Role of biotransformation in determining aldicarb toxicity in fish

The carbamate pesticide, aldicarb, demonstrates significant acute toxicity in fish, and is readily biotransformed by most organisms studied. In fish, both the cytochrome P450 (CYP) and the flavin monooxygenase systems (FMO) are involved in bioactivating aldicarb to aldicarb sulfoxide, which is a more potent inhibitor of acetylcholinesterase (AChE). Channel catfish (Ictalurus punctatus), along with many other fresh water species, do not express FMO and are relatively resistant to the effects of aldicarb. This project examined the toxicity, AChE inhibition, metabolism, and toxicokinetic of aldicarb in channel catfish, and compared these values with an aldicarb-sensitive species, rainbow trout, which expresses FMO. Studies of in vitro and in vivo aldicarb biotransformation in catfish suggest that a low rate of bioactivation (10 times slower V_max), resulting in less initial conversion to the activated metabolite, aldicarb sulfoxide, may be a contributing factor to resistance of channel catfish to aldicarb toxicity. These data are supported by toxicokinetic and enzyme inhibition studies. This work demonstrates that differences in FMO expression among fish species may have significant influence on toxicity resulting from exposure to some xenobiotics.     

Effect of cortisol and urea on flavin monooxygenase activity and expression in rainbow trout,Oncorhynchus mykiss

Expression of flavin-containing monooxygenase(s) (FMO) correlates with salinity exposure in certain species of euryhaline fish, such as the rainbow trout, Oncorhynchus mykiss. The mechanism(s) by which salinity regulates FMO is unclear. Adult rainbow trout were infused through the dorsal aorta with either cortisol or urea. At 500 ng/ml, cortisol caused a significant increase in FMO-catalyzed thiourea oxidase activity in gill and liver microsomes. FMOI expression, however, was significantly increased by the high cortisol dose only in gill microsomes. The levels of TMAO and urea were not altered by cortisol. In the liver, urea infusion caused an increase in hepatic FMO activity. FMO expression and activity correlated with elevated tissue urea levels, but TMAO concentrations were not related. These results indicate that FMO expression and activity may be partially controlled by the osmoregulatory/stress hormone. cortisol, and concentrations of the organic osmolyte, urea, in the rainbow trout.     

Expression of branchial flavin-containing monooxygenase is directly correlated with salinity-induced aldicarb toxicity in the euryhaline fish (Oryzias latipes)

Earlier studies in our laboratory have demonstrated a reduction of flavin-containing monooxygenase (FMO) activity when salt-water adapted euryhaline fish were transferred to water of less salinity. Since FMOs have been shown to be responsible for the bioactivation of the carbamate insecticide, aldicarb, to a more potent cholinesterase inhibitor, it would be predicted that euryhaline fish exposed to aldicarb at higher salinity should have greater levels of FMO and, hence, be more susceptible to aldicarb toxicity. It was not surprising, therefore, that mature female Japanese medaka (Oryzias latipes) were significantly more susceptible to aldicarb toxicity at higher salinity. A direct correlation was observed between salinity and FMO expression, but salinity had no significant effect on the uptake of aldicarb. These data suggest that FMOs are upregulated by salinity and may be responsible for the enhanced toxicity of aldicarb at higher salinities.     

The use of polyclonal antibodies raised against rat and trout cytochrome P450 CYP1A1 orthologues to monitor environmental induction in the channel catfish (Ictalurus punctatus)

Induction of hepatic cytochrome P450-dependent microsomal mono-oxygenase by xenobiotics is a well-established phenomenon in teleost fish. As in laboratory mammals, fish possess multiple forms of cytochrome P450 that display overlapping substrate specificity. One such isoform, CYP1A1, which has been cloned and sequenced from rainbow trout, has been shown to be orthologous to rat CYP1A1 and, as in mammals, is inducible up to several hundred-fold by planar aromatic hydrocarbons, PCBs and dioxins. It has been suggested that induction of CYP1A1 orthologues might provide a sensitive biomonitor for environmental pollution by mixtures of such compounds. In the current study, polyclonal antibodies directed against CYP1A1 purified from rat and trout liver were used to monitor induction of the CYP1A1 orthologue in hepatic microsomes from the fresh water species, the channel catfish (Ictalurus punctatus). Catfish from a local fish farm were induced in the laboratory by three daily injections of 50 mg/kg of the PCB mixture Aroclor 1254 and compared with fish taken from a site in central Arkansas—the Bayou Meto, known to be polluted with dioxin. Hepatic microsomal activities towards ethoxyresorufin (EROD) and pentoxyresorufin (PROD) were measured and Western blot analysis carried out with the two antibodies. EROD was elevated in both the Aroclor-treated fish and in the Bayou Meto fish compared with untreated fish farm controls; smaller but significant increases were observed in PROD. Spearman's rank correlations of 0·74 and 0·89 were observed between EROD and immunoquantified cross-reactivity towards the rat CYP1A1 and trout CYP1A1 antibodies.     

