Embryolethality and induction of 7-ethoxyresorufin O-deethylase in chick embryos by polychlorinated biphenyls and polycyclic aromatic hydrocarbons having Ah receptor affinity.

The lethality and 7-ethoxyresorufin O-deethylase (EROD)-inducing potency of some individual polycyclic aromatic hydrocarbons (PAHs) and coplanar polychlorinated biphenyls (PCBs) in chick embryos were measured in order to compare the mechanisms of action of these compounds. In previous studies it was found that coplanar PCBs and certain PAHs have a high embryolethality in the chicken and that they induce embryonic EROD activity. Although the most potent PAHs were almost as embryolethal as the PCBs when injected into hens' eggs 72 h prior to measurement, they were considerably less potent EROD inducers. In the present study, three coplanar PCBs (3,3',4,4'-tetrachlorobiphenyl (TCB), 3,3',4,4',5-pentachlorobiphenyl (PeCB) and 3,3',4,4',5,5'-hexachlorobiphenyl (HCB)) and four of the most toxic PAHs (benzo[a]anthracene (BaA), benzo[k]fluoranthene (BkF), indeno[1,2,3-cd]pyrene (IP) and dibenzo[a, h]-anthracene (DBahA] were administered to chick embryos in different ways, including co-administration. Additive embryolethality was found when BkF and PeCB were co-administered as well as when BaA and DBahA were given simultaneously. The PAHs were more effective as EROD inducers when injected on day 9 (24 h prior to measurement) than when injected on day 7 (72 h prior to measurement). The opposite was found for PeCB and HCB, whereas no difference in potency was noted when comparing TCB injected 24 and 72 h before EROD determination. These substance-related differences were probably due, at least partly, to differences in biotransformation rates. EROD activities found after treatment with high doses of BkF, IP, or DBahA on day 9 were similar to those measured after treatment with PeCB in doses high enough to give maximal induction. Co-administration of high doses of BkF and PeCB did not further increase the activity, indicating that the PAHs and coplanar PCBs induce EROD to a common maximal value. To decrease the influence of metabolization of the PAHs on their EROD-inducing potency, EROD was determined early in development (day 8) and soon after treatment (24 h) in one experiment. In that experiment, the PAHs proved to be only a few times less potent EROD inducers in relation to their embryolethalities compared with the PCBs. The results of the present study, a previously observed similarity in pathology between chick embryos treated with PAHs and embryos treated with coplanar PCBs, and the fact that the most toxic PAHs also are the most avid Ah receptor binders suggest that the coplanar PCBs and the PAHs largely exert their toxicity in chick embryos via an Ah receptor-mediated mechanism. The differences between the compounds in their EROD-inducing potency/embryolethality ratios could probably be explained by their different rates of biotransformation.     

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.     

Gas-liquid chromatographic determination of the distribution of 3,3',4,4'-tetrachlorobiphenyl in the adult female rat following short-term oral administration

A gas-liquid chromatographic assay using electron-capture detection was developed for the quantitation of 3,3',4,4'-tetrachlorobiphenyl (TCBP) in the serum, urine, brain, liver, adipose tissue, and feces of the rat. The sample preparation involves extraction of 3,3',4,4'-TCBP with hexane under neutral or alkaline conditions (and washing with concentrated acid for feces only). Aqueous standards are used for calibration of the assay, except for adipose tissue. The lower limit of quantitative sensitivity of the assay for 3,3',4,4'-TCBP is 25 ng/mL for serum and urine and 125 ng/g for brain, liver, adipose tissue, and feces, which can be extended to 5 ng/mL and 25 ng/g, respectively, by analyzing a larger aliquot of the hexane extract. The overall accuracy is greater than 95% for serum, urine, brain and feces and 86% for liver, and the within-day coefficient of variation does not exceed 8.6%. 3,3',4,4'-TCBP was administered orally to adult, female, Sprague-Dawley rats in the dosage regimens: 0.2, 0.5 and 2 mg X kg-1 X day-1 for 10 days and 5 mg X kg-1 X day-1 for 4 days. 3,3',4,4'-TCBP distributed preferentially into adipose tissue and liver, where the xenobiotic concentration was greater in adipose tissue. The adipose tissue and hepatic 3,3',4,4'-TCBP concentrations were dependent on both the absolute dose and dosing schedule of the xenobiotic. Only trace concentrations, usually below the lower limit of quantitation, were detected in the serum, brain and kidney. Fecal excretion of 3,3',4,4'-TCBP was greater than urinary excretion for the 5 mg X kg-1 X day-1 X 4-day regimen.     

