A nitrite reductase with cytochrome oxidase activity from Micrococcus denitrificans

The formation of nitrite reductase and cytochrome c in Micrococcus denitrificans was repressed by O₂. The purified nitrite reductase utilized reduced forms of cytochrome c, phenazine methosulphate, benzyl viologen and methyl viologen, respectively, as electron donors. The enzyme was inhibited by KCN, NaN₃ and NH₂OH each at 1 mM, whereas CO and bathocuproin, diethyl dithiocarbamate, o-phenanthroline and ,'-dipyridyl at 1 mM concentrations were relatively ineffective. The purified enzyme contains cytochromes, probably of the c and a₂ types, in one complex. A K_m of 46 μM for NO₂⁻ and a pH optimum of 6.7 were recorded for the enzyme. The molecular weight of the enzyme was estimated to be around 130000, and its anodic mobility was 6.8·10⁻⁶ cm²·sec⁻¹·V⁻¹ at pH 4.55.

The most highly purified nitrite reductase still exhibited cytochrome c oxidase activity with a K_m of 27 μM for O₂. This activity was also inhibited by KCN, NaN₃ and NH₂OH and by NO₂⁻.

A constitutive cytochrome oxidase associated with membranes was also isolated from cells grown anaerobically with NO₂⁻. It was inhibited by smaller amounts of KCN, NaN₃ and NH₂OH than the cytochrome oxidase activity of the nitrite reductase enzyme and also differed in having a pH optimum of about 8 and a K_m for O₂ of less than 0.1 μM. Spectroscopically, cytochromes b and c were found to be associated with the constitutive oxidase in the particulate preparation. Its activity was also inhibited by NO₂⁻.

The physiological role of the cytochrome oxidase activity associated with the purified nitrite reductase is likely to be of secondary importance for the following reasons: (a) it accounts for less than 10% of total cytochrome c oxidase activity of cell extracts; (b) the constitutive cytochrome c oxidase has a smaller K_m for O₂ and would therefore be expected to function more efficiently especially at low concentrations of O₂.     

Particulate formate oxidase from Nitrobacter agilis

1. The nitrite oxidase particles obtained by sonic oscillation of Nitrobacter agilis cells also possessed appreciable formate oxidase activity, ranging from about 25 to 50% of the nitrite oxidase activity depending upon the N. agilis strain. Both activities distributed themselves in the same pattern and proportions during differential centrifugation, and resided solely in the pellet resulting from high-speed centrifugation.

2. Difference spectra of formate-reduced particles or intact cells demonstrated the presence of cytochromes of the c- and a-types like those of the NO₂⁻-reduced material. Under anaerobic conditions NO₃⁻ or fumarate acted as an alternate electron acceptor in place of O₂ in formate oxidation. Under aerobic conditions increasing NO₃⁻ concentrations resulted in (a) an increased role of NO₃⁻ as a terminal electron acceptor compared to O₂, (b) a greater total enzymatic transfer of electrons from formate than if O₂ were the sole electron acceptor, and (c) a partial inhibition of O₂ uptake suggestive of a competition for electrons by the two acceptors. The formate oxidase system failed to catalyze consistently the transfer of electrons to either added mammalian cytochrome c or Fe(CN)₆³⁻. The marked sensitivity of the system to certain inhibitors implicated cytochrome oxidase as an integral part of the formate oxidase. The system was also inhibited significantly by a variety of chelating agents, indicating a metal component in the formate dehydrogenase or early portion of the electron transfer sequence.

3. The stoichiometry of the formate oxidase system was shown to approach the theoretical value of 2 moles of CO₂ evolved per mole of O₂ or per 2 moles of formate consumed.

4. To a limited extent, phosphorylation occurred concomittantly with the oxidation of formate in the presence of the cell-free particulate system.     

Biochemical and biophysical studies on cytochrome c oxidase XV. Reaction with fluoride

1. Fluoride is a mixed-type inhibitor of the cytochrome c oxidase activity with a K_i for the free enzyme of 10 mM and a K_i for the cytochrome c-complexed enzyme of 35 mM.

