Reactions of thiols and selenols with the FeMoS cluster [Fe(MoS4)2]3−

The known complex [Et₄N]₃[Fe(MoS₄)₂] has been shown by EPR and visible spectral studies to react with both thiophenol and selenophenol. The reaction results in a change in the characteristic S=3/2 EPR spectrum of this species from a complex rhombic pattern to one of a very simple axial appearance. Although this effect is similar to that observed for reaction of these species with the iron- molybdenum cofactor of nitrogenase, a moiety known to consist of a FeMoS cluster species, the large excesses of reagents and the long reaction times required for complete formation of product indicate that these reactions are of questionable direct relevance to the biological system. The reaction corresponding to the EPR spectral change from rhombic to axial in the [Fe(MoS₄)₂]³⁻/PhSeH system has also been partially characterized by product isolation which indicates that attack by selenol of the two terminal MoS₂ moieties in the starting material has occurred.     

Chemiluminescent reactions of Ru(2, 2′-bipyridine)31+,3+ and Mo6Cl141−,3−

A number of new chemiluminescent reactions are reported. These include the reaction of Mo₆Cl₁₄^1- and Mo₆Cl₁₄^3- with solvent acetonitrile, of the latter species with Ru(bipyr)₃³⁺ (bipyr=2,2′-bipyridine) and of Ru(bipyr)₃⁺ and Ru(bipyr)₃³⁺ with solvent acetonitrile and with various oxidants and reductants. Approximate chemiluminescence yields and kinetics are also reported for the reduction of acidic aqueous solutions of Ru(bipyr)₃³⁺ by luminol, SnCl₂, SO₃^2-, H₂O₂, ethylenediaminetetracetic acid, N₃^-, ethanol, Pt(CN)₄^2-, Fe(CN)₆^4- and W(CN)₈^4-.     

Kinetics and mechanisms of Fe(III) complexation by lipophilic 3-hydroxy-2-methyl-1(γ-stearoamidopropyl)-4-pyridinone (HMSP)

 The kinetics of Fe(III) complexation by lipophilic 3-hydroxy-2-methyl-l(γ-stearoamidopropyl)-4-pyridinone (HMSP) were studied when [Fe(III)] > [HMSP] in MeOH/H₂O mixed solvent and [Fe(III)] < [HMSP] in MeOH, respectively. When Fe(III) was in excess, the observed rate constants depend on [Fe(III)]² _tot and on the reciprocal of [H⁺] and decrease with increasing pressure. ΔV ^‡ values are around +8.0 cm³ mol^–1. A mechanism consisting of the complexations of the hydrolyzed monomer Fe(H₂O)₅OH²⁺ and dimer species Fe₂(H₂O)₇ (μ-OH)₂OH³⁺ by HMSP is proposed. This mechanism is supported by the solvent effect and the work of other researchers. When HMSP is in excess, Fe(HMSP)₃ is formed and three kinetic steps on different time-scales are observed. An "intermolecular chelate ring-closure" mechanism is proposed, differing from the "intramolecular chelate ring-closure" complexation reported for the formation of ferrioxamine B. Received: 14 February 1997 / Accepted: 1 September 1997     

Inhibition of NO3? and NO2? Reduction by Microbial Fe(III) Reduction: Evidence of a Reaction between NO2? and Cell Surface-Bound Fe2+

A recent study (D. C. Cooper, F. W. Picardal, A. Schimmelmann, and A. J. Coby, Appl. Environ. Microbiol. 69:3517-3525, 2003) has shown that NO₃⁻ and NO₂⁻ (NO_x⁻) reduction by Shewanella putrefaciens 200 is inhibited in the presence of goethite. The hypothetical mechanism offered to explain this finding involved the formation of a Fe(III) (hydr)oxide coating on the cell via the surface-catalyzed, abiotic reaction between Fe²⁺ and NO₂⁻. This coating could then inhibit reduction of NO_x⁻ by physically blocking transport into the cell. Although the data in the previous study were consistent with such an explanation, the hypothesis was largely speculative. In the current work, this hypothesis was tested and its environmental significance explored through a number of experiments. The inhibition of ~3 mM NO₃⁻ reduction was observed during reduction of a variety of Fe(III) (hydr)oxides, including goethite, hematite, and an iron-bearing, natural sediment. Inhibition of oxygen and fumarate reduction was observed following treatment of cells with Fe²⁺ and NO₂⁻, demonstrating that utilization of other soluble electron acceptors could also be inhibited. Previous adsorption of Fe²⁺ onto Paracoccus denitrificans inhibited NO_x⁻ reduction, showing that Fe(II) can reduce rates of soluble electron acceptor utilization by non-iron-reducing bacteria. NO₂⁻ was chemically reduced to N₂O by goethite or cell-sorbed Fe²⁺, but not at appreciable rates by aqueous Fe²⁺. Transmission and scanning electron microscopy showed an electron-dense, Fe-enriched coating on cells treated with Fe²⁺ and NO₂⁻. The formation and effects of such coatings underscore the complexity of the biogeochemical reactions that occur in the subsurface.     

