Catalysis of the Haber-Weiss reaction by iron-diethylenetriaminepentaacetate.

To help settle controversy as to whether the chelating agent diethylenetriaminepentaacetate (DTPA) supports or prevents hydroxyl radical production by superoxide/hydrogen peroxide systems, we have reinvestigated the question by spectroscopic, kinetic, and thermodynamic analyses. Potassium superoxide in DMSO was found to reduce Fe(III)DTPA. The rate constant for autoxidation of Fe(II)DTPA was found (by electron paramagnetic resonance spectroscopy) to be 3.10 M-1 s-1, which leads to a predicted rate constant for reduction of Fe(III)DTPA by superoxide of 5.9 x 10(3) M-1 s-1 in aqueous solution. This reduction is a necessary requirement for catalytic production of hydroxyl radicals via the Fenton reaction and is confirmed by spin-trapping experiments using DMPO. In the presence of Fe(III)DTPA, the xanthine/xanthine oxidase system generates hydroxyl radicals. The reaction is inhibited by both superoxide dismutase and catalase (indicating that both superoxide and hydrogen peroxide are required for generation of HO.). The generation of hydroxyl radicals (rather than oxidation side-products of DMPO and DMPO adducts) is attested to by the trapping of alpha-hydroxethyl radicals in the presence of 9% ethanol. Generation of HO. upon reaction of H2O2 with Fe(II)DTPA (the Fenton reaction) can be inhibited by catalase, but not superoxide dismutase. The data strongly indicate that iron-DTPA can catalyze the Haber-Weiss reaction.     

Cellobiose dehydrogenase (cellobiose oxidase) from Phanerochaete chrysosporium as a wood-degrading enzyme. Studies on cellulose,xylan and synthetic lignin

Degradation of carboxymethylcellulose (CMC), xylan and synthetic lignin was studied in a cellobiose dehydrogenase system, that reduced Fe(III) to Fe(II) with cellobiose as electron donor, which in the presence of hydrogen peroxide degraded all the above representatives of the main wood components, probably by forming Fenton's reagent. The production of hydroxyl radicals was shown by benzoate decarboxylation. For the CMC and xylan studies viscometry was used, while lignin degradation was studied by measuring the passage of ¹⁴C-labelled synthetic lignin (DHP) through membranes of different molecular-mass cut-off. The possible participation of cellobiose dehydrogenase, Fe(III) and hydrogen peroxide in wood degradation by white-rot and brown-rot fungi is discussed.     

Hemoglobin: A mechanism for the generation of hydroxyl radicals

Oxyhemoglobin (HbO₂) reduces Fe(III) NTA aerobically to become methemoglobin (metHb) and Fe(II)NTA. These conditions are favorable for the generation via Fenton chemistry of the hydroxyl radical that was measured by HPLC using salicylate as a probe. The levels of hydroxyl radicals generated are a function of both the percent metHb formed and the chemical nature of the buffer. The rates of formation of both metHb and hydroxyl radicals were dependent upon the concentration of Fe(III)NTA. Of the buffers tested, HEPES was the most effective scavenger of hydroxyl radicals while the other buffers scavenged in the order: HEPES > Tris > MOPS > NaCl ≈ unbuffered. The addition of catalase to remove H₂0₂ or bathophenanthroline to chelate Fe(II) inhibited virtually all hydroxyl radical formation. Carbonyl formation from free radical oxidation of amino acids was found to be 0.1 mol/mol of hemoglobin. These experiments demonstrate the ability of hemoglobin to participate directly in the generation of hydroxyl radicals mediated by redox metals, and provide insight into potential oxidative damage from metals released into the blood during some pathologic disorders including iron overload.     

