Polychlorinated biphenyl isomers and congeners as inducers of both 3-methylcholanthrene- and phenobarbitone-type microsomal enzyme activity

Highly purified synthetic polychlorinated biphenyls substituted in the meta and para positions of both phenyl rings and at one ortho position were administered to male Wistar rats and the effects of these compounds on the microsomal drug-metabolising enzymes were evaluated. The in vivo effects of these compounds were determined by measuring the microsomal benzo[a]pyrene hydroxylase, dimethylaminoantipyrine N-demethylase and NADPH-cytochrome c reductase enzyme activities, the cytochrome b5 content and the relative peak intensities and spectral shifts of the reduced microsomal cytochrome P-450 : CO and ethylisocyanide binding difference spectra. The results were compared to the effects of administering phenobarbitone (PB), 3-methylcholanthrene (MC), 2,2',4,4'-tetrachlorobiphenyl (TCBP-II) (a PB-type inducer), 3,3',4,4'-tetrachlorobiphenyl (TCBP-I) (an MC-type inducer), PB plus MC (coadministered) and TCBP-II + TCBP-I (coadministered) to the test animals. At dosage levels of 30 and 150 mumol . kg-1, pretreatment with 2,3,3',4,4'-pentachlorobiphenyl (PCBP-II), 2,3',4,4',5-pentachlorobiphenyl (PCBP-I), 2,3,3',4,4',5-hexachlorobiphenyl (HCBP-II) and 2,3,3',4,4',5-hexachlorobiphenyl (HCBP-III) gave hepatic microsomes with enzymic and spectral properties consistent with a mixed pattern of induction. These polychlorinated biphenyl (PCB) isomers and congeners have been identified as either major or minor components of the commercial PCB mixtures and must contribute to their activity as MC-type inducers. The only PCB isomer in this series which was not a mixed type inducer was 2,3',4,4',5,5'-hexachlorobiphenyl (HCBP-I) which appeared to be a PB-type inducer. This contrasted to the mixed-type activity observed for 2,3',4,4',5,5'-hexabromobiphenyl which was isolated from a commercial polybrominated biphenyl (PBB) mixture.     

Polychlorinated biphenyls as inducers of hepatic microsomal enzymes: effects of di-ortho substitution

All of the 13 possible polychlorinated biphenyl (PCB) isomers and congeners substituted at both para positions, at least two meta positions (but not necessarily on the same ring) and at two ortho positions have been synthesized and tested as rat hepatic microsomal enzyme inducers. The effects of these compounds were evaluated by measuring microsomal benzo-[a]pyrene (B[a]P) hydroxylase, 4-chlorobiphenyl (4-CBP) hydroxylase, 4-dimethylaminoantipyrine (DMAP) N-demethylase and NADPH-cytochrome c reductase activities, the cytochrome b5 content and the relative peak intensities and spectral shifts of the carbon monoxide(CO)- and ethylisocyanide(EIC)-difference spectra of ferrocytochrome P-450. The results were compared to the effects of administering phenobarbitone (PB), 3-methylcholanthrene (MC) and PB plus MC (coadministered). At dose levels of 150 mumol . kg-1, all of the PCB congeners, except 2,3',4,4',5',6-hexachlorobiphenyl, significantly enhanced hepatic microsomal cytochrome P-450 content, B[a] P hydroxylase and/or DMAP N-demethylase activities compared to the control (corn oil-treated) animals. Only 5 of these compounds, namely 2,3,4,4',5,6-hexa-, 2,2',3,3',4,4'-hexa-, 2,2',3',4,4',5-hexa-, 2,3,3',4,4',6-hexa-and 2,2',3,3',4,4',5-heptachlorobiphenyl, enhanced microsomal B[a]P hydroxylase, 4-CBP hydroxylase, NADPH-cytochrome c reductase and DMAP N-demethylase activities in a manner consistent with a mixed pattern of induction. The results suggest that PCB isomers and congeners substituted at both para positions, at least two meta positions, at two ortho positions and containing a 2,3-4-trichloro substitution pattern on one ring are mixed-type inducers; in addition the effects of 2,3,4,4',5,6-hexachlorobiphenyl were also consistent with a mixed pattern of induction.     