2. Fluoride shifts the γ-band of the enzyme from 423 to 421 nm and the -band from 597 to 598 nm. The difference spectrum (oxidized enzyme in the presence of fluoride minus oxidized enzyme) has peaks at 400, 453, 482, 605 and 638 nm and troughs at 430, 520, 552 and 674 nm. The changes in absorbance are small (about 3% at absorbance maxima) with respect to those of other hemoproteins.

3. On addition of fluoride to isolated cytochrome c oxidase 3 reactions can be distinguished: (I) a bimolecular binding reaction (K_on = 4 M⁻¹ · s⁻¹ and k_off = 2.9 · 10⁻²s⁻¹ at 25 °C, pH 7.4) contributing at 638 nm and 430 nm; (II) a first-order reaction (k = 2.4 · 10⁻²) s⁻¹ at 22 °C, pH 7.2) visible mainly at 430 nm and (III) a very slow reaction with a half-time in the order of 10 min.

4. The spectroscopic dissociation constants for the fluoride binding, determined from Hill plots using the absorbance changes at 638 and 430 nm, are similar (7 and 10 mM, respectively, at 22 °C, pH 7.2).

5. A mechanism for the reaction is discussed in which the bimolecular binding reaction is followed by a conformational change of the enzyme-fluoride complex.     

Biochemical and biophysical studies on cytochrome c oxidase XIV. The reaction with cytochrome c as studied by pulse radiolysis

1. The reduction of cytochrome c oxidase by hydrated electrons was studied in the absence and presence of cytochrome c.

2. Hydrated electrons do not readily reduce the heme of cytochrome c oxidase. This observation supports our previous conclusion that heme a is not directly exposed to the solvent.

3. In a mixture of cytochrome c and cytochrome c oxidase, cytochrome c is first reduced by hydrated electrons (k = 4 · 10¹⁰ M⁻¹ · s⁻¹ at 22 °C and pH 7.2) after which it transfers electrons to cytochrome c oxidase with a rate constant of 6 · 10⁷ M⁻¹ · s⁻¹ at 22 °C and pH 7.2.

4. It was found that two equivalents of cytochrome c are oxidized initially per equivalent of heme a reduced, showing that one electron is accepted by a second electron acceptor, probably one of the copper atoms of cytochrome c oxidase.

5. After the initial reduction, redistribution of electrons takes place until an equilibrium is reached similar to that found in redox experiments of Tiesjema, R. H., Muijsers, A. O. and Van Gelder, B. F. (1973) Biochim. Biophys. Acta 305, 19–28.     

Reactions of the ferri-ferrocytochrome-c system with superoxide/oxygen and CO2/CO2 studied by fast pulse radiolysis

The reduction of ferricytochrome c by O₂⁻ and CO₂⁻ was studied in the pH range 6.6–9.2 and Arrhenius as well as Eyring parameters were derived from the rate constants and their temperature dependence. Ionic effects on the rate indicate that the redox process proceeds through a multiply-positively charged interaction site on cytochrome c. It is shown that the reaction with O₂⁻ and correspondingly with O₂ of ferrocytochrome c) is by a factor of approx. 10³ slower than warranted by factors such as redox potential. Evidence is adduced to support the view that this slowness is connected with the role of water in the interaction between O₂⁻/O₂ and ferri-ferrocytochrome c in the positively charged interaction site on cytochrome c in which water molecules are specifically involved in maintaining the local structure of cytochrome c and participate in the process of electron equivalent transfer.     

The reaction between the superoxide anion radical and cytochrome c

1. 1. The superoxide anion radical (O₂⁻) reacts with ferricytochrome c to form ferrocytochrome c. No intermediate complexes are observable. No reaction could be detected between O₂⁻ and ferrocytochrome c.

