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.     

Disposition and metabolism of 2,3,7,8-tetrachlorodibenzofuran (TCDF) in rainbow trout

In order to elucidate the metabolic fate of 2,3,7,8-tetrachlorodibenzofuran (TCDF) in fish and to thereby facilitate the assessment of the risks posed by this environmental toxin, we determined the whole body half-life, tissue distribution and metabolism of [³H TCDF in rainbow trout (Onchorynchus mykiss), treated orally. A whole body biphasic elimination pattern resulted in the excretion of 60% of the administered chemical during the first 3 days, after which a much slower elimination-rate (half-life = 14 days) was observed. Significant amounts of water-soluble metabolites were found in both bile and liver. Of the TCDF-derived radioactivity in bile, approximately 50% represented glucuronide conjugates, predominantly 4-hydroxy-2,3,7,8-TCDF: substantial amounts of the sulfate conjugate of this same metabolite were also present. Except at early time points, muscle contained the predominant fraction of TCDF-derived radioactivity, amounting to 25–65% of the total radioactivity present in the fish. More than 95% of the radioactivity present in muscle represented unmetabolized TCDF.     

In vitro mechanistic differences in benzo[a]pyrene–DNA adduct formation using fish liver and mussel digestive gland microsomal activating systems

Turbot (Scophthalmus maximus) and mussel (Mytilus edulis) microsomes were incubated with DNA to examine if microsomal in vitro metabolism of BaP could result in DNA adducts detected by ³²P-postlabelling. Turbot DNA was incubated with benzo[a]pyrene (BaP), NADPH and microsomal activating systems prepared from either livers of unexposed turbot, turbot exposed to BaP or β-naphthoflavone (ß-NF) or digestive glands from mussels. The β-NF activating system generated the highest levels of DNA adducts detected in this study (451.7 adducts per 10⁸ nucleotides) and were distributed in three discrete adduct TLC spots, one of which (97% of the total adducts) co-migrated with the ³²P-postlabelled BaP 7,8-diol, 9,10-epoxide-N²-guanine adduct. Fewer adducts (P <0.05) were generated by BaP-induced microsomes (9.4–30.6 adducts per 10⁸ nucleotides) but levels were higher (P <0.05) than those generated from untreated fish (3.5 adducts per 10⁸ nucleotides). Co-incubation with 500 μM α-naphthoflavone (α-NF) resulted in 97–99% inhibition in adduct formation implicating cytochrome P450-dependent (CYP) bioactivation however there was some evidence for carry over of BaP in the liver microsomal preparations from BaP injected fish. In contrast to the fish activating systems, no DNA adducts were observed when mussel microsomes were incubated with BaP, DNA and NADPH.     

Metabolism of tributyltin oxide by crabs, oysters and fish

Bis(tributyltin) oxide (TBTO) is widely used as an antifouling agent in various antifouling paints. Thus, some marinas have TBTO concentrations as high as 2 μg/liter.¹ These concentrations can be toxic to zooplankton.² The objectives of the present study were to determine the ability of a number of marine animals, including crabs, oysters and fish, to metabolize TBTO. Earlier work showed that extracts of rat liver were able to metabolize TBTO to a variety of metabolites, e.g. β-hydroxybutyldibutylin.³ The role of the cytochrome P-450 dependent mixed-function oxygenase system in oxidizing TBTO in marine animals was also of interest. Both in vivo (uptake of ¹⁴C-TBTO from food or water) and in vitro studies demonstrated that all the animals were able to metabolize TBTO. The oysters metabolized TBTO at a much slower rate than the other animals. The mixed-function oxygenase system from hepatic tissues of the various animals was able to metabolize TBTO by forming a number of hydroxylated metabolites.     

Correlative changes in metabolism and DNA damage in turbot (Scophthalmus maximus) exposed to benzo[a]pyrene

Juvenile turbot (Scophthalmus maximus) were injected intraperitoneally with either corn oil or 5 mg/kg benzo[a]pyrene (BaP) dissolved in corn oil and sampled I and 3 days after injection. After 1 day, no elevation of 7-ethoxyresorufin O-deethylase (EROD) activity was observed, however bile metabolites (BaP-7,8 dihydrodiol representing 70% of the total metabolites) and a single hepatic DNA adduct spot (0.47 adducts/10(8) nucleotides) identified by 32P-postlabelling were formed. No BaP metabolites or DNA adducts were observed in either control or carrier control fish. Fish sampled after 3 days reported 5-fold higher (P < 0.05) levels of EROD activity, a shift in the bile metabolite profile towards BaP phenol formation (1OH and 30H BaP comprising up to 60% of total metabolites detected) and the formation of two adduct spots (0.86 and 0.71 adducts/10(8) nucleotides). These results show that BaP can be metabolised and form hydrophobic DNA adducts in turbot without EROD elevation. Following EROD elevation, a shift in the profile of both BaP metabolites and BaP metabolite-DNA interactions occurs indicative of other oxidative processes.     

