the first 13 days after emergence. Increased gonadal cell apoptosis may be related to later reproductive impairment documented in field studies of pink salmon up to 4 years after the Exxon Valdez oil spill.

Induction and post-transcriptional suppression of hepatic cytochrome P450 1A1 by 3,3',4,4'-tetrachlorobiphenyl

3,3',4,4'-Tetrachlorobiphenyl (TCB) can induce and inhibit cytochrome P450 1A1 (CYP1A1) in vertebrates. TCB may also suppress CYP1A1 protein levels, but the mechanism is unknown. This study examined transcriptional and translational aspects of hepatic CYP1A1 regulation in the fish scup (Stenotomus chrysops) given single intraperitoneal injections of low (0.1 mg/kg) or high (5 mg/kg) doses of TCB, and sampled over 16 days. The low dose strongly induced hepatic CYP1A1 mRNA (25-fold), protein (12-fold), and activity [ethoxyresorufin O-deethylase (EROD)] (15-fold). The high dose also strongly induced CYP1A1 mRNA (29-fold), in a pattern like that at the low dose, but microsomal CYP1A1 protein content was induced only 4-fold and EROD rates were near control levels. Both TCB doses caused similar increases in microsomal cytochrome b5 content, and in rates of NADPH-cytochrome c (P450) reductase and UDP-glucuronosyltransferase (with p-nitrophenol). The contents of CYP forms other than CYP1A1 (putative CYP2B or CYP3A) were only weakly affected by TCB at either dose. The strong and largely specific post-transcriptional suppression of CYP1A1 content was associated with high concentrations of TCB measured in the liver. Incubation of scup hepatic microsomes with TCB plus NADPH led to a time-dependent inactivation of CYP1A1 that was distinct from catalytic inhibition, and appeared not to involve reactive metabolites of TCB. This in vitro result suggests that TCB may inactivate CYP1A1 in vivo, which could account for the apparent antagonistic effect of TCB on CYP1A1 induction.

EROD and CYP1A protein in channel catfish (Ictalurus punctatus) from an urban estuary relative to that in benzo[a]pyrene-exposed hatchery specimens

Bottom-feeding fish such as flounder and killifish have been widely used in monitoring hepatic monooxygenase induction in polluted water bodies. While channel catfish are often utilized in tissue monitoring of fresh and estuarine water bodies, few data are available on their use in environmental monitoring of hepatic monooxygenase activity. In this project, the presence of CYP1A protein was verified in channel catfish through recognition by Mab 1-12-3, an antibody which recognizes the CYP1A homologue in a variety of teleost species. CYP1A protein levels and 7-ethoxyresorufin-o-deethylase (EROD) activity in laboratory control and benzo-a-pyrene (BaP)-challenged channel catfish were compared to those in feral channel catfish from Back River, an urban estuarine tributary to Chesapeake Bay. Though more variable, mean CYP1A protein levels in the field-collected fish were similar to those of the BaP-induced laboratory fish. However, EROD activity of the Back River fish was less than one half that observed in the BaP-induced laboratory fish. When normalized to CYP1A protein levels, EROD activity was slightly lower in the Back River fish than either the laboratory control or BaP-treated fish. This finding may indicate possible inhibition or inactivation of the CYP1A protein in the feral fish.

Cytochromes P450 (CYP) in tropical fishes: catalytic activities, expression of multiple CYP proteins and high levels of microsomal P450 in liver of fishes from Bermuda

