Reactivity of hypotaurine and cysteine sulfinic acid toward carbonate radical anion and nitrogen dioxide as explored by the peroxidase activity of Cu,Zn superoxide dismutase and by pulse radiolysis

Abstract

Hypotaurine and cysteine sulfinic acid are known to be readily oxidized to the respective sulfonates, taurine and cysteic acid, by several oxidative agents that may be present in biological systems. In this work, the relevance of both the carbonate anion and nitrogen dioxide radicals in the oxidation of hypotaurine and cysteine sulfinic acid has been explored by the peroxidase activity of Cu,Zn superoxide dismutase (SOD) and by pulse radiolysis. The extent of sulfinate oxidation induced by the system SOD/H₂O₂ in the presence of bicarbonate (CO₃^?– generation), or nitrite (^?NO₂ generation) has been evaluated. Hypotaurine is efficiently oxidized by the carbonate radical anion generated by the peroxidase activity of Cu,Zn SOD. Pulse radiolysis studies have shown that the carbonate radical anion reacts with hypotaurine more rapidly (k = 1.1 × 10⁹ M^?1s^?1) than nitrogen dioxide (k = 1.6 × 10⁷ M^?1s^?1). Regarding cysteine sulfinic acid, it is less reactive with the carbonate radical anion (k = 5.5 × 10⁷ M^?1s^?1) than hypotaurine. It has also been observed that the one-electron transfer oxidation of both sulfinates by the radicals is accompanied by the generation of transient sulfonyl radicals (RSO₂^?). Considering that the carbonate radical anion could be formed in vivo at high level from bicarbonate, this radical can be included in the oxidants capable of performing the last metabolic step of taurine biosynthesis. Moreover, the protective effect exerted by hypotaurine and cysteine sulfinate on the carbonate radical anion-mediated tyrosine dimerization indicates that both sulfinates have scavenging activity towards the carbonate radical anion. However, the formation of transient reactive intermediates during sulfinate oxidation by carbonate anion and nitrogen dioxide radical may at the same time promote oxidative reactions.     

Properties of [3H] prostaglandin F2α binding to dispersed bovine luteal cells

Intact viable bovine luteal cell suspensions prepared by collagenase digestion of luteal tissue were used in studying the selected properties of [³H] prostaglandin (PG) F_2α binding and compared with those observed in plasma membranes. [³H]PGF_2α specific binding to luteal cells was a rapid (K₁ = 8.4 × 10⁴M^?12αS^?1), reversible (K_?1 = 1.8 × 10^?4S^?1) and saturable process at 24°. There was a single class of receptors with an apparent dissociation constant of 10.6 nM and 1.8 × 10⁵ receptors per cell. The presence of increasing amounts of unlabeled PGs inhibited [³H]PGF_2α binding in a dose-dependent manner. The potency order for this inhibition was: (15S) 15-methyl-PGF_2α methyl ester > ICI-80,996 > PGF_2α > ICI-81,008 > PGF_1α > PGE₂, (15S) 15-methyl-PGE₂ methyl ester > PGF_2α metabolites > other PGs, PGF_1α metabolites and PGE metabolites. Other than the homegeneous nature of binding and a greater association rate in cells, the rest of the [³H]PGF_2α binding properties in cells were in good agreement with those observed in plasma membranes.     

Inhibition of gibberellin biosynthesis by paclobutrazol in cell-free homogenates ofCucurbita maxima endosperm andMalus pumila embryos

The plant growth retardant paclobutrazol, (PP333) (2RS, 3RS)-1-(4-chlorophenyl)-4,4-dimethyl-2-(1,2,4-triazol-1-yl)pentan-3-ol, inhibits specifically the three steps in the oxidation of the gibberellin-precursorent-kaurene toent-kaurenoic acid in a cell-free system fromCucurbita maxima endosperm. The KI₅₀ for this inhibition is 2×10^?8 M. The KI₅₀ values for the separated2S, 3S, and2R, 3R enantiomers of paclobutrazol in this system are 2×10^?8 M and 7×10^?7 M, respectively. A cell-free preparation from immatureMalus pumila embryos convertsent-kaurene to gibberellin A₉, whereas no conversion occurs in a similar preparation fromMalus endosperm. The conversion ofent-kaurene by the embryo preparation is inhibited by paclobutrazol with KI₅₀ values for the2S,3S and2R,3R enantiomers of 2×10^?8 M and 6×10^?8 M, respectively.     