In vitro metabolism of polychlorinated biphenyl congeners by beluga whale (Delphinapterus leucas) and pilot whale (Globicephala melas) and relationship to cytochrome P450 expression

We measured rates of oxidative metabolism of two tetrachlorobiphenyl (TCB) congeners by hepatic microsomes of two marine mammal species, beluga whale and pilot whale, as related to content of selected cytochrome P450 (CYP) forms. Beluga liver microsomes oxidized 3,3',4,4'-TCB at rates averaging 21 and 5 pmol/min per mg for males and females, respectively, while pilot whale samples oxidized this congener at 0.3 pmol/min per mg or less. However, rates of 3,3',4,4'-TCB metabolism correlated with immunodetected CYP1A1 protein content in liver microsomes of both species. The CYP1A inhibitor alpha-naphthoflavone inhibited 3,3',4,4'-TCB metabolism by 40% in beluga, supporting a role for a cetacean CYP1A as a catalyst of this activity. Major metabolites of 3,3',4,4'-TCB generated by beluga liver microsomes were 4-OH-3,3',4',5-TCB and 5-OH-3,3',4,4'-TCB (98% of total), similar to metabolites formed by other species CYP1A1, and suggesting a 4,5-epoxide-TCB intermediate. Liver microsomes of both species metabolized 2,2',5,5'-TCB at rates of 0.2-1.5 pmol/min per mg. Both species also expressed microsomal proteins cross-reactive with antibodies raised against some mammalian CYP2Bs (rabbit; dog), but not others (rat; scup). Whether CYP2B homologues occur and function in cetaceans is uncertain. This study demonstrates that PCBs are metabolized to aqueous-soluble products by cetacean liver enzymes, and that in beluga, rates of metabolism of 3,3',4,4'-TCB are substantially greater than those of 2,2',5,5'-TCB. These directly measured rates generally support the view that PCB metabolism plays a role in shaping the distribution patterns of PCB residues found in cetacean tissue.     

The in vitro metabolism of benzo[a]pyrene by polychlorinated and polybrominated biphenyl induced rat hepatic microsomal monooxygenases

The metabolism of benzo[a]pyrene by halogenated biphenyl-induced rat hepatic microsomal monooxygenases was determined using a high pressure liquid chromatographic assay system. Incubation of benzo[a]pyrene with microsomes from rats pretreated with phenobarbitone or phenobarbitone-type inducers (2,2',4,4',5,5'-hexachlorobiphenyl, 2,2',4,4',6,6'-hexachlorobiphenyl, 2,2',5,5'-tetrachlorobiphenyl, 2,2',4,4',5,5'-hexabromobiphenyl, and 2,2',5,5'-tetrabromobiphenyl) resulted in increased overall metabolism of the hydrocarbon (less than fourfold) into phenolic, quinone, and diol metabolites, with the most striking increase observed in the formation of 4,5-dihydro-4,5-dihydroxybenzo[a]pyrene. In contrast, the metabolism of benzo[a]pyrene by microsomes from rats induced with 3-methylcholanthrene or 3,3',4,4'-tetrachlorobiphenyl resulted in a greater than 10-fold increase in overall benzo[a]pyrene metabolism, with the largest increases observed in the formation of the trans-7,8- and -9,10-dihydrodiol metabolites of benzo[a]pyrene. However, in comparison to control and phenobarbitone-induced microsomes, the oxidative conversion of benzo[a]pyrene by microsomes induced with 3-methylcholanthrene and 3,3',4,4'-tetrachlorobiphenyl into the 6,12-quinone was substantially inhibited. Previous reports have shown that the commercial halogenated biphenyl mixtures, fireMaster BP-6, and Aroclor 1254 are mixed-type inducers and that microsomes from rats pretreated with these mixtures markedly enhance the overall metabolism of benzo[a]pyrene. Not surprisingly, the metabolism of benzo[a]pyrene by microsomes from rats pretreated with the mixed-type inducers, 2,3,3',4,4'-penta-,2,3,3',4,4',5-hexa-, and 2',3,3',4,4',5-hexa- chlorobiphenyl was also increased and the metabolic profile was similar to that observed with fireMaster BP-6 and Aroclor 1254 induced microsomes.     

