Gene/Protein Disease Symptom Drug Enzyme Compound
Pivot Concepts:   Target Concepts:
Query: EC:1.11.1.7 (peroxidase)
 65,474 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

The effect of brain lesion or surgical isolation of the neural circuit on SWS and PS circadian rhythm have been studied in female rats under a 14/10 light-dark schedule. Cortical EEG'S AND DORSAL NECK EMG were used to monitor SWS, PS and alertness in female rats. Intact and operated controls showed regular 4-5-day vaginal cycles and nocturnal sleep rhythm, but the night PS value on proestrus was lower than in other cycles. Following septal lesion, MPO roof cut, vaginal cycles and SWS rhythm were regularly maintained; however, the PS appearance at night, except during proestrus, increased (night PS peak). These results were similar to those for pinealectomized or ovariectomized female rats. A frontal cut of the MBH produced persistent estrus and disturbed both SWS and PS circadian rhythm. The suprachiasmatic-lesioned rats showed persistent estrus and disrupted SWS rhythm, but regularly maintained the circadian PS rhythm. The vaginal cycles and SWS rhythm in the fornical-transected rats were regularly maintained, but the PS rhythm was disturbed during diestrus and showed ultradian rhythm. From these results, it is suggested that the pineal hormone and the gonadal feedback mechanisms may be involved in the night PS peak and this mechanism may involve the septal- and amygdaloid-hypothalamic systems. A different neural mechanism exist for SWS and PS circadian rhythm; SWS rhythm involves the suprachiasmatic-basal hypothalamic system and PS circadian rhythm is related, in part, to the hippocampal-hypothalamic system.
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PMID:Participation of limbic-hypothalamic structures in circadian rhythm of slow wave sleep and paradoxical sleep in the rat. 20 63

One-month-old male Sprague-Dawley rats maintained for 19 weeks on a low selenium diet with or without supplementation of 2.0 ppm selenium were injected intraperitoneally with either 500 mg PCB (Aroclor 1254)/kg body weight or placebo 5 days prior to sacrifice. In addition to aryl hydrocarbon hydroxylase (AHH) activity, PCB treatment also caused a significant increase in hepatic levels of thiobarbituric acid reactants (TBAR), reduced glutathione (GSH), GSH-peroxidase, GSH reductase, glucose-6-phosphate dehydrogenase (G-6-PD), and GSH-S-transferase in rats on the low selenium diet. The non-selenium-dependent form of GSH peroxidase was mainly responsible for the increase of hepatic GSH peroxidase upon PCB treatment. Only the activities of AHH, GSH-S-transferase, and G-6-PD were significantly higher in the liver of PCB-treated rats fed the selenium-supplemented diet. In contrast, except for AHH activity, the lung GSH and related enzymes were not significantly affected by PCB in either of the two dietary groups. The results suggest that dietary selenium deprivation renders the livers of rats more sensitive to PCB effects.
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PMID:Influence of dietary selenium on the hepatic and pulmonary enzymes in polychlorobiphenyls-treated rats. 681 90