Retinoid metabolism (LRAT,REH) in the yolk-sac membrane of Japanese quail eggs and effects of mono-ortho-PCBs

Retinoids stored in the avian egg are essential for normal development, however, laboratory and field experiments suggest that they are affected by environmental contaminants. Lecithin:retinol acyltransferase (LRAT) activity was detected in the microsomal fraction of the yolk-sac membrane of the Japanese quail at day 6 of development. LRAT activity was maximal at pH 7.0 having apparent kinetic parameters of K(m)=1.35 microM and V(max)=0.21 nmol/mg protein/h and was inhibited by the sulfhydryl modifying agent N-ethyl-maleimide. Retinol ester hydrolase (REH) activity in the microsomal fraction of the yolk-sac membrane was stimulated by the bile salt analogue 3-[(3-cholamidopropyl) dimethyl-ammonio]-1-propane sulfonate and was maximal at pH 9.0 with apparent K(m)=77 microM and V(max)=34.3 nmol/mg protein/h. Injection of the PCB congener 2,3,3',4,4'-pentachlorobiphenyl increased both REH and LRAT activities, whereas 2,3,3',4-tetrachlorobiphenyl stimulated LRAT. Yolk retinol concentration and the molar ratio retinol:retinyl palmitate were lower in the exposed eggs. Yolk retinol concentration decreased as LRAT increased (R(2)=0.89) suggesting that certain PCB congeners may affect vitamin A mobilization in ovo by increasing LRAT activity in the yolk-sac membrane.     

Fungal bioconversion of toxic polychlorinated biphenyls by white-rot fungus, Phlebia brevispora

Toxic coplanar polychlorinated biphenyls (Co-PCBs) were used as substrates for a degradation experiment with white-rot fungus, Phlebia brevispora TMIC33929, which is capable of degrading polychlorinated dibenzo-p-dioxins. Eleven PCB congener mixtures (7 mono-ortho- and 4 non-ortho-PCBs) were added to the cultures of P. brevispora and monitored by high resolution gas chromatography and mass spectrometry (HRGC/HRMS). Five PCB congeners, 3,3′,4,4′-tetrachlorobiphenyl, 2,3,3′,4,4′-pentachlorobiphenyl, 2,3′,4,4′,5-pentachlorobiphenyl, 3,3′,4,4′,5-pentachlorobiphenyl, and 2,3′,4,4′,5,5′-hexachlorobiphenyl were degraded by P. brevispora. To investigate the fungal metabolism of PCB, each Co-PCB was treated separately by P. brevispora and the metabolites were analyzed by gas chromatography and mass spectrometry (GC/MS) and identified on the basis of the GC/MS comparison with the authentic compound. Meta-methoxylated metabolite was detected from the culture containing each compound. Additionally, para-dechlorinated and -methoxylated metabolite was also detected from the culture with 2,3,3′,4,4′-pentachlorobiphenyl, 2,3′,4,4′,5-pentachlorobiphenyl, and 2,3′,4,4′,5,5′-hexachlorobiphenyl, which are mono-ortho-PCBs. In this paper, we identified the congener specific degradation of coplanar PCBs by P. brevispora, and clearly proved for the first time by identifying the metabolites that the white-rot fungus, P. brevispora, transformed recalcitrant coplanar PCBs.     

Reconstituted human breast milk PCBs as potent inducers of aryl hydrocarbon hydroxylase

The major polychlorinated biphenyl (PCB) components identified in human breast milk have been synthesized and a reconstituted breast milk PCB mixture representing the average levels determined in the Osaka Prefecture in Japan has been prepared. The dose effecting the half-maximal (ED₅₀) induction of rat hepatic microsomal aryl hydrocarbon hydroxylase (AHH) for the reconstituted breast milk PCBs (ED₅₀ ～12 μmol·kg^?1) was approximately seven times less than the ED₅₀ for the commercial PCB mixture, Kanechlor 500. The increased biological potency of the former mixture reflects the preferential bioconcentration of the toxic PCB congeners, 2,3,3′,4,4′-penta-, 2,3′,4,4′,5-penta- and 2,3,3′,4,4′,5-hexachlorobiphenyl.     