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.     

Increased toxicity of benzo(a)pyrene-7,8-dihydrodiol in the presence of polychlorobiphenylols

Benzo(a)pyrene (BaP) and polychlorinated biphenyls (PCBs) often co-exist in contaminated environments. Polychlorobiphenylols (OH-PCBs), formed by CYP-dependent monooxygenation of PCBs, are potent inhibitors of the glucuronidation of hydroxylated BaP metabolites. We hypothesized that OH-PCBs could drive the biotransformation of (−)BaP-7,8-dihydrodiol (BaP-7, 8-D) away from detoxication and towards formation of the reactive metabolite. A mixture of five OH-PCBs with 4–6 Cl atoms was infused into isolated, perfused, biliary intact livers (n=3 fish) removed from 3-methylcholanthrene-induced channel catfish. Controls (n=3) were infused with vehicle. Subsequently, [³H]-BaP-7, 8-D was infused into each liver and bile was collected for 1 h. The livers were taken for analysis of metabolites and DNA adducts. Induction status was confirmed by EROD assay. Bile was analyzed for metabolites. It was found that preinfusion of the mixture of OH-PCBs reduced the extent of glucuronidation of BaP-7, 8-D and increased the formation of DNA adducts 5-fold over controls. GSH conjugates, tetrols and triols were increased in the OH-PCB-infused fish, providing further support for our hypothesis that if the glucuronidation were inhibited, CYP-dependent activation would increase. These studies suggest a mechanism for synergy of toxicity of PAH and PCBs.     

Simultaneous exposure of English sole (Parophrys vetulus) to sediment-associated xenobiotics: Part 1—uptake and disposition of 14C-polychlorinated biphenyls and 3H-benzo[a]pyrene

English sole (Parophrys vetulus) were exposed to environmentally realistic levels of sediment-associated ³H-benzo[a]pyrene (3 μg BaP/g sediment, dry weight) and ¹⁴C-Aroclor 1254 (1 μg PCBs/g), separately and together, for up to 10 days. BaP and its metabolites in tissues reached steady-state concentrations by the first day of the exposure, whereas PCBs did not approach steady-state concentrations until the tenth day of exposure. Simultaneous exposure of sole to BaP and PCBs, relative to separate exposure to the xenobiotics, significantly increased the concentrations of BaP-derived radioactivity and decreased the concentrations of PCB-derived radioactivity in some tissues and bile. Accumulation of PCB-derived radioactivity, estimated as the burden in tissues, was significantly greater (4- to 13-fold) than that of BaP-derived radioactivity throughout the experiments and regardless of the type of exposure. The rank of the concentrations of PCB-derived radioactivity in tissues and bile was: bile ～ liver > brain > kidney ～ gill > skin ～ blood ～ muscle and for BaP-derived radioactivity the order was: bile > liver > gill > kidney > skin ～ blood > muscle > brain. BaP-derived radioactivity in liver and bile was present primary (85–99%) as metabolites, whereas PCB-derived radioactivity was present equally as parent compounds and metabolites in bile and primarily (98 %) as parent compounds in liver. Hydrolysis of bile from PCB/BaP-exposed sole with β-glucuronidase/arylsulfatase released 35 % of the BaP-derived radioactivity and 32 % of the PCB-derived radioactivity as primary metabolites. A much higher proportion of the BaP-derived radioactivity (64 %) than the PCB-derived radioactivity (13 %) in bile was unaffected by the enzyme treatment, indicating differences in the conjugation of the primary metabolites of PCBs and BaP. The results suggest that in contaminated environments the tissue to sediment concentration ratios for PCBs would exceed that for BaP and its metabolites; however, BaP would be continually absorbed and metabolized by sole to potentially carcinogenic and mutagenic compounds. In addition, the tissue levels of these toxic compounds may be increased by simultaneous exposure to PCBs.     