The effects of structure on the estrogenicity and antiestrogenicity of hydroxylated polychlorinated biphenyls were investigated using the following estrogen-sensitive assays: competitive binding to the rat and mouse cytosolic estrogen receptor (ER); immature rat and mouse uterine wet weight, peroxidase and progesterone receptor (PR) levels; induction of luciferase activity in HeLa cells stably transfected with a Gal4:human ER chimera and a 17mer-regulated luciferase reporter gene; proliferation of MCF-7 human breast cancer cells; induction of chloramphenicol acetyl transferase (CAT) activity in MCF-7 cells transiently transfected with a full-length human ER expression plasmid and a plasmid containing an estrogen-responsive vitellogenin A2 promoter linked to a CAT reporter gene. The chemicals synthesized for this study contained a 4-hydroxy group in one ring, a 2- or 3-chloro substituent meta or ortho to the hydroxyl group, and variable substitution (2',3',4',5'-, 2',3',4',6'-, 2',3',5',6'-tetrachloro and 2',4',6'-trichloro) in the chlorophenyl ring. The compounds included: 2,2',3',4',5'- (A), 2,2',3',4',6'- (B), and 2,2',3',5',6'-pentachloro- (C); 2,2',4',6'-tetrachloro-4-biphenylol (D); 2',3,3',4',5'- (E), 2',3,3',4',6'- (F), and 2',3,3',5',6'-pentachloro (G); and 2',3,4',6'-tetrachloro-4-biphenylol (H). With the exception of 2',3,4',6'-tetrachloro-4-biphenylol (H), all of the compounds competitively bound to the mouse and rat ER with relative binding affinities [compared to 17beta-estradiol (E2)] varying from 1.4 x 10(-3) to 5.3 x 10(-5). The structure-ER binding relationships for the hydroxy-PCB congeners were different in the rat and mouse, and no dose-dependent estrogenic activities were observed in the mouse or rat uterus. Several hydroxy-PCB congeners exhibited antiestrogenic activity (primarily in the mouse uterus) and two compounds, 2,2',3',5',6- and 2,2',3',4',6'-pentachloro-4-biphenylol, inhibited E2-induced uterine wet weight, PR binding, and peroxidase activity in the mouse uterus. 2,2',3',4',5'- and 2,2',3',4',6'-Pentachloro-4-biphenylol induced CAT activity in MCF-7 cells transiently transfected with the Vit-CAT plasmid; the remaining congeners did not induce CAT activity but exhibited antiestrogenic activity in MCF-7 cells cotreated with 10(-9) E2 plus 10(-5) M hydroxy-PCBs. Complementary structure-estrogenicity relationships were observed utilizing the HeLa cell luciferase induction and MCF-7 cell proliferation assays. The placement of the 2- or 3-chloro groups in the phenolic ring had minimal effects on estrogenic activity, whereas 2,4,6-trichloro- and 2,3,4,6-tetrachloro substitution in the chlorophenyl ring (B, D, F, and H) were required for this response. Substitution in the phenolic ring was also not important for structure-antiestrogenicity relationships, and the most active compounds (A, C, E, and G) contained 2',3',4',5'- and 2',3',5',6'-tetrachlorophenyl groups. Thus, structure-estrogenicity/antiestrogenicity relationships for this series of hydroxy-PCBs were complex and response-specific.
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PMID:Hydroxylated polychlorinated biphenyls (PCBs) as estrogens and antiestrogens: structure-activity relationships. 922 30

The ability of Phanerochaete chrysosporium, Trametes versicolor, Coriolopsis polyzona, and Pleurotus ostreatus growing in a mitogen-limited mineral medium (NMM) to degrade PCBs in a commercial, Delor 106 mixture at a concentration of 0.9 ppm was compared. The respective amount of PCBs removed from the fungal cultures within 3 weeks were 25, 50, 41 and 0%. The capacities of the individual fungal species to remove PCBs correlated to some extent with their capabilities of decolorization of NMM agar containing both Poly R-478 or Remazol Brilliant Blue R dyes. Enzyme estimations indicated that both high and relatively stable activities of Mn-dependent peroxidase, Mn-independent peroxidase, lignin peroxidase, and laccase characterized efficient PCB degraders.
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PMID:Removal of PCBs by various white rot fungi in liquid cultures. 934 Mar 10

The estrogenic activity of 2',4',6'-trichloro-4-biphenylol (HO-PCB3), 2',3',4',5'-tetrachloro-4-biphenylol (HO-PCB4), and an equimolar mixture of both compounds (HO-PCB3/HO-PCB4) was investigated in the 21-day-old B6C3F1 mouse uterus, MCF-7 and MDA-MB-231 human breast cancer cells, HepG2 cells, and in a yeast-based reporter gene assay. Treatment of the animals with 17beta-estradiol (E2) (0.02 microg/kg/day x3) resulted in increased uterine wet weight, peroxidase activity and progesterone receptor binding. Treatment with 18, 73, 183 or 366 micromol/kg (x3) doses of HO-PCB3, HO-PCB4, or HO-PCB3/HO-PCB4 (equimolar) caused a dose-dependent increase in estrogenic activity; a maximal-induced response was not observed at any dose and the activity of the mixture was additive. Binding of E2, HO-PCB3, HO-PCB4, and HO-PCB3/HO-PCB4 to the mouse uterine estrogen receptor (ER) was determined in a competitive binding assay using [3H]E2 as the radioligand. The IC50 values were 1.1 x 10(-8), 3.4 x 10(-6), 9.9 x 10(-7), and 4.25 x 10(-6) m, respectively. HO-PCB3 and HO-PCB4 maximally induced MCF-7 cell proliferation, rat creatine kinase, and human complement C3 (C3-LUC) reporter gene activity at concentrations of 10(-5) to 10(-6) m, and these compounds were 10(3) to 10(4) less potent than E2. The HO-PCB3/HO-PCB4 mixture was active at the high concentration (10(-5) m) and was additive for these responses. HO-PCB3 and HO-PCB4 also exhibited estrogenic activity in human HepG2 cells cotransfected with C3-LUC and an ER expression plasmid, and the estrogenic activity of the HO-PCB mixture was additive. Similar results were obtained in yeast transformed with the human ER and a double estrogen responsive element upstream of the beta-gal reporter gene. The effects of variable ER expression on the potential synergistic interactions of HO-PCB3/HO-PCB4 were investigated in HepG2 cells cotransfected with C3-LUC (405 ng/well) and variable amounts of ER expression plasmid (270, 27, 2.7, or 0.27 ng/well). The results show that as ER levels decreased, the magnitude of the induction response by E2, HO-PCB3, HO-PCB4, and HO-PCB3/HO-PCB4 also decreased. However, the activities of the HO-PCB mixture were additive at high and low levels of ER. Similar results were obtained in MDA-MB-231 cells cotransfected with C3-LUC and variable amounts of ER expression plasmid. The results of this study demonstrate that for several estrogen-responsive assays in the mouse uterus; MCF-7, HepG2, and MDA-MBA-231 human cancer cells; and a yeast based-reporter gene assay, both HO-PCB3 and HO-PCB4 exhibited estrogenic activity. The estrogenic activity of an equimolar mixture of these compounds was additive at high and low levels of ER expression.
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PMID:Additive estrogenic activities of a binary mixture of 2',4',6'-trichloro- and 2',3',4',5'-tetrachloro-4-biphenylol. 935 11

