Mixed-function oxygenase in juvenile rainbow trout exposed to hexachlorobenzene or 3, 3′, 4, 4′-tetrachlorobiphenyl

• 1.1. 3,3',4,4'-tetrachlorobiphenyl (PCB 77), but not hexachlorobenzene, induced liver micro-somal cytochrome P-450 (Cyt P-450), ethoxycoumarin-O-deethylase (ECOD) and ethoxyresorufin-O-deethylase (EROD) in rainbow trout. Maximum induction was observed in a PCB 77 injected group of fish (1.0mg/kg, i.p. injection) 13 days after the injections being 2, 10 and 50 times the values of non-induced fish, respectively.
• 2.2. The apparent K_m value of ethoxyresorufin of this induced group of fish differed only slightly from that of non-induced fish. The apparent V_max value (EROD) was 50 times higher.
• 3.3. Freezing small pieces of liver in liquid nitrogen did not produce cytochrome P-420.
• 4.4. Fluorimetric and spectrophotometric measurements of EROD correlated.

     

Cytochrome P-450 levels and EROD activity in the Adriatic sturgeon (Acipenser naccarii, Chondrostei) and its induction by β-Naphthoflavone

The cytochrome P-450 enzyme system was studied in juvenile Acipenser naccarii (317.6±77 g initial live weight) reared at 23°C and at a standard diet over a period of two month before using for experiments (final weight 546.3±148.8 g). While determining normal levels of cytochrome P-450 in liver tissue its induction was also studied under exposure to P-naphthoflavone (BNF; single dose at 80 mg/Kg body weight 52 hrs prior to sampling). Control fish showed total cytochrome P-450 levels in liver microsomes around 0.40±0.12 nmoles/mg proteins (n=12) while in BNF exposed fish the values increased significantly (0.55±0.11nmoles/mg proteins; n=12). Ethoxyresorufin-O-deethylase (EROD) in control fish was 0.015±0.02 nmoles/mg proteins/min (n=12); it was found to be NADPH dependent and inducible by BNF. Western Immunoblotting and enzyme-linked-immunosorbent (ELISA) analyses of liver microsomes from untreated and BNF-exposed fish, using an antibody to rat cytochrome P-450 1A1 isoform (P-450 1A1) (Nelson et al.,1996) suggested the presence of a constitutive and BNF-inducible cytochrome P-450 homologous to rat P-450 protein.
Measurement of cytochrome P-450-dependent EROD activity and P-450 1A1 expression levels in A. naccarii may be a useful parameter in monitoring environmental pollution.     

Effects of polychlorinated biphenyls on cytochrome P450 induction in the chick embryo hepatocyte culture

The effects of pure synthetic polychlorinated biphenyl (PCB) congeners on the induction of cytochrome P450 and associated activities were examined in cultured chick embryo hepatocytes. Dose-response effects for the induction of total cytochrome P450 ethoxyresorufin-O-deethylase (EROD) activity, and benzphetamine demethylase (BPDM) activity were studied using 10 selected tetra- to hexachlorinated PCB congeners. These studies revealed that PCBs caused effects in the chick hepatocyte culture different from previously observed effects in rat liver. Based on their effects in chick hepatocytes, the PCBs could be categorized into two groups. The first group (consisting of 3,3',4,4'-PCB, 3,3',4,4',5-PCB, 3,3',4,4',5,5'-PCB, 2',3,3',4,5-PCB, 2,3,3',4,4',5'-PCB, and 2,3,4,4',5-PCB) induced total cytochrome P450 2.4- to 2.9-fold and EROD activity from 1-2 pmol/min/mg protein to 162-247. There was marked variation in potency, but all these congeners had a maximal inducing dose above which cytochrome P450 concentrations and EROD activities declined. BPDM activities were increased only slightly (1.2- to 1.6-fold) at the maximal cytochrome P450 inducing dose. The second group of congeners (consisting of 2,2',4,5,5'-PCB. 2,2',4,4',5,5'-PCB, and 2,2',3,4,4',6-PCB) induced total cytochrome P450 concentrations 4.0-fold and BPDM activities 2.2- to 2.6-fold with greatest activity occurring at the highest doses which could be added (10-50 microM). However, EROD activities were also increased by these congeners to 60-112 pmol/min/mg protein with declining activities seen at the highest PCB doses (i.e., resembling EROD induction patterns of the first group). The EROD induction patterns with these latter PCB congeners are noteworthy since these PCBs do not induce EROD activity in the rat. For both groups of PCB congeners, EROD induction was associated with increased accumulation of uroporphyrin in cultures exposed to exogenous 5-aminolevulinate. Studies investigating the reason for the depression of cytochrome P450 concentrations and/or EROD activities by high doses of the PCBs revealed that with the first group there was slightly decreased total protein synthesis, decreased total cell heme concentrations, and decreased accumulation of radiolabeled heme synthesized from 5-[14C]aminolevulinate. These changes might represent nonspecific toxic effects of the first group of PCBs. However, since these changes were not seen with the second group of PCBs, it is unlikely that either inhibition of heme synthesis or toxicity cause the depression of EROD activity with high PCB doses.     

