Formation of cyclo- and polystannanes by dehydrogenative stannane coupling catalyzed by platinum(II) complexes

Reaction of (PhMe₂P)₂PtMe₂ or [(κ²-P,N)-Ph₂PC₂H₄NMe₂]PtMe₂ with an excess of H₂SnBu₂ or H₂SnPh₂ resulted in the catalytic formation of cyclo-, oligo- and/or polystannanes. In the reaction of (PhMe₂P)₂PtMe₂ with H₂SnBu₂, linear oligomeric species H(SnBu₂)_nH were observed in the initial stage of the reaction, which eventually converted into cyclostannanes. Only polystannanes were observed in the reaction of [(κ²-P,N)-Ph₂PC₂H₄NMe₂]PtMe₂ with H₂SnBu₂. The reactions of H₂SnPh₂ were similar, but more difficult to analyze due to redistribution reactions and the formation of insoluble products. The mechanism of the reactions is clearly different to that previously observed for HSnR₃ because metal complexes indicative of oxidative addition/reductive elimination reactions were only observed as minor products.     

Antibacterial effect of hydrogen peroxide-titanium dioxide suspensions in the decontamination of rough titanium surfaces

The chemical decontamination of infected dental implants is essential for the successful treatment of peri-implantitis. The aim of this study was to assess the antibacterial effect of a hydrogen peroxide-titanium dioxide (H₂O₂–TiO₂) suspension against Staphylococcus epidermidis biofilms. Titanium (Ti) coins were inoculated with a bioluminescent S. epidermidis strain for 8 h and subsequently exposed to H₂O₂ with and without TiO₂ nanoparticles or chlorhexidine (CHX). Bacterial regrowth, bacterial load and viability after decontamination were analyzed by continuous luminescence monitoring, live/dead staining and scanning electron microscopy. Bacterial regrowth was delayed on surfaces treated with H₂O₂–TiO₂ compared to H₂O₂. H₂O₂-based treatments resulted in a lower bacterial load compared to CHX. Few viable bacteria were found on surfaces treated with H₂O₂ and H₂O₂–TiO₂, which contrasted with a uniform layer of dead bacteria for surfaces treated with CHX. H₂O₂–TiO₂ suspensions could therefore be considered an alternative approach in the decontamination of dental implants.     

The chemical reactivity of tetraisobutyldialuminum towards ethers,nitrogen lewis bases,aluminumtrimethyl, borontrichloride and ethylene

Treatment of Al₂ⁱBu₄ with THF and Et₂O results in partial decomposition to afford Al metal while reaction with γ-picoline products a bis-adduct of limited stability. Reactions with AlMe₃ and BCl₃, separately, involves ligand exchange with accompanying disproportionation to yield Al metal. Dimethylamine induces disproportionation to afford AlⁱBu₃·HNMe₂ and an intemediate trialuminum species. The latter undergoes AlAl bond cleavage with formation of H₂, _iBu₂AlNMe₂, and [Me₂N- (ⁱBu)AlAlⁱBu₂]₂· Al₂iBu₄ eliminates Me₂CCH₂ in solution at 80 °C, and the catenated AlH intermediate reacts with ethylene to afford AlEt and AlCH₂CH₂CH₂CH₃ moieties.     

Photosynthetic and growth response to fumigation with SO2 at elevated CO2 for C3 and C4 plants

Summary Six early successional plant species with differing photosynthetic pathways (3 C₃ species and 3 C₄ species) were grown at either 300, 600, or 1,200 ppm CO₂ and at either 0.0 or 0.25 ppm SO₂. Total plant growth increased with CO₂ concentration for the C₃ species and varied only slightly with CO₂ for the C₄ species. Fumigation with SO₂ caused reduced growth of the C₃ species at 300 ppm CO₂ but not at the higher concentrations of CO₂. Fumigation with SO₂ reduced growth of the C₄ species at high CO₂ and increased growth at 300 ppm CO₂. Leaf area increased with increasing CO₂ for all plant species. Fumigation with SO₂ reduced leaf area of C₃ plants more at low CO₂ than at high CO₂ while leaf area of C₄ plants was reduced more at high CO₂ than at low CO₂. These results support the notion that C₃ species are more sensitive to SO₂ fumigation than are C₄ species at concentrations of CO₂ equal to that found in normal ambient air. However, the difference in sensitivity to SO₂ between C₃ and C₄ species was found to be reversed at higher concentrations of CO₂. A possible explanation for this reversal based upon differences in stomatal response to elevated CO₂ between C₃ and C₄ species is discussed.     