Effects of two prototypic polychlorinated biphenyls (PCBs) on lipid composition of rat liver and serum

Mature male Sprague-Dawley rats received a single IP injection of either 2,2',4,4',5,5'-hexachlorobiphenyl (HCB), 3,3',4,4'-tetrachlorobiphenyl (TCB) (300 microm/kg) in corn oil (10 ml/kg) or the corn oil vehicle alone, and were killed four days later after having been fasted overnight. The vehicle control group consisted of rats which were allowed free access to feed as well as pair-fed animals. Lipid analyses were conducted on liver, hepatic microsomes and serum. TCB- (but no HCB-) treatment resulted in a statistically significant increase in total liver lipids and triglycerides. Liver phospholipids remained unchanged. Both PCBs increased the cholesterol and phospholipids content of the liver microsomal fraction. Serum lipids measured were not statistically different from control values. While HCB had little effect on the fatty acid composition of liver lipids, TCB caused an increase in C 18:1 (n-9) and a decrease in C 20:4 (n-6). Both PCBs increased C 18:0 in the hepatic microsomal fraction, but TCB also decreased C 16:0. Neither PCB altered the fatty acid composition of serum total lipids. These data are consistent with the concept that specific alterations in lipid metabolism are dependent on the structure of the PCB.     

Prostaglandin release by the chick embryo heart is increased by 2,3,7,8-tetrachlorodibenzo-p-dioxin and by other cytochrome P-448 inducers

Exposure of chick embryos in ovo to cytochrome P-448 inducers 2,3,7,8-tetrachlorodibenzo-p-dioxin, 3,4,3',4'-tetrachlorobiphenyl, 3,4,5,3',4',5'-hexachlorobiphenyl and beta-napthoflavone, increased cardiac prostaglandins in vitro. The dose response relationships were biphasic with prostaglandin release increasing at the low doses and returning to basal levels at higher doses. Phenobarbital was ineffective. Increased cardiac prostaglandin release was detected at doses that induced hepatic 7-ethoxyresorufin deethylase (7-ER) but which were below the threshold for cardiac induction. The fall in prostaglandin release coincided with induction of cardiac 7-ER and therefore may be attributable to increased prostaglandin metabolism. These studies show that the P-450 system may interact with the arachidonic acid metabolizing system to increase PG release and that this effect may be part of the pleiotypic response to Ah-receptor activation.     

Ah receptor for 2,3,7,8-tetrachlorodibenzo-p-dioxin: ontogeny in chick embryo liver

Aryl hydrocarbon hydroxylase (AHH, cytochrome P1-450) is induced in chick liver very early during embryonic development if embryos are treated with 3-methylcholanthrene-type compounds such as 3,4,3'4'-tetrachlorobiphenyl. In mammals, AHH induction is known to be mediated by the Ah receptor. Liver from embryonic and newly hatched chicks was found to contain a cytosolic receptor for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) which has properties that are very similar to properties of the Ah receptor previously characterized in mammalian tissues. In chick embryo liver, cytosolic binding sites for TCDD were of high affinity (Kd for [3-H]-TCDD = 0.2 nM) and were specific for 3-methylcholanthrene-type inducers. The specific binding component sedimented at about 9S on sucrose density gradients prepared at low ionic strength. A high level of Ah receptor was detected in chick embryo liver by the fifth day of incubation (5 DI); this is at least 24 hours prior to the onset of AHH inducibility. The Ah receptor concentration increased from 5 DI to 8 DI, the period when chick liver is undergoing early morphological differentiation. After 8 DI, Ah receptor levels dropped substantially and remained low into the posthatching period. In contrast, AHH inducibility was high by 7 DI and remained high throughout embryonic development and into the posthatching period. The discrepancy between Ah receptor levels and the degree of AHH inducibility suggests that only a small fraction of the Ah receptor population is required for maximal AHH induction.     

Differences between chick and turkey embryos in sensitivity to 3,3′,4,4′-tetrachloro-biphenyl and in concentration/affinity of the hepatic receptor for 2,3,7,8-tetrachlorodibenzo-p-dioxin

• 1.1. 3,3′,4,4′-Tetrachlorobiphenyl (TCB) was 20–100 times more toxic in chick embryos than in turkey embryos when injected into eggs.
• 2.2. The ed₅₀-value for induction of AHH activity by TCB in the liver of early chick and turkey embryos was estimated to be 0.6 and 6 μg/kg egg, respectively.
• 3.3. In both species α-naphthoflavone was more effective than metyrapone at inhibiting basal and TCB-induced AHH activities.
• 4.4. The TCDD receptor was detected in the liver of 7-day-old chick embryos, while it was not found in 9-day-old turkey embryo liver.