Relationship between visible and heritable chromosome damage in trout cells and embryos

The disruption of chromosome segregation which is detected visually by the anaphase aberration (aa) test suggests that unequal amounts of DNA are distributed to daughter cells and possibly to subsequent cell generations. To investigate this possibility trout cell cultures and trout embryos (blastodisc) were exposed to benzo[a]pyrene (B[a]P) and the nitrosamide, MNNG, respectively. They were then examined by flow cytometry to determine if anaphase damage resulted in unequal DNA distribution to daughter cells. Both B[a]P and MNNG produced a significant increase (P < 0·01) in aa in cultured cells after 48 h exposure. These values returned to normal by 10 days in the absence of the genotoxic agents, except for the highest concentration (0·5 μg/ml MNNG), which showed only a 50% recovery by that time. Likewise, the coefficient of variation (CV) of nuclear DNA content of the cells also rose significantly after treatment and remained elevated for as long as 14 days following exposure. Experiments with rainbow trout embryos also showed a significant increase in both aa and CV following exposure to MNNG. Flow cytometric analysis of DNA content of trout cells and embryos following exposure to mutagens showed an unequal distribution of DNA that was transmissible through several cell generations. These findings indicate that visible anaphase aberrations could predict heritable genetic defects such as those associated with aneuploidy.     

7-ethylresorufin O-deethylase activity and level of DNA-adducts in trout treated with benzo(a)pyrene

In fish, as well as in mammals, it is well known that the cytochrome P450-dependent oxidative metabolism of xenobiotics can generate DNA-reactive species. Moreover, this metabolism is known to be inducible by several compounds of environmental significance, such as polychlorobiphenyls, polycyclic aromatic hydrocarbons (PAHs) and dioxins. Consequently, we studied the relationship between the degree of induction of the cytochrome P4501A, expressed as that of 7-ethylresorufin O-deethylase (EROD) activity, and the level of DNA-adducts, using the post-labelling assay, in the liver of rainbow trout exposed to benzo(a)pyrene (a representative PAH). The results showed a significant 2- to 4-fold increase in EROD activity 2, 4 and 8 days after treatment, paralleled by an increase in DNA-adduct levels. This work further emphasizes the involvement of cytochrome P4501A in the metabolism of benzo(a)pyrene into genotoxic metabolites in rainbow trout.     

Glucuronidation in the polar bear (Ursus maritimus)

Polar bears bioaccumulate lipophilic pollutants, including polychlorinated biphenyls (PCBs), into their bodies from their exclusive diet of marine organisms. Hydroxylated PCB metabolites (OH-PCBs) have been found in plasma, presumably due to CYP-dependent biotransformation of PCBs in liver. Little is known about the phase 2 metabolism of hydroxylated xenobiotics in polar bears. The objective of this study was to examine UDP-glucuronosyltransferase (UGT) activity with OH-PCBs and a hydroxylated polycyclic aromatic hydrocarbon, 3-hydroxy-benzo(a)pyrene (3-OH-BaP), in polar bear liver. Samples of frozen polar bear liver were used to prepare microsomes. UGT activity with 3-OH-BaP in Brij-treated microsomes, measured by a fluorescence assay, was readily measurable with protein concentrations in assay tubes of up to 10 μg/ml, but dropped off very sharply at higher protein concentrations. The apparent K_m for 3-OH-BaP was 1.71 ± 0.04 μM, and V_max 1.26 ± 0.16 nmol/min/mg protein (mean ± SD, n=3). UGT activities with a model tetrachloro-OH-PCB (4^′-OH-CB72) and a model hexachloro-OH-PCB (4^′-OH-CB159) were assayed with [¹⁴-C]-UDPGA and separation of the [¹⁴-C]-glucuronide by ion-pair extraction and thin-layer chromatography. [¹⁴-C]-glucuronide conjugates were readily formed by polar bear liver microsomes in the absence of added substrate, apparently from contaminants present in liver. This phenomenon was not observed using hepatic microsomes from laboratory-held catfish. Glucuronidation efficiency was much higher with 4^′-OH-CB72 (K_m 7.3 μM; V_max 1.55 nmol/min/mg) than 4^′-OH-CB159 (K_m 16.1 μM; V_max 0.46 nmol/min/mg). The identities of the aglycones present in polar bear liver are not known, but could include OH-PCBs or hydroxylated metabolites of other persistent organic pollutants. This study demonstrates that UGT with high activity for 3-OH-BaP and other substrates is present in polar bear liver.     