Effect of PCBs on androgen production by suspension of adult rat Leydig cells in vitro

The effects of PCBs (mixture of 2, 3, 4, 5-tetra; 2, 2′, 4, 5, 5′-penta; 2, 2′, 3, 3′, 6, 6′-hexa and 2, 2′, 3, 3′, 4, 4′, 5, 5′-octa congeners) on androgen production were investigated by suspension of Leydig cells from adult rat testis. hCG-stimulated androgen production was significantly inhibited by PCBs while progesterone level was not affected. Progesterone supported testosterone production was also decreased by PCBs, while conversion of androstenedione to testosterone was unchanged. These results suggest that the activity of microsomal enzyme C21 side-chain cleveage P450 was decreased by PCB treatment of Leydig cells in vitro.     

Degradation of Polychlorinated Biphenyls by UV-Catalyzed Photolysis

Photolysis of five polychlorinated biphenyl (PCB) congeners [2,4,4′-trichlorobiphenyl (PCB 28), 2,2′,5,′5-tetrachlorobiphenyl (PCB 52), 2,2′,4,5,5′-pentachlorobiphenyl (PCB 101), 2,2′,4,4′,5,′5-hexachlorobiphenyl (PCB 153) and 2,2′,3,4,4′,5,′5-heptachlorobiphenyl (PCB 180)] individually and in combination were carried out in the solvents methanol, ethanol, and 2-propanol. The disappearance of parent congener generally increased with UV intensity. The solvents had significant or limited effect on the removal of PCBs depending on the congener used. Because 2-propanol was highly toxic and methoxylated products were formed when methanol was used, ethanol was selected as the optimum solvent. The results of photolysis of the PCB mixture showed that PCB 52 was formed and accumulated after 4 h of photolysis. The addition of sodium hydroxide increased the rate of photolysis of the PCB mixture. One hundred percent removal can be obtained of the PCB in mixture in 90 min under optimized conditions. Gas chromatography–mass spectrometry was used to determine the intermediates of the photolysis of PCBs under optimized conditions. For the PCB congeners and mixture studied, the major photolytic intermediates were less chlorinated congeners, and biphenyl was the major product with minor amounts of hydroxylated PCBs, ethylated, dimethylated, and methylated biphenyls. Biphenyl could be further degraded by a prolonged photolysis. Toxicity of the PCB mixture during photolysis was monitored by the Microtox^® test. It was found that the toxicity increased at the early stage of photolysis, and gradually decreased as the reaction proceeded. After 90 min, the EC₅₀ of the reaction mixture was similar to that of the untreated sample.     

3,5,3′,5′-Tetrachlorobiphenyl is a weak oestrogen agonist in vitro and in vivo

Polychlorinated biphenyls (PCBs) are widespread, persistent environmental contaminants of which some congeners can act as endocrine disrupters. Previous work has shown that 3,4,3′,4′-tetrachlorobiphenyl (PCB77) can act as an oestrogen with actions mediated through the oestrogen receptor. Here, oestrogenic actions have been assessed for two further tetrachlorobiphenyl isomers. Assays of oestrogenic action have involved (1) ligand regulation of oestrogen-sensitive gene expression; (2) ligand regulation of cell growth in oestrogen-dependent human breast cancer cell lines MCF7 McGrath and ZR-75-1; and (3) ligand activity in the immature mouse uterine weight bioassay in vivo. These results demonstrate that 3,5,3′,5′-tetrachlorobiphenyl (PCB 80) can be considered to be a weak oestrogen agonist, but the 2,5,2′,5′-congener (PCB 52) revealed no oestrogenic properties in any of these assays. Implications of these results are discussed in relation to structure-activity predictions for environmental oestogens.     