Hymenolepis diminuta: Chloride fluxes and membrane potentials associated with sodium-coupled glucose transport

Glucose transport by Hymenolepis diminuta was inhibited when Cl^? in the bathing medium was replaced with acetate (C₂H₃O₂^Post?), but was unaffected when Cl^? was replaced with SCN^?. The relative effectiveness of the anions to inhibit influx of 7.4 mM Cl^? in the presence of 1 mM glucose was SCN^? > Cl^? > C₂H₃O₂^Post?. Glucose stimulated the influxes of 120 mM Cl^? and SCN^?, but had little effect on 120 mM C₂H₃O₂^Post? influx. While the diffusion rates of the anions were C₂H₃O₂^Post? > SCN^? = Cl^?, the preference of the glucose transport system for the anions was SCN^? > Cl^? > C₂H₃O₂^Post?. Efflux of Cl^? was not affected by the rate of glucose influx. Finally, microelectrode recordings of worms anesthetized with 2 mM arecoline revealed a transmembrane potential (TMP) of ?45 ± 3.6 mV (inside negative). Three to four minutes after addition of glucose (5 mM) there was a progressive hyperpolarization of the TMP to ?58 mV. A revised model of the glucose transport system that is consistent with previous observations on this organism is proposed.     

Electrochemical behavior of S,S-bridged adducts of square planar metalladithiolene complexes [M(S2C2Ph2)2](M=Ni, Pd, and Pt)

The electrochemical behavior of the S,S^′-bridged adducts of square planar metalladithiolene complexes was investigated by using cyclic voltammetry and electrochemical spectroscopies (visible, near-IR, and ESR). The norbornene-bridged S,S^′-adduct [Ni(S₂C₂Ph₂)₂(C₇H₈)] (2a; C₇H₈=norbornene) formed by [Ni(S₂C₂Ph₂)₂] (1a) and quadricyclane (Q) was dissociated by an electrochemical reduction, and anion 1a⁻ and norbornadiene (NBD) were formed. Q was isomerized to NBD in the overall reaction. The o-xylyl-bridged S,S^′-adduct [Ni(S₂C₂Ph₂)₂(CH₂)₂(C₆H₄)] (3a; (CH₂)₂(C₆H₄)=o-xylyl) was also dissociated by an electrochemical reduction, and this reaction gave the o-xylyl radical (o-quinodimethane). The reduction of complex 3a in the presence of excess o-xylylene dibromide underwent the catalytic formation of o-quinodimethane. The butylene-bridged S,S^′-adduct [Ni(S₂C₂Ph₂)₂(CH₂)₄] (4a; (CH₂)₄=butylene) was stable on an electrochemical reduction. The lifetimes of reduced species of these adducts 2a-4a were influenced by the stability of the eliminated group (stability: NBD > o-xylyl radical (o-quinodimethane) > butylene radical). Therefore, the reduced species are stable in the sequence 4a⁻ > 3a⁻ > 2a⁻. Although the palladium complex [Pd(S₂C₂Ph₂)₂] (1b) was easier to reduce than the nickel complex 1a or the platinum complex [Pt(S₂C₂Ph₂)₂] (1c), their S,S^′-adducts were easier to reduce in the order of Ni adduct > Pd adduct > Pt adduct.     

Metal cation toxicity in the alga Gracilaria domingensis as evaluated by the daily growth rates in synthetic seawater

Macroalgae of the genus Gracilaria have considerable economic importance as raw material for agar production and belong to an important group of organisms that are tolerant of high concentrations of metal. The median inhibitory concentration (IC₅₀) values obtained by measuring the ratio of fresh mass variation (i.e., daily growth rates) of the red macroalga Gracilaria domingensis during a 48-h aquatic toxicity assay are reported here. The alga was exposed to 14 different metal cations as well as the molybdate anion in synthetic seawater. The actual concentrations of these ionic species (at IC₅₀ values) and the proportion of free ions (aqueous complexes) were determined by inductively coupled plasma atomic emission spectroscopy and the Environmental Protection Agency-recommended software, MINTEQA2, respectively. Based on the free IC₅₀ values (IC₅₀ ^F), the ions were ranked in terms of toxicity: Cd²⁺???Cu²⁺???Pb²⁺???Zn²⁺???Ni²⁺?>?Co²⁺?>?La³⁺???Mn²⁺?>?Ca²⁺?~?Li⁺???MoO₄ ^2????Sr²⁺?>?Mg²⁺???K⁺?>?Na⁺. As a member of the first trophic level in the marine food chain, G. domingensis is an appropriate target organism both for the development of toxicological assays and as a bioindicator of marine degradation.     