Increased toxicity of benzo(a)pyrene-7,8-dihydrodiol in the presence of polychlorobiphenylols

Benzo(a)pyrene (BaP) and polychlorinated biphenyls (PCBs) often co-exist in contaminated environments. Polychlorobiphenylols (OH-PCBs), formed by CYP-dependent monooxygenation of PCBs, are potent inhibitors of the glucuronidation of hydroxylated BaP metabolites. We hypothesized that OH-PCBs could drive the biotransformation of (-)BaP-7,8-dihydrodiol (BaP-7, 8-D) away from detoxication and towards formation of the reactive metabolite. A mixture of five OH-PCBs with 4-6 Cl atoms was infused into isolated, perfused, biliary intact livers (n=3 fish) removed from 3-methylcholanthrene-induced channel catfish. Controls (n=3) were infused with vehicle. Subsequently, [3H]-BaP-7, 8-D was infused into each liver and bile was collected for 1 h. The livers were taken for analysis of metabolites and DNA adducts. Induction status was confirmed by EROD assay. Bile was analyzed for metabolites. It was found that preinfusion of the mixture of OH-PCBs reduced the extent of glucuronidation of BaP-7, 8-D and increased the formation of DNA adducts 5-fold over controls. GSH conjugates, tetrols and triols were increased in the OH-PCB-infused fish, providing further support for our hypothesis that if the glucuronidation were inhibited, CYP-dependent activation would increase. These studies suggest a mechanism for synergy of toxicity of PAH and PCBs.     

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.     

Effects of petroleum hydrocarbons on the hepatic cytochrome P450 1A1 system in rainbow trout

Effects on the hepatic cytochrome P450 1A1 system were investigated in juvenile rainbow trout i.p. injected with three different aromatic containing fractions: kerosene, light gas oil or heavy gas oil, originated from distilled North Sea crude oil. Kerosene treatment resulted in no effect on the P450 1A1 system, light gas oil injection caused a weak induction of EROD activities and heavy gas oil treatment resulted in a prominent induction of EROD activities as well as accumulation of CYP1A1 mRNA and P450 1A1 protein levels. The effects of heavy gas oil were compared with effects of β-napthoflavone (β-NF) on the P450 1A1 system. It was obvious that important discrepancies seemed to exist between EROD activities and corresponding CYP1A1 mRNA and P450 1A1 levels in rainbow trout treated with either heavy gas oil or β-NF i.e. heavy gas oil treatment resulted in higher specific EROD activities (EROD/P450 1A1) compared to β-NF. GC-MS analyses revealed that liver and bile from heavy gas oil treated rainbow trout in addition to naphthalene also contained polycyclic aromatic hydrocarbons such as phenanthrenes, anthracene, pyrenes, fluoranthene benz(a)anthracene and chrysene, while none of these compounds were detected in control trout.     

Estrogenicity of xenobiotics in rainbow trout (Oncorhynchus mykiss) using in vivo synthesis of vitellogenin as a biomarker

The estrogenicity of several xenobiotics was evaluated using in vivo vitellogenin (Vtg) synthesis in immature rainbow trout as a biomarker. 17β-estradiol, DES and ethinyl estradiol were tested as positive controls. The xenobiotic compounds tested were technical nonylphenol, bisphenol A, butylbenzylphthalate (BBP) and dibutylphthalate (DBF). Measurements of the Vtg concentration was performed with a direct sandwich ELISA. 17β-estradiol, DES and ethinyl estradiol caused up to 100 000-fold increases in the Vtg-levels. Nonylphenol and bisphenol A had the highest estrogenic potency of the xenobiotics increasing the vitellogenin level approximately 300-fold while BBP was only weakly estrogenic, increasing the concentration about 3 times. DPB did not raise the vitellogenin contration above the detection limit.     

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.     