The effect of sex steroids and pregnenolone-16 alpha-carbonitrile on the hepatic microsomal monooxygenase system of rainbow trout (Salmo gairdneri)

Estradiol benzoate (EB-5 mg/kg) or testosterone propionate (TP-50 mg/kg) administration to sexually immature rainbow trout resulted in an increase in liver weight to body weight ratios, and a diminution in hepatic microsomal benzphetamine-N-demethylation (BeND), ethoxycoumarin- and ethoxyresorufin-O-deethylations (ECOD, EROD) and cytochrome(s) P-450 content when compared to corn oil-pretreated controls. A low dose of TP (2 mg/kg) caused an increase in cytochrome(s) P-450 content but had no effect on the selected monooxygenase activities. EB administration prior to treatment with 150 mg/kg beta-naphthoflavone caused a dose-dependent decrease in the magnitude of induction of cytochrome(s) P-450 and associated catalytic activities. These data suggest that the sex differences in monooxygenation observed in prespawning trout are mediated via the sex steroids and that fish may respond differently to inducers depending on their reproductive state at the time of exposure. Administration of the synthetic steroid, pregnenolone-16 alpha-carbonitrile (PCN), resulted in an increase in BeND and ECOD but had no effect on EROD or cytochrome(s) P-450 content.     

Further consideration of phenobarbital effects on cytochrome P-450 activity in the killifish, Fundulus heteroclitus

1. Ethoxyresorufin O-deethylase (EROD) activity, aldrin epoxidase (AE) activity, cytochrome P-450 content, and levels of cytochrome P-450E (the major BNF-inducible P-450 form and primary EROD catalyst in scup) or its homologues were measured in hepatic microsomes isolated from Fundulus heteroclitus, scup (Stenotomus chrysops) and brook trout (Salvelinus fontinalis) treated with beta-naphthoflavone (BNF) or phenobarbital (PB). 2. In all three teleost species, BNF treatment caused expected increases in P-450 content, EROD activity and P-450E level; but either no change or a slight decrease in AE turnover rate (nmol/min/nmol P-450). 3. Polyclonal antibodies to P-450E did not inhibit AE activity in microsomes from BNF-treated scup, confirming that this major BNF-inducible P-450 form does not catalyze AE activity in fish. 4. In contrast, PB treatment did not affect hepatic AE activity, P-450 content or levels of "P-450E" in F. heteroclitus, but did variably affect EROD activity which was suppressed in one experiment and elevated in another. 5. The results indicate that (i) contrary to previous reports, neither PB nor MC-type inducers increase AE activity in F. heteroclitus, (ii) MC-type inducers do not affect AE activity in the other teleost species examined, and (iii) AE activity is not a reliable indicator of P-450 induction by environmental chemicals. 6. We emphasize the need to establish the mechanism of PB action, and the nature of any fish P-450 forms analogous to PB-inducible forms in mammals in order to conclusively evaluate PB-responses in fish.     