Activation of [C]chlorobiphenyls to protein-binding metabolites by rat liver microsomes

The irreversible binding of [¹⁴C]2,2′-di- and [¹⁴C]2,4,5,2′,4′,5′-hexachlorobiphenyl ([¹⁴C]DCB and [¹⁴C]HCB) to protein was studied in the presence of rat liver microsomes and a NADPH-generating system. Protein-bound radioactivity was found with [¹⁴C]DCB but not with [¹⁴C]HCB. The binding of ¹⁴C-metabolites was increased by pretreatment of the rats with phenobarbital or polychlorinated biphenyls. Protein binding was linear for 80 min. In contrast, monohydroxy-metabolites of DCB were formed and degraded within 40 min. Inhibition of secondary oxidation of DCB by scavening superoxide anions or by glucuronidation of the monophenols markedly decreased the protein binding. Addition of trichloropropene oxide or styrene oxide, both inhibitors of epoxide hydrase, did not significantly stimulate the binding. The results suggest that the majority of reactive metabolites of DCB arise from secondary metabolism, i.e., the subsequent oxidation of the phenolic metabolites. Arene oxides, the primary products, appear to play a minor role in the protein binding of DCB.     

3,3',4,4',5-Pentachlorobiphenyl (PCB 126) impacts hepatic lipid peroxidation, membrane fluidity and beta-adrenoceptor kinetics in chick embryos

Polychlorinated biphenyls (PCB) and other aryl hydrocarbon receptor (AHR) agonists induce oxidative stress and alter membrane lipid peroxidation and fluidity. This study tested the hypothesis that PCB-induced changes in membrane properties impact membrane beta-adrenoceptor (beta-AR) affinity and capacity in chick embryo hepatocytes. Embryos were injected into the air cell with 1.6 microg 3,3',4,4',5-pentachlorobiphenyl (PCB 126)/kg egg at day 0, and incubated to day 19 when livers were removed. This dose resulted in hepatic PCB 126 levels of 0.67 ng/g liver or 10.2 ng/g liver lipid; levels in untreated embryos were non-detectable. Hepatic microsomal EROD activity was elevated by approximately 12-fold and embryo mortality was significantly increased compared with the untreated group. Hepatic lipid peroxidation increased and membrane order (steady-state fluorescence anisotropy values) decreased with in ovo PCB 126 exposure. Consistent with changes in membrane structure, hepatic beta-AR affinity for CGP 12177 significantly decreased (Kd increased) without changes in receptor numbers. This study demonstrates that in ovo exposure to PCB 126 in chick eggs significantly impacted embryo survival, and this was correlated with altered hepatic membrane structure and ultimately membrane function.     

Microbial Reductive Dechlorination of Weathered and Exogenous Co-planar Polychlorinated Biphenyls (PCBs) in an Anaerobic Sediment of Venice Lagoon

The occurrence of reductive dechlorination processes towards pre-existing PCBs and five exogenous coplanar PCBs were investigated in a contaminated sediment of Porto Marghera (Venice Lagoon, Italy) suspended, under strictly anaerobic conditions, in water collected from the same site. PCB dechlorination started after five months of incubation, when sulfate initially occurring in the microcosms was completely depleted and methanogenesis was in progress. It was ascribed to sulfate-reducing bacteria. Several pre-existing hexa-, penta- and tetra-chlorinated biphenyls were slowly bioconverted into tri- and di-, ortho-substituted PCBs from the 5th to the 16th month of experiment. Spiked coplanar PCBs, i.e., 3,3′,4,4′-tetrachlorobiphenyl, 3,3′,4,4′,5- and 2,3′,4,4′,5-pentachlorobiphenyls, 3,3′,4,4′,5,5′- and 2,3,3′,4,4′,5-hexachlorobiphenyls, were extensively transformed (by about 90%) into lower chlorinated congeners, such as 3,3′,5,5′-/2,3′,4,4′-tetrachlorobiphenyl, 3,3′,5-, 2,4,4′-, 2,3′,4- and 2,3′,5-trichlorobiphenyl, 3,4-/3,4′- and 3,3′-dichlorobiphenyl and 2-chlorobiphenyl. The reductive dechlorination of spiked PCBs did not influence significantly the biotransformation rate and extent of pre-existing PCBs.     

Accumulation of polychlorinated biphenyls in adipocytes: selective targeting to lipid droplets and role of caveolin-1

Background

Polychlorinated biphenyls (PCBs) are persistent environmental pollutants that preferentially accumulate in lipid-rich tissues of contaminated organisms. Although the adipose tissue constitutes a major intern reservoir of PCBs and recent epidemiological studies associate PCBs to the development of obesity and its related disorders, little is known about the mechanisms involved in their uptake by the adipose tissue and their intracellular localization in fat cells.