Tissue slice technology for assessing alterations in fish hepatic phase I and phase II XME activity

Alterations to hepatic xenobiotic metabolizing enzymes (XMEs) is an important biomarker of contaminant exposure in aquatic toxicology. Measurement of XMEs in fish liver slices in vitro is an emerging tool for examining enzyme activity and response within the intact 3-D architecture of the liver tissue. We examined integrated phase I/phase II, and phase II metabolism of XMEs from liver slices in control and B[a]P-treated rainbow trout and channel catfish. Fluorescent assay substrates to measure rates of metabolism included 7-methoxycoumarin (7-MC), 7-ethoxycoumarin (7-EC) and 7-hydroxycoumarin (7-HC). Time-dependent increases in metabolism, and a lower rate of 7-MC metabolism compared with 7-EC metabolism, were observed at all time points for both fish species. In rainbow trout, B[a]P pretreatment caused a 10-fold increase in phase I metabolism of both 7-MC and 7-EC, and a 1.6-fold increase in phase II metabolism of 7-HC. Phase I activity in channel catfish was not notably altered by B[a]P pretreatment. However, B[a]P pretreatment in channel catfish caused a 48% decrease in phase II metabolism of 7-HC. These results indicate differences in baseline and B[a]P-altered XME profiles between rainbow trout and channel catfish.     

Ethoxyresorufin-O-deethylase activity and fixed wavelength fluorescence detection of PAHs metabolites in bile in turbot (Scophthalmus maximus L.) Exposed to a dispersed topped crude oil in a Continuous Flow System

Long term effects of sublethal concentrations of oil on the marine environment have become of general concern. Cytochrome P4501A activity (EROD) in liver and fixed wavelength fluorescence detection of PAHs metabolites (FF) have in this study been used as biomarkers for dispersed oil exposure on a long term period of juvenile turbot (Scophthalmus maximus L.). A Continuous Flow System was used to carry out the study. The fish were continuously exposed to 0.125, 0.5 or 2.0 mg litre⁻¹ dispersed topped crude oil for 6, 15, 24 h, 4 and 21 days followed by a 9 days recovery period in clean seawater. No induction of the cytochrome P4501A was measured. A maximum level in bile metabolites (4- to 5-fold) was recorded after 24 h of exposure revealing thereby a detoxification process, but a decline occurred from day 4 to day 21. This study demonstrated that FF detection of PAHs metabolites in bile could be a more sensitive biomarker than EROD activity in a long term exposure to sublethal concentration of oil.     

Simultaneous exposure of English sole (Parophrys vetulus) to sediment-associated xenobiotics: Part 2—chronic exposure to an urban estuarine sediment with added 3H-benzo[a]pyrene and 14C-polychlorinated biphenyls

• 1.1. The accumulation of aromatic hydrocarbons (AHs) and polychlorinated biphenyls (PCBs) kv English sole (Parophrys vetulus) exposed for up to 108 days to an urban (test) sediment was compared to that for English sole exposed to sediment from a reference area. The concentrations of identified AHs and PCBs in the test sediment were 32 μg/g dry weight and 2·2 μg/g dry weight, respectively. English sole exposed to test and reference sediments for 108 days had biliary concentrations of aromatic compounds fluorescing at BaP wavelengths of 0·6 μg/g, wet weight and hepatic concentrations of PCBs of 1·4 ± 0·6 μg/g wet weight which were ten and eight times, respectively, as great as those in reference sole. These results show that accumulation of AHs and PCBs from sediment by English sole is a significant route of uptake in contaminated environments.
• 2.2. ³H-benzo(a)pyrene (BaP) and ¹⁴C-PCBs were added to the test sediment to compare the uptake and metabolism of BaP to that of PCBs by sole. Steady-state concentrations of ³H-BaP and ¹⁴C-PCBs in tissues and fluids were reached by 4 days and 14 days, respectively. At steady state, the level of covalent binding of ³H-BaP to hepatic proteins in test sole was six times greater than that of ¹⁴C-PCBs, and there was significantly greater relative formation of BaP-glutathione (GSH) conjugates than PCB-GSH conjugates. Thus, the amount of BaP metabolized to reactive metabolites was greater than that for PCBs, even though the concentration of ¹⁴C-PCBs in liver of test sole was five times as great as that of ³H-BaP.
• 3.3. Trace amounts of ³H-BaP were also added to the reference sediment to determine how simultaneous exposure of English sole to those contaminants already present in the test sediment affected the metabolism and disposition of BaP. The ³H-BaP concentration ratios for liver to sediment and bile to sediment, as well as proportions of biliary BaP-GSH conjugates in test sole, were significantly greater than in reference sole. Thus, the formation and accumulation of potentially toxic metabolites of a carcinogenic AH (BaP) in sole liver were increased by simultaneous exposure to contaminants present in an urban sediment.