     

Immunochemical detection of different isoenzymes of cytochrome P-450 induced in chick hepatocyte cultures.

This study investigated whether the same cytochrome P-450 (P-450) isoenzymes were inducible in cultures of chick-embryo hepatocytes as in the liver of chicken embryos. We purified two isoenzymes of cytochrome P-450 from the livers of 17-day-old-chick embryos: one of molecular mass approx. 50 kDa induced in vivo by the phenobarbital-like inducer glutethimide, and the second of approx. 57 kDa induced by 3-methylcholanthrene. Rabbit antiserum against the 50 kDa protein inhibited benzphetamine demethylase activity in hepatic microsomes (microsomal fractions) from glutethimide-treated chick embryo. Antiserum to the 57 kDa protein inhibited ethoxyresorufin de-ethylase activity in hepatic microsomes from methylcholanthrene-treated chick embryo. Cultured chick hepatocytes were treated with chemicals known to induce isoenzymes of P-450 in rodent liver. The induced P-450s were quantified spectrophotometrically and characterized by immunoblotting and enzyme assays. From these studies, chemical inducers were classified into three groups: (i) chemicals that induced a P-450 isoenzyme of 50 kDa and increased benzphetamine demethylase activity: glutethimide, phenobarbital, metyrapone, mephenytoin, ethanol, isopentanol, isobutanol, lindane, lysodren; (ii) chemicals that induced a P-450 isoenzyme of 57 kDa and increased ethoxyresorufin de-ethylase activity: 3-methylcholanthrene and 3,3',4,4'-tetrachlorobiphenyl; and (iii) the mono-alpha-substituted 2,3',4,4',5-pentabromobiphenyl, which induced both proteins and both activities. The immunochemical data showed that chick-embryo hepatocytes in culture retain the inducibility of glutethimide- and methylcholanthrene-induced isoenzymes of P-450 that are inducible in the liver of the chicken embryo.     

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.     

Thyroid hormone deiodination in tissues of American plaice, Hippoglossoides platessoides: characterization and short-term responses to polychlorinated biphenyls (PCBs) 77 and 126

We have described the tissue distribution and properties of thyroid hormone (TH) deiodination activities of the marine American plaice, Hippoglossoides platessoides. We then studied the 1- or 4-week responses of the plaice liver and brain deiodination activities and the plasma thyroxine (T4) and 3,5,3'-triiodothyronine (T3) levels to an intraperitoneal injection (5-500 ng/g) of the polychlorinated biphenyl (PCB) congeners 77 (3,3'-4,4'-tetrachlorobiphenyl) or 126 (3,3',4,4',5-pentachlorobiphenyl). T4 and 3,3'5'-triiodothyronine (rT3) outer-ring deiodination (ORD) activities were greater in liver than in kidney, gill, heart, brain, intestine or muscle; inner-ring deiodination (IRD) activity occurred in all tissues but was consistently higher in brain. Deiodination characteristics (optimal pH, optimal dithiothreitol concentration, responses to inhibitors and apparent Km values of 0.6-4 nM) fell in the same rage as those of low-Km deiodinases in other teleosts. Deiodination activities were maximal when assayed at 25 degrees C but uniformly low over the natural range of 0-9 degrees C. Neither PCB 77 nor PCB 126 altered brain T4ORD activity or plasma T4 levels (P < 0.05). However, at 1 week post injection hepatic T4ORD activity was increased and plasma T3 levels lowered by PCB 77 (5 and 25 ng/g), while hepatic IRD activity was increased by PCB 126 (50 and 500 ng/g). Neither PCB 77, PCB 126 nor selected hydroxylated. PCBs given in vitro compared with T4 for binding sites on plasma proteins or altered hepatic deiodination activity, indicating no direct action on plasma proteins or deiodinases We conclude that plaice TH deiodination tissue distribution and characteristics resemble those of other teleosts. Deiodination activities are low at natural assay temperatures but at 1 week show some responses to PCBs 77 and 126.     

