Fatty acid metabolism in neonatal chickens (Gallus domesticus) treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or 3,3',4,4',5-pentachlorobiphenyl (PCB-126) in ovo

Treatment of chickens as pre-incubation embryos with TCDD or PCB-126 altered fatty acid concentrations in their plasma 21 days later, compared with their oil vehicles (sunflower and corn oils, respectively). TCDD increased the concentrations of total fatty acids, lipid classes (phospholipids and cholesterol ester), fatty acid families (saturated, n-7 and n-6), and many specific fatty acids. The only fatty acid concentrations decreased by TCDD treatment were those of cholesterol ester fatty acids 20:3n3 and 24:6n3 and overall plasma 24:6n3. In contrast, PCB-126 treatment decreased total phospholipid, saturated and plasmogen fatty acid concentrations with generally decreasing trends in specific fatty acid concentrations. However, both TCDD and PCB-126 treatments increased total 22:1n9 and decreased 24:6n3 concentrations compared with their respective vehicles. The potential relationship between those fatty acid concentrations altered by toxicant treatment and alterations in brain symmetry was then examined using correlation analysis. Several fatty acid concentrations were significantly correlated with differences in brain morphology between the right and left hemispheres and these potential associations were different between toxicant and vehicle.     

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.     

Hepatic biotransformation responses in Atlantic salmon exposed to retinoic acids and 3,3',4,4'-tetrachlorobiphenyl (PCB congener 77)

Active derivatives of vitamin A are essential in physiological processes such as cell growth, differentiation, morphogenesis and development. The biological functions of vitamin A are mediated through the retinoid acid receptors (RARs) and retinoid X receptors (RXRs). Aryl hydrocarbon receptor (AhR) agonists such as planar halogenated compounds are known to interfere with vitamin A homeostasis in both field and laboratory studies. In this study, we have investigated the molecular interactions between vitamin A and AhR signalling pathways using juvenile Atlantic salmon and agonists for both receptor pathways. Groups of juvenile salmon were treated with all-trans- and 9-cis-retinoic acid mixture (7:3 ratio) dissolved in DMSO (dimethyl sulfoxide) at 0.1, 1 and 10 mg/kg fish weight. The mixture was force fed singly or in combination with 0.1 mg 3,3',4,4'-tetrachlorobiphenyl (co-planar congener 77)/kg fish weight dissolved in DMSO. Liver samples were collected 3 days after PCB-77 exposure. A separate group exposed to combined retinoic acid (1 mg/kg for 5 days) and PCB-77, was sampled at 3, 7 and 14 days after PCB-77 exposure. Liver samples collected from all exposure groups were analyzed for gene (RARalpha, AhR2alpha, AhR2beta, CYP1A1, UGT1 and GSTpi) expression using real-time PCR and activity (7-ethoxyresorufin O-deethylase (EROD), UGT and GST) using biochemical methods with specific substrates. Our data showed that exposure to RA alone did not produce a significant increase of RARalpha mRNA levels, and the presence of PCB-77 attenuated the expression of RARalpha in RA dose- and time-specific manner. In addition, RA produced a dose-dependent increase of CYP1A1 mRNA and activity (EROD) levels without concomitant increase in AhR2 isoforms. When administered alone, PCB-77 produced increased CYP1A1, UGT1 and GSTpi mRNA and enzyme levels. The PCB-77-induced CYP1A1, UGT1 and GSTpi (mRNA and activity) levels were modulated by RA, in a parameter and dose-specific manner. In general, our data show an interaction between vitamin A and AhR signalling that may affect retinoid homeostasis in fish.     

Mixed-function oxygenase in juvenile rainbow trout exposed to hexachlorobenzene or 3,3',4,4'-tetrachlorobiphenyl.

1. 3,3',4,4'-tetrachlorobiphenyl (PCB 77), but not hexachlorobenzene, induced liver microsomal cytochrome P-450 (Cyt P-450), ethoxycoumarin-O-deethylase (ECOD) and ethoxyresorufin-O-deethylase (EROD) in rainbow trout. Maximum induction was observed in a PCB 77 injected group of fish (1.0 mg/kg, i.p. injection) 13 days after the injections being 2, 10 and 50 times the value of non-induced fish, respectively. 2. The apparent Km value of ethoxyresorufin of this induced group of fish differed only slightly from that of non-induced fish. The apparent Vmax value (EROD) was 50 times higher. 3. Freezing small pieces of liver in liquid nitrogen did not produce cytochrome P-420. 4. Fluorimetric and spectrophotometric measurements of EROD correlated.     