Carbohydrate oxidases in ericoid and ectomycorrhizal fungi: a possible source of Fenton radicals during the degradation of lignocellulose

Isolates of the ericoid mycorrhizal fungus Hymenoscyphus ericae (Read) Korf et Kernan, and the ectomycorrhizal fungi Suillus variegatus (Swartz ex Fr.) and Pisolithus tinctorius (Pers.) Coker & Couch, along with a Cortinarius sp. and the white rot Phanerochaete chrysosporium Burdsall were examined for the ability to oxidize carbohydrates to their corresponding lactones and to excrete the H₂O₂ produced thereby. All except Phanerochaete chrysosporium were found to express cellobiose oxidase (cellobiose dehydrogenase, EC 1.1.19.88) and glucose oxidase (β- d -glucose:oxygen 1-oxidoreductase, EC 1.1.3.4) when grown on cellobiose and glucose respectively. Production of extracellular H₂O₂ was visualized during growth on both substrates using ABTS as the chromogen. According to the Fenton reaction, H₂O₂ will react with hydrated or chelated Fe(II) in the environment to produce hydroxyl (Fenton) radicals, HO^·. Mycelial extracts from each of the mycorrhizal fungi produced HO^· in the presence of cellobiose and Fe(II), presumably mediated by H₂O₂ produced by cellobiose oxidase activity in the extracts. Conditions favourable to HO^· production were shown to exist in Modified Melin–Norkrans medium, and the data discussed in relation to previously observed lignin degradation by mycorrhizal fungi.     

Site-specific DNA damage induced by hydrazine in the presence of manganese and copper ions. The role of hydroxyl radical and hydrogen atom.

The mechanism of DNA damage by hydrazine in the presence of metal ions was investigated by DNA sequencing technique and ESR-spin trapping method. Hydrazine caused DNA damage in the presence of Mn(III), Mn(II), Cu(II), Co(II), and Fe(III). The order of inducing effect on hydrazine-dependent DNA damage (Mn(III) greater than Mn(II) approximately Cu(II) much greater than Co(II) approximately Fe(III)) was related to that of the accelerating effect on the O2 consumption rate of hydrazine autoxidation. DNA damage by hydrazine plus Mn(II) or Mn(III) was inhibited by hydroxyl radical scavengers and superoxide dismutase, but not by catalase. On the other hand, bathocuproine and catalase completely inhibited DNA damage by hydrazine plus Cu(II), whereas hydroxyl radical scavengers and superoxide dismutase did not. Hydrazine plus Mn(II) or Mn(III) caused cleavage at every nucleotide with a little weaker cleavage at adenine residues, whereas hydrazine plus Cu(II) induced piperidine-labile sites frequently at thymine residues, especially of the GTC sequence. ESR-spin trapping experiments showed that hydroxyl radical is generated during the Mn(III)-catalyzed autoxidation of hydrazine, whereas hydrogen atom adducts of spin trapping reagents are generated during Cu(II)-catalyzed autoxidation. The results suggest that hydrazine plus Mn(II) or Mn(III) generate hydroxyl free radical not via H2O2 and that this hydroxyl free radical causes DNA damage. A possibility that the hydrogen atom releasing compound participates in hydrazine plus Cu(II)-induced DNA damage is discussed.     

The cellobiose-oxidizing enzymes CBQ and CbO as related to lignin and cellulose degradation — a review

Abstract: In this review properties of cellobiose:quinone oxidoreductase (CBQ) and cellobiose oxidase (CbO) are presented and their possible involvement in lignin and cellulose degradation is discussed. Although these enzymes are produced by many different fungi, their importance for wood-degrading fungi is the topic here. CBQ is a FAD enzyme, while CbO also contains a heine group of the cytochrome b type. Protease activity is reported to convert CbO to CBQ. During oxidation of cellobiose (emanating from cellulose) to cellobiono-l,5-lactone, both enzymes reduce quinones produced by laccase and peroxidase during lignin degradation to the corresponding phenols. Many phenoxy and cation radicals are also reduced. Quinone reduction is more rapid than oxygen reduction, although oxygen is slowly reduced to superoxide and/or hydrogen peroxide. Thus, a more appropriate name for CbO is cellobiose dehydrogenase. CbO also reduces Fe(III) and together with hydrogen peroxide produced by the enzyme Fenton's reagent may be formed, resulting in hydroxyl radical production. This radical can degrade both lignin and cellulose, possibly indicating that cellobiose oxidase has a central role in degradation of wood by wood-degrading fungi.     