2. 2. At 20 °C the rate constant for the reaction at pH 4.7 to 6.7 is 1.4 · 10⁶ M⁻¹ · s⁻¹ and as the pH increases above 6.7 the rate constant steadily decreases. The dependence on pH is the same for tuna heart and horse heart cytochrome c. No reaction could be demonstrated between O₂⁻ and the form of cytochrome c which exists above pH ≈ 9.2. The dependence of the rate constant on pH can be explained if cytochrome c has pKs of 7.45 and 9.2, and O₂⁻ reacts with the form present below pH 7.45 with k = 1.4 · 10⁶ M⁻¹ · s⁻¹, the form above pH 7.45 with k = 3.0 · 10⁵ M⁻¹ · s⁻¹, and the form present above pH 9.2 with k = 0.

3. 3. The reaction has an activation energy of 20 kJ mol⁻¹ and an enthalpy of activation at 25 °C of 18 kJ mol⁻¹ both above and below pH 7.45. It is suggested that O₂⁻ may reduce cytochrome c through a track composed of aromatic amino acids, and that little protein rearrangement is required for the formation of the activated complex.

4. 4. No reduction of ferricytochrome c by HO₂ radicals could be demonstrated at pH 1.2–6.2 but at pH 5.3, HO₂ radicals oxidize ferrocytochrome c with a rate constant of about 5 · 10⁵–5 · 10⁶ M⁻¹ · s⁻¹

.     

Oxidative phosphorylation coupled to oxygen uptake and nitrate reduction in Micrococcus denitrificans

A procedure is described for preparing particles from cells of Micrococcus denitrificans which were broken osmotically after treatment with lysozyme.

1. 1. The preparations catalysed ATP synthesis coupled to O₂ uptake or NO₃⁻ reduction. With NADH or succinate as the electron donors the P:O ratios were about 1.5 and 0.5, respectively; and the P:NO₃⁻ ratios were about 0.9 and 0.06, respectively.

2. 2. Addition of ADP or P_i to the reaction mixture increased the rates of NADH-dependent O₂ uptake and NO₃⁻ reduction. Addition of 1 mM 2,4-dinitrophenol, which inhibited phosphorylation by 50–60%, increased the basal rates of electron transport.

3. 3. Evidence derived from spectrophotometry and from the differential inhibition by antimycin A of O₂ and NO₃⁻ reduction leads to the conclusion that the nitrate reductase interacted with the respiratory chain in the region of the b-type cytochrome, and that the c-type cytochrome present was not involved in the reduction of NO₃⁻ to NO₂⁻.

Redox potentials of the pyridine-haem c system

1. Haem c was synthesized and purified. It was shown unequivocally that the method gives a product with the cysteine residues on the -carbon atoms at the 2 and 4 positions of the haem.

2. Redox potentials of haem c in the presence of 2.5 M pyridine were determined in the pH range 1.5–13; it was found necessary to add cetyl trimethyl ammonium bromide (CTAB) to prevent precipitation in the acid range below about pH 4. The E_m vs pH curve shows three slopes (−dE/dpH) of value, 0.18, 0.01 and 0.06 with points of inflexion at pH 3.8 and 10.6. The potentials are intermediate between those of protohaem and mesohaem obtained under similar conditions.

3. With constant haem c concentration (a) 10⁻⁴ M and (b) 10⁻⁵ M and varying pyridine concentration (0.12–5 M) it was found at pH 9.0 that E_m values increased as the pyridine concentration was increased and there was a tendency to reach a plateau value. The explanation appears to be that pyridine binds more firmly to ferroporphyrin c than to ferriporhyrin c.

4. When the pyridine concentration was kept constant (2.5 M) and the haem c concentration was varied in the range 7 · 10⁻⁴–7 · 10⁻⁶ M, it was found that a decrease in haem c concentration brought about an increase in redox potential. The results are explained as being due to dimerization of the oxidized form.

5. The results are discussed in comparison with a number of related haem systems.     

Nitrite reduces the effects of HOCl on unsaturated phosphatidylcholines--a MALDI-TOF MS study

The concentration of nitrite (NO₂⁻) increases under inflammatory conditions. However, the physiological role of nitrite is so far controversial discussed: it was reported that effects of HOCl (an important inflammation mediator) on phospholipids (PL) may be enhanced but also reduced in the presence of nitrite.

