Induction of choline kinase by polycyclic aromatic hydrocarbon carcinogens in rat liver

The administration to rats of polycyclic aromatic hydrocarbons such as 3-methylcholanthrene, 3,4-benzo(a) pyrene and β-naphthoflavone caused a significant elevation of hepatic choline kinase activity. On the other hand, phenobarbital-type inducers (phenobarbital, 1,1,1-trichloro 2,2-bis (ρ-chlorophenyl) ethane (DDT) and hexachlorobenzene) did not stimulate the activity at all. The administration of either cycloheximide or actinomycin D completely depressed the elevation of choline kinase activity induced by polycyclic aromatic hydrocarbons, indicating that the elevated activity by these chemicals could be due to the change in the enzyme level. These results strongly suggest that induction of choline kinase are involved in the sequence of events leading to the induction of hepatic drug metabolism by polycyclic aromatic hydrocarbons.     

Potency of various polycyclic aromatic hydrocarbons as inducers of CYP1A1 in rat hepatocyte cultures

A number of highly toxic environmental pollutants including certain polychlorinated dibenzo-p-dioxins (PCDD), polychlorinated dibenzofurans (PCDF), and 'dioxin-like' polychlorinated biphenyls (PCB) are among the most potent agonists of the aryl hydrocarbon receptor (AHR). Induction of cytochrome P4501A1 (CYP1A1) in mammalian cell culture is widely used as a functional parameter for AHR activation providing an estimate for 'dioxin-like' inducing equivalents in extracts from environmental samples. Since a number of polycyclic aromatic hydrocarbons (PAHs) also act as AHR-agonists, the CYP1A1-inducing potencies, measured as induction of 7-ethoxyresorufin O-deethylase (EROD) activity in rat hepatocyte cultures were analyzed for 16 PAHs frequently present in environmental samples. Among these, seven PAHs including benzo[a]pyrene were relatively potent inducers allowing the determination of Induction Equivalency Factors (IEF). For three PAHs including benzo[k]fluoranthene which acted as weak inducers, IEFs were estimated, while six PAHs including acenaphthylene were classified as inactive. Based on different efficacies the concentration-response characteristics of CYP1A1 induction were analyzed in more detail for benzo[a]pyrene, benzo[k]fluoranthene, and acenaphthylene. Benzo[k]fluoranthene was markedly less effective than benzo[a]pyrene as inducer of EROD activity but even more effective than benzo[a]pyrene as inducer of CYP1A1 protein and mRNA. Acenaphthylene was highly more effective on the level of mRNA than on the levels of protein or EROD activity. Further analysis revealed that the low efficacy of acenaphthylene as inducer of CYP1A1 protein and EROD activity is due to its marked cytotoxicity while no clear-cut explanation was found for the differences in efficacy between benzo[k]fluoranthene and benzo[a]pyrene. The EROD-inducing potency of a mixture of 16 PAH was about 2-fold higher than that calculated on the basis of IEFs of the individual constituents of the mixture.     

Effects of various inducers on diethylstilbestrol metabolism, drug-metabolizing enzyme activities and the aromatic hydrocarbon (Ah) receptor in male Syrian golden hamster liver

In order to elucidate the role of metabolic activation of the synthetic estrogen, diethylstilbestrol (DES), in the mechanism of liver tumor formation in male Syrian golden hamsters observed after combined treatment with DES and 7,8-benzoflavone (7,8-BF), the metabolism of DES and the concentrations and activities of various drug-metabolizing enzymes were studied in hamster liver microsomes after various pretreatments. The levels of the hepatic aromatic hydrocarbon (Ah) receptor were also determined. Pretreatment with 7,8-BF increased both P450 and cytochrome b5 levels, whereas phenobarbital (PB) and 3-methylcholanthrene (MC) induced P450 but not cytochrome b5. 7,8-BF pretreatment increased 7-ethoxyresorufin-O-deethylase (EROD) 3-fold and 7-pentoxyresorufin-O-dealkylase (PROD) 2.5-fold, whereas aromatic hydrocarbon hydroxylase (AHH) and 7-ethoxycoumarin-O-deethylase (ECOD) activities were only slightly induced by 7,8-BF. MC pretreatment increased EROD 8-fold and PROD activity 7-fold, whereas PB pretreatment enhanced AHH 4.5-fold and PROD activity 4-fold. In contrast to PB, pretreatment with 7,8-BF and MC reduced the oxidative metabolism of DES in hepatic microsomes, but the pattern of metabolites was identical with that in untreated controls. Treatment of hamsters with the inducers changed the hepatic Ah receptor level. PB and MC-pretreatment resulted in an increase of the receptor level 1.5-fold and 1.3-fold, respectively, whereas 7,8-BF-pretreatment leads to a 1.5-fold decrease. The dissociation constant Kd is 170 nM for the reaction of 7,8-BF with the hamster Ah receptor compared to 70 nM for 5,6-BF and 38 nM for 2,3,7,8-tetrachlorodibenzofuran (TCDF). The Kd-value is 3.6 nM for TCDF with the rat receptor protein. It is concluded from these data that metabolic activation of DES is not involved in the mechanism of hepatocarcinogenesis in this animal tumor model.     