Downstream reaction of cisplatin with methionine-containing peptides: pH-dependent competition between hydrolytic cleavage and macrochelation

The pH- and time-dependent reactions of the antitumor drug cisplatin, cis-[PtCl₂(NH₃)₂], with the methionine-containing peptides Ac-Met-Gly-OH, Ac-Met-Pro-OH, Ac-Met-Pro-Gly-Gly-OH and Ac-Gly-Met-Pro-Gly-Gly-OH (Gly = glycyl, Met = d-methionyl, Pro = L-prolyl) at 313 K have been investigated by high performance liquid chromatography, mass spectrometry and nuclear magnetic resonance. As a result of the strong trans influence of the methionyl S_M atom, initial Pt-S_M binding at pH > 5 is followed by a rapid formation of tridentate machrochelates for the N-acetylated peptides. The site trans to S_M is occupied by a carboxylate O atom in the case of the κ³S_M,N_M,O_G/P macrochelates of the dipeptides and by the C-terminal glycylamide N_G2 atom for the κ³S_M,O_M,N_G2 macrochelate of Ac-Met-Pro-Gly-Gly-OH. Cisplatin simultaneously mediates the rapid hydrolytic cleavage of the Met-X (X = Gly, Pro) amide bond for both dipeptides over the whole range 2.8 ? pH ? 10.0. The released amino acids X react with the resulting κ²S_M, N_M chelate of N-acetylmethionine to afford mixed κS_M:κ²N_x,O_x complexes of the type cis-[Pt(NH₃)(Ac-Met-OH-κS)(H-X-O-κ²N_x,O_x)]⁺ as final products at pH < 5 for X = Gly and pH < 8 for X = Pro. In contrast to the dipeptides, hydrolytic cleavage of the Met-Pro amide bond in Ac-Met-Pro-Gly-Gly-OH at pH > 5 is significantly inhibited by the presence of high concentrations of the macrochelate [Pt(NH₃)(Ac-Met-Pro-Gly-Gly)-κ³S_M,O_M,N_G2]⁺. Downstream hydrolysis of the Met-Gly amide bond is competitive with upstream Ac-Gly cleavage for Ac-Gly-Met-Pro-Gly-Gly-OH at pH < 4.5.     

Transport of ions across peritoneal membrane

The electrical conductance of ions across the peritoneal membrane of young buffalo (approximately 18-24 months old) has been recorded. Aqueous solutions of NaF, NaNO₃, NaCl, Na₂SO₄, KF, KNO₃, KCl, K₂SO₄, MgCl₂, CaCl₂, CrCl₃, MnCl₂, FeCl₃, CoCl₂, and CuCl₂ were used. The conductance values have been found to increase with increase in concentration as well as with temperature (15 to 35 °C) in these cases. The slope of plots of specific conductance, κ, versus concentration exhibits a decrease in its values at relatively higher concentrations compared to those in extremely dilute solutions. Also, such slopes keep on increasing with increase in temperature. In addition, the conductance also attains a maximum limiting value at higher concentrations in the said cases. This may be attributed to a progressive accumulation of ionic species within the membrane. The κ values of electrolytes follow the sequence for the anions: SO₄²⁻>Cl⁻>NO₃⁻>F⁻ while that for the cations: K⁺>Na⁺>Ca²⁺>Mn²⁺>Co²⁺>Cu²⁺>Mg²⁺>Cr³⁺>Fe³⁺. In addition, the diffusion of ions depends upon the charge on the membrane and its porosity. The membrane porosity in relation to the size of the hydrated species diffusing through the membrane appears to determine the above sequence. As the diffusional paths in the membrane become more difficult in aqueous solutions, the mobility of large hydrated ions gets impeded by the membrane framework and the interaction with the fixed charge groups on the membrane matrix. Consequently, the membrane pores reduce the conductance of small ions, which are much hydrated. An increase in conductance with increase in temperature may be due to the state of hydration, which implies that the energy of activation for the ionic transport across the membrane follows the sequence of crystallographic radii of ions accordingly. The Eyring's equation, κ=(RT/Nh)exp[−ΔH*/RT]exp[ΔS*/R], has been found suitable for explaining the temperature dependence of conductance in the said cases. This is apparent from the linear plots of log[κNh/RT] versus 1/T. The results indicate that the permeation of ions through the membrane giving negative values of ΔS* suggest that there may be formation of either covalent linkage between the penetrating ions and the membrane material or else the permeation may not be the rate-determining step. On the one hand, a high ΔS* value associated with the high value of energy of activation, E_a, for diffusion may suggest the existence of either a large zone of activation or loosening of more chain segments of the membrane. On the other hand, low value of ΔS* implies that converse is true in such cases, i.e., either a small zone of activation or no loosening of the membrane structure upon permeation.     