In this paper a simple model system was used: unsaturated phosphatidylcholine (PC) vesicles were treated with HOCl in the presence of varying NaNO₂ concentrations and the yield of reaction products was determined by MALDI-TOF MS: the extent of chlorohydrin generation was significantly reduced in the presence of NaNO₂ because HOCl is consumed by the oxidation of NO₂⁻ to NO₃⁻.

Similar results were obtained when HOCl was generated by the myeloperoxidase (MPO)/H₂O₂/Cl⁻ system or the experiments were carried out in the presence of a simple peptide. It is concluded that the transient products of the reaction between HOCl and NO₂⁻ do not have a sufficient reactivity to modify PL.     

The preparation and properties of the membranal DPNH dehydrogenase from Escherichia coli

1. The membrane bound DPNH oxidase of Escherichia coli can reduce the artificial electron acceptors: ferricyanide, dichlorophenolindophenol (DCIP) and menadione. All three are reduced by the flavoprotein of DPNH oxidase, but at different sites of the enzyme.

2. Freeze-drying of the bacterial membranes causes a selective detachment of DPNH dehydrogenase (DPNH: (acceptor) oxidoreductase, EC 1.6.99.3) from the membranes. This solubilization is accompanied by a decrease of K_m(K₃Fe(CN)₆) from 2.0 to 0.25 mM, while no change is detected in K_m(DPNH). This enzyme is not the DPNH diaphorase found in the bacteria.

3. DPNH dehydrogenase of E. coli is a metalloflavoprotein, containing non-heme iron, labile sulfide, FMN and FAD.

4. Reduction of the enzyme with DPNH in the absence of electron acceptor (ferricyanide or DCIP) causes a rapid and irreversible change to a less active state, Form II. Form II is characterized by a higher K_m(DPNH) and slower v_max., while the K_m(K₃Fe(CN)₆) remains unchanged.

5. The transformation of the enzyme to Form II is accompanied by the reduction of the non-heme iron component. The role of non-heme iron in the enzymic reaction is discussed.     

Kinetics of the reactions of nitrogen dioxide with glutathione,cysteine, and uric acid at physiological pH

Nitrogen dioxide (NO₂^•) is a key biological oxidant. It can be derived from peroxynitrite via the interaction of nitric oxide with superoxide, from nitrite with peroxidases, or from autoxidation of nitric oxide. In this study, submicromolar concentrations of NO₂^• were generated in < 1 μs using pulse radiolysis, and the kinetics of scavenging NO₂^• by glutathione, cysteine, or uric acid were monitored by spectrophotometry. The formation of the urate radical was observed directly, while the production of the oxidizing radical obtained on reaction of NO₂^• with the thiols (the thiyl radical) was monitored via oxidation of 2,2′-azino-bis-(3-ethylthiazoline-6-sulfonic acid). At pH 7.4, rate constants for reaction of NO₂^• with glutathione, cysteine, and urate were estimated as 2 × 10⁷, 5 × 10⁷, and 2 × 10⁷ M⁻¹ s⁻¹, respectively. The variation of these rate constants with pH indicated that thiolate reacted much faster than undissociated thiol. The dissociation of urate also accelerated reaction with NO₂^• at pH > 8. The thiyl radical from GSH reacted with urate with a rate constant of 3 × 10⁷ M⁻¹ s⁻¹. The implications of these values are: (i) the lifetime of NO₂^• in cytosol is < 10 μs; (ii) thiols are the dominant ‘sink’ for NO₂^• in cells/tissue, whereas urate is also a major scavenger in plasma; (iii) the diffusion distance of NO₂^• is 0.2 μm in the cytoplasm and < 0.8 μm in plasma; (iv) urate protects GSH against depletion on oxidative challenge from NO₂^•; and (v) reactions between NO₂^• and thiols/urate severely limit the likelihood of reaction of NO₂^• with NO• to form N₂O₃ in the cytoplasm.     