Metabolic activation of polycyclic aromatic hydrocarbons by fish liver cytochrome P-450

The incidence of hepatoma, epidermal and other forms of cancerous growths in fish is well documented (Halver, 1967; Matsushima & Sugimura, 1976; Dawe et al., 1964). In fish, as in mammals, cancer may be a result of metabolically activated carcinogens. In mammals the primary enzyme system involved in the activation of environmental carcinogens is the cytochrome P-450 linked mixed-function oxidase (MFO). The hepatic microsomes of the species offish studied contain variable levels of cytochrome P-450. Liver microsomes of the trout Salmo trutta lacustris are surprisingly active in metabolising benzo-[a]pyrene (BP) and other compounds preferentially metabolised by polycyclic aromatic hydrocarbon (PAH)-specific cytochrome P-450. This finding may be significant, because it is apparent that the detrimental effects of PAHs require metabolic activation.We have studied the production of reactive intermediates of BP by following their binding to DNA and by measuring the specific nucleotide-BP metabolite complexes by chromatography. Untreated S. trutta liver microsomes catalyse the production of reactive intermediates of BP which bind to nucleotides of DNA at a rate that is 3–4 times higher than that catalysed by control rat liver microsomes. The most prominent DNA-BP metabolite adducts produced by trout liver microsomes are the nucleoside adduct of BP-7, 8-diol-9,10-epoxide and 9-OH-BP-4,5-oxide and other phenol oxides. In contrast to the trout, another fish species, roach (Rutilus rutilus), has extremely low activity. Although the in vitro binding of BP to DNA is not strictly correlated to in vivo binding or biological effects, our results show that reactive intermediates are formed by trout liver and thus the prerequisite for chemical carcinogenesis or mutagenesis is ful filled. This is further supported by the fact that in Ames's test, trout liver preparations produce mutagenic products from promutagens.     

Quantification of cytochrome P4501A1 and catalytic activities in liver microsomes of isosafrol- and β-Naphthoflavone-treated rainbow trout (Oncorhynchus mykiss)

The effects of isosafrol (ISF) or β-naphthoflavone (βNF) treatments on cytochrome P450 (P450) levels in rainbow trout liver were investigated using immunochemical and catalytic techniques. The discrepancies in catalytic activities and ELISA quantification of rainbow trout P4501A1 protein levels between ISF- and βNF-treated fish indicate that important differences exist between the responses induced by βNF and ISF treatments in the rainbow trout liver.     

Characterization and induction of cytochrome P-450 in the rainbow trout kidney

Cytochrome P-450 monooxygenases catalyze the biotransformation of a great variety of foreign, as well as endogenous, lipid-soluble compounds to more water-soluble products. As in mammals, highest concentration of cytochrome P-450 in fish is found in the liver. However, previous studies have indicated that fish kidney contains relatively high cytochrome P-450-mediated activities.^1,2 We have therefore prepared and characterized subcellular fractions from the kidney of rainbow trout suitable for studies on cytochrome P-450-dependent reactions. Furthermore, as in the liver, several cytochrome P-450-mediated reactions in the kidney were induced following treatment of the fish with β-naphthoflavone.     

Characterization and molecular analysis of hepatic microsomal UDP-glucuronosyltransferases in the marine fish, Pleuronectes platessa

Here we report the results of the first molecular enzymological study of fish UDP-glucuronosyltransferase (UDPGT). UDPGT activities of plaice liver microsomes were greatest for planar phenols and there was low but measurable conjugation of bilirubin, testosterone and androsterone. A highly purified preparation was isolated which possessed activities towards 1-naphthol, bilirubin and testosterone, containing several molecular weight species of M_r 52–56 kDa. On immunoblot analysis these proteins cross-reacted with a polyspecific anti-rat UDPGT antibody, suggesting that a number of plaice UDPGT isoforms with epitopes in common with the corresponding rat enzymes had been purified.     