The Autoxidation of Iron(Ii) in Aqueous Systems: The Effects of Iron Chelation by Physiological, Non-Physiological and Therapeutic Chelators on the Generation of Reactive Oxygen Species and the Inducement of Biomolecular Damage

The ability of various iron(II)-complexes of biological, clinical and chemical interest to reduce molecular oxygen to reactive oxy-radicals has been investigated using complementary oxygen-uptake studies and e.s.r. techniques. It is demonstrated that although the rate of oxygen reduction by a given iron complex is directly related to its redox potential [thus complexes with low values of E⁰ for the Fe(III)/Fe(II) couple are the most effective reductants of oxygen], the overall ability of an iron(II) complex to induce oxidative biomolecular damage is also determined by its ability to undergo redox-cycling reactions with reducing radicals formed following the reaction of hydroxyl radicals with organic substrates present in the system (e.g. metal-ion chelators and organic buffers). Evidence is presented to suggest that the “Good” buffer MOPS forms a reducing radical following attack by -OH, and hence encourages the autoxidation of iron with the generation of oxy-radicals (as also observed for some of the chelates studied); this may have important implications for the use of such buffers in free-radical studies.     

Comparative study of the formation of oxidative damage marker 8-hydroxy-2'-deoxyguanosine (8-OHdG) adduct from the nucleoside 2'-deoxyguanosine by transition metals and suspensions of particulate matter in relation to metal content and redox reactivity

An association between exposure to ambient particulate matter (PM) and increased incidence of mortality and morbidity due to lung cancer and cardiovascular diseases has been demonstrated by recent epidemiological studies. Reactive oxygen species (ROS), especially hydroxyl radicals, generated by PM, have been suggested by many studies as an important factor in the oxidative damage of DNA by PM. The purpose of this study was to characterize quantitatively hydroxyl radical generation by various transition metals in the presence of H₂O₂ in aqueous buffer solution (pH 7.4) and hydroxylation of 2'-deoxyguanosine (dG) to 8-hydroxy-2'-deoxyguanosine (8-OHdG) under similar conditions. The order of metals' redox reactivity and hydroxyl radical production was Fe(II), V(IV), Cu(I), Cr(III), Ni(II), Co(II), Pb(II), Cd(II). Then, we investigated the generation of hydroxyl radicals in the presence of H₂O₂ by various airborne PM samples, such as total suspended particulate (TSP), PM₁₀, PM_2.5 (PM with aerodynamic diameter 10 and 2.5 μm), diesel exhaust particles (DEP), gasoline exhaust particles (GEP) and woodsmoke soot under the same conditions. When suspensions of PMs were incubated with H₂O₂ and dG at pH 7.4, all particles induced hydroxylation of dG and formation of 8-OHdG in a dose-dependent increase. Our findings demonstrated that PM's hydroxyl radical (HO√) generating ability and subsequent dG hydroxylation is associated with the concentration of water-soluble metals, especially Fe and V and other redox or ionizable transition metals and not their total metal content, or insoluble metal oxides, via a Fenton-driven reaction of H₂O₂ with metals. Additionally, we observed, by Electron paramagnetic resonance (EPR), that PM suspensions in the presence of H₂O₂ generated radical species with dG, which were spin-trapped by 2-methyl-2-nitroso-propane (MNP).     

Mechanism of reaction of a suggested superoxide-dismutase mimic, Fe(II)-N,N,N',N'-tetrakis(2-pyridylmethyl)ethylenediamine.

The interaction of a recently developed intracellular superoxide dismutase analogue, Fe(II)-N,N,N',N'-tetrakis(2- pyridylmethyl)ethylenediamine (Fe(II)-TPEN), with reactive oxygen species was investigated under in vitro conditions. The complex catalyzed the dismutation of enzyme- or radiolysis-generated superoxide with the production of H2O2; under steady-state conditions the equilibrium was strongly shifted toward Fe(III)-TPEN. Fe(II)-TPEN reacted with H2O2 to generate hydroxyl radicals in a Fenton reaction. The oxidized Fe(III)-TPEN was readily reduced by ascorbate or glutathione. Given the capacity to produce hydroxyl radicals and the reaction with cellular reductants it seems unlikely that Fe-TPEN may find widespread use as an intracellular superoxide dismutase substitute.     