Nitrogen mineralisation and plant nitrogen acquisition in a nitrogen-limited calcareous grassland

A field study measured the rate of soil mineral N supply and its effects on plant biomass and N accumulation in a 13-year-old, naturally regenerating, calcareous grassland. Gross rates of N mineralisation (2 μg g⁻¹ day⁻¹, i.e. 0.69 kg ha⁻¹ day⁻¹), assessed using ¹⁵N pool dilution, were at the lower end of the range previously reported for grasslands. Weekly additions of liquid N fertiliser ([NH₄]₂SO₄, NH₄NO₃ or KNO₃) and, to a lesser extent the addition of water, increased plant growth substantially, demonstrating that the primary constraint to plant growth was low N availability. In plants that had received NO₃⁻, the activity of the inducible enzyme nitrate reductase in shoots initially increased in proportion to the amount of NO₃⁻ supplied. However, as above-ground herbage accumulated, nitrate reductase activity declined to similar low levels in all treatments, despite the continuance of the constant NO₃⁻ additions. The decline in NR specific activity reflected declining tissue NO₃⁻ concentrations, although total plant NRA may have remained constant during the period of study. The study has shown that plant growth is limited by low N mineralisation rates and indeed the soil is a sink for much added N. Low water availability provides an additional constraint on N mineralisation in this calcareous grassland soil. Any disturbances in the N cycle which increase the availability of mineral N will result in a substantial increase in plant growth within this ecosystem.     

Properties and function of the respiratory chain of freshwater mussel spermatozoa in relation to motility

1. The spermatozoa of the freshwater mussel (Hyriopsis schlegelii) contain cytochromes aa₃, b and c, flavoproteins and nicotinamide nucleotides in molar ratios of 1.0:0.9:1.8:1.8:8.7. Cytochrome c₁ is not detectable even at liquid-N₂ temperature, but a c₁-like cytochrome with an -band at 550 mμ is found at liquid-N₂ temperature in a cell preparation from which cytochrome c is completely removed.

2. The near-ultraviolet difference spectrum of whole cells reveals an absorption peak at 315 mμ with a shoulder around 350 mμ.

3. Both the endogenous respiration and motility of spermatozoa are completely blocked by 0.2 mM CN⁻ and by 0.2 μM antimycin A. 2,4-Dinitrophenol and pentachlorophenol completely inhibit motility at the maximal stimulation of respiration. Rotenone strongly inhibits NADH oxidase of spermatozoa, although it has no effect on the respiration of whole cells.

4. It is concluded that the motility of mussel spermatozoa is tightly coupled to respiration, and the respiratory chain phosphorylating process is the only energy-supplying system for motility.     

Nitrite effect on nitrous oxide emission from denitrifying activated sludge

Laboratory-scale experiments were conducted to examine the N₂O emission during the denitrification process. For each of the 6 runs carried out, synthetic effluent was fed in a 10 l batch mixed liquor to investigate the effect of nitrite on N₂O emission and Helium was continuously bubbled through the reactor at constant rate (0.12 l/min) to favour N₂O transfer and detection. An increasing COD/NO₃⁻-N influent ratio from 3 to 7 was firstly applied (runs 1–3). Secondly, NO₂⁻ pulse additions were performed during run 4 and 5 (10 and 20 mg N/l, respectively). Finally, the reactor was fed with influent containing both NO₂⁻ and NO₃⁻. We showed that N₂O emission was detected shortly after NO₂⁻ accumulation, few minutes after the substrate feeding. The highest emission occurred at the lower COD/NO₃⁻-N ratio (=3) and at the higher NO₂⁻ addition (20 mg N/l). In addition, the higher nitrogen conversion to N₂O gas (14.4%) was obtained with an influent containing initially both NO₂⁻ and NO₃⁻. Our results suggest a direct effect of the NO₂⁻ concentration on the N₂O emission. We have also confirmed the inhibitory effect of NO₂⁻ concentration on N₂O reduction.     

Bipyridylium quaternary salts and related compounds. V. Pulse radiolysis studies of the reaction of paraquat radical with oxygen. Implications for the mode of action of bipyridyl herbicides

1. Rate constants for reduction of paraquat ion (1,1′-dimethyl-4,4′-bipyridy-lium, PQ²⁺) to paraquat radical (PQ⁺·) by e⁻_aq and CO₂⁻· have been measured by pulse radiolysis. Reduction by e⁻_aq is diffusion controlled (k = 8.4·10¹⁰ M⁻¹·s⁻¹) and reduction by CO₂⁻· is also very fast k = 1.5·10¹⁰ M⁻¹·s⁻¹).