NADH chemistry ancillary to the oscillatory peroxidase-oxidase (PO) reaction has been reexamined. Previously, (NAD)2 has been thought of as a terminal, inert product of the PO reaction. We now show that (NAD)2 is a central reactant in this system. Although we found traces of the dimer after several hours of the PO reaction, no accumulation of the dimer occurred, regardless of the reaction time or the number of oscillations. (NAD)2 can convert horseradish peroxidase (HRP) compound I (CpI) to compound II (CpII) with apparent rate constant (2.7 +/- 0.2) x 105 M-1.s-1 and CpII to HRP at 1 x 105 M-1.s-1. Moreover, a reduction of HRP compound III (CpIII) to CpI by (NAD)2 occurs with a rate constant faster than 5 x 106 M-1.s-1. The (NAD)2 reduction of CpIII provides an alternative to the reduction by NAD radical suggested by Yokota and Yamazaki. HRP catalyzes oxidation of alpha-NADH, not only the beta anomer as previously assumed. Rate constants of alpha- and beta-NADH reactions with CpI are (7.4 +/- 0.4) x 105 M-1.s-1, and (1.7 +/- 0.2) x 105 M-1.s-1, and with CpII are estimated as 5 x 104 M-1.s-1, and 4 x 104 M-1.s-1. Apparent rate constants of reduction of methylene blue (MB) to leuco-methylene blue (MBH) are 3.8 x 104 M-1.s-1 for NADH and 6.4 x 104 M-1.s-1 for NAD dimer, (NAD)2, while reoxidation of MBH proceeds at (2.1 +/- 0.2) x 103 M-1.s-1 All the rates were measured in 0.1 M acetate buffer, pH 5.1.
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PMID:Nicotinamide adenine dinucleotide species in the horseradish peroxidase-oxidase oscillator. 1093 Nov 83

It is known that lower-chlorinated biphenyls are metabolically activated to electrophilic quinoid species capable of binding to DNA. Also, certain metabolites are capable of redox cycling, thereby increasing oxidative stress in biological systems. In the present study, we tested mono-, di-, tri-, tetra-, penta-, hexa-, and heptachlorinated biphenyls for their ability to bind with DNA and to induce oxidative DNA damage. We present additional evidence that several PCB congeners form DNA adducts after metabolic activation, which can be detected by the nuclease P1- or butanol-enrichment procedures of the (32)P-postlabeling technique. Butanol and nuclease P1 enrichments showed different adduct recoveries, depending on the level of chlorination of the biphenyls. Application of the nuclease P1 enrichment showed that the incubation of 2-chloro-; 3, 4-dichloro-; 2,4,4'-trichloro-; 3,4,5-trichloro-; and 2,2',5, 5'-tetrachlorobiphenyl with calf thymus DNA and liver microsomes from rats treated with phenobarbital, followed by oxidation with a peroxidase, produced five to eight different DNA adducts. For these lower-chlorinated biphenyls, butanol enrichment generally showed a lower recovery. For some higher substituted congeners (3,3',4,4', 5-pentachloro-, 2,2',3,4,4',5'-hexachloro-, 2,2',4,4',5, 5'-hexachloro-, and 2,2',3,4,4',5,5'-heptachlorobiphenyl), after butanol enrichment a single dominant spot was observed, which was absent in the nuclease P1 procedure. After incubation of calf thymus DNA with either higher- or lower-chlorinated PCB congeners, we were not able to detect significantly increased levels of oxidative DNA damage above background levels, measured as 8-oxo-7, 8-dihydro-2'deoxyguanosine. In view of the carcinogenicity of PCB mixtures in animals and the ability of PCB metabolites to bind covalently to DNA, rats were orally treated with a mixture of PCBs (Aroclor 1242). PCB-DNA adduct levels were analyzed in PCB target organs: liver, thymus, glandular stomach, spleen, testes, seminal vesicles and prostate DNA. In vivo PCB-DNA adducts could not be detected by either the butanol- or by the NP1-enrichment procedure in rat target tissue DNA. Also, no differences in oxidative DNA damage could be observed between PCB-treated rats and controls. These results indicate a lack of DNA reactivity of PCB mixtures in vivo.
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PMID:Induction of DNA adducts by several polychlorinated biphenyls. 1101 5