Methodology/Principal Findings

We have examined the intracellular distribution of PCBs in mouse cultured adipocytes and tested the potential involvement of caveolin-1, an abundant adipocyte membrane protein, in the uptake of these compounds by fat cells. We show that 2,4,4′-trichlorobiphenyl (PCB-28), 2,3′,4,4′,5-pentachlorobiphenyl (PCB-118) and 2,2′,4,4′,5,5′-hexachlorobiphenyl (PCB-153) congeners rapidly and extensively accumulate in 3T3-L1 or mouse embryonic fibroblast (MEF) derived cultured adipocytes. The dynamics of accumulation differed between the 3 congeners tested. By subcellular fractionation of primary adipocytes, we demonstrate that these pollutants were almost exclusively recovered within the lipid droplet fraction and practically not associated to cell membranes. The absence of caveolin-1 expression in primary adipocytes from cav-1 deficient mice did not modify lipid droplet selective targeting of PCBs. In cav-1 KO MEF differentiated adipocytes, PCB accumulation was decreased, which correlated with reduced cell triglyceride content. Conversely, adenoviral mediated cav-1 overexpressing in 3T3-L1 cells, which had no impact on total cell lipid content, did not change PCB accumulation.

Conclusion/Significance

Our data indicate that caveolin-1 per se is not required for selective PCB accumulation, but rather point out a primary dependence on adipocyte triglyceride content. If the crucial role of lipid droplets in energy homeostasis is considered, the almost exclusive accumulation of PCBs in these organelles warrants future attention as the impairment of their function could be linked to the worldwide obesity epidemic.     

Genotoxic effects of PCB 52 and PCB 77 on cultured human peripheral lymphocytes

Polychlorinated biphenyls (PCBs) are known to be carcinogenic, but the mechanisms of this action are uncertain. Most, but not all, studies have concluded that PCBs are not directly mutagenic, and that much if not all of the carcinogenic activity resides in the fraction of the PCB mixture that contains congeners with dioxin-like activity. The present study was designed to determine genotoxic effects of an ortho-substituted, non-coplanar congener, 2,2′,5,5′-tetrachlorobiphenyl (PCB 52), and a non-ortho-substituted coplanar congener with dioxin-like activity, 3,3′,4,4′-tetrachlorobiphenyl (PCB 77) on cultured human peripheral lymphocytes. DNA damage was assessed by use of the comet assay (alkaline single-cell gel electrophoresis). After cell cultures were prepared, test groups were treated with different concentrations of PCB 52 (0.2 and 1 μM) and PCB 77 (1 and 10 μM) for 1 h at 37 °C in a humidified carbon dioxide incubator, and compared to a DMSO vehicle control group. The cells were visually classified into four categories on the basis of extent of migration such as undamaged (UD), low damage (LD), moderate damage (MD) and high damage (HD). The highest concentration of PCBs 52 and 77 significantly increased DNA breakage in human lymphocytes (p < 0.001). Our results indicate that both the non-coplanar PCB 52 and coplanar PCB 77 cause DNA damage, and that the ortho-substituted congener was significantly more potent than the dioxin-like coplanar congener.     

In vivo binding of 2,3,6,2′,3′,6′-hexachlorobiphenyl and 2,4,5,2′,4′,5′-hexachlorobiphenyl to mouse liver macromolecules