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.     

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.     

Reactions of 2,2′,5,5′-tetrachlorobiphenyl 3,4-oxide with methionine, cysteine and glutathione in relation to the formation of methylthio-metabolites of 2,2′,5,5′-tetrachlorobiphenyl in the rat and mouse

Non-enzymatic reactions of the 3,4-oxide of 2,2′,5,5′-tetrachlorobiphenyl (TCB) with methionine or N-acetylmethionine in ethanol/neutral buffer at 37°C proceeded very slowly to yield an approx. 1 : 1 ratio of 3- and 4-methylthio-TCB. Under similar conditions reaction of TCB 3,4-oxide with cysteine proceeded about 100 times more rapidly to yield an approx. 1 : 1 ratio of 3- and 4-(cystein-S-yl)-TCB as the major products. Cystein-S-yl-3,4-dihydro-hydroxy-TCB(s) was also formed as a minor product from reaction of TCB 3,4-oxide with cysteine in dimethyl sulfoxide/neutral buffer. TCB 3,4-oxide did not react detectably with glutathione in ethanol/neutral buffer at 37°C or 70°C, but reaction in ethanol/pH 8.7 buffer at 37°C proceeded very rapidly to yield about a 1 : 1 ratio of 3- and 4-(glutathion-S-yl)-TCB and of two glutathion-S-yl-TCB precursors. Glutathion-S-yl-TCB(s) and its precursor(s) were also formed rapidly in a rat liver cytosol-catalyzed reaction of TCB 3,4-oxide with glutathione at neutral pH. The glutathion-S-yl-TCBs readily degraded upon concentration in aqueous alcohol solutions under mild conditions to yield compounds tentatively identified as [N-(5-carboxy-1-pyrrolin-2-yl)-1-glycinocystein-S-yl]-TCBs, (1-glycinocystein-S-yl)-TCBs and 2-oxopyrrolidine-5-carboxylic acid.

Rats given a single dose of TCB excreted about 0.07% of the dose in the feces during the first 4 days as 3-methylthio-TCB, 4-methylthio-TCB, 4-methylsulfonyl-TCB, methylthio-hydroxy-TCBs (tentatively identified) and mercapto-TCB(s) (tentatively identified) in about a 1 : 5 : 0.1 : 0.1 : 0.05 ratio, respectively. Rats given an equimolar dose of TCB 3,4-oxide excreted similar ratios of these fecal metabolites in approx. 10-fold greater quantities. Mice given TCB excreted about 0.1% of the dose in the feces during the first 4 days as 3-methylthio-TCB, 4-methylthio-TCB and 3-methylsulfonyl-TCB in about a 1.5 : 1 : 0.05 ratio, respectively. Methylthio-TCBs were not detected (<0.0004% of the dose) in the bile of a cannulated rat given a single dose of TCB. About 1.5% of the TCB dose was excreted in the bile as glutathion-S-yl-TCB(s) and its precursor(s). Collectively, the data indicate that TCB 3,4-oxide is a primary metabolic intermediate in the formation of methylthio-metabolites of TCB.     

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

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

Inhibition of chick embryo hepatic uroporphyrinogen decarboxylase by components of xenobiotic-treated chick embryo hepatocytes in culture. II.

A variety of xenobiotics, viz., 3,3',4,4'-tetrachlorobiphenyl (TCBP), sodium phenobarbital (PB), 3,5-diethoxycarbonyl-2, 4,6-trimethylpyridine (OX-DDC), and nifedipine, cause a decrease in uroporphyrinogen decarboxylase (UROG-D) activity, accompanied by uroporphyrin accumulation, in chick embryo hepatocytes in culture. In this study the activity of 17-day-old chick embryo hepatic UROG-D was determined by measuring the conversion of pentacarboxylporphyrinogen I to coproporphyrinogen I, and it was shown that a UROG-D inhibitor, previously reported to accumulate in TCBP-treated and PB-treated chick embryo hepatocytes in culture, also accumulates in OX-DDC-treated and nifedipine-treated chick embryo hepatocytes in culture. It was concluded that the accumulation of a UROG-D inhibitor provides an explanation for the UROG-D inhibition observed in this culture system with xenobiotics that cause uroporphyrin accumulation. Studies of the UROG-D inhibitory fraction isolated from the 10,000 x g, 40,000 x g, and 100,000 x g supernatant fractions of cultured chick embryo hepatocyte homogenate led to the conclusion that the UROG-D inhibitor is derived from a soluble component of the homogenate.     