Genetic engineering of sunflower (<Emphasis Type="Italic">Helianthus annuus</Emphasis> L.) for resistance to necrosis disease through deployment of the TSV coat protein gene

Nitrogen is a major driver of plant growth and the nitrogen source can be critical to good growth in vitro. A response surface methodology mixture-component design and a data mining algorithm were applied to nitrogen (N) nutrition for improving the micropropagation of Prunus armeniaca Lam. Data taken on shoot cultures included a subjective quality rating, shoot number, shoot length, leaf characteristics and physiological disorders. Data were analyzed using the Classification and Regression Tree data mining algorithm. The best overall shoot quality as well as leaf color were on medium with NO₃^??>?25 mM and NH₄⁺/Ca⁺ >?0.8. Improving shoot length to15 mm required 25?<?NO₃^? ≤?35 mM with NH₄⁺/Ca²⁺ ≤?2.33. The most shoots (11.6) were produced with NO₃^? >?25 mM and NH₄⁺/Ca²⁺ ≤ 0.8, but there were 5–10 shoots at other NO₃^? concentrations regardless of NH₄⁺/Ca²⁺ proportion. Leaves increased in size with higher NO₃^? concentrations (>?55 mM). Physiological disorders were also influenced by the nitrogen components. Shoot tip necrosis was rarely present with NO₃^? > 45 mM. Callus production decreased somewhat with NH₄⁺/Ca²⁺ >?2.33. Suggested concentrations for an improved medium considering all of these growth characteristics would be 25?<?NO₃^? ≤?35 mM and NH₄⁺/Ca⁺ ≤ 0.8. Validation experiments comparing WPM and three trial media showed improvements in several shoot growth parameters on medium with optimized mesos and optimized nitrogen components.     

Probing the electronic structures and properties of neutral and charged arsenic sulfides [As n S2 (−1,0,+1), n = 1–6] with Gaussian-3 theory

The structures and energies of neutral and charged arsenic sulfides As _n S₂ ^(?1,0,+1) (n?=?1–6) were investigated systematically by means of the Gaussian-3 (G3) scheme. The ground-state structures of these species are presented. The ground-state structures of As _n S₂ can be viewed as the lowest-energy structure of neutral As _n+1S by replacing an As atom with a S atom. To be more precise, the ground-state structures of As _n S₂ can be viewed as the lowest-energy structure of neutral As _n+2 by replacing two As atoms with two S atoms, in which the feature of sulfur bonding is edge-bridging. No rule could be found for the ground state structure of As _n S₂ ^? and As _n S₂ ⁺. In As _n S₂ ^?, the feature of sulfur bonding is either edge-bridging or a terminal atom, and in As_nS₂ ⁺ the feature of sulfur bonding is edge-bridging analogous to As _n S₂. The potential energy surfaces of As₄S₂ and its charged species are very flat. So co-existence for many isomers of As₄S₂ and its charged species are possible. The reliable adiabatic electron affinities (AEAs) and adiabatic ionization potentials (AIPs) of As _n S₂ were estimated. There are odd-even alternations in both AEAs and AIPs as a function of size of As _n S₂. The dissociation energies (DEs) of S [and/or its ion S^(?/+)] from As _n S₂ clusters and their ions were calculated and used to reveal relative stability.     

Soil nitrous oxide emissions from a typical semiarid temperate steppe in inner Mongolia: effects of mineral nitrogen fertilizer levels and forms

Nitrous oxide (N₂O) emissions can be significantly affected by the amounts and forms of nitrogen (N) available in soils, but the effect is highly dependent on local climate and soil conditions in specific ecosystem. To improve our understanding of the response of N₂O emissions to different N sources of fertilizer in a typical semiarid temperate steppe in Inner Mongolia, a 2-year field experiment was conducted to investigate the effects of high, medium and low N fertilizer levels (HN: 200 kg N?ha^-1y^-1, MN: 100 kg N ha^-1y^-1, and LN: 50 kg N ha^-1y^-1) respectively and N fertilizer forms (CAN: calcium ammonium nitrate, AS: ammonium sulphate and NS: sodium nitrate) on N₂O emissions using static closed chamber method. Our data showed that peak N₂O fluxes induced by N treatments were concentrated in short periods (2 to 3 weeks) after fertilization in summer and in soil thawing periods in early spring; there were similarly low N₂O fluxes from all treatments in the remaining seasons of the year. The three N levels increased annual N₂O emissions significantly (P?<?0.05) in the order of MN > HN > LN compared with the CK (control) treatment in year 1; in year 2, the elevation of annual N₂O emissions was significant (P?<?0.05) by HN and MN treatments but was insignificant by LN treatments (P?>?0.05). The three N forms also had strong effects on N₂O emissions. Significantly (P?<?0.05) higher annual N₂O emissions were observed in the soils of CAN and AS fertilizer treatments than in the soils of NS fertilizer treatments in both measured years, but the difference between CAN and AS was not significant (P?>?0.05). Annual N₂O emission factors (EF) ranged from 0.060 to 0.298% for different N fertilizer treatments in the two observed years, with an overall EF value of 0.125%. The EF values were by far less than the mean default EF proposed by the Intergovernmental Panel on Climate Change (IPCC).     