Inactivation of alcohol dehydrogenase by piroxicam-derived radicals

Alcohol dehydrogenase (ADH) was used as a marker molecule to clarify the mechanism of gastric mucosal damage as a side effect of using piroxicam. Piroxicam inactivated ADH during interaction of ADH with horseradish peroxidase and H₂O₂ (HRP-H₂O₂). The ADH was more easily inactivated under aerobic than anaerobic conditions, indicating participation by oxygen. Superoxide dismutase, but not hydroxyl radical scavengers, inhibited inactivation of ADH, indicating participation by superoxide. Sulfhydryl (SH) groups in ADH were lost during incubation of piroxicam with HRP-H₂O₂. Adding reduced glutathione (GSH) efficiently blocked ADH inactivation. Other SH enzymes, including creatine kinase and glyceraldehyde-3-phosphate dehydrogenase, were also inactivated by piroxicam with HRP-H₂O₂. Thus SH groups in the enzymes seem vulnerable to piroxicam activated by HRP-H₂O₂. Spectral change in piroxicam was caused by HRP-H₂O₂. ESR signals of glutathionyl radicals occurred during incubation of piroxicam with HRP-H₂O₂ in the presence of GSH. Under anaerobic conditions, glutathionyl radical formation increased. Thus piroxicam free radicals interact with GSH to produce glutathionyl radicals. Piroxicam peroxyl radicals or superoxide, or both, seem to inactivate ADH. Superoxide may be produced through interaction of peroxyl radicals with H₂O₂. Thus superoxide dismutase may inhibit inactivation of ADH through reducing piroxicam peroxyl radicals or blocking interaction of SH groups with O₂^-, or both. Other oxicam derivatives, including isoxicam, tenoxicam and meloxicam, induced ADH inactivation in the presence of HRP-H₂O₂.     

Reactions of captopril and epicaptopril with transition metal ions and hydroxyl radicals: An EPR spectroscopy study

In the present study, using the technique of EPR spin trapping with DMPO a spin trap, we demonstrated formation of thiyl radicals from thiol-containing angiotensin converting enzyme (ACE) inhibitor captopril (CAP) and from its stereoisomer epicaptopril (EPICAP), a non-ACE inhibitor, in the process of ^.OH radical scavenging. Splitting constants of DMPO/thiyl radical adducts were identical for both thiols and were a_N = 15.3 G, and a_H = 16.2 G. Bimolecular rate constants for the reaction of CAP and EPICAP with ^.OH radicals were close to a diffusion-controlled rate (≈ 2 × 10¹⁰ M⁻¹s⁻¹). Our data also show that both CAP and EPICAP reduce Fe(III) ions and that their respective thiyl radicals are formed in this reaction. In the presence of Fe(III), H₂O₂, and CAP, or EPICAP, ^.OH radicals were produced by a thiol-driven Fenton mechanism. Copper(II) ions were also reduced by these thiols, but no thiyl radicals could be detected in these reactions, and no ^.OH or other Fenton oxidants were observed in the presence of H₂O₂. Our data show direct evidence that thiol groups of CAP and EPICAP are involved in scavenging of ^.OH radicals. The direct ^.OH radical scavenging, together with the reductive “repair” of other sites of ^.OH radical attack, may contribute to the known protective effect of CAP against ischemia/reperfusion-induced arrhythmias. The formation of reactive thiyl radicals in the reactions of the studied compounds with ^.OH radicals and with Fe(III) ions may play a role in some of the known adverse effects of CAP.     

Formation of dioxygen complexes of transition metal chelates in oxygen saturated aprotic solvents. Cyclic voltammetric evidence at a micro glassy carbon disk electrode

Cyclic voltammetry at a micro electrode of Co(II) salen, Fe(II) salen, electrode generated Fe(II)(acac)₂, Fe(II) (salicylaldehyde)₂, Fe(II) (salicylaldoxime)₂, Fe(II) (bipy)₃, Fe(II) (bipy)₂, Co(II) (bipy)₃, Co(II) (benzacac)₂, and electrode generated Co(acac)₂ in oxygen saturated aprotic solvents show positive shift of the O₂ sigmoidal wave, as well as enhancement of the limiting current in the case of the first five compounds. In the case of Co(II) (bipy)₃ the slope of the sigmoidal wave due to O₂ becomes more positive, while for the other two Co(II) complexes there is no change except a small decrease in the wave height. The data are used to correlate and predict the O₂ binding properties of the chelates in solution. The data for the diketone complexes of Co(II) indicate absence of any direct association, which is in line with the interpretation offered in the literature on the mechanism of their catalytic role in the O₂ oxidation of substrates. The mechanism of the autoxidation of dimethylformamide in the presence of Fe(III) (bipy)₃ and Cu(II) (bipy)₂ is elucidated by the observation that these higher valent compounds are reduced to their next lower oxidation state by DMF.     