Cytochromes P-450 in cod (Gadus morhua): Effects of induces on regiospecificity of phenanthrene metabolism and immunochemical properties

The metabolism of some xenobiotics can lead to the formation of reactive intermediates with mutagenic/carcinogenic properties. With the carcinogenic PAH these have been identified as bay-region diol-epoxides.¹ Phenanthrene, a non-carcinogenic, bay-region containing model PAH, is metabolised in vivo by bony fish at the proximate bay-region position, whereas mammals and other marine organisms mainly form the K-region metabolite 9,10-dihydro-9,10-dihydroxy-phenanthrene.² We wanted to investigate this difference more closely by studying the regiospecificity of phenanthrene metabolism in vitro both with microsomes from differently pretreated cod and with isolated cytochrome P-450 isozymes from BNF-induced cod.³ Secondly, by preparing antibodies to the major isozyme isolated (called cod P-450c), we investigated the immunochemical properties of the variously treated cod liver microsomes.     

Microsomal estrogen metabolism in channel catfish

Our goal was to study the involvement of cytochrome P450 genes in estrogen metabolism and the extent to which the potentially carcinogenic 4-hydroxyestradiol metabolite is formed by channel catfish (Ictalurus punctatus; CC). Estradiol metabolism and ethoxyresorufin-O-deethylase (EROD) activity were assessed in several tissues from fish collected from three variably contaminated sites in the Mississippi River Delta, from laboratory control fish, and from fish exposed to 20 mg/kg benzo(a)pyrene (BaP) i.p. for 4 days. Liver EROD activity was induced by BaP, but Delta fish EROD activities were not statistically higher than activities in control fish. Gill microsomal EROD activity was also induced by BaP, but activities were 8- to 77-fold lower than those from liver. The predominant estrogen metabolites formed by CC liver, gill and gonad microsomes were 2-hydroxyestradiol and estrone as detected by GC/MS. Liver and gill 2-hydroxyestradiol formation was induced in BaP-dosed fish. The trends in hydroxyestradiol formation in field collected fish were more variable. In all fish liver microsomes there was more 2- compared to 4-hydroxyestradiol formed. However, BaP-treatment increased the 4:2 hydroxyestradiol ratio from 0.04 in control fish to 0.2 in BaP-exposed fish, suggesting that BaP induces the formation of the potentially genotoxic estrogen metabolite. No detectable 4-hydroxyestradiol was produced by gill and gonad microsomes. These results will ultimately help in determining which fish P450 genes are susceptible to environmental contamination and may be involved in estrogen genotoxicity.     

Kinetics of hepatic phase I and II biotransformation reactions in eight finfish species

Hepatic microsomes and cytosols of channel catfish (Ictalurus punctatus), rainbow trout (Oncorhynchus mykiss), Atlantic salmon (Salmo salar), red tilapia (Oreochromis sp.), largemouth bass (Micropterus salmoides), striped bass (Morone saxatilis), hybrid striped bass (M. saxatilis × M. crysops), and bluegill (Lepomis macrochuris) (n = 8) were used to study the kinetics of phase I (ECOD, EROD, PROD, BROD) and phase II (UDP-glucuronosyltransferase (UDPGT)-, sulfotransferase (ST)- and glutathione-s-transferase (GST)-mediated) reactions. The best catalytic efficiency for ECOD and GST activities was performed by channel catfish, Atlantic salmon, rainbow trout and tilapia. The highest EROD catalytic efficiency was for Atlantic salmon. None of the species had either PROD or BROD activities. Rainbow trout had very similar UDPGT catalytic efficiency to tilapia, channel catfish, Atlantic salmon, largemouth bass and bluegill. Sulfotransferase conjugation had no significant differences among the species. In summary, tilapia, channel catfish, Atlantic salmon and rainbow trout had the best biotransforming capabilities; striped bass, hybrid striped bass and bluegill were low metabolizers and largemouth bass shared some capabilities with both groups.     

Time-course studies of the biotransformation enzymes in control rainbow trout when adjusting to new habitats

Hepatic monooxygenase enzyme activities and relative cytochrome P4501A protein content were measured to evaluate the time-course alterations in rainbow trout after change in living habitat. Fish were transferred from one fish farm to the tanks of another hatchery and/or into cages kept in a lake. In the new habitats, cytochrome P450-dependent enzyme activities in rainbow trout decreased, and were at their lowest levels after two or three weeks in the summer. Later the activities partly reversed. The immunodetection of cytochrome P4501A protein expressed a similar trend as for catalytic monooxygenase activities.     