Binding analysis of ytterbium(III) complex containing 1,10-phenanthroline with DNA and its antimicrobial activity

To evaluate the biological preference of [Yb(phen)₂(OH₂)Cl₃](H₂O)₂ (phen is 1,10-phenanthroline) for DNA, interaction of Yb(III) complex with DNA in Tris–HCl buffer is studied by various biophysical and spectroscopic techniques which reveal that the complex binds to DNA. The results of fluorescence titration reveal that [Yb(phen)₂(OH₂)Cl₃](H₂O)₂ has strongly quenched in the presence of DNA. The binding site number n, apparent binding constant K _b, and the Stern–Volmer quenching constant K _SV are determined. ΔH ⁰, ΔS ⁰, and ΔG ⁰ are obtained based on the quenching constants and thermodynamic theory (ΔH ⁰?>?0, ΔS ⁰?>?0, and ΔG ⁰?<?0). The experimental results show that the Yb(III) complex binds to DNA by non-intercalative mode. Groove binding is the preferred mode of interaction for [Yb(phen)₂(OH₂)Cl₃](H₂O)₂ to DNA. The DNA cleavage results show that in the absence of any reducing agent, Yb(III) complex can cleave DNA. The antimicrobial screening tests are also recorded and give good results in the presence of Yb(III) complex.     

Identifying key factors of groundwater chemistry in three diverse Landscapes of Central Mexico

In order to understand the hydrogeochemical pattern, ground (n = 23) and surface water (n = 2) samples were collected from three different landscapes (mountain, plain, valley) of Hidalgo State, Central Mexico. Physicochemical characteristics (pH, electrical conductivity, total hardness, alkalinity, total acidity, total solids, total dissolved solids, total suspended solids, CO₂; cations (Ca²⁺, Mg²⁺, Na⁺), anions (NO₃^?, Cl^?, PO₄^3?and SO₄^2?) and dissolved geochemical elements (Fe, Mn, Cr, Cu, Ni, Co, Pb, Zn, Cd and As) were analyzed. Results illustrated they are neutral to slightly alkaline due to the dissolution of carbonates. Average concentrations of anions and cations presented an order of (in mg/l): Na⁺ (273) > Ca²⁺ (206) > SO₄^2? (181) > Cl^? (163) > Mg²⁺ (115) > NO₃^? (11.07) > PO₄^3? (0.12) revealing the local geogenic and anthropogenic influences. High mean concentrations of dissolved trace metals (0.052 mg/l) in the mountains is attributed to their diverse geochemical environment of the terrain and climatic variability. Concentrations of Cr, Cu, Ni and Zn were below the permissible limits set forth by WHO and the Mexican Government. Piper trilinear diagram revealed that they are mainly of Ca-Mg-HCO₃ and Ca-Mg-SO₄ type. Sodium Absorption Ratio (SAR) indicated that nearly 96% are of excellent quality, while Magnesium Adsorption Ratio (MAR) showed that 68% of them are unsuitable for irrigation purposes.     

Inorganic carbon and pH effect on growth and lipid productivity of Tetraselmis suecica and Chlorella sp (Chlorophyta) grown outdoors in bag photobioreactors