Synthesis and characterization of [Pt(COD)Cl(NO3)] and [Pt(COD)(NO3)2] and the use of [Pt(COD)Clx(NO3)2−x] in the preparation of cis[Pt(PPh3)2Clx(NO3)2−x] (x=0, 1, 2) and [Pt(PPh3)3L](NO3) (L=Cl,NO3)

[Pt(COD)Cl₂] (COD=1,5-cyclooctadiene) is a versatile starting material for the synthesis of Pt(II) compounds. The preparations of the new compounds [Pt(COD)Cl(NO₃)], [Pt(COD)(NO₃)₂] and [Pt(PPh₃)₃(NO₃)](NO₃) and also of the known compounds cis[Pt(PPh₃)₂Cl₂], cis [Pt(PPh₃)₂Cl(NO₃)], cis[Pt(PPh₃)₂(NO₃)₂] and [Pt(PPh₃)₃Cl](NO₃)are reported. The compounds are characterized by elemental analysis, ³¹P{¹H} NMR spectroscopy and IR spectroscopy.     

Binding of α-synuclein with Fe(III) and with Fe(II) and biological implications of the resultant complexes

Parkinson’s disease (PD) is hallmarked by the abnormal intracellular inclusions (Lewy bodies or LBs) in dopaminergic cells. Amyloidogenic protein α-synuclein (α-syn) and iron (including both Fe(III) and Fe(II)) are both found to be present in LBs. The interaction between iron and α-syn might have important biological relevance to PD etiology. Previously, a moderate binding affinity between α-syn and Fe(II) (5.8 × 10³ M⁻¹) has been measured, but studies on the binding between α-syn and Fe(III) have not been reported. In this work, electrospray mass spectrometry (ES-MS), cyclic voltammetry (CV), and fluorescence spectroscopy were used to study the binding between α-syn and Fe(II) and the redox property of the resultant α-syn-Fe(II) complex. The complex is of a 1:1 stoichiometry and can be readily oxidized electrochemically and chemically (by O₂) to the putative α-syn-Fe(III) complex, with H₂O₂ as a co-product. The reduction potential was estimated to be 0.025 V vs. Ag/AgCl, which represents a shift by −0.550 V vs. the standard reduction potential of the free Fe(III)/Fe(II) couple. Such a shift allows a binding constant between α-syn and Fe(III), 1.2 × 10¹³ M⁻¹, to be deduced. Despite the relatively high binding affinity, α-syn-Fe(III) generated from the oxidation of α-syn-Fe(II) still dissociates due to the stronger tendency of Fe(III) to hydrolyze to Fe(OH)₃ and/or ferrihydrite gel. The roles of α-syn and its interaction with Fe(III) and/or Fe(II) are discussed in the context of oxidative stress, metal-catalyzed α-syn aggregation, and iron transfer processes.     

Synthesis and structural characterization of a mixed-ligand diiron(II) complex formed by a linked bitopic tris(pyrazolyl)methane ligand: {HC(3,5-Me2pz)3Fe[μ-p-C6H4(CH2OCH2C(pz)3)2]Fe(3,5-Me2pz)3CH}(BF4)4 (pz = pyrazolyl ring)

The structure of {HC(3,5-Me₂pz)₃Fe[μ-p-C₆H₄(CH₂OCH₂C(pz)₃)₂]Fe(3,5-Me₂pz)₃CH}(BF₄)₄ (pz = pyrazolyl ring) contains two octahedral iron(II) centers linked by a semirigid, bitopic tris(pyrazolyl)methane ligand. The solid-state structure shows the two heteroleptic-bonded iron(II) centers are low-spin at 200 K and situated in a trans orientation with respect to the central linking arene ring.     