The role of iron in oxygen radical mediated lipid peroxidation

The role of iron in the peroxidation of polyunsaturated fatty acids is reviewed, especially with respect to the involvement of oxygen radicals. The hydroxyl radical can be generated by a superoxide-driven Haber-Weiss reaction or by Fenton's reaction; and the hydroxyl radical can initiate lipid peroxidation. However, lipid peroxidation is frequently insensitive to hydroxyl radical scavengers or superoxide dismutase. We propose that the hydroxyl radical may not be involved in the peroxidation of membrane lipids, but instead lipid peroxidation requires both Fe2+ and Fe3+. The inability of superoxide dismutase to affect lipid peroxidation can be explained by the fact that the direct reduction of iron can occur, exemplified by rat liver microsomal NADPH-dependent lipid peroxidation. Catalase can be stimulatory, inhibitory or without affect because H2O2 may oxidize some Fe2+ to form the required Fe3+, or, alternatively, excess H2O2 may inhibit by excessive oxidation of the Fe2+. In an analogous manner reductants can form the initiating complex by reduction of Fe3+, but complete reduction would inhibit lipid peroxidation. All of these redox reactions would be influenced by iron chelation.     

Redox Properties of Iron in the Binding Site(s) of F1ATPase from Mammalian Mitochondria and Thermophilic Bacterium PS3: A Comparative Study

Iron ions in the two iron centers of beef heart mito-chondrial F, ATPase, which we have been recently characterized (FEBS Letters 1996,379, 231-235), exhibit different redox properties. In fact, the ATP-dependent site is able to maintain iron in the redox state of Fe(II) even in the absence of reducing agents, whereas in the nucleotide-independent site iron is oxidized to Fe(III) upon removal of the reductant. Fe(III) ions in the two sites display different reactivity towards H₂O₂, because only Fe(III) bound in the nucleotide-independent site rapidly reacts with H₂O₂ thus mediating a 30% enzyme inactivation. Thermophilic bacterium PS3 bears one Fe(III) binding site, which takes up Fe(III) either in the absence or presence of nucleotides and is unable to maintain iron in the redox state of Fe(II) in the absence of ascorbate. Fe(III) bound in thermophilic F₁ATPase in a molar ratio 1:1 rapidly reacts with H₂O₂ mediating a 30% enzyme inactivation. These results support the presence in mitochon-drial and thermophilic F₁ATPase of a conserved site involved in iron binding and in oxidative inactivation, in which iron exhibits similar redox properties. On the other hand, at variance with thermophilic F₁ATPase, the mitochondrial enzyme has the possibility of maintaining one equivalent of Fe(II) in its peculiar ATP-dependent site, besides one equivalent of Fe(III) in the conserved nucleotide-independent site. In this case mitochondrial F, ATPase undergoes a higher inactivation (75%) upon exposure to H₂O₂. Under all conditions the inactivation is significantly prevented by PBN and DMSO but not by Cu, Zn superoxide dis-mutase, thus suggesting the formation of OH radicals as mediators of the oxidative damage. No dityrosines, carbonyls or oxidized thiols are formed. In addition, in any cases no protein fragmentation or aggregation is observed upon the treatment with H₂O₂.     

The role of superoxide and hydroxyl radicals in phospholipid peroxidation catalysed by iron salts

Iron(II) salts in aqueous solution, or iron(III) salts in the presence of an O√⁻₂ generating system, can activate dioxygen to produce hydroxyl radicals. These are detected indirectly by their ability to degrade deoxyribose with the formation of thiobarbituric acid-reactive (TBA) products. Iron salts also catalyse the peroxidation of phospholipids resulting in the formation of TBA-reactive products. Hydroxyl radicals were responsible for the degradation of deoxyribose but not for the observed peroxidation of phospholipid. The function of O√⁻₂ in both deoxyribose degradation and phospholipid peroxidation seems to be that of reducing iron(III) into iron(II).     