There has been considerable interest in cultivation of green microalgae (Chlorophyta) as a source of lipid that can alternatively be converted to biodiesel. However, almost all mass cultures of algae are carbon-limited. Therefore, to reach a high biomass and oil productivities, the ideal selected microalgae will most likely need a source of inorganic carbon. Here, growth and lipid productivities of Tetraselmis suecica CS-187 and Chlorella sp were tested under various ranges of pH and different sources of inorganic carbon (untreated flue gas from coal-fired power plant, pure industrial CO₂, pH-adjusted using HCl and sodium bicarbonate). Biomass and lipid productivities were highest at pH 7.5 (320?±?29.9 mg biomass L^?1 day^?1and 92?±?13.1 mg lipid L^?1 day^?1) and pH 7 (407?±?5.5 mg biomass L^?1 day^?1 and 99?±?17.2 mg lipid L^?1 day^?1) for T. suecica CS-187 and Chlorella sp, respectively. In general, biomass and lipid productivities were pH 7.5?>?pH 7?>?pH 8?>?pH 6.5 and pH 7?>?pH 7.5?=?pH 8?>?pH 6.5?>?pH 6?>?pH 5.5 for T. suecica CS-187 and Chlorella sp, respectively. The effect of various inorganic carbon on growth and productivities of T. suecica (regulated at pH?=?7.5) and Chlorella sp (regulated at pH?=?7) grown in bag photobioreactors was also examined outdoor at the International Power Hazelwood, Gippsland, Victoria, Australia. The highest biomass and lipid productivities of T. suecica (51.45?±?2.67 mg biomass L^?1 day^?1 and 14.8?±?2.46 mg lipid L^?1 day^?1) and Chlorella sp (60.00?±?2.4 mg biomass L^?1 day^?1 and 13.70?±?1.35 mg lipid L^?1 day^?1) were achieved when grown using CO₂ as inorganic carbon source. No significant differences were found between CO₂ and flue gas biomass and lipid productivities. While grown using CO₂ and flue gas, biomass productivities were 10, 13 and 18 %, and 7, 14 and 19 % higher than NaHCO₃, HCl and unregulated pH for T. suecica and Chlorella sp, respectively. Addition of inorganic carbon increased specific growth rate and lipid content but reduced biomass yield and cell weight of T. suecica. Addition of inorganic carbon increased yield but did not change specific growth rate, cell weight or content of the cell weight of Chlorella sp. Both strains showed significantly higher maximum quantum yield (F_v/F_m) when grown under optimum pH.     

Probing the proton release by Photosystem II in the S1 to S2 high-spin transition

The stoichiometry and kinetics of the proton release were investigated during each transition of the S-state cycle in Photosystem II (PSII) from Thermosynechococcus elongatus containing either a Mn₄CaO₅ (PSII/Ca) or a Mn₄SrO₅ (PSII/Sr) cluster. The measurements were done at pH 6.0 and pH 7.0 knowing that, in PSII/Ca at pH 6.0 and pH 7.0 and in PSII/Sr at pH 6.0, the flash-induced S₂-state is in a low-spin configuration (S₂^LS) whereas in PSII/Sr at pH 7.0, the S₂-state is in a high-spin configuration (S₂^HS) in half of the centers. Two measurements were done; the time-resolved flash dependent i) absorption of either bromocresol purple at pH 6.0 or neutral red at pH 7.0 and ii) electrochromism in the Soret band of P_D1 at 440 nm. The fittings of the oscillations with a period of four indicate that one proton is released in the S₁ to S₂^HS transition in PSII/Sr at pH 7.0. It has previously been suggested that the proton released in the S₂^LS to S₃ transition would be released in a S₂^LSTyr_Z^? → S₂^HSTyr_Z^? transition before the electron transfer from the cluster to Tyr_Z^? occurs. The release of a proton in the S₁Tyr_Z^? → S₂^HSTyr_Z transition would logically imply that this proton release is missing in the S₂^HSTyr_Z^? to S₃Tyr_Z transition. Instead, the proton release in the S₁ to S₂^HS transition in PSII/Sr at pH 7.0 was mainly done at the expense of the proton release in the S₃ to S₀ and S₀ to S₁ transitions. However, at pH 7.0, the electrochromism of P_D1 seems larger in PSII/Sr when compared to PSII/Ca in the S₃ state. This points to the complex link between proton movements in and immediately around the Mn₄ cluster and the mechanism leading to the release of protons into the bulk.     