Stereospecific Synthesis and Anti-HIV Activity of (Z)2′- and (E)3′-Deoxy-2′(3′)-C-(chloromethylene) Pyrimidine Nucleosides

Abstract

Reaction of 1-[2,5(and 3,5)-di-O-trityl-β-D-erythro-pentofuran-3 (and 2)-ulosyl]uracil derivatives 5 and 6 with (chloromethyl)triphenylphosphorane resulted in the stereoselective formation of (E)-3′- and (Z)-2′-chloromethylene derivatives 7 (69%) and 8 (53%), respectively, deprotection of which gave 9 and 10. Transformation of the uracil nucleoside 7 into cytosine one followed by deprotection yielded 12. The latter was converted into the arabinoside 14. The fully deprotected chloromethylene nucleosides were tested for their activity against HIV-1 and HIV-2.     

Fast atom bombardment,electron impact and chemical ionization mass spectrometry of the neutral 18-electron species M(CO)2(CNR)2(PR′3)2 (MMo or W)

The molybdenum(0) and tungsten(O) complexes of the type M(CO)₂(CNR)₂(PR′₃)₂ have been studied using a variety of mass spectral techniques, viz. fast atom bombardment (FAB), electron impact (EI), and both positive- and negative-ion chemical ionization (PICI and NICI) mass spectrometry. The FABMS technique gave the most structurally informative spectra with the observation of the molecular ions M⁺ (100% relative abundance in the case of MW) and in some instances the pseudomolecular ion (M + H)⁺. Fragmentation ions arising from competitive ligand loss (CO versus RNC versus PR′₃) were observed, as well as those formed by loss of H from fragment ions and dealkylation of RNC ligands. The EI and PICI spectra were not especially useful due to the relatively low thermal stability of these complexes, while the NICI spectra gave an abundance of ions that resulted from ligand redistribution reactions. Of special note were anions that contained M(CO)₄ and M(CO)₃ fragments. Dealkylation of the RNC ligands to give cyanometallate anions was also prevalent.     

Structure of microbial communities performing the simultaneous reduction of Fe(II)EDTA.NO2−and Fe(III)EDTA−

BioDeNOx is a combined physicochemical and biological process for the removal of nitrogen oxides (NOx) from flue gas. In the present study, two anaerobic bioreactors performing BioDeNOx were run consecutively (RUN-1 and RUN-2) at a dilution rate of 0.01 h⁻¹ with Fe(II)EDTA.NO²⁻ and Fe(III)EDTA⁻ as electron acceptors and ethanol as electron donor. The measured protein concentration of the reactor biomass of both runs was 120 mg/l. Different molecular methods were used to determine the identity and abundance of the bacterial populations in both bioreactors. Bacillus azotoformans strain KT-1 was recognized as a key player in Fe(II)EDTA.NO²⁻ reduction. PCR-denaturing gradient gel electrophoresis analysis of the reactor biomass showed a greater diversity in RUN-2 than in RUN-1. Enrichments of Fe(II)EDTA.NO²⁻ and Fe(III)EDTA⁻ reducers and activity assays were conducted using the biomass from RUN-2 as an inoculum. The results on substrate turnover, overall microbial diversity, and enrichments and finally activity assays confirmed that ethanol was used as electron donor for Fe(II)EDTA.NO²⁻ reduction. In addition, the Fe(III)EDTA⁻ reduction rate of the microbial community proved to be feasible enough to run the bioreactors, ruling out the chemical reduction of Fe(III)EDTA⁻ with sulfide as was proposed by other researchers.     

The reactions of organosulfur transfer reagents with Fe2(CO)9 and the synthesis of the Fe2(CO)6 derivative of α-lipoic acid

Treatment of Fe₂(CO)₉ with sulfur-transfer reagents of the types ImideSSImide and RSSImide where H-imide = phthalimide, succinimide, benzimidazole, morpholine and piperazine, and R  CH₂Ph and CMe₃ leads to cleavage of both the sulfursulfur bond and the sulfurnitrogen bond to give Fe₃(CO)₉S₂ in varying yields, some Fe₂(CO)₆S₂ plus low yields of the appropriate dimers of the type Fe₂(CO)₆(SR)(SR′), where R = R′ = phthal imido, CH₂Ph, CMe₃ and R = CH₂Ph, CMe₃, R′ = phthalimido. The naturally occurring cyclic disulfide D,L-α-lipoic acid, its methyl ester and amide react with Fe₂(CO)₉ to give Fe₂(CO)₆ derivatives wherein the sulfursufur bond has been broken.