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

Monoclonal antibody (MAb) 1-12-3 generated against liver cytochrome P-450E (P-450E), an aryl hydrocarbon hydroxylase of the marine fish Stenotomus chrysops (scup), reacted only with P-450E when tested in immunoblot analysis with five P-450 fractions from scup liver. This and six other MAbs against P-450E recognized purified P-450E, as well as a single band in beta-naphthoflavone (BNF)-induced scup microsomes that comigrated with authentic P-450E. Like MAb 1-12-3, polyclonal anti-P-450E reacted with P-450E but not with other scup P-450 fractions and reacted strongly with a band coincident to P-450E in BNF-treated scup microsomes. However, the polyclonal antibody (PAb) also faintly recognized additional microsomal proteins. MAb 1-12-3 recognized P-450E induced by 3,3',4,4',5,5'-hexachlorobiphenyl and by polychlorinated biphenyl mixtures in scup, and a single band induced by BNF or 3-methylcholanthrene (MC) in microsomes of other teleosts, including two trout species, killifish and winter flounder. The content of the P-450E counterpart in these fish and also in untreated scup coincided with induced ethoxyresorufin O-deethylase (EROD) activity. Induced EROD activity in scup and trout was strongly inhibited by MAb 1-12-3, further demonstrating the relationship between P-450E and induced P-450E in trout. MAb 1-12-3, two other MAbs, and anti-P-450E PAb recognized a band comigrating with P-450c in BNF-induced rat microsomes. MAb 1-12-3 also recognized purified rat P-450c. MAb 1-12-3 and anti-P-450E PAb recognized a second band of lower molecular weight than P-450c in BNF rat microsomes which may correspond to P-450d, the MC- and isosafrole-inducible rat isozyme. The results firmly establish the identity of scup P-450E, the relationship of BNF-induced P-450 in other teleosts with P-450E, and the immunochemical relationship of P-450E with rat P-450c. Furthermore, results with untreated fish suggest that effects of environmental chemicals may be detected by immunoblotting with monoclonal anti-P-450E.     

Drug-induction decreases the mobility of cytochrome P-450 in rat liver microsomes: protein rotation study

Effect of drug-induction on the rotation of cytochrome P-450 and on lipid fluidity in rat liver microsomes was examined. Rotational diffusion of cytochrome P-450 was examined by observing the decay of absorption anisotropy, r(t), after photolysis of the heme.CO complex by a vertically polarized laser flash. Analysis of r(t) was based on a "rotation-about-membrane normal" model. Microsomal lipid fluidity was measured by observing fluorescence anisotropy of DPH incorporated in the lipid bilayer. The absorption anisotropy decayed within 2 ms to a time-independent value. Rotational diffusion of cytochrome P-450 was dependent on the drug-induction with PB, MC, and PCB when compared with non-induced CON-microsomes. The observed values for the normalized time-independent anisotropy r(infinity)/r(0) are r(infinity)/r(0) = 0.41 (CON-microsomes), 0.54 (PB-microsomes), 0.52 (MC-microsomes), and 0.57 (PCB-microsomes). The average rotational relaxation time phi = 580-690 microseconds was almost unchanged over all microsomes presently examined. A significantly high value of r(infinity)/r(0) = 0.41-0.57 implies the co-existence of mobile and immobile populations of cytochrome P-450. Based on the assumption that the heme tilts about 55 degrees from the membrane plane for all species of P-450s besides P-450PB, 59% (CON-microsomes), 46% (PB-microsomes), 48% (MC-microsomes), and 43% (PCB-microsomes), respectively, of the cytochrome P-450 in microsomes is calculated to be mobile. Upon drug-induction the microsomal membrane was fluidized to some extent as judged by the steady-state fluorescence anisotropy of 0.156 for CON-microsomes and 0.139-0.148 for drug-induced microsomes.(ABSTRACT TRUNCATED AT 250 WORDS)     

Application of a cytochrome P-450 IA1-ELISA in environmental monitoring and toxicological testing of fish.