The reduction of the oxygen-evolving system in chloroplasts by thylakoid components

Using thoroughly dark-adapted thylakoids and an unmodulated Joliot-type oxygen electrode, the following results were obtained. (i) At high flash frequency (4 Hz), the oxygen yield at the fourth flash (Y₄) is lower compared to Y₃ than at lower flash frequency. At 4 Hz, the calculated S₀ concentration after thorough dark adaptation is found to approach zero, whereas at 0.5 Hz the apparent $\text{S}{}_0\text{(}\text{S}{}_0\text{+}\text{S}{}_1\text{)}$ ratio increases to about 0.2. This is explained by a relatively fast donation ($\text{t}{}_{\mathrm{<mtext>1</mtext><mtext>2</mtext>}}\text{= 1.0–1.5}\text{s}$) of one electron by an electron donor to S₂ and S₃ in 15–25% of the Photosystem II reaction chains. The one-electron donor to S₂ and S₃ appears to be rereduced very slowly, and may be identical to the component that, after oxidation, gives rise to ESR signal II_s. (ii) The probability for the fast one-electron donation to S₂ and S₃ has nearly been the same in triazine-resistant and triazine-susceptible thylakoids. However, most of the slow phase of the S₂ decay becomes 10-fold faster ($\text{t}{}_{\mathrm{<mtext>1</mtext><mtext>2</mtext>}}\text{= 5–6}\text{s}$) in the triazine-resistant ones. In a small part of the Photosystem II reaction chains, the S₂ decay was extremely slow. The S₃ decay in the triazine-resistant thylakoids was not significantly different from that in triazine-susceptible thylakoids. This supports the hypothesis that S₂ is reduced mainly by Q^?_A, whereas S₃ is not. (iii) In the absence of CO₂/HCO^?_A and in the presence of formate, the fast one-electron donation to S₂ and S₃ does not occur. Addition of HCO^?₃ restores the fast decay of part of S₂ and S₃ to almost the same extent as in control thylakoids. The slow phase of S₂ and S₃ decay is not influenced significantly by CO₂/HCO^?₃. The chlorophyll a fluorescence decay kinetics in the presence of DCMU, however, monitoring the Q^?_A oxidation without interference of Q_B, were 2.3-fold slower in the absence of CO₂/HCO^?₃ than in its presence. (iv) An almost 3-fold decrease in decay rate of S₂ is observed upon lowering the pH from 7.6 to 6.0. The kinetics of chlorophyll a fluorescence decay in the presence of DCMU are slightly accelerated by a pH change from 7.6 to 6.0. This indicates that the equilibrium Q^?_A concentration after one flash is decreased (by about a factor of 4) upon changing the pH from 7.6 to 6.0. When direct or indirect protonation of Q^?_B is responsible for this shift of equilibrium Q^?_A concentration, these data would suggest that the pK_a value for Q^?_B protonation is somewhat higher than 7.6, assuming that the protonated form of Q^?_B cannot reduce Q_A.     

Reactive oxygen and nitrogen species’ effect on <Emphasis Type="Italic">lux</Emphasis>-biosensors based on <Emphasis Type="Italic">Escherichia coli</Emphasis> and <Emphasis Type="Italic">Salmonella typhimurium</Emphasis>

The effect of reactive oxygen and nitrogen species on lux-biosensors based on the Escherichia coli K12 MG1655 and Salmonella typhimurium LT2 host strains was investigated. The bioactivity of exogenous free radicals to the constitutively luminescent E. coli strain with plasmid pXen7 decreased in the order H₂O₂ > OCl^– > NO^? > RОO^? > ONOO^–> O₂^?- while the bioluminescence of S. typhimurium strain transformed with this plasmid decreased in the order NO^? > H₂O₂ > ONOO^– > RОO^? > OCl^– > O₂^?- The cross-reactivity of induced lux-biosensors to reactive oxygen and nitrogen species, the threshold sensitivity and the luminescence amplitude dependences from the plasmid specificity and the host strain were indicated. The biosensors with plasmid pSoxS′::lux possessed a wider range of sensitivity, including H₂O₂ and OCl^–, along with O₂^?- and NO^?. Among the used reactive oxygen and nitrogen species, H₂O₂ showed the highest induction activity concerning to the plasmids pKatG′::lux, pSoxS′::lux and pRecA′::lux. The inducible lux-biosensors based on S. typhimurium host strain possessed a higher sensitivity to the reactive oxygen and nitrogen species in comparison with the E. coli lux-biosensors.     