Hepatic microsomes prepared from 10 fish species from Bermuda were studied to establish features of cytochrome P450 (CYP) systems in tropical marine fish. The majority (7/10) of the species had total P450 content between 0.1 and 0.5 nmol/mg, and cytochrome b5 content between 0.025 and 0.25 nmol/mg. Ethoxycoumarin O-deethylase (ECOD) and aminopyrine N-demethylase (APND) rates in these 7 species were 0.23-2.1 nmol/min/mg and 0.5-11 nmol/min/mg, respectively, similar to rates in many temperate fish species. In contrast to those 7 species, sergeant major (Abudefduf saxatilis) and Bermuda chub (Kyphosus sectatrix) had microsomal P450 contents near 1.7 nmol/mg, among the highest values reported in untreated fish, and had greater rates of ECOD, APND, ethoxyresorufin O-deethylase (EROD) and pentoxyresorufin O-depentylase than did most of the other species. Freshly caught individuals of all species had detectable levels of EROD and aryl hydrocarbon hydroxylase (AHH) activities. Those individuals with higher rates of EROD activity had greater content of immunodetected CYP1A protein, consistent with Ah-receptor agonists acting to induce CYP1A in many fish in Bermuda waters. Injection of tomtate and blue-striped grunt with beta-naphthoflavone (BNF; 50 or 100 mg/kg) induced EROD rates by 25 to 55-fold, suggesting that environmental induction in some fish was slight compared with the capacity to respond. AHH rates were induced only 3-fold in these same fish. The basis for disparity in the degree of EROD and AHH induction is not known. Rates of APND and testosterone 6 beta- and 16 beta-hydroxylase were little changed by BNF, indicating that these are not CYP1A activities in these fish. Antibodies to phenobarbital-inducible rat CYP2B1 or to scup P450B, a putative CYP2B, detected one or more proteins in several species, suggesting that CYP2B-like proteins are highly expressed in some tropical fishes. Generally, species with greater amounts of total P450 had greater amounts of proteins related to CYP2B. These species also had appreciable amounts of CYP3A-like proteins. Thus, many fishes in Bermuda appear to have induced levels of CYP1A; some also have unusually high levels of total P450 and of CYP2B-like and CYP3A-like proteins. These species may be good models for examining the structural, functional and regulatory properties of teleost CYP and the environmental or ecological factors contributing to high levels of expression of CYP in some fishes.

Identification of cytochrome P-450 1A (CYP1A) genes from two teleost fish, toadfish (Opsanus tau) and scup (Stenotomus chrysops), and phylogenetic analysis of CYP1A genes

Cytochrome P-450-mediated responses to environmental challenges are well known in diverse animal taxa, but the evolution of the complex gene superfamily coding for these enzymes is poorly understood. Here we report a phylogenetic analysis of the cytochrome P-450 1A (CYP1A) genes including two new sequences determined from teleost fish, toadfish (Opsanus tau) and scup (Stenotomus chrysops). Degenerate PCR primers were used to amplify a 1.2 kbp fragment from liver cDNA. The toadfish PCR product was used as a probe to identify a full-length CYP1A clone from a toadfish liver cDNA library. The entire coding region of the scup CYP1A was obtained by rapid amplification of cDNA ends (RACE) using specific primers based on the sequence of the partial PCR product. The predicted protein sequences for toadfish and scup CYP1A shared 78% and 83% amino acid identity with rainbow trout CYP1A1 respectively. Amino acid identity with mammalian CYP1A proteins ranged from 51 to 60% for 505 aligned positions. Phylogenetic analysis of four teleost fish CYP1A genes (trout, toadfish, scup and plaice) and 12 mammalian CYP1A genes suggests a monophyletic origin of the teleost genes, with the trout gene being most divergent, and indicates three distinct groupings: mammalian 1A1, mammalian 1A2, and fish 1A. This supports the idea that the gene duplication event which gave rise to CYP1A1 and CYP1A2 occurred after the divergence of the lines leading to mammals and fish. These results establish a molecular phylogeny within the CYP1A subfamily, the first such detailed phylogenetic analysis within a cytochrome P-450 family.