Molecular characterization of polycyclic aromatic hydrocarbon (PAH)-degrading methanogenic communities

Previous research demonstrated that methanogenic cultures enriched from Baltimore Harbor (Baltimore, MD) sediments were able to degrade naphthalene and phenanthrene. In this report, the degradation activity was maintained through a sequential transfer without adding additional sediments and the established polycyclic aromatic hydrocarbon (PAH)-degrading methanogenic communities were characterized via comparative sequence analysis of clone libraries of 16S rRNA genes amplified using bacteria-specific and Archaea-specific primers. The phylogenetic analysis indicated that the addition of PAHs clearly shifted the structure of the methanogenic community and resulted in an increase in populations of species previously found in other hydrocarbon-degrading communities. Of particular interest is the fact that the dominant microbial population of the naphthalene cultures was different from that of the phenanthrene cultures, suggesting that different species are involved in the degradation. Finally, this information may lead to the identification and isolation of methanogenic populations that can degrade PAHs.     

Degradation of polycyclic aromatic hydrocarbon compounds under various redox conditions in soil-water systems

This study evaluated the microbial degradation of naphthol, naphthalene, and acenaphthene, under aerobic, anaerobic, and denitrification conditions in soil-water systems. Chemical degradation of naphthol and naphthalene in the presence of a manganese oxide was also studied. Naphthol, naphthalene, and acenaphthene were degraded microbially under aerobic conditions from initial aqueous-phase concentrations of 9, 7, and 1 mg/liter to nondetectable levels in 3, 10, and 10 days, respectively. Under anaerobic conditions naphthol degraded to nondetectable levels in 15 days, whereas naphthalene and acenaphthene showed no significant degradation over periods of 50 and 70 days, respectively. Under denitrification conditions naphthol, naphthalene, and acenaphthene were degraded from initial aqueous-phase concentrations of 8, 7, and 0.4 mg/liter to nondetectable levels in 16, 45, and 40 days, respectively. Acclimation periods of approximately 2 days under aerobic conditions and 2 weeks under denitrification conditions were observed for both naphthalene and acenaphthene. Abiotic degradation of naphthalen and naphthol were evaluated by reaction with manganese oxide, a minor soil constituent. In the presence of a manganese oxide, naphthalene showed no abiotic degradation over a period of 9 weeks, whereas the aqueous naphthol concentration decreased from 9 mg/liter to nondetectable levels in 9 days. The results of this study show that low-molecular-weight, unsubstituted, polycyclic aromatic hydrocarbons are amenable to microbial degradation in soil-water systems under denitrification conditions.     

Heterocyclic polycyclic aromatic hydrocarbon carcinogenesis: 7H-dibenzo[c,g]carbazole metabolism by microsomal enzymes from mouse and rat liver

The metabolism of dibenzo[c,g]carbazole (DBC), was studied in vitro using microsomal fractions of mouse and rat liver from animals, which were treated with 3-methylcholanthrene (MC). The separation of extractable metabolites by high pressure liquid chromatography (HPLC) and thinlayer chromatography (TLC) as well as identification of most of them by nuclear magnetic resonance, mass spectrometry and comparison with synthetically obtained products are described. The microsomes of both species produced the same twelve compounds of which the following have been identified: five monohydroxylated derivatives (phenols), the product of further oxidation of one of them, and a dihydrodiol. The 5-OH-DBC (60% including its spontaneously-formed dimer) and the 3-OH-DBC (14%) are the main metabolites. Three minor metabolites cochromatographed with synthetically prepared 2-OH-DBC, 4-OH-DBC and 6-OH-DBC. The dihydrodiol detectable in small quantity (4–6%) was tentatively identified as 3,4-dihydroxy-3,4-dihydro-DBC by the sensitivity of its formation to very low concentrations of the inhibitor of microsomal epoxide hydrolase, 1,1,1-trichloropropene oxide, by its molecular ion and major fragment in mass spectrometry and by its dehydration product 3-OH-DBC. No other dihydrodiols were detected. The qualitative and quantitative effects of various modulators of metabolism (enzyme inhibitors, apparently homogeneous epoxide hydrolase, glutathione, supernatant fraction) were investigated. The results are discussed with respect to possible ultimate carcinogens.     