Structural basis of species differences between human and experimental animal CYP1A1s in metabolism of 3,3',4,4',5-pentachlorobiphenyl

Coplanar polychlorinated biphenyls included in dioxin-like compounds are bio-accumulated and adversely affect wildlife and human health. Although many researchers have studied the metabolism of PCBs, there have been few reports of the in vitro metabolism of 3,3',4,4',5-pentachlorobiphenyl (PCB126), despite the fact that it has the highest toxicity among PCB congeners. Cytochrome P450 (CYP) 1A1 proteins can metabolize some dioxins and PCBs by hydroxylation, but the activities of human and rat CYP1A1 proteins are very different. The mechanism remains unclear. From our results, rat CYP1A1 metabolized PCB126 into 4-OH-3,3',4',5-tetrachlorobiphenyl and 4-OH-3,3',4',5,5'-pentachlorobiphenyl, but human CYP1A1 did not metabolize. Homology models of the two CYP proteins, and docking studies, showed that differences in the amino acid residues forming their substrate-binding cavities led to differences in the size and shape of the cavities; only the cavity of rat CYP1A1 allowed PCB126 close enough to the haem to be metabolized. Comparison of the amino acid residues of other mammalian CYP1A1 proteins suggested that rats have a unique metabolism of xenobiotics. Our results suggest that it is necessary to be careful in human extrapolation of toxicity data estimated by using the rat as an experimental animal, especially in the case of compounds metabolized by CYP1A1.     

Interaction of benzo[a]pyrene, 2,3,3',4,4',5 hexachlorobiphenyl (PCB 156) and cadmium on biomarker responses in flounder (Platichthys flesus L.)

Interactive effects of a mixed pollutant exposure on biomarker responses were studied in European flounder (Platichthys flesus L.). The model chemicals, benzo[a]pyrene (BaP, 2.5 mg kg^-1), 2,3,3',4,4'5 hexachlorobiphenyl (PCB-156, 2.5 mg kg^-1), and cadmium (cadmium, 1 mg kg^-1), were administered to fish by subcutaneous injections. Biomarker responses were quantified both following administration of single chemicals and sequential combinations of the chemicals in pairs. Significant induction of CYP1A protein levels and corresponding ethoxyresorufin-O-deethylase (EROD) activities was observed in BaP and PCB treated flounder after 2 and 8 days, respectively. The strongest induction (44 fold) was caused by BaP. No further induction was observed after additional treatment with PCB 156. CYP1A induction caused by BaP was inhibited (40% compared with BaP treatment alone) in flounder pre treated with cadmium, whereas induction by PCB 156 appeared to be unaffected by pre treatment with cadmium. Flounder treated with cadmium only had significantly elevated hepatic levels of metallothionein (MT) after 15 days. Pre treatment with BaP and PCB prior to cadmium inhibited the MT induction (30-50%) compared with cadmium alone. Furthermore, significantly higher glutathione S transferase activities were observed in flounder administered cadmium alone, and in flounder treated with BaP or PCB 156 prior to cadmium. GST selenium independent peroxidase activities appeared to be unaffected by any of the treatments in the present study. The results indicate that chemical mixtures may affect biomarker responses differently from compounds administered alone, and that the sensitivity of both CYP1A and MT are influenced by pollutants other than their primary inducers.     

Chiral overcrowded alkenes; asymmetric synthesis of (3S,3'S)-(M, M)-(E)-(+)-1,1',2,2',3,3',4,4'-octahydro-3,3',7,7'-tetramethyl-4, 4'-biphenanthrylidenes

An asymmetric synthesis route towards (3S,3'S)-(M,M)-(E)-(+)-1,1',2, 2',3,3',4,4'-octahydro-3,3',7,7'-tetramethyl-4,4'-biphenanthrylidene was developed using the Evans procedure as a key step. The absolute configurations of the title compound and of its parent ketone were determined by CD spectroscopy and could be correlated with the stereochemical results of the asymmetric alkylation. Furthermore, a comparison was made with the known (3R,3'R)-(P,P)-(E)-(-)-1,1',2,2', 3,3',4,4'-octahydro-3,3',7,7'-dimethyl-4,4'-biphenanthrylidene. Finally, the X-ray crystallographic analysis of (3S,3'S)-(M, M)-(E)-(+)-1,1',2,2',3,3',4,4'-octahydro-3,3',7,7'-tetramethyl-4, 4'-biphenanthrylidene is presented.     