Cobalt-mediated generation of reactive oxygen species and its possible mechanism

Electron spin resonance spin trapping was utilized to investigate free radical generation from cobalt (Co) mediated reactions using 5,5-dimethyl-l-pyrroline (DMPO) as a spin trap. A mixture of Co with water in the presence of DMPO generated 5,5-dimethylpyrroline-(2)-oxy(1) DMPOX, indicating the production of strong oxidants. Addition of superoxide dismutase (SOD) to the mixture produced hydroxyl radical (OH). Catalase eliminated the generation of this radical and metal chelators, such as desferoxamine, diethylenetriaminepentaacetic acid or 1,10-phenanthroline, decreased it. Addition of Fe(II) resulted in a several fold increase in the OH generation. UV and O₂ consumption measurements showed that the reaction of Co with water consumed molecular oxygen and generated Co(II). Since reaction of Co(II) with H₂O₂ did not generate any significant amount of OH radicals, a Co(I) mediated Fenton-like reaction [Co(I) + H₂O₂ → Co(II) + OH + OH⁻] seems responsible for OH generation. H₂O₂ is produced from O₂⁻ via dismutation. O₂⁻ is produced by one-electron reduction of molecular oxygen catalyzed by Co. Chelation of Co(II) by biological chelators, such as glutathione or β-ananyl-3-methyl- -histidine alters, its oxidation–reduction potential and makes Co(II) capable of generating OH via a Co(II)-mediated Fenton-like reaction [Co(II) + H₂O₂ → Co(III) + OH + OH⁻]. Thus, the reaction of Co with water, especially in the presence of biological chelators, glutathione, glycylglycylhistidine and β-ananyl-3-methyl- -histidine, is capable of generating a whole spectrum of reactive oxygen species, which may be responsible for Co-induced cell injury.     

Mitoxantrone and ametantrone inhibit hydroperoxide-dependent initiation and propagation reactions in fatty acid peroxidation

The anthracenedione antineoplastic agents mitoxantrone and ametantrone are potent inhibitors of basal and drug-stimulated lipid peroxidation in a variety of subcellular systems (Kharasch, E. D., and Novak, R. F. (1983) J. Pharmacol. Exp. Ther. 226, 500-506). The mechanism by which these compounds function as antioxidants has been investigated using enzymic and chemical systems. Mitoxantrone and ametantrone inhibited NADPH-cytochrome P-450 reductase- and xanthine oxidase-catalyzed conjugated diene formation from linoleic acid in a concentration-dependent manner with half-maximal inhibition achieved at approximately 0.5 microM anthracenedione. Inhibition of linoleic acid peroxidation was not attributable to a decrease in P-450 reductase activity, hydroxyl radical scavenging, or iron chelation by the anthracenediones. Nonenzymic fatty acid peroxidation was also inhibited by the anthracenediones. Linoleic acid oxidation initiated by superoxide (ferrous iron autoxidation) or by hydroxyl radicals (Fenton's reagent) was diminished by mitoxantrone and ametantrone after a brief delay, suggesting an effect subsequent to activated oxygen-dependent initiation. In contrast, linoleic acid oxidation initiated by iron-dependent hydroperoxide decomposition was inhibited immediately. Reinitiation of linoleic acid oxidation in an anthracenedione-inhibited system was accomplished only by superoxide generation, but not by fatty acid hydroperoxide decomposition. These results suggest the anthracenediones diminished neither oxygen radical formation nor oxygen radical-dependent initiation of peroxidation. Rather, inhibition of fatty acid peroxidation by mitoxantrone and ametantrone results from the inhibition of hydroperoxide-dependent initiation and propagation reactions.     

Ecophysiology and the energetic benefit of mixotrophic Fe(II) oxidation by various strains of nitrate-reducing bacteria