Cross-reactivity of thirteen monoclonal antibodies with ten vaccinia cDNA expressed rat, mouse and human cytochrome P450s

Twelve monoclonal antibodies (MAbs) to rat cytochrome P450s and one MAb to a scup (fish) P450 have been isolated, characterized, and are currently in common use. Expression of cDNAs for different P450s from a vaccinia vector offers a rapid and simple way toward the production of individual P450s. The thirteen MAbs were examined for their cross-reactivity with ten cDNA expressed human, rat, and mouse P450s. Three MAbs to rat 1A1 and fish 1A1 cross-reacted with cDNA expressed mouse 1A1. One of the latter MAbs, 1-7-1 but none of the others cross-reacted with mouse 1A2. Surprisingly, the fish MAb to 1A1 also cross-reacted with human 2E1. Two MAbs to rat 2B1/2B2 cross-reacted with rat 2A1. An MAb to rat 2C11 cross-reacted with human 2C9. Two MAbs to rat 2E1 cross-reacted with human 2E1. Finally, two MAbs to rat 3A1 cross-reacted strongly with human 3A4. These studies open the door to constructing a library of MAbs with defined binding activity to the P450s of human and other species.

Effects of temperature acclimation on the expression of hepatic cytochrome P4501A mRNA and protein in the fish Fundulus heteroclitus

Previous studies showed that hydrocarbon induction of hepatic microsomal monooxygenase activity is attenuated in the teleost fish Fundulus heteroclitus acclimated to low temperature. The basis of that attenuation, and the effects of temperature on monooxygenase activity, were examined by analyzing liver cytochrome P4501A (CYP1A) mRNA, protein, and catalytic activity in control and beta-naphthoflavone (BNF)-treated F. heteroclitus acclimated to 6 or 16 degrees C. There were no temperature-related differences in total P450 content, NADPH-cytochrome c (P450) reductase activity, ethoxyresorufin O-deethylase (EROD) activity, or immunoquantified CYP1A content in hepatic microsomes of untreated fish. Fish acclimated to 16 degrees C and given a single intraperitoneal injection of BNF exhibited a rapid rise and fall in CYP1A mRNA content and an induction of EROD activity and CYP1A protein that was undiminished over 7 days. Similarly treated fish acclimated at 6 degrees C showed an increase in CYP1A mRNA content greater than that in 16 degrees C fish, but with no significant increase in EROD activity or CYP1A content over 7 days. Examined over a longer term, microsomal EROD activity was significantly induced by BNF in fish at both temperatures; activity peaked at 5-7 days in 16 degrees C fish, while in 6 degrees C fish the activity continued to rise slowly over 25 days. However, the greatest activity reached in 6 degrees C fish (0.68 nmol/min/mg) was less than half that seen in the warmer animals (1.46 nmol/min/mg). Immunodetectable CYP1A content showed the same trend as EROD activity, and the turnover number (nmol product formed/min/nmol CYP1A) for EROD activity was about the same in all groups, indicating that concentration of the catalyst alone could account for the different patterns of microsomal activity. CYP1A mRNA content was again induced to a similar degree by BNF in both the 6 and the 16 degrees C fish; the apparent half-life of the mRNA was substantially longer in cold-acclimated than in warm-acclimated BNF-treated fish. Comparing the levels of CYP1A mRNA and protein at the two acclimation temperatures following BNF treatment indicates that translational activity, rather than transcriptional activity, is the sensitive point in the effect of temperature on CYP1A induction in these fish.

Immunohistochemical localization of environmentally induced cytochrome P450IA1 in multiple organs of the marine teleost Stenotomus chrysops (Scup)