1. An enzyme-linked immunosorbent assay (ELISA) based on polyclonal rabbit anti-cod cytochrome P-450 IA1 IgG has been developed in our laboratory. 2. The antibodies employed in the ELISA demonstrate good cross-reactivity with the homologous protein in a number of other fish species, giving cross-reacting protein bands o 54-59 kDa in liver microsomes, as determined by Western blotting. 3. The ELISA technique has been used in numerous experiments with both field collected and laboratory exposed fish of different species, showing good correlation with contaminant exposure. 4. In some instances of PCB exposure where the classical P-450 IA1 monooxygenase assay 7-ethoxyresorufin O-deethylase (EROD) failed to reveal any induction, the ELISA technique demonstrated increased levels of P-450 IA1 protein, indicating inhibiting effects of the PCBs on EROD measurement. 5. In tissues like gill filaments, and in whole cod larvae, where EROD activity is barely detectable, if at all, the ELISA technique showed induction after exposure to a water soluble fraction (WSF) of North Sea crude oil. 6. The results reviewed indicate the usefulness of the ELISA technique to allow rapid screening of a large number of samples, and especially when catalytic measurement is difficult or impossible due to (a) small sample or tissue size, (b) loss of activities in bad storage conditions, or (c) presence of compounds inhibiting activity.     

The liver monooxygenase system of Brazilian freshwater fish

Content of cytochromes b5 and P-450, and activities of NADPH-cytochrome c (P-450) reductase (NCR) and 7-ethoxyresorufin O-deethylase (EROD) were measured in liver microsomes prepared from two South American endemic fish, Brycon cephalus and Colossoma macropomum, from tilapia, Oreochromis niloticus, and from Swiss mice, Mus musculus, which served as a control. Strong hemoglobin binding to fish liver microsomal membranes (FLM) altered visible spectra of microsomal cytochromes. Consequently, special precautions during FLM preparation, including liver perfusion followed by repeated washing of microsomes, were required in the study of microsomal cytochromes from these fish. FLM from all fish studied here had a significantly lower content of microsomal cytochromes but a similar level of NCR and EROD activities compared to mouse liver microsomes (MLM). Strong response of the monooxygenase system in O. niloticus to water pollution was detected with both specific cytochrome P-450 content and EROD activity increasing sharply. The optical spectra of hemoglobin from B. cephalus and C. macropomum were analyzed and some differences in shape and relative extinction were observed compared to known hemoglobins.     

Cytochrome P-450 arachidonic acid epoxygenase. Regulatory control of the renal epoxygenase by dietary salt loading.

The rat kidney microsomal epoxygenase catalyzed the asymmetric epoxidation of arachidonic acid to generate as major products: 8(R),9(S)-, 11(R),12(S)- and 14(S),15(R)-epoxyeicosatrienoic acids with optical purities of 97, 88, and 70%, respectively. Inhibition studies utilizing a panel of polyclonal antibodies to several rat liver cytochrome P-450 isoforms, indicated that the renal epoxygenase(s) belongs to the cytochrome P-450 2C gene family. Dietary salt, administered either as a 2-2.5% (w/v) solution in the drinking water or as a modified solid diet containing 8% NaCl (w/w), resulted in marked and selective increases in the renal microsomal epoxygenase activity (416 and 260% of controls, for the liquid and solid forms of NaCl, respectively) with no significant changes in the microsomal omega/omega-1 oxygenase or in the hepatic arachidonic acid monooxygenase reaction. Immunoblotting studies demonstrated that dietary salt induced marked increases in the concentration of a cytochrome P-450 isoform(s) recognized by polyclonal antibodies raised against human liver cytochrome P-450 2C10 or rat liver cytochrome P-450 2C11. Comparisons of the stereochemical selectivity of the induced and non-induced microsomal epoxygenase(s) with that of purified rat liver cytochrome P-450 2C11 suggest that the salt-induced protein(s) is catalytically and structurally different from liver cytochrome P-450 2C11. The in vivo significance of dietary salt in regulating the activities of the kidney endogenous arachidonic acid epoxygenase was established by the demonstration of a salt-induced 10-20-fold increase in the urinary output of epoxygenase metabolites. These results, in conjunction with published evidence demonstrating the potent biological activities of its metabolites, suggest a role for the epoxygenase in the renal response to dietary salt.     