Effect of progesterone on rat plasma and liver lipid levels (author's transl)

The effect of progesterone upon several lipidic parameters on rat liver and plasma was studied. Progesterone administration led to a significant increase in the hepatic triacylglyceride and cholesterol esterified levels and to a decrease in the phospholipid content. After progesterone treatment decreases in plasma total lipids, phospholipids, cholesterol and cholesterol esterified were observed, whereas plasma triacylglyceride and free fatty acid levels increased. The hormonal treatment altered the lipoprotein pattern, which significantly reduced the beta-lipoprotein fraction.     

Degradation of polycyclic aromatic hydrocarbon compounds under various redox conditions in soil-water systems.

This study evaluated the microbial degradation of naphthol, naphthalene, and acenaphthene, under aerobic, anaerobic, and denitrification conditions in soil-water systems. Chemical degradation of naphthol and naphthalene in the presence of a manganese oxide was also studied. Naphthol, naphthalene, and acenaphthene were degraded microbially under aerobic conditions from initial aqueous-phase concentrations of 9, 7, and 1 mg/liter to nondetectable levels in 3, 10, and 10 days, respectively. Under anaerobic conditions naphthol degraded to nondetectable levels in 15 days, whereas naphthalene and acenaphthene showed no significant degradation over periods of 50 and 70 days, respectively. Under denitrification conditions naphthol, naphthalene, and acenaphthene were degraded from initial aqueous-phase concentrations of 8, 7, and 0.4 mg/liter to nondetectable levels in 16, 45, and 40 days, respectively. Acclimation periods of approximately 2 days under aerobic conditions and 2 weeks under denitrification conditions were observed for both naphthalene and acenaphthene. Abiotic degradation of naphthalen and naphthol were evaluated by reaction with manganese oxide, a minor soil constituent. In the presence of a manganese oxide, naphthalene showed no abiotic degradation over a period of 9 weeks, whereas the aqueous naphthol concentration decreased from 9 mg/liter to nondetectable levels in 9 days. The results of this study show that low-molecular-weight, unsubstituted, polycyclic aromatic hydrocarbons are amenable to microbial degradation in soil-water systems under denitrification conditions.     

Binding of polycyclic aromatic hydrocarbons (PAHs) to teleost aryl hydrocarbon receptors (AHRs)

Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous, environmental contaminants that pose a potential risk to fish populations. Both field and laboratory studies suggest that exposure of the early life stages of fish to PAH can mimic the embryotoxic effects of the planar halogenated hydrocarbons (PHHs), the most potent of which is 2,3,7,8-tetrachlorodibenzo-p-dioxin. PHH toxicity is mediated by the aryl hydrocarbon receptor (AHR) and PHH potency is predicted by its AHR-binding affinity and CYP1A induction potency. However, the role of the AHR, if any, in mediating the developmental effects of PAH to fish remains unknown. In this study we looked at the AHR binding affinity of a test set of PAH that had been previously ranked for their potency for inducing teleost CYP1A. PAH that induced CYP1A inhibited [3H]TCDD binding to in vitro-expressed AHRs from rainbow trout and the AHR expressed in PLHC-1 fish hepatoma cells. Generally, the relative rank order for AHR binding affinity predicted the rank order of these same PAH for inducing CYP1A reported in other studies. There was a strong, positive relationship between binding to the PLHC-1 AHR (stimulus) and the EC50s for CYP1A induction (response) in whole juvenile trout and in RTL-W1 cells, but EC50s were much higher than expected for a 1:1 stimulus/response relationship. These data show that the ability of PAH to bind to teleost AHR predicts PAH potency for CYP1A induction. If PAH toxicity is receptor-mediated and predicted by induction potencies, we will have a powerful mechanistic-based tool for rapidly assessing the risk of toxicity to fish of PAH from any source.     

Transfer of glucose from UDP-glucose in microsomal membranes of rat hepatocytes (author's transl)]

Microsomal preparations from rat liver mediate transfer of glucosyl units from UDP-glucose to three different kinds of acceptors: an endogenous glycoprotein, exogenous glycogen and collagen. Both glucosyl transferases work at acidic pH, 6.5 for transfer on endogeneous acceptor and glycogen and at pH 5.5 for transfer on collagen. None of these enzymes require divalent cations for activity. While transfers on endogenous acceptor and glycogen are inhibited by the presence of a non-ionic detergent, Triton X-100, the transfer on collagen is activated by the same detergent. Glycogen-synthase activity requires glucose 6-phosphate at an optimal concentration of 1 mM. The Km values for UDP-glucose are respectively: 0.5 mM, 0.33 mM, and 1 mM for transfer on endogenous acceptor, glycogen and collagen. Characterisation of the product indicates that a protein-bound alpha1-4 glucan is formed when no primer is added. Enzymatic and acidic hydrolyses of radioactive glycogen and collagen show only glucose as a radioactive sugar identified by thin layer chromatography on cellulose. Pre-treatment of microsomal membranes by alpha-amylase demonstrates that glucosyltransferases are not adsorbed on endogenous glycogen and seem to be really membranous enzymes.