The role of metabolic activation in the binding of polychlorinated biphenyls (PCBs) to cellular macromolecules was investigated in vivo by comparing the relative binding of 2,4,5,2′,4′,5′-[U-¹⁴C]hexachlorobiphenyl (2,4,5), a slowly metabolized PCB, with that of 2,3,6,2′,3′,6′-[U-¹⁴C]hexachlorobiphenyl (2,3,6), a rapidly metabolized PCB, and the appropriate controls. Each hexachlorobiphenyl was administered to mice, orally for 5 days (7.28 mg/kg/day). Following the dosing schedule, animals were killed at 1, 5 and 8 days. The concentration of each PCB was determined in liver, muscle and kidney and in purified macromolecules isolated from those tissues. The concentration of 2,4,5 was consistently higher than the concentration of 2,3,6 in all tissues studied. However, the amount of 2,3,6 bound to the purified macromolecules was consistently at least one order of magnitude greater than that of 2,4,5. The greatest binding was observed in RNA followed by protein and DNA, respectively. The purity of the macromolecules and the presence of PCB-derived radioactivity at the monomer level were confirmed. This is the first report of ¹⁴C-labeled PCB being bound to purified RNA, DNA, and proteins isolated from the tissues of animals treated in vivo. The binding is thought to be covalent and to be the result of metabolic activation.     

Induction of porphyrin synthesis in chick embryo liver cell culture by synthetic polychlorobiphenyl isomers

The effects of a series of synthetic di-tetra- and hexachlorobiphenyl isomers and commercial polychlorinated biphenyls on the porphyrin biosynthesis in chick embryo liver cells in culture were examined.It was found that 3,4,3′,4′-tetra- and 3,4,5,3′,4′,5′-hexachlorobiphenyl isomers were the most active inducers, which were approximately 20 times as active as 1,4-dihydro-3,5-dicarbethoxy-2,4,6-trimethylpyridine (DDC) in porphyrin production. 3,5,3′,5′-Tetra- and 2,3,4,2′,3′,4′-hexachlorobiphenyl isomers were moderate inducers, which were approximately 2.0 to 2.5 times as active as DDC. 2,4,6,2′,4′,6′-Hexachlorobiphenyl showed the same activity as DCC. Compounds such as 4,4′-di-, 2,3,2′,3′-, 2,4,2′,4′- and 2,6,2′,6′-tetrachlorobiphenyl were weak inducers and 2,5,2′,5′-tetrachloro- and decachlorobiphenyl isomers were found to be inactive. Kanechlor-400 was the strongest inducer among the commercial polychlorinated biphenyls investigated.The structural requirements for potent porphyrin-inducing activity of chlorobiphenyl isomers were found to be the para and meta substituted structure causing a more highly conjugated and nearly coplanar conformation. It was found that induction caused by some chlorobiphenyls was subject to feed-back repression by end-product heme. In addition, the metabolism of chlorobiphenyls in mice was influenced by the unsubstituted pairs of carbon atoms in the molecule. These results lead us to postulate the following hypothesis, namely, that strong inducers may displace heme directly and incorporate into a hydrophobic pocket of the apo-represor protein, thus causing an induction of δ-aminolevulinic acid synthetase.     

Exposure to polychlorinated biphenyls causes endothelial cell dysfunction

Environmental chemicals, such as polychlorinated biphenyls (PCBs), may be atherogenic by disrupting normal functions of the vascular endothelium. To investigate this hypothesis, porcine pulmonary artery-derived endothelial cells were exposed to 3,3′,4,4′-tetrachlorobiphenyl (PCB 77), 2,3,4,4′,5-pentachlorobiphenyl (PCB 114), or 2,2′,4,4′,5,5′-hexachlorobiphenyl (PCB 153) for up to 24 hours. These PCBs were selected for their varying binding avidities with the aryl hydrocarbon (Ah) receptor and differences in their induction of cytochrome P450. PCB 77 and PCB 114 significantly disrupted, in a dose-dependent manner, endothelial barrier function by allowing an increase in albumin transfer across endothelial monolayers. These PCBs also contributed markedly to cellular oxidative stress, as measured by 2,7-dichlorofluorescin (DCF) fluorescence and lipid hydroperoxides, and caused a significant increase in intracellular calcium ([Ca²⁺]_i) levels. Enhanced oxidative stress and [Ca²⁺]_i in PCB 77- and PCB 114-treated cells were accompanied by increased activity and content of cytochrome P450 1A and by a decrease in the vitamin E content in the culture medium. In contrast to the effects of PCB 77 and PCB 114, cell exposure to PCB 153 had no effect on cellular oxidation, [Ca²⁺]_i, or endothelial barrier function. These results suggest that certain PCBs may play a role in the development of atherosclerosis by causing endothelial cell dysfunction and a decrease in the barrier function of the vascular endothelium. It is possible that interaction of PCBs with the Ah receptor and activation of the cytochrome P450 1A subfamily are involved in this pathology. © 1995 John Wiley & Sons, Inc.     