Xenobiotic biotransformation in the rainbow trout liver and kidney during starvation

Microsomal cytochrome P-450-dependent activities in the kidney of fish starved for 6 weeks were significantly lower than in fed fish whereas these activities in the liver were only depressed after 12 weeks of starvation. Hepatic cytochrome P-450-dependent activities were depressed to varying extents after 12 weeks of starvation when different substrates were used. The content of hepatic cytochrome P-450 was not affected by starvation. Hepatic UDP-glucuronosyl transferase activities were not affected by starvation. Induction of several hepatic cytochrome P-450-dependent activities by treatment of fish with beta-naphthoflavone was not influenced by starvation. In the kidneys of fish starved for 12 weeks induced levels of cytochrome P-450-dependent benzo(a)pyrene hydroxylase activities were significantly lower than in the kidneys of fed induced fish.     

Differential inhibition of hepatic microsomal alkoxyresorufin O-dealkylation activities by tetrachlorobiphenyls

Polychlorinated biphenyls (PCBs) elicit a spectrum of biochemical and toxic effects in exposed animals. In the present study, we assessed the effect of PCB structure, using four symmetrically-substituted PCBs, on cytochrome P450 (CYP)-mediated methoxy-, ethoxy- and benzyloxyresorufin O-dealkylase (MROD, EROD and BROD, respectively) activities. We found that 2,2',4,4'-tetrachlorobiphenyl (PCB 47), 2,2',5,5'-tetrachlorobiphenyl (PCB 52), 2,2',6,6'-tetrachlorobiphenyl (PCB 54) and 3,3',4,4'-tetrachlorobiphenyl (PCB 77) inhibited alkoxyresorufin O-dealkylase activities in hepatic microsomes from 3-methylcholanthrene (MC) or phenobarbital (PB)-treated rats. Measurement of the in vitro inhibitory potencies of the tetrachlorobiphenyls revealed that MROD, EROD and BROD activities were differentially inhibited and the degree of inhibition was determined by the chlorination pattern of the PCB. PCB 77 was more potent than PCB 47 or PCB 52 at inhibiting MROD and EROD activities in hepatic microsomes from MC-treated rats, while no inhibition of either activity was observed with PCB 54. In contrast, BROD activity measured in hepatic microsomes from PB-treated rats was inhibited by PCB 47, PCB 52 and PCB 54 but not by PCB 77. The mode of inhibition for each activity was also evaluated statistically. Inhibition of the alkoxyresorufin O-dealkylase activities could not be discerned in hepatic microsomes from corn oil-treated rats because the activities were inherently too low. No evidence for mechanism-based inhibition of MROD, EROD or BROD activities or an effect via CYP reductase was found. The results demonstrate that relatively coplanar PCBs such as PCB 77 preferentially inhibit EROD and MROD activities, whereas noncoplanar PCBs such as PCB 54 preferentially inhibit BROD activity.     