Redistribution of cPLA(2) in rat renal tubular cell cultures in response to PCBs

The influence of different polychlorinated biphenyls (PCBs) upon the cytosolic phospholipase A(2) (cPLA(2)) redistribution to the particulate fraction has been investigated in rat renal proximal tubule culture cells. Treatment with Aroclor 1248 increased PLA(2) activity in the particulate fraction in a concentration-dependent manner using two radioactive substrates. However, the activity of PLA(2) in the cytosolic fraction decreased. This work also shows that 2,2',4,4',5,5'-hexachlorobiphenyl (HCB) (a di-ortho-substituted nonplanar congener) can increase the activity of PLA(2) in the particulate fraction and decrease the enzyme activity in the cytosolic fraction. The exposure of cell cultures to 3,3',4,4'-tetrachlorobiphenyl (TCB) (a non-ortho-subtituted planar congener) does not alter PLA(2) activity. These results suggest that PCBs, depending on their planar or nonplanar structures, cause a translocation of the enzyme from the cytosol to membranes. To evaluate this possibility, the contents of immunoreactive cPLA(2) were examined by immunoblot analysis in the high-speed supernatant and the particulate fraction of treated cell cultures. The increases/decreases in the amounts of cPLA(2) protein agree with the increases/decreases of PLA(2) activity previously cited. These data demonstrate that the PCB-stimulated redistribution of cPLA(2) to membranes is associated, at least in part, with the changes detected in the activity of the enzyme.     

Degradation of 4,4'-dichlorobiphenyl, 3,3',4,4'-tetrachlorobiphenyl, and 2,2',4,4',5,5'-hexachlorobiphenyl by the white rot fungus Phanerochaete chrysosporium.

The white rot fungus Phanerochaete chrysosporium has demonstrated abilities to degrade many xenobiotic chemicals. In this study, the degradation of three model polychlorinated biphenyl (PCB) congeners (4,4'-dichlorobiphenyl [DCB], 3,3',4,4'-tetrachlorobiphenyl, and 2,2',4,4',5,5'-hexachlorobiphenyl) by P. chrysosporium in liquid culture was examined. After 28 days of incubation, 14C partitioning analysis indicated extensive degradation of DCB, including 11% mineralization. In contrast, there was negligible mineralization of the tetrachloro- or hexachlorobiphenyl and little evidence for any significant metabolism. With all of the model PCBs, a large fraction of the 14C was determined to be biomass bound. Results from a time course study done with 4,4'-[14C]DCB to examine 14C partitioning dynamics indicated that the biomass-bound 14C was likely attributable to nonspecific adsorption of the PCBs to the fungal hyphae. In a subsequent isotope trapping experiment, 4-chlorobenzoic acid and 4-chlorobenzyl alcohol were identified as metabolites produced from 4,4'-[14C]DCB. To the best of our knowledge, this the first report describing intermediates formed by P. chrysosporium during PCB degradation. Results from these experiments suggested similarities between P. chrysosporium and bacterial systems in terms of effects of congener chlorination degree and pattern on PCB metabolism and intermediates characteristic of the PCB degradation process.     

Diprenylated chalcones and other constituents from the twigs of Dorstenia barteri var. subtriangularis

The twigs of Dorstenia barteri var. subtriangularis yielded three diprenylated chalcones: (-)-3-(3,3-dimethylallyl)-5'-(2-hydroxy-3-methylbut-3-enyl)-4,2',4'-trihydroxychalcone, (+)-3-(3,3-dimethylallyl)-4',5'-[2'-(1-hydroxy-1-methylethyl)-dihydrofurano]-4,2'-dihydroxychalcone and 3,4-(6",6"-dimethyldihydropyrano)-4',5'-[2',-(1-hydroxy-1-methylethyl)-dihydrofurano]-2'-hydroxychalcone for which the names bartericins A, B and C, respectively, are proposed. Stipulin, beta-sitosterol and its 3-beta-D-glucopyranosyl derivative were also isolated. The structures of these secondary metabolites were determined on the basis of spectroscopic analysis, especially, NMR spectra in conjunction with 2D experiments, COSY, HMQC and HMBC. The structural relationship of bartericins B and C was further established by the chemical cyclization of one to the other.