Time- and dose-dependent biom arker responses in flounder (Platichthys flesus L.) exposed to benzo[a]pyrene, 2,3,3',4,4', 5-hexachlorobiphenyl (PCB-156) and cadmium

Responses in flounder (Platichthys flesus) towards benzo [a]pyrene (BaP), 2,3,3',4,4',5-hexachlorobiphenyl (PCB-156), and cadmium (Cd) were investigated in time-course and dose-response studies of selected biomarkers. Measurements of biliary fluorescent BaP metabolites and hepatic concentrations of PCB-156 and cadmium showed that the injected toxicants were rapidly m obilized from the muscle to the liver, but a depot effect was indicated in the highest dose groups of BaP and PCB-156 (12 mg kg^-1 bodyweight). Clearest biomarker responses were found in the induction of hepatic cytochrome P450 1A (CYP1A) enzymes as a response towards BaP and PCB-156 exposure. Maximum induction of CYP1A dependent 7-ethoxyresorufin O-deethylase (EROD) activity was observed after 2 and 8 days in BaP and PCB-156-treated flounder, respectively. Positive dose-effect relationships were observed towards both compounds, but the CYP1A induction was more persistent with PCB exposure than with BaP exposure. In Cd-exposed fish, the hepatic level of metallothionein responded more slowly with highest levels observed after 16 days in the time-study. In the combined BaP + Cd treatment, the CYP1A induction was only slightly suppressed. Aspartate aminotransferase in serum appeared to be responsive towards BaP, but also towards the acetone vehicle in controls in the first part of the exposure period. Hematocrit as well as hepatic activities of aldrin epoxidase, glutathione S-transferase, and UDP-glucuronyl transferase were not responsive to any treatm ent in the present study. In general, the results demonstrate that selected biom arkers in flounder are responsive to PAH, PCB, and heavy metal pollutant exposure, indicating the applicability of this species in future environmental pollution monitoring programmes.     

Effects of 2,2'4,4'5,5'-hexachlorobiphenyl (PCB 153) on plasma sex steroids and vitellogenin in rockfish (Sebastes schlegeli)

We examined the estrogenic effect of 2,2'4,4'5,5'-hexachlorobiphenyl (PCB 153) on the rockfish, Sebastes schlegeli. We measured levels of plasma estradiol-17beta (E(2)) and testosterone (T) by radioimmunoassay (RIA). Plasma concentrations of T and 17alpha-hydroxyprogesterone in female and male fish injected with PCB 153 using two dosages (0.16 mg/kg body weight. and 0.57 mg/kg) did not differ significantly between sexes or from sham-injected controls of the same sex. Plasma concentrations of E(2) in females injected with PCB 153 (both levels) increased at 12 and 24 h. Concentrations of plasma vitellogenin (VTG) in females increased 72 h after injection with PCB 153 and reached 0.38 and 1.25 mg/mL, respectively. No VTG was detected in males injected with the same dosage. These results suggest that PCB 153 may lead to the production VTG in female rockfish through a synergistic effect with E(2), resulting in indirect disruption of the aromatization process.     

Co-planar 3,3',4,4',5-pentachlorinated biphenyl and non-co-planar 2,2',4,6,6'-pentachlorinated biphenyl differentially induce recruitment of oestrogen receptor alpha to aryl hydrocarbon receptor target genes