Cytochrome P-450 mediated reductive dehalogenation of the perhalogenated aromatic compound hexachlorobenzene

Hexachlorobenzene (HCB) elicits concentration-dependent and saturable type 1 binding spectra when added to oxidized (Fe3+) cytochrome P-450 (CYT P-450) in control, phenobarbital- (PB) induced, and beta-naphthoflavone- (BNF) induced male Sprague-Dawley rat liver microsomes. The spectral binding constants (Ks) for HCB in control and PB-induced microsomes are 180 microM and 83 microM, respectively, and correlate inversely with the specific content of CYT P-450 (0.9 and 2.1 nmol/mg) in the two microsomal preparations. BNF-induced microsomes show type 1 interaction only at low HCB concentration. Overall biotransformation of HCB, monitored by loss of [14C]HCB from the reaction medium, is dependent on NADPH and intact microsomes. Dimethyl sulfoxide (Me2SO), a potent hydroxyl radical scavenger and the solvent used for HCB dissolution, does not affect the biotransformation of HCB in aerobic reactions. Pentachlorobenzene (PCB) appears to be the initial and major isolatable CYT P-450 mediated dechlorination product of HCB with NADPH-fortified rat liver microsomes. Trace levels of pentachlorophenol (PCP) and an unidentified metabolite are also observed. PCB formation is enhanced under anaerobic conditions but is inhibited by metyrapone and carbon monoxide. PCB formation is also inhibited with aerobic reaction conditions, while PCP formation is observed. The data indicate that CYT P-450 in hepatic microsomes supports the reductive dechlorination of HCB to PCB.     

Nucleotide sequence of a human liver cytochrome P-450 related to the rat male specific form

P-450 human-2 is a human cytochrome P-450 that is immunochemically related to a constitutive male-specific cytochrome P-450 (P-450-male) and the phenobarbital-inducible P-450b/e in rat liver. By screening a human liver cDNA library in bacteriophage lambda gt11, we isolated a clone with an insert length of 1,847 bases (pHY13). The clone was sequenced and shown to code for a protein of 487 amino acids. The N-terminal 11-amino-acid sequence was in agreement with the protein sequence of P-450 human-2. The nucleotide sequence of pHY13 showed less than 50% similarity with those of human cytochrome P-450s, pHP-450(1), HLp, P-450NF, P1-450 4, and P3(450), but the nucleotide sequence of pHY13 is 80% similar to the reported sequence of rat cytochrome P-450, P-450(M-1). In addition, the coding sequence of pHY13 showed close similarity to that of MP-8, which was recently reported as the sequence corresponding to human cytochrome P-450MP, although no apparent similarity was observed in their 3' non-coding sequences except for the first 75 bases and the expected length of the complete sequences. These results, together with the immunochemical data, indicate that P-450 human-2 is closely related, but not identical, to P-450MP, and may belong to the category of developmentally regulated constitutive cytochrome P-450s.     

Monoclonal antibodies to liver microsomal cytochrome P-450E of the marine fish Stenotomus chrysops (scup): cross reactivity with 3-methylcholanthrene induced rat cytochrome P-450

Hybridomas were prepared from myeloma cells and spleen cells of BALB/c female mice immunized with hepatic cytochrome P-450E purified from the marine fish, Stenotomus chrysops (scup). Nine independent hybrid clones produced MAbs, either IgG1, IgG2b, or IgM, that bound to purified cytochrome P-450E in radioimmunoassay. Antibodies from one clone MAb (1-12-3), also strongly recognized rat cytochrome P-450MC-B (P-450BNF-B; P-450c). The nine antibodies inhibited reconstituted aryl hydrocarbon hydroxylase (AHH) and ethoxycoumarin O-deethylase of scup cytochrome P-450E to varying degrees, and inhibited AHH activity of beta-naphthoflavone-induced scup liver microsomes in a pattern similar to that in reconstitutions, indicating that cytochrome P-450E is identical to the AHH catalyst induced in this fish by beta-naphthoflavone. MAb 1-12-3 also inhibited the reconstituted AHH activity of the major BNF-induced rat isozyme. Conversely, MAb 1-7-1 to rat cytochrome P-450MC-B had little effect on AHH activity of scup cytochrome P-450E, and did not recognize cytochrome P-450E in radioimmunoassay nor in an immunoblot. Scup cytochrome P-450E and rat cytochrome P-450MC-B thus have at least one common epitope recognized by MAb 1-12-3, but the epitope recognized by Mab 1-7-1 is absent or recognized with low affinity in cytochrome P-450E. The various assays indicate that the nine MAbs against cytochrome P-450E are directed to different epitopes of the molecule. These MAbs should be useful in determining phylogenetic relationships of the BNF- or MC-inducible isozymes and their regulation by other environmental factors.     