Metabolism of 2-acetylaminofluorene by rainbow trout

In order to examine factors that may contribute to the reported resistance of rainbow trout, Shasta strain, to the well-known hepatocarcinogenic effects of 2-acetylaminofluorene (AAF), the in-vitro and in-vivo metabolism of [¹⁴C]AAF in trout has been examined. Trout (compared to rat) liver microsomes metabolized AAF more efficiently, producing 3-fold larger amounts of ring-hydroxylated metabolites (7-hydroxy-AAF and 5-hydroxy-AAF), but 5-fold less N-hydroxy-AAF. Freshly isolated trout hepatocytes extensively metabolized AAF to form the same ring-hydroxylated metabolites and their respective glucuronide and sulfate conjugates. N-OH-AAF (plus its conjugates) and covalently-bound AAF derivatives amounted, respectively, to < 1% and 1.4–1.6% of total metabolites. Liver DNA of trout treated with AAF contained a single AAF-DNA adduct identified as N-(deoxyguanosin-8-yl)-2-aminofluorene (the major persistent AAF-DNA adduct found in rat liver). The level of this adduct (12 attomoles/μg DNA) was about 1000-fold lower than the level of AAF-DNA adduct previously reported in rat liver. The data show that trout liver, compared to rat liver, is considerably less efficient in metabolizing AAF to carcinogenic metabolites, and more efficient in forming nontoxic products, thus possibly explaining, in part, the resistance of trout to AAF-induced hepatocarcinogenesis.     

The cytochrome P450 1A1 response in fish: application of immunodetection in environmental monitoring and toxicological testing

We have developed polyclonal and, recently, monoclonal antibodies against the aromatic hydrocarbon-inducible P450 1A1 form purified from Atlantic cod (Gadus morhua). A simple, indirect enzyme-linked immunosorbent assay (ELISA) based on these antibodies has been developed in our laboratory and tested in numerous experiments with both field-collected and laboratory-exposed fish of different species. The exposure situations studied to date include complex mixtures such as polychlorinated biphenyls (PCBs), dioxins and water-soluble oil fractions, as well as defined compounds such as CB congeners, TCDD, and pesticides. Factors affecting the induction response, including sexual maturation and dietary factors, have also been investigated. The ELISA technique generally shows good correlation with contaminant exposure and catalytic measurements, but has also given new and important information in certain cases where catalytic measurements failed to reveal effects.     

Cytochrome P-450 isozymes in salmonids determined with antibodies to purified forms of P-450 from rainbow trout

Purification of cytochromes P-450 from liver microsomes of β-naphthoflavone (BNF)-fed rainbow trout yielded three apparently homogeneous forms. The major form (LM_4b)^* appears to be a P-448 type of cytochrome. A minor form (LM_4a), having properties very similar to LM_4b, was also obtained. In addition, a P-450 form (LM₂) was isolated, with properties quite different from LM_4a or LM_4b, including a high rate of aflatoxin B₁ (AFB₁) metabolism (Williams & Buhler, 1983c). Antibodies to all three forms were obtained from rabbits. The IgGs prepared against LM_4a and LM_4b both cross-reacted (forming lines of identity) equally well with both antigens on Ouchterlony plates. Rat P-448 cross-reacted (without lines of identity) with both LM_4a- and LM_4b-IgG. LM_4b-IgG was much more effective than LM_4a-IgG for inhibition of LM_4a or LM_4b reconstituted benzo[a]pyrene (BP) hydroxylase, suggesting that these two antibodies recognize different antigenic sites. The LM₂-IgG did not cross-react with any of the other rat or trout cytochromes P-450 examined. Levels of LM₂ and LM_4b in microsomes from untreated, polychlorinated biphenyl (PCB), phenobarbital (PB) or BNF-treated trout were estimated with an immunological technique involving electrophoresis on SDS-PAGE, followed by transfer to nitrocellulose and staining with either LM ₂ - or LM_4b -IgG. The ratio of in microsomes from PCB- or BNF-treated rainbow trout was much higher than 1, whereas the reverse was true with microsomes from untreated rainbow trout. These results are consistent with previous observations (Vodicnik et al., 1982) that pretreatment with BNF induced the synthesis of a P-448 type cyytochrome, presumably responsible for the great increase in the metabolism and activation of BP seen in these fish. Conversely, pretreatment with PB did not affect the levels of either LM₂ or LM_4b. This specific immunological technique should make it possible to assay the levels of these P-450 and P-448 isozymes in various strains of rainbow trout and other species of fish. In addition, the effect of age, sex, diet and exposure to P-450 and P-448 inducers could be examined and, perhaps, utilized to predict the relative risk of certain populations to pollutants activated by these different isozymes.     