Differences in expression of cytochrome P450 forms and their functions in different organs and cell types could determine the response of those cells and organs to xenobiotics. Recently, we described the cellular localization of cytochrome P450IA1 (P450E) induced in 10 organs or organ systems of the fish, Stenotomus chrysops (scup) treated with 3,3',4,4'-tetrachlorobiphenyl or with 2,3,7,8-tetrachlorodibenzofuran. (R.M. Smolowitz, M.E. Hahn, and J.J. Stegeman, Drug Metab. Dispos. 19, 113, 1991). Here we describe the presence and localization of P450IA1 in organs of scup sampled directly from an environment contaminated by chlorinated biphenyls and bibenzofurans, the outer New Bedford Harbor of Massachusetts. Western blot analysis of microsomes from selected organs (liver, kidney, gill, and heart), using monoclonal antibody 1-12-3, revealed induced levels of P450IA1 in each. The localization of P450IA1 in these and other organs was determined in sections prepared by standard histological methods and stained with MAb 1-12-3 in an indirect peroxidase labeling method. P450IA1 was detected in multiple cell types in liver, including hepatic, pancreatic, and vascular tissue. Kidney and gut also showed prominent P450IA1 levels in epithelial structures and in vascular endothelial cells. Specific staining was detected in endothelial cells, but not other cell types, in heart, gill, spleen, testis, ovary, nose, and brain. In heart, the staining was present in the endocardium of atrium and ventricle, and endothelium of the coronary vasculature and great vessels. The results demonstrate that P450IA proteins are induced in many organs of fish exposed to environmental chemicals in the wild, with patterns of cellular localization like those seen in fish experimentally treated with known inducers. The strong staining of P450IA1 in endothelial cells in all organs examined supports experimental results indicating that endothelium is a major site of P450IA1 induction. Our results indicate further that immunohistochemistry is a useful method for detecting P450 induction as a biomarker for exposure.

Sex differences in hepatic monooxygenases in winter flounder (Pseudopleuronectes americanus) and scup (Stenotomus chrysops) and regulation of P450 forms by estradiol

Details concerning the endogenous regulation of hepatic cytochrome P450 monooxygenases in teleosts, and the features of this regulation common among fish species, are poorly known. Gonadally mature female winter flounder (Pseudopleuronectes americanus) have been reported to have severalfold lower levels of microsomal cytochromes P450 and b5 and NADPH-cytochrome c reductase than do males (Stegeman and Woodin ('84) Mar. Environ. Res., 14:422-425). These strong sex differences prompted more detailed study of P450 regulation in winter flounder liver, and a comparison with sex differences in another marine teleost, scup (Stenotomus chrysops). Ethoxyresorufin O-deethylase (EROD) activity/nmol P450 was less in gonadally mature females than in males of both species. Immunoblot analysis with MAb 1-12-3 to P450E (the EROD catalyst) showed that the content of P450E counterpart was also much less in females of both species. Aminopyrine N-demethylase (APND) and testosterone 6 beta-hydroxylase (6 beta-OHase) activities per nmol P450 were higher in gonadally mature female than in mature male flounder, differences not seen in scup. Polyclonal antibodies to scup P450A were shown to detect proteins in a number of teleosts. The levels of anti-P450A cross-reacting protein were greater in mature female than in male flounder, but as with 6 beta-OHase activity, the content of this protein was not sexually differentiated in scup. Estradiol treatment of winter flounder depressed the rates of EROD, APND, 6 beta-OHase, and estradiol 2-OHase activities per mg protein, but APND and 6 beta-OHase activities per nmol P450 were unchanged. Thus, E2 promotes general decreases in some hepatic P450-catalyzed activities, but in achieving sex differences there is also specific regulation of the P450E counterpart, and possibly of the 6 beta-OHase (P450A?). Other factors, temporal or hormonal, can modify the effect of E2 treatment, and may contribute to the specific regulation of P450 forms in naturally maturing fish, and to species differences in this regulation.