An immunochemical analysis of the induction of cytochrome P-450 isoforms in the liver of fresh-water fishes by 3-methylcholanthrene, beta-naphthoflavone and aroclor 1254

The cytochrome P-450 isoforms have been studied in liver microsomes of some fish species from Lake Baikal. Using the inhibitory analysis of microsomal monooxygenase activities carried out by the specific polyclonal antibodies it has been shown that 3-methylcholanthrene, beta-naphthoflavone and arochlor 1254 induce isoforms immunologically related to cytochrome P-488c but not to the rat cytochrome P-450b in fish liver microsomes. The immunologic identity in isoforms of fish and rat cytochromes induced by methylcholanthrene has not been revealed. A possibility to use the method of the inhibitory analysis of fish microsomal activities by specific antibodies to the rat cytochrome P-450 isoforms for biomonitoring and biotesting of polycyclic hydrocarbons and polychlorinated biphenyls in aquatic systems is discussed.     

Musk xylene is a novel specific inducer of cytochrome P-450IA2.

The effect of musk xylene on contents of both cytochrome P-450IA1 and cytochrome P-450IA2 in rat liver was investigated using Western blotting analysis. Rats were treated i.p. for five consecutive days with either 50, 100 or 200 mg musk xylene/kg body weight. Musk xylene increased both total cytochrome P-450 and cytochrome b5 contents in rat liver microsomes. Musk xylene induced cytochrome P-450IA2 (384 pmol/mg protein) strongly and preferentially and the ratio of cytochrome P450IA2/P-450IA1 was about 12 at the lowest dose tested. Musk xylene also induced the cytochrome P-450IA1 dose-dependently, but these extents were very small (32-174 pmol/mg protein). These results suggest that musk xylene may be a more specific inducer for cytochrome P-450IA2 than any other inducers reported.     

Molecular cloning of monkey liver cytochrome P-450 cDNAs: similarity of the primary sequences to human cytochromes P-450.

Three cDNAs coding for monkey cytochrome P-450 (P450) 2C, 2E and 3A (MKmp13, MKj1 and MKnf2, respectively) were isolated from a lambda gt11 cDNA library of a liver from a 3-methylcholanthrene (3MC)-treated crab-eating monkey, using cDNA fragments for human P450 2C, 2E and 3A as respective probes. MKmp13 and MKnf2 were 1901 and 2032 bp long, containing entire coding regions for polypeptides of 490 and 503 residues, respectively. The deduced N-terminal amino acid sequences of MKmp13 and MKnf2 were identical with those of P450-MK1 and P450-MK2, which had been purified from liver microsomes of untreated and polychlorinated biphenyl (PCB)-treated crab-eating monkeys, respectively. MKj1 was 1508 bp long, encoding a polypeptide of 449 residues, which is presumed to lack N-terminal 45 residues as compared with the sequence for human P450 2E1. Northern blot analysis indicated that monkey P450 2C, 2E and 3A mRNAs were expressed constitutively in monkey livers. P450 2E and 3A mRNAs were induced by both 3MC and PCB, while P450 2C mRNA was induced only by PCB. The deduced amino acid sequences of four monkey cytochrome P-450 cDNAs, including P450 1A1 (MKah1) which we isolated previously, were more than 92% identical with those of corresponding human cytochrome P-450 cDNAs.     