In order to assess the importance of nitrate-dependent Fe(II) oxidation and its impact on the growth physiology of dominant Fe oxidizers, we counted these bacteria in freshwater lake sediments and studied their growth physiology. Most probable number counts of nitrate-reducing Fe(II)-oxidizing bacteria in the sediment of Lake Constance, a freshwater lake in Southern Germany, yielded about 10⁵ cells mL⁻¹ of the total heterotrophic nitrate-reducing bacteria, with about 1% (10³ cells mL⁻¹) of nitrate-reducing Fe(II) oxidizers. We investigated the growth physiology of Acidovorax sp. strain BoFeN1, a dominant nitrate-reducing mixotrophic Fe(II) oxidizer isolated from this sediment. Strain BoFeN1 uses several organic compounds (but no sugars) as substrates for nitrate reduction. It also reduces nitrite, dinitrogen monoxide, and O₂, but cannot reduce Fe(III). Growth experiments with cultures amended either with acetate plus Fe(II) or with acetate alone demonstrated that the simultaneous oxidation of Fe(II) and acetate enhanced growth yields with acetate alone (12.5 g dry mass mol⁻¹ acetate) by about 1.4 g dry mass mol⁻¹ Fe(II). Also, pure cultures of Pseudomonas stutzeri and Paracoccus denitrificans strains can oxidize Fe(II) with nitrate, whereas Pseudomonas fluorescens and Thiobacillus denitrificans strains did not. Our study demonstrates that nitrate-dependent Fe(II) oxidation contributes to the energy metabolism of these bacteria, and that nitrate-dependent Fe(II) oxidation can essentially contribute to anaerobic iron cycling.     

Dopamine Neurotoxicity: Inhibition of Mitochondrial Respiration

Abstract: Dopamine, due to metabolism by monoamine oxidase or autoxidation, can generate toxic products such as hydrogen peroxide, oxygen-derived radicals, semiquinones, and quinones and thus exert its neurotoxic effects. Intracerebroventricular injection of dopamine into rats pretreated with the monoamine oxidase nonselective inhibitor pargyline caused mortality in a dose-dependent manner with LD₅₀ = 90 µg. Norepinephrine was less effective with LD₅₀ = 141 µg. The iron chelator desferrioxamine completely protected against dopamine-induced mortality. In the absence of pargyline more rats survived, indicating that the products of dopamine enzymatic metabolism are not the main contributors to dopamine-induced toxicity. Biochemical analysis of frontal cortex and striatum from rats that received a lethal dose of dopamine did not show any difference from control rats in lipid and protein peroxidation and glutathione reductase and peroxidase activities. Moreover, dopamine significantly reduced the formation of iron-induced malondialdehyde in vitro, thus suggesting that earlier events in cell damage are involved in dopamine toxicity. Indeed, dopamine inhibited mitochondrial NADH dehydrogenase activity with IC₅₀ = 8 µ M , and that of norepinephrine was twice as much (IC₅₀ = 15 µ M ). Dopamine-induced inhibition of NADH dehydrogenase activity was only partially reversed by desferrioxamine, which had no effect on norepinephrine-induced inhibition. These results suggest that catecholamines can cause toxicity not only by inducing an oxidative stress state but also possibly through direct interaction with the mitochondrial electron transport system. The latter was further supported by the ability of ADP to reverse dopamine-induced inhibition of NADH dehydrogenase activity in a dose-dependent manner.     

Degeneration of biogenic superparamagnetic magnetite

Magnetite crystals precipitated as a consequence of Fe(III) reduction by Shewanella algae BrY after 265 h incubation and 5-year anaerobic storage were investigated with transmission electron microscopy, Mössbauer spectroscopy and X-ray diffraction. The magnetite crystals were typically superparamagnetic with an approximate size of 13 nm. The lattice constants of the 265 h and 5-year crystals are 8.4164Å and 8.3774Å, respectively. The Mössbauer spectra indicated that the 265 h magnetite had excess Fe(II) in its crystal-chemistry (Fe³⁺_1.990Fe²⁺_1.015O₄) but the 5-year magnetite was Fe(II)-deficient in stoichiometry (Fe³⁺_2.388Fe²⁺_0.419O₄). Such crystal-chemical changes may be indicative of the degeneration of superparamagnetic magnetite through the aqueous oxidization of Fe(II) anaerobically, and the concomitant oxidation of the organic phases (fatty acid methyl esters) that were present during the initial formation of the magnetite. The observation of a corona structure on the aged magnetite corroborates the anaerobic oxidation of Fe(II) on the outer layers of magnetite crystals. These results suggest that there may be a possible link between the enzymatic activity of the bacteria and the stability of Fe(II)-excess magnetite, which may help explain why stable nano-magnetite grains are seldom preserved in natural environments.