In the present study we examined the ability of 3,3',4,4',5-pentachlorinated biphenyl [PCB126 (polychlorinated biphenyl 126)], a prototypical AHR (aryl hydrocarbon receptor) agonist, and 2,2',4,6,6'-PCB (PCB104), which does not activate AHR, to induce the recruitment of ERalpha (oestrogen receptor alpha) to CYP1A1 (cytochrome P4501A1 gene) and CYP1B1 promoters in T-47D human breast cancer cells and other cell lines. PCB126 treatment strongly induced CYP1A1 and CYP1B1 mRNA expression that was unaffected by co-treatment with E2 (17beta-oestradiol). PCB104 failed to induce changes in either CYP1A1 or CYP1B1 expression levels. ChIP (chromatin immunoprecipitation) assays show that PCB126, but not PCB104, increased the promoter occupancy by ERalpha to CYP1A1 and CYP1B1 promoters. Co-treatment with PCB126+E2 significantly enhanced the promoter occupancy of ERalpha at CYP1A1, whereas co-treatment with PCB126+4-hydroxytamoxifen or ICI182,780 did not. Competitive binding studies revealed that neither PCB126 nor PCB104 bound to ERalpha. HEK-293 cells (human embryonic kidney-293 cells) stably transfected with ERalpha showed significantly higher PCB126-induced CYP1A1 expression compared with empty vector controls, whereas no increase was observed in cells stably transfected with ERalpha lacking its N-terminal AF1 (activation function-1) domain (ERalphaDeltaAF1). Despite no increase in AHR-mediated gene expression, ChIP assays revealed that ERalphaDeltaAF1 was present at CYP1A1 and CYP1B1 promoters. HC11 mouse mammary cells stably expressing shRNA (small-hairpin RNA) against ERalpha showed an 8-fold reduction in PCB126-dependent Cyp1a1 expression. Our results provide further evidence that AHR agonists induce ERalpha promoter occupancy at AHR target genes through indirect activation of ERalpha, and support a role for ERalpha in AHR transactivation.     

Enantioselective disposition of PCB 136 (2,2',3,3',6,6'-hexachlorobiphenyl) in C57BL/6 mice after oral and intraperitoneal administration

Studies of xenobiotic disposition in rodents often employ experimental designs using differing routes of administration. In an effort to investigate the effects of route of administration on enantioselective disposition of xenobiotics, a chiral polychlorinated biphenyl (PCB), racemic PCB 136, was administered as a single dose (50 mg/kg body weight) to male or female C57BL/6 mice either orally or via intraperitoneal injection. Mice were sacrificed after either 3 or 6 days, and blood and organs were collected for PCB analysis. Intraperitoneal injection of PCB 136 produced statistically higher PCB levels in blood and organs than did the oral administration. Tissue levels were higher after 3 days than those after 6 days. Enantioselective analysis showed that (+)-PCB 136 was enriched in most organs, with the most pronounced enrichment found in the liver and the brain of animals dosed orally or by intraperitoneal injection, respectively. Significantly higher retained enantiomeric fractions of PCB 136 were found in the oral treatment groups compared with those found in intraperitoneal treatment groups, possibly as a result of the lower PCB levels in oral treatment groups. Therefore, the choice of administration route may well have implications for the enantioselective disposition of PCB 136 and other chiral substances.     

Computational study of conformational and chiroptical properties of (2R,3S,4R)-(+)-3,3',4,4',7-flavanpentol

Conformational analysis of (2R,3S,4R)-(+)-3,3',4,4',7-flavanpentol, a flavonoid compound displaying both antioxidant and pro-oxidant properties, is performed by molecular mechanics and density functional theory calculations both in the gas phase and in methanol solution by using the Polarizable Continuum Model. Nine different conformations are identified. Absorption (UV) and circular dichroism (CD) spectra and optical rotations are calculated by means of time dependent density functional theory (TDDFT) and compared with experiments. The effects of a complex environment formed by water and proline-rich peptide molecules on the conformational characteristics of (2R,3S,4R)-(+)-3,3',4,4',7-flavanpentol and therefore on its UV and CD spectra are investigated by atomistic molecular dynamics simulations.     

Effect of 3,3',5' triiodo-L-Thyronine (rT3) on the serum concentration of thyroid hormones in rats

50, 100 or 150 micrograms/100 g body weight/day of very pure 3,3',5' triiodo-L-thyronine (rT3), obtained from a new synthetic method, was intraperitoneally administered in male Wistar rats for 5 weeks. Serum total thyroxine (T4), free thyroxine (FT4) and total 3,5,3' triiodo-L-thyronine (T3) concentrations were increased with all the doses of rT3. Free T3 (FT3) was also but non-significantly elevated. Different assumptions are put forward in order to explain this rT3 effect.     