Catalytic activity and immunochemical quantification of hepatic cytochrome P-450 in β-naphthoflavone and isosafrol treated rainbow trout (Oncorhynchus mykiss)

In addition to catalytical assays, immunochemical techniques have recently been employed to measure induction of the cytochrome P-450 (P450) monooxygenase system in fish with polyaromatic hydrocarbons (PAH). In the present study, polyclonal antibodies were raised against rainbow trout P450IA1. Levels of rainbow trout P450IA1 determined using protein blotting- and ELISA procedures were compared with levels of 7-ethoxyresorufin-O-deethylase (7-EROD) activity in liver microsomes from rainbow trout. These comparisons showed that values of P450A1 were positively correlated (r=0.99 and r=0.97) with 7-EROD activities. In addition, the effects of isosafrol (ISF) or β-naphthoflavone (βNF) treatments on P450 levels in rainbow trout liver were investigated using immunochemical and catalytical methods. ISF treatment induced 7-EROD activity as well as 7-methoxycoumarin-O-demethylase-, 7-ethoxycoumarin-O-deethylase-, 7-propoxy-coumarin-O-depropylase and 7-butoxycoumarin-O-debutylase activities, although to a lesser extent, compared with the βNF treatment. In contrast, immunochemical quantification of rainbow trout P450IA1 protein revealed a slightly different pattern. ISF appeared to be a weak inducer of P450IA1 in rainbow trout compared with βNF. In addition, the degree of inhibition of 7-alkoxycoumarin-O-dealkylase activities in ISF microsomes differed from that measured in control- and βNF microsomes. The discrepancies between catalytic and immunochemical estimates of rainbow trout P450IA1 in ISF treated fish in addition to differencs between specific inhibitory pattern by specific polyclonal antibodies raised against rainbow trout P450IA1, indicate that important differences exists between the responses induced by βNF- and ISF treatments in the rainbow trout liver.

Induction of hepatic cytochrome P-450IA1 in pigeons treated in vivo with Aroclor 1254, a commercial mixture of polychlorinated biphenyls (PCBs)

1. Treatment with a commercial mixture of polychlorinated biphenyls (PCBs) resulted in highly significant increases in pigeon hepatic microsomal proteins (100-fold), cytochrome P-450 (11-fold), cytochrome b5 (7-fold), NADPH-cytochrome c-(P450) reductase (7-fold), ethoxycoumarin-O-deethylation (9-fold), aldrin epoxidase (22-fold), ethoxyresorufin-O-deethylation (48-fold), N-demethylation of dimethylnitrosamine (28-fold) but not of lauric acid 12-hydroxylation. 2. SDS-PAGE analysis of pigeon hepatic microsomal proteins induced by Aroclor 1254 suggested highly significant increases in the density of staining in bands of estimated Mr 51-52 kD, 54-54.5 kD, 57-58 kD, 59-60 kD and of 77.5-78.5 kD. 3. The induction of cytochrome P-450IA1 was confirmed by Western immunoblotting using the monoclonal antibodies MAB 1-12-3 and MAB 1-8-4. 4. There was agreement between the 8-fold increase in cytochrome P-450IA1 increased staining of microsomal proteins, as judged by SDS-PAGE, and the 24-fold increase in the amount of protein that reacted with the monoclonal antibodies MAB 1-12-3 and MAB 1-8-4, as judged by Western immunoblotting. 5. It is concluded that treatment with a commercial PCB mixture resulted in the induction of several isoforms of pigeon hepatic cytochrome P-450 in a fashion that is likely to be similar to that reported for mammals.

Immunological characterization of constitutive isozymes of cytochrome P-450 from rainbow trout. Evidence for homology with phenobarbital-induced rat P-450s