Bleached kraft pulpmill effluents and TCDD: Effects on biotransformation and testosterone status of mature male rainbow trout (Salmo gairdneri)

The aim of this study was to examine the effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD, given intraperitoneally) alone and together with bleached kraft pulpmill effluents (BKME) on fish biotransformation reactions and testosterone levels in mature male rainbow trout (Salmo gairdneri Richardson). The results show extremely high induction in liver and kidney monooxygenase (PSMO) activities in 3 weeks caused by TCDD alone or TCDD together with BKME. BKME alone did not cause significant effects. 7-Pentoxyresorufin O-dealkylase activity, previously shown to be an indicator of phenobarbital-type induction, was shown to be highly inducible by TCDD in fish. Plasma testosterone levels, although decreased in another subacute exposure to BKME, showed only slight changes due to TCDD and TCDD + BKME.     

Comparative oxygen radical formation and toxicity of BDE 47 in rainbow trout cell lines

The polybrominated diphenyl ethers (PBDEs) constitute a class of flame retardants whose residues have markedly increased in fish and human tissues during the last decade. In particular, the levels of certain PBDE congeners in salmon have raised concern regarding potential risks associated with dietary PBDE exposures. However, little is known regarding PBDE-mediated cell injury in relevant in vitro cell models. We conducted a comparative study of oxyradical production and cell injury in rainbow trout gill (RTgill-W1) and trout liver cells (RTL-W1) exposed to 2,2',4,4'-tetrabromodiphenyl ether (BDE 47), a predominant BDE residue found in fish tissues such as salmonids. Exposure to low micromolar concentrations of BDE 47 elicited a significant loss in RTgill-W1 and RTL-W1 cell viability as measured by alamarBlue assay. The dose-response of BDE toxicity differed among the two cell lines, with the RTL-W1 liver cells showing greater resistance to toxicity at lower BDE 47 doses, but a more dramatic loss of viability relative to gill cells when challenged with higher (50 microM) doses. The sensitivity of the trout liver cells at higher BDE 47 exposures was reflected by a higher basal production of oxygen radical production by 6-carboxy-2',7'-dichlorodihydrofluorescein diacetate (DCFH-DA) fluorescence that was markedly enhanced in the presence of BDE 47, suggesting an overwhelming of trout liver cell antioxidant defense pathways. Collectively, our data indicate that RTgill-W1 and RTL-W1 liver cells are sensitive to BDE 47-mediated cell injury through a mechanism that may involve oxidative stress. Our data also provide an in vitro basis for potential tissue differences in BDE 47-mediated cell injury.     

Growth hormone effect on xenobiotic-metabolizing activities of rainbow trout

In recent years several studies reported the regulation by growth hormone (GH) of the expression of a variety of P450 forms in mammals. However the effect of GH on the xenobiotic-metabolizing enzymes of fish are still unknown. The aim of this work was to investigate the effects of ovine GH—a growth hormone known to be efficient in trout—on the cytochrome P450 level and on aryl hydrocarbon hydroxylase, aminopyrine-N-demethylase, glucuronyl transferase and glutathione transferase activities in trout. The GH-implanted trout (n = 50) each received a single cholesterol pellet containing ovine GH and were compared to control animals (n = 50) receiving a single cholesterol pellet without GH. After 15 days fish were killed and the liver and gills were excised for the measurement of xenobiotic-metabolizing enzyme activities. GH treatment significantly decreased the level of hepatic cytochrome P450 and the activities of cytochrome P450 dependent monooxygenases. In contrast, no significant effect of the treatment was observed on the glutathione transferase and UDP-glucuronyl transferase activities. Moreover, GH treatment had no effect on branchial phase I and phase II enzyme activities. This study provides evidence that GH level significantly affects the expression of several members of the hepatic cytochrome P450 family in trout.     

Cloning and sequencing of cytochrome P450 2X1 from channel catfish (Ictalurus punctatus)

Previous purification and immunochemical studies in livers of channel catfish indicated the presence of at least four cytochrome P450 (CYP) 2-like isoforms. Sequencing of the first 18 amino acids of one purified form indicated a CYP2 isoform. From this N-terminal sequence and other published CYP2 sequences from fish, primers were designed and a full-length CYP cDNA was identified from reverse-transcribed catfish liver mRNA. 5' and 3' RACE was used to obtain an open reading frame of 1470 bp encoding a 490 amino acid protein (approximately 57 kD). CYP2X1 was most identical to Fundulus heteroclitus CYP2P2 (41%); CYP2N2 (40%): and CYP2N1 (39%).