Specific phosphorylase from Euglena gracilis splits diadenosine 5',5''-P(1),P(4)-tetraphosphate (Ap(4)A) and diadenosine 5',5''-P(1),P(3)-triphosphate (Ap(3)A)

1. Phosphorolytic cleavage of Ap(4),A was demonstrated in cell-free extracts from two protozoan organisms, Euglena gracilis and Acanthamoeba castellanii. 2. A specific dinucleoside oligophosphate (DNOP) alpha, beta-phosphorylase which degrades substrates with formation of corresponding nucleoside 5'-diphosphate (NDP) as one of the reaction products was purified 625-fold from Euglena gracilis cells. 3. In addition to Ap(4)A, the phosphorylase degrades AP(3)A, Ap(5)A, Gp(4)G and one of phosphonate analogs, ApppCH(2)pA. The K(m) values for Ap(4), A and Ap(3) A are 27 and 25 micron, and relative velocities 100 and 14, respectively. The K(m) for phosphate is 0.5 mM. 4. Some anions (arsenate, chromate, molybdate and vanadate) can substitute for phosphate in the catalyzed reactions and in their presence the DNOPs yield corresponding nucleoside 5'-monophosphate as one of the reactions' product. The enzyme supports also an anion-dependent dephosphorylation of NDPs. 5. Molecular weight of the native Euglena phosphorylase is 30,000. Optimum pH for its activity is at 8.0 Divalent metal cations are essential for the phosphorolysis of DNOPs but are not for the NDP dephosphorylation mentioned.     

3,3',4,4'-tetrachlorobiphenyl: metabolism by the chick embryo in ovo and toxicity of hydroxylated metabolites

The metabolism of 3,3',4,4'-tetrachlorobiphenyl (TCB) has been studied in the chicken in ovo by analysis of bile from chick embryos. Four percent of the [14C]TCB dose injected into the air sac on day 13 of incubation was detected in the bile by day 19. An increase of more lipophilic TCB metabolites was observed by HPLC analysis after hydrolysis of the bile. TCB and three phenolic TCB metabolites were identified and quantified in the hydrolyzed bile: TCB (14 ng/gall bladder), 5-hydroxy-3,3',4,4'-tetrachlorobiphenyl (234 ng/gall bladder), 4-hydroxy-3,3',4',5-tetrachlorobiphenyl (45 ng/gall bladder) and 2-hydroxy-3,3',4,4'-tetrachlorobiphenyl (3 ng/gall bladder). The presence of two other TCB metabolites in the bile, a dihydroxy-tetrachlorobiphenyl and a dihydroxy-trichlorobiphenyl was also indicated. The method used in the present study is well suited for studies of metabolism in avian embryos in ovo. The three TCB metabolites identified all proved to be at least two orders of magnitude less toxic than TCB in a chick embryo test. These metabolites were also shown to bind with significantly lower affinity than TCB to the Ah receptor. TCB, 5-hydroxy-3,3',4,4'-tetrachlorobiphenyl, 4-hydroxy-3,3',4',5-tetrachlorobiphenyl and 2-hydroxy-3,3',4,4'-tetrachlorobiphenyl gave Kd values of 16, 33, 45 and 37 nM, respectively, in the Ah receptor test.     

Conversion of thyroxine to 3,3',5'-triiodothyronine (reverse-T3) by a soluble enzyme system of rat liver

Infrared spectra of N₂O in a variety of solvents and in the brain of a dog under typical conditions of halothane-N₂O anesthesia have been determined. The appearance or disappearance of N₂O in the brain was readily followed as N₂O was administered or withdrawn. The sites in brain were of two major types; one, with ν₃ = 2229.8 ± 0.4 cm^?1 and $\text{Δν}{}_{\mathrm{<mtext>1</mtext><mtext>2</mtext>}}\text{= 13.0 ± 0.6}\text{cm}{}^{\mathrm{?1}}$, is rather like the polar site in water and the other, with ν₃ = 2216.8 ± 0.8 cm^?1 and $\text{Δν}{}_{\mathrm{<mtext>1</mtext><mtext>2</mtext>}}\text{= 9.6 ± 1.0}\text{cm}{}^{\mathrm{?1}}$, is non-polar and is probably associated with membrane lipid. The significant variations in the antisymmetric stretch (ν₃) of N₂O as the polarity and other properties of the medium (solvent) vary make possible the characterization of $\text{in tissue}$ sites occupied by this anesthetic.