Lanthanide ions induce hydrolysis of hemoglobin-bound 2,3-diphosphoglycerate (2,3-DPG), conformational changes of globin and bidirectional changes of 2,3-DPG-hemoglobin’s oxygen affinity

The changes in structure and function of 2,3-diphosphoglycerate-hemoglobin (2,3-DPG-Hb) induced by Ln³⁺ binding were studied by spectroscopic methods. The binding of lanthanide cations to 2,3-DPG is prior to that to Hb. Ln³⁺ binding causes the hydrolysis of either one from the two phosphomonoester bonds in 2,3-DPG non-specifically. The results using the ultrafiltration method indicate that Ln³⁺ binding sites for Hb can be classified into three categories: i.e. positive cooperative sites (N_I), non-cooperative strong sites (N_S) and non-cooperative weak sites (N_W) with binding constants in decreasing order: K_I>K_S>K_W. The total number of binding sites amounts to about 65 per Hb tetramer. Information on reaction kinetics was obtained from the change of intrinsic fluorescence in Hb monitored by stopped-flow fluorometry. Fluctuation of fluorescence dependent on Ln³⁺ concentration and temperature was observed and can be attributed to the successive conformational changes induced by Ln³⁺ binding. The results also reveal the bidirectional changes of the oxygen affinity of Hb in the dependence on Ln³⁺ concentration. At the range of [Ln³⁺]/[Hb]<2, the marked increase of oxygen affinity (P₅₀ decrease) with the Ln³⁺ concentration can be attributed to the hydrolysis of 2,3-DPG, while the slight rebound of oxygen affinity in higher Ln³⁺ concentration can be interpreted by the transition to the T-state of the Hb tetramer induced by Ln³⁺ binding. This was indicated by the changes in secondary structure characterized by the decrease of α-helix content.     

GC–MS analysis of S-nitrosothiols after conversion to S-nitroso-N-acetyl cysteine ethyl ester and in-injector nitrosation of ethyl acetate

S-Nitrosothiols from low-molecular-mass and high-molecular-mass thiols, including glutathione, albumin and hemoglobin, are endogenous potent vasodilators and inhibitors of platelet aggregation. By utilizing the S-transnitrosation reaction and by using the lipophilic (pK_L 0.78) and strong nucleophilic synthetic thiol N-acetyl cysteine ethyl ester (NACET) we have developed a GC–MS method for the analysis of S-nitrosothiols and their ¹⁵N- or ²H–¹⁵N-labelled analogs as S-nitroso-N-acetyl cysteine ethyl ester (SNACET) and S¹⁵NACET or d₃-S¹⁵NACET derivatives, respectively, after their extraction with ethyl acetate. Injection of ethyl acetate solutions of S-nitrosothiols produced two main reaction products, compound X and compound Y, within the injector in dependence on its temperature. Quantification was performed by selected-ion monitoring of m/z 46 (i.e., [NO₂]^?) for SNACET and m/z 47 (i.e., [¹⁵NO₂]^?) for S¹⁵NACET/d₃-S¹⁵NACET for compound X, and m/z 157 for SNACET and m/z 160 for d₃-S¹⁵NACET for compound Y. In this article we describe the development, validation and in vitro and in vivo applications of the method to aqueous buffered solutions, human and rabbit plasma. Given the ester functionality of SNACET/S¹⁵NACET/d₃-S¹⁵NACET, stability studies were performed using metal chelators and esterase inhibitors. The method was found to be suitable for the quantitative determination of various S-nitrosothiols including SNACET externally added to human plasma (0–10 μM). Nitrite contamination in ethyl acetate was found to interfere. Our results suggest that the concentration of endogenous S-nitrosothiols in human plasma does not exceed about 200 nM in total. Oral administration of S¹⁵NACET to rabbits (40–63 μmol/kg body weight) resulted in formation of ALB-S¹⁵NO, [¹⁵N]nitrite and [¹⁵N]nitrate in plasma.     

Major Ion Chemistry of Soil Solution of Mountainous Soils,Alvand, Hamedan,Western Iran

Soil solution chemistry reflects the most dynamic processes occurring in soils and is responsible for their current status. This study was undertaken to determine the soil solution status in 25 mountainous soils. The major cations in the studied soil solutions are in the decreasing order of Ca²⁺ > Mg²⁺ > Na⁺ > K⁺. The anions are also arranged in decreasing order as HCO^? ₃ > Cl^? > NO^? ₃ > SO ^2? ₄ . Concentrations of NO^? ₃ , P, and K⁺ in soil solutions were in the range of 12–364 mg l^?1, 1.75–34.8 mg l^?1, and 0.78– 198 mg l^?1, respectively. Results suggest that the concentration of P in the soil solutions could be primarily controlled by of the solubility of octacalcium phosphate and ß-tricalcium phosphate. In general, the greater the dissolved P concentration in the soil solution, the closer the solution was to equilibrium with respect to the more soluble Ca²⁺ phosphate minerals. Surface soil accumulations of P, NO^? ₃ , and K⁺ have occurred in these soils to such an extent that loss of these nutrients in surface runoff and the high risk for nutrient transfer into groundwater in concentrations exceeding the groundwater quality standard has become a priority management concern.