2. The reaction of paraquat radical with oxygen has been analysed to give rate constants of 7.7·10⁸ M⁻¹·s⁻¹ and 6.5·10⁸ M⁻¹·s⁻¹ for the reactions of paraquat radical with O₂ and O₂⁻·, respectively. The similarity in these rate constants is in marked contrast to the difference in redox potentials of O₂ and O₂⁻· (− 0.59 V and + 1.12 V, respectively).

3. These rate constants, together with that for the self-reaction of O₂⁻·, have been used to calculate the steady-state concentration of O₂⁻· under conditions thought to apply at the site of reduction of paraquat in the plant cell. On the basis of these calculations the decay of O₂⁻· appears to be governed almost entirely by its self-reaction, and the concentration 5 μm away from the thylakoid is still 90% of that at the thylakoid itself. Thus, O₂⁻· persists long enough to diffuse as far as the chloroplast envelope and tonoplast, which are the first structures to be damaged by paraquat treatment. O₂⁻· is therefore sufficiently long-lived to be a candidate for the phytotoxic product formed by paraquat in plants.     

The reaction of antimycin with a cytochrome b preparation active in reconstitution of the respiratory chain

1. Succinate-cytochrome c reductase activity was reconstituted by incubating a mixture of succinate dehydrogenase, cytochrome c₁, ubiquinone-10, phospholipid and a preparation of cytochrome b, made by the method of .

2. Preparations of cytochrome b active in reconstitution contained 5–28% native cytochrome b, as adjudged by reducibility with succinate in the reconstituted preparation and by lack of reaction with CO. Preparations of cytochrome b containing no native cytochrome b according to this criterion were inactive in reconstitution.

3. With a fixed amount of cytochrome b, the activity of the reconstituted preparation increased with increasing amounts of cytochrome c₁ until a ratio of about 2b (total): 1c₁ (allowing for the cytochrome c₁ present in the cytochrome b preparation) was reached.

4. The amount of antimycin necessary for maximal inhibition of the reconstituted enzyme is a function of the amount of the cytochrome b and is independent of the amount of cytochrome c₁. It is equal to about one half the amount of native cytochrome b.

5. Preparations of intact or reconstituted succinate-cytochrome c reductase or of cytochrome b completely quench the fluorescence of added antimycin, until an amount of antimycin equal to onehalf the amount of native cytochrome b present was added. Antimycin added in excess of this amount fluoresces with normal intensity. The quenching is only partial in the presence of Na₂S₂O₄. Denatured cytochrome b does not quench the fluorescence.

6. Since preparations of cytochrome b active in reconstitution contained cytochrome c₁ in an amount exceeding one half the amount of native cytochrome b present in the preparation, there is no evidence that native cytochrome b has been resolved from cytochrome c₁. The stimulatory action of cytochrome c₁ may be due to the restoration of a damaged membrane conformation.

7. Based on the assumption that the bc₁ segment of the respiratory chain contains 2b:1c₁:1 antimycin-binding sites, the specific quenching of antimycin fluorescence by binding to cytochrome b enables an accurate determination of the absorbance coefficients of cytochromes b and c₁. These are 25.6 and 20.1 mM⁻¹×cm⁻¹ for the wavelength pairs 563–577 nm and 553–539 nm, respectively, in the difference spectrum reduced minus oxidized.     