Immunoglobulin G fractions (IgGs), isolated from rabbits immunized against hepatic cytochrome P-450 isozymes were used to investigate the immunochemical homology among trout P-450s and between trout and rat P-450s. The antigens used for immunization were five constitutive trout P-450s (LMC1 to LMC5), one beta-naphthoflavone (BNF)-inducible trout P-450 (LM4b), and one phenobarbital-induced rat P4500IIB1 (PB-B). In the enzyme-linked immunosorbent assay (ELISA), strong cross-reactivity was observed between anti-LMC2 IgG and P-450 LMC1, and between anti-LMC3 IgG and P-450 LMC4. There was little or no cross-reactivity of anti-LMC5 IgG with other trout P-450s. Trout P-450 LM4b was not recognized by any of the antibodies against constitutive trout P-450s. Antibodies to P-450 LMC1 and P450 LMC2 cross-reacted strongly with rat P450IIB1 and with proteins of PB-induced rat liver microsomes. Rat P450IA1 (BNF-B) did not cross-react with anti-LMC1 or anti-LMC2 IgG. These cross-reactions were essentially confirmed by immunoblot (Western blot) analysis. Western blots of PB-induced rat liver microsomes probed with anti LMC1 revealed two major immunoreactive proteins in the P-450 region, one of which co-migrated with rat P450IIB1. P450IIB1 itself cross-reacted strongly with anti-LMC1 IgG. In control rats, a single protein band cross-reacted poorly with anti-LMC1 IgG. Antibodies to LMC1 and LMC2 did not cross-react with rat P450IA1 in Western blots. The antigenic epitopes in rat P450IIB1 recognized by anti-LMC1 IgG and anti-LMC2 IgG are probably not located at or near the active site of the enzyme since these antibodies did not inhibit benzphetamine N-demethylase activity of P450IIB1 or of PB-induced rat liver microsomes. In general, our results demonstrate: (1) the presence of a significant homology between LMC1 and LMC2, and between constitutive trout P-450 (LMC1) and PB-induced rat P-450 (P450IIB1); and (2) distant homology between constitutive trout P-450s and constitutive rat P-450s or BNF-induced rat P-450s.

Feminization of the hepatic microsomal cytochrome P-450 system in brook trout by estradiol, testosterone, and pituitary factors

The effects of estradiol, testosterone, and pituitary extract on hepatic microsomal enzymes were studied in sham-operated and gonadectomized immature brook trout. Estradiol reduced the specific content of cytochromes P-450 and b5 by 70% or more in both groups. Testosterone and pituitary extract also decreased the levels of total P-450 and b5, but to a lesser extent. These latter effects were not evident when the contents of P-450 and b5 were normalized per g liver. Immunoblot analysis with antibodies to P-450 forms from a teleost (scup) showed the presence of cross-reacting proteins in control fish, presumed counterparts to the scup forms. Levels of a trout counterpart to P-450A (a putative testosterone 6 beta-hydroxylase) were strongly suppressed in estradiol-treated fish. A trout P-450B counterpart was suppressed in estradiol-treated fish, but less strongly than was the P-450A counterpart. The trout orthologue of hydrocarbon-inducible P-450E (P-450IA1), the aryl hydrocarbon hydroxylase (AHH) catalyst, was undetectable in any group, consistent with very low levels of AHH activity in these fish. Estradiol or pituitary extract also decreased the levels of NADH-cytochrome b5 and NADPH-cytochrome P-450 reductase activities in sham-operated but not in total P-450 or b5, suggesting an influence of gonads in maintaining normal levels of the reductases. The results support a prominent suppressive role for estrogens in producing the general sex differences in microsomal enzymes in fish liver and indicate that there could be affects on several P-450 forms. However, the mechanism of hormone action in this regulation is uncertain. The results also suggest the existence of unidentified, possibly gonadal, factors which contribute to the regulation of reductases in teleost liver.

Cytochrome P450 forms in fish: catalytic, immunological and sequence similarities