The enzyme-induced decomposition and biodegradation of PCB were investigated. 2,5-Dichlorobiphenyl (PCB 9) and 2,2',5,5'-tetrachlorobiphenyl (PCB 52) were used as example compounds to study efficiency and mechanism of the degradation processes. It was found that the application of horseradish peroxidase (HRP) together with defined amounts of hydrogen peroxide removed 90%, of the initial concentration of PCB 9 and 55% of the initial concentration of PCB 52 from an aqueous solution after a reaction period of 220 min. Dechlorination was observed as the initial step. Although the metabolites identified were mainly chlorinated hydroxybiphenyls, benzoic acids and non-substituted 1,1'-biphenyl, some higher chlorinated biphenyl isomers also appeared. The biodegradation of PCB 9 using the white rot fungus Trametes multicolor took about four weeks and reduction was about 80%, of the initial concentration. The metabolites produced (dichlorobenzenes, chlorophenols and alkylated benzenes) were not quite the same as those observed upon incubation with HRP.
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PMID:Peroxidative degradation of selected PCB: a mechanistic study. 1106 4

The ability of the ligninolytic fungus Trametes trogii to degrade in vitro different xenobiotics (PCBs, PAHs and dyes) was evaluated. Either 200 ppm of a PCB mixture (Aroclor 1150) or 160 ppm of an industrial PAH mixture (10% V/V of PAHs, principal components hexaethylbenzene, naphthalene, 1-methyl naphthalene, acenaphthylene, anthracene, fluorene and phenanthrene), were added to trophophasic and idiophasic cultures growing in a nitrogen limited mineral medium (glucose/asparagine) and in a complex medium (malt extract/glucose). Gas-liquid chromatography proved that within 7 to 12 d more than 90% of the organopollutants added were removed. The decrease in absorbance at 620 nm demonstrated that cultures of this fungus were able to transform 80% of the dye Anthraquinone-blue (added at a concentration of 50 ppm) in 1.5 h. Enzyme estimations indicated high activity of laccase (up to 0.55 U/mL), as well as lower production of manganese-peroxidase. Laccase activity, detected in all the conditions assayed, could be implicated in the degradation of these organopollutants. Considering the results obtained, T. trogii seems promising for detoxification.
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PMID:Degradation of environmental pollutants by Trametes trogii. 1241 98

Two wetland plant species, Phragmites australis and Oryza sativa, were grown in a glasshouse under hydroponics conditions. Enzyme extracts from different parts of the plants were used to determine the transformation rate of o,p'-DDT, p,p'-DDT and PCBs. The organic pollutants were directly spiked into the enzyme extracts, and samples were collected every 30 min and analyzed with a GC-ECD. Root extracts of P. australis readily degraded and transformed DDT and some PCB congeners with a low degree of chlorination. In contrast, crude extracts of O. sativa showed no appreciable degradation or transformation of DDT or PCBs. Inhibition studies indicated that the degradation and transformation of both DDT and PCBs by P. australis enzymes were partly mediated by peroxidase and the plant P-450 system. PCBs with a high degree of chlorination were highly resistant to transformation or degradation by plant enzymes. Both wetland plant species accumulated substantial quantities of the persistent organic chemicals but had different degradation capacities. The enzyme systems in P. australis were much more effective that those in rice in the degradation and transformation of the organic pollutants.
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PMID:Accumulation, distribution and transformation of DDT and PCBs by Phragmites australis and Oryza sativa L.: II. Enzyme study. 1654 64


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