Hepatic mitochondrial cytochrome P-450 system. Purification and characterization of two distinct forms of mitochondrial cytochrome P-450 from beta-naphthoflavone-induced rat liver

We have purified two distinct isoforms of mitochondrial cytochrome P-450 from beta-naphthoflavone (beta-NF)-induced rat liver to greater than 85% homogeneity and characterized their molecular and catalytic properties. One of these isoforms showing an apparent molecular mass of 52 kDa is termed P-450mt1 and the second isoform with 54-kDa molecular mass is termed P-450mt2. Cytochrome P-450mt2 comigrates with similarly induced microsomal P-450c (the major beta-NF-inducible form) on sodium dodecyl sulfate-polyacrylamide gels and cross-reacts with polyclonal antibody monospecific for cytochrome P-450c. Cytochrome P-450mt2, however, represents a distinct molecular species since it failed to react with a monoclonal antibody to P-450c and produced V8 protease fingerprints different from P-450c. Cytochrome P-450mt1, on the other hand, did not show any immunochemical homology with P-450c or P-450mt2 as well as partially purified P-450 from control mitochondria. Electrophoretic comparisons and Western blot analysis show that both P-450mt1 and P-450mt2 are induced forms not present in detectable levels in control liver mitochondria. A distinctive property of mitochondrial P-450mt1 and P-450mt2 was that their catalytic activities could be reconstituted with both NADPH-cytochrome P-450 reductase as well as mitochondrial specific ferredoxin and ferredoxin reductase electron transfer systems, while P-450c showed exclusive requirement for NADPH-cytochrome P-450 reductase. Cytochromes P-450mt1 and P-450mt2 were able to metabolize xenobiotics like benzo(a)pyrene and dimethyl benzanthracene at rates only one-tenth with cytochrome P-450c. Furthermore, P-450mt1, P-450mt2, as well as partially purified P-450 from control liver, but not P-450c, showed varying activities for 25- and 26-hydroxylation of cholesterol and 25-hydroxylation of vitamin D3. These results provide evidence for the presence of at least two distinct forms of beta-NF-inducible cytochrome P-450 in rat hepatic mitochondria.     

Metabolic disturbances in fish exposed to sodium pentachlorophenate (NaPCP) and 3,3',4,4',5-pentachlorobiphenyl (PCB126), individually or combined

The Swan River Estuary is the recipient of multiple urban and agricultural contaminants which have the potential to induce liver detoxication enzymes as well as altering the metabolism of aquatic organisms. To test if altered liver metabolism would influence liver detoxication capacities, pink snapper (Pagrus auratus) were i.p. injected with peanut oil (controls), or pentachlorobiphenyl #126 (PCB126), with sodium pentachlorophenate (NaPCP), or PCB126+NaPCP. Relative to controls, ethoxyresorufin-O-deethylase (EROD) activity was induced in the PCB126 and PCB126+NaPCP fish, but not in the NaPCP group. In the liver, cytochrome c oxidase (CCO) activity was enhanced by the treatments while citrate synthase (CS) activity remained unchanged and lactate dehydrogenase (LDH) activity was increased in the NaPCP treatment only. The results suggest that liver CCO activity may be a suitable biomarker of effect following exposure to PCBs or phenolic compounds. In the white muscle, only the PCB126+NaPCP treatment enhanced CCO activity, with all other enzymatic activities remaining unchanged. It appears that the resilience to metabolic perturbations is greater for white muscle than for liver. Low serum sorbitol dehydrogenase (sSDH) activity and histopathology of the liver indicated no significant alteration of cellular structure, albeit the lipid droplet size was increased in the PCB126 and in the PCB126+NaPCP treatments. It is concluded that the hepatic metabolic changes correspond to histopathological observations, but an altered metabolic capacity do not influence the metabolism of xenobiotics by liver enzymes, as measured by EROD activity.