In vitro effects of l-ascorbic acid (vitamin C) on aryl hydrocarbon hydroxylase activity in hepatic microsomes of mice

When aromatic hydrocarbon (Ah)-responsive and -non-responsive strains of mice were pretreated with 3-methylcholanthrene (MC) or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), vitamin C reduced the microsomal aryl hydrocarbon hydroxylase (AHH) activity. The AHH inhibitors 7,8-benzoflavone (7,8-BF) and 3-methylsulfonyl-3′,4,4′,5-tetrachlorobiphenyl (3-MSF-3′,4,4′,5-tetraCB) showed various inhibitory effects depending upon the types of microsomes, whereas vitamin C exhibited inhibition irrespective of the types of microsomes. 7,8-BF and 3-MSF-3′,4,4′,5-tetraCB as well as vitamin C suppressed the reverse mutation of the Salmonella typhimurium tester strains TA98 and TA100 induced by benzo[a]pyrene.     

The Formation of g=2.49-Species of Cytochrome P450 in the Rat Liver by PCB126 Oral Administration: Identification of Heme Axial Ligands by EPR Spectroscopy

Rat livers and microsomes were subjected to electron paramagnetic resonance (EPR) measurements at 77 K. The EPR spectra of the livers from the control group, carbon tetrachloride-, 3-methylcholanthrene-, and 3,3′,4,4′,5-pentachlorobiphenyl (PCB126)-treated rats exhibited an EPR spectrum at g=2.40, 2.24, and 1.93, which is characteristic of P450 in a resting state. The liver of the PCB126-treated rats showed an additional distinct EPR spectrum at g=2.49, 2.26, and 1.87 (g=2.49-species). The heme environmental structure of g=2.49-species was identified by crystal field analysis using three EPR g-values of the microsome treated with various chemicals. These results indicated that g=2.49-species is a hemeprotein with cysteine thiolate at the 5th coordination site, and a nitrogenous ligand at the 6th site.     

Composition of the photosystems and chloroplast structure in extreme shade plants

Chloroplasts were isolated from leaves of three species of tropical rainforest plants, Alocasia macrorrhiza, Cordyline rubra and Lomandra longifolia; these species are representative of extreme “shade” plants. It was found that shade plant chloroplasts contained 4–5 times more chlorophyll than spinach chloroplasts. Their chlorophyll a/chlorophyll b ratio was 2.3 compared with 2.8 for spinach. Electron micrographs of leaf sections showed that the shade plant chloroplasts contained very large grana stacks. The total length of partitions relative to the total length of stroma lamellae was much higher in Alocasia than in spinach chloroplasts. Freeze-etching of isolated chloroplasts revealed both the small and large particles found in spinach chloroplasts.

Despite their increased chlorophyll content, low chlorophyll a/chlorophyll b ratio, and large grana, the shade plant chloroplasts were fragmented with digitonin to yield small fragments (D-144) highly enriched in Photosystem I, and large fragments (D-10) enriched in Photosystem II. The degree of fragmentation of the shade plant chloroplasts was remarkably similar to that of spinach chloroplasts, except that the subchloroplast fragments from the shade plants had lower chlorophyll a/chlorophyll b ratios than the corresponding fragments from spinach. The D-10 fragments from the shade plants had chlorophyll a/chlorophyll b ratios of 1.78-2.00 and the D-144 fragments ratios of 3.54–4.07. We conclude that Photosystems I and II of the shade plants have lower proportions of chlorophyll a to chlorophyll b than the corresponding photosystems of spinach. The lower chlorophyll a/chlorophyll b ratio of shade plant chloroplasts is not due to a significant increase in the ratio of Photosystem II to Photosystem I in these chloroplasts.

The extent of grana formation in higher plant chloroplasts appears to be related to the total chlorophyll content of the chloroplast. Grana formation may simply be an means of achieving a higher density of light-harvesting assemblies and hence a more efficient collection of light quanta.     

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.