1. Hepatic microsomal enzymes from teleost and elasmobranch fishes catalyse a diversity of monooxygenase reactions, consistent with the presence of multiple, distinct P450 forms. Protein purification and immunological studies have confirmed that multiple microsomal P450s occur in teleosts. 2. A member of the aromatic hydrocarbon-inducible P450 IA family is present in all fish species examined to date. This protein appears to be most closely related to P450 IA1. Certain of the immunological probes for a teleost P450 IA1 (scup P450E) appear to be reagent antibodies, recognizing the homologous protein in members of all vertebrate groups examined. The nature of the epitope recognized by such antibodies is not known. 3. Based on immunological and amino acid sequence comparisons, teleost P450 IA1 appears to be orthologous to both P450 IA1 and P450 IA2 in mammals. Multiple P450 IA genes may appear in teleosts, but divergence on separate lines from that involving mammalian P450 IA2 could include additional, new members (P450 IA3?) of the P450 IA family. 4. There are greater similarities in the N-terminal amino acid sequences of different teleost (scup and trout) P450 IA1 forms, than seen in the N-terminal sequence relationships found in P450 IA1 of mammalian species. Whether this similarity extends to the rest of these teleost proteins is unknown. 5. The induction of P450 IA1 in teleosts involves transcriptional and translational events. However, the temporal patterns involved in induction of mRNA or protein are different from those in mammalian species, indicating additional aspects of the regulation in teleosts. 6. Relationships between other teleost and mammalian P450 forms, or between other P450 forms isolated from different teleosts, remain to be conclusively established. However, certain relationships are suggested, based on catalytic and other comparisons.

Cytochromes P-450 of sea birds: cross-reactivity studies with purified rat cytochromes

1. Polyclonal antibodies against rat cytochrome P-450c (IA1), P-450d (IA2), P-450b (IIB1), P-450h (IIC11) and P-450j (IIE1), were used to probe liver microsomes prepared from six sea bird species collected from the Irish Sea between 1978 and 1988. 2. Significant cross-reactivity in all the sea bird species was seen only with antibodies to P450 IA1. Expression of cross-reactivity proteins was highly variable between individual birds, which show evidence of environmental induction. 3. Shared epitopes to P450 IA1 and IA2 were seen on a single protein expressed in liver microsomes from the cormorant (Phalacrocorax carbo). 4. Antibodies against members of rat P450 gene family II showed a small degree of cross-reactivity with sea bird microsomes. Antibodies against P450 IIB1 and IIC11 showed weak cross-reactivity in all species with little inter-individual variation. Antibodies to P450 IIE1 showed no cross-reactivity in any bird species. 5. P450 gene family I appears to be well represented in sea birds while P450 gene family II is not well developed in this group of lower vertebrates.

The hepatic microsomal mixed-function oxygenase (MFO) system of Alligator mississippiensis: induction by 3-methylcholanthrene (MC)

1. Pretreatment of alligators i.p. with 3-methylcholanthrene (MC) resulted in a 1.6-fold increase (P less than 0.001) in cytochrome P-450 specific content and a bathochromic shift in the absorption maximum of reduced, CO-liganded microsomes (448 nm). 2. Control and MC microsomal cytochrome P-450 binding spectra with a number of type I and type II ligands were similar. 3. MC treatment of alligators resulted in a 12-fold increase in benzo[a]pyrene hydroxylase activity, which was inhibited 82% by 0.1 mM alpha-naphthoflavone. The turnover number (units/nmol P-450) of aminopyrine N-demethylase and 7-ethoxycoumarin O-deethylase were unaffected by MC treatment. 4. The O-dealkylation (OD) of a series of alkoxyresorufins (ethoxyresorufin (ER), methoxyresorufin (MR), benzyloxyresorufin (BR), and pentoxyresorufin (PR] was investigated. MC treatment resulted in a significant (P less than 0.001) increase in turnover number of EROD, MROD, and BROD over control values. The turnover number of PROD was unaltered by MC treatment. 5. Western blots showed that control alligator microsomes contain a protein band of lower mol. wt. than either rat cytochrome P-450c (P450 IA1) or P-450d (P450 IA2), which was recognized by antibodies to both P-450c and P-450d but preferentially by that against P-450c. This protein band was induced 3-4-fold by MC. MC treatment induced a second protein band in alligator microsomes of the same mol. wt. as rat P-450d, recognized preferentially by antibodies to rat cytochrome P-450d. 6. These results illustrate that the alligator mixed-function oxidase (MFO) system responds to MC in a similar manner as described in mammals, i.e. induction in P-450 content, increases in specific MFO activities, and the apparent expression of different P-450 isoenzymes.