Perchlorate and nitrate reductase activity in the perchlorate-respiring bacterium perclace

The perchlorate (ClO₄⁻)-respiring organism, strain perc1ace, can grow using nitrate (NO₃⁻) as a terminal electron acceptor. In resting cell suspensions, NO₃⁻ grown cells reduced ClO₄⁻, and ClO₄⁻ grown cells reduced NO₃⁻. Activity assays showed that nitrate reductase (NR) activity was 1.31 μmol min⁻¹ (mg protein)⁻¹ in ClO₄⁻ grown cells, and perchlorate reductase (PR) activity was 4.24 μmol min⁻¹ (mg protein)⁻¹ in NO₃⁻ grown cells. PR activity was detected within the periplasmic space, with activities as high as 14 μmol min⁻¹ (mg protein)⁻¹. The NR had a pH optimum of 9.0 while the PR had an optimum of 8.0. This study suggests that separate terminal reductases are present in strain perclace to reduce NO₃⁻ and ClO₄⁻.     

Autocatalytic peroxidation of ferrocytochrome c

1. Ferricytochrome c acts as a catalyst in the peroxidation of ferrocytochrome c thereby giving rise to an autocatalytic reaction.

2. The rate of the peroxidation reaction is proportional to the concentration of H₂O₂ and ferricytochrome c but is independent of the concentration of ferrocytochrome c in the concentration ranges studied.

3. Integration of the rate equation, d[c³⁺]/dt = k[c³⁺][H₂O₂], gives a theoretical expression which fits the experimental time courses for the ferrocytochrome c peroxidation reaction.

4. No direct spectral evidence was found for the formation of a catalytically active ferricytochrome c-H₂O₂ derivative. Kinetic evidence is presented, however, which indicates the existence of such an intermediate.

5. Ferricytochrome c was more susceptible than ferrocytochrome c to an apparent degradation reaction caused by excess H₂O₂, thus supporting the idea that the cytochrome c heme iron is more accessible in the oxidized form.     

Nutrient removal by thermophilic Fischerella (Mastigocladus laminosus) in a simulated algaculture process

A novel nutrient removal/waste heat utilization process was simulated using semicontinuous cultures of the thermophilic cyanobacterium Fischerella. Dissolved inorganic carbon (DIC)-enriched cultures, maintained with 10 mg l⁻¹ daily productivity, diurnally varying temperature (from 55°C to 26–28°C), a 12:12 light cycle (200 μE sec⁻¹ m⁻²) and 50% biomass recycling into heated effluent at the beginning of each light period, removed > 95% of NO₃⁻ + NO₂⁻−N, 71% of NH₃-N, 82% of PO₄³⁻ −P, and 70% of total P from effluent water samples containing approximately 400 μg l⁻¹ combined N and 60 μg l⁻¹ P. Nutrient removal was not severely impaired by an altered temperature gradient, doubled light intensity, or DIC limitation. Recycling 75% of the biomass at the end of each light period resulted in unimpaired NO₃⁻ + NO₂⁻ removal, 38–45% P removal and no net NH₃ removal. Diurnally varying P removal, averaging 50–60%, and nearly constant > 80% N removal, are therefore projected for a full-scale process with continuous biomass recycling.     

Pulse radiolysis kinetics of the reaction of the hydrated electron and the carboxyl anion radical with Pseudomonas aeruginosa cytochrome c-551

The kinetics of the reaction of hydrated electron (e⁻_aq) and carboxyl anion radical (CO₂) with Pseudomonas aeruginosa ferricytochrome c-551 were studied by pulse radiolysis. The rate of reaction of e⁻_aq with the negatively charged ferricytochrome c-551 (17 nM⁻¹ · s⁻¹) is significantly slower than the larger positively charged horse heart ferricytochrome c (70 nM⁻ · s⁻). This difference cannot be explained solely by electrostatic effects on the diffusion-controlled reactions. After the initial encounter of e⁻_aq with the protein, ferricytochrome c-551 is less effective in transferring an electron to the heme which may be due to the negative charge on the protein. The charge on ferricytochrome c-551 is estimated to be −5 at pH 7 from the effect of ionic strength on the reaction rate. A slower relaxation (2 · 10⁴ s⁻¹) observed after fast e⁻_aq reduction is attributed to a small conformational change. The rate of reaction of CO₂ with ferricytochrome c-551 (0.7 nM⁻¹ · s⁻) is, after electrostatic correction, the same as ferricytochrome c, indicating that the steric requirements for reaction are similar. This reaction probably takes place through the exposed heme edge.