Syntheses and michael additions to vinylidene diphosphine complexes of type [M(CO)4{(Ph2P)2CCH2}] (MCr,Mo or W)

Treatment of [M(CO)₄Ph₂PCHPPh₂]⁻ with CH₃- OCH₂Cl at 20 °C gave the methoxymethyl derivations [M(CO)₄{Ph₂PCH(CH₂OCH₃)PPh₂}] (MCr or W), but a similar treatment at 80 °C gave derivatives of a vinylidene diphosphine [M(CO)₄(Ph₂P)₂C CH₂]. Treatment of [M(CO)₄Ph₂PCHPPh₂]⁻with CH₃CHClOCH₃ at 20 or 80 °C gave only [M(CO)₄- (Ph₂P)₂CHCH(CH₃)OCH₃] (MCr or W). The vinylidene diphosphine complexes [M(CO)₄(Ph₂P)2- CCH₂] (MCr, Mo or W) were even more easily prepared by treating [M(CO)₆] with (Ph₂P)₂CCH₂ (vdpp) in hot solvents such as CH₃OCH₂CH₂OCH₂- CH₂OCH₃.Treatment of [W(CO)₄vdpp] with LiBuⁿ followed by methanol gave [W(CO)₄(Ph₂P)₂CHCH₂Buⁿ] (1c), i.e. conjugate addition to the CCH₂ occurs. 1c was also made by treating [W(CO)₄(Ph₂P)₂CH]⁻ with n-pentyl-iodide. Similarly LiMe was added to [W(CO)₄(Ph₂P)₂CCH₂]. Treatment of [M(CO)₄- vdpp] with NaCH(COOEt)₂ gave [M(CO)₄(Ph₂- P)₂CHCH₂CH(COOEt)₂] (MW or Mo). Pyrrolidine added to the CCH₂ bonds of [M(CO)₄vddp] to give [M(CO)₄(Ph₂P)₂CHCH₂NC₄H₈]. ³¹p and ¹H NMR and IR data are given.     

Levels of 13,14-dihydro-15-keto-PGE2 in some biological fluids as measured by radioimmunoassay

A rabbit antiserum directed toward the prostaglandin E₂ metabolite 13,14-dihydro-15-keto-prostaglandin E₂ (KH₂PGE₂) was produced by immunization with a human albumin-KH₂PGE₂ conjugate. The antiserum recognized the 15-keto-group (it cross reacts with 13,14-dihydro-prostaglandin E₂ 0.2%); the saturated 13,14-bond (it cross reacts with 15-keto-prostaglandin E₂ 7%); the 9-keto group (it cross reacts with 13,14-dihydro-15-keto-prostaglandin F_2α 5%); and the 11-hydroxy group (it cross reacts with 13,14-dihydro-15-keto-PGA₂ 0.4%).By subjecting the antiserum to preparative isoelectric electrofocusing, populations of antibodies that varied in their cross reaction with 13,14-dihydro-15-keto-prostaglandin F_2α (KH₂PGF_2α) from 20% to 1% were obtained. The levels of KH₂PGE₂ in plasma of rat and mouse as measured by radioimmunoassay of the unfractionated plasma were 0.39 ± 0.07 ng/ml and 0.41 ± 0.13 ng/ml, respectively. Recovery of exogenously added KH₂PGE₂ from human plasma was 100%. Radioimmunoassay with two antisera; an antiserum directed toward KH₂PGF_2α that cross reacts with KH₂PGE₂ 1% and the antiserum to KH₂PGE₂, demonstrated that KH₂PGE₂, not KH₂PGF_2α, was being measured with the anti-KH₂PGE₂. The levels of KH₂PGE₂ in rat plasma did not vary with sex. In rats, the levels of KH₂PGE₂ markedly increased after exercise stress.In mice carrying a spindle-cell sarcoma (SAI) and a fibrosarcoma (SaD2), the levels of KH₂PGE₂ in the plasma increased with time after transplantation. The increase was not observed in the plasma of mice carrying a transplantable anaplastic carcinoma (15091AK), a lymphatic leukemia (AW5147), two mammary adenocarcinomas (CADI, CAD2), a myeloid leukemia (C1498), and a hepatoma (BW7756).     

Density functional theory study on the mechanism and thermochemistry of olefins addition to nickel dithiolenes

We investigated the reaction mechanism and thermochemical property of conjugated dienes or mono-olefins with nickel dithiolenes (Ni(S₂C₂R₂)₂) using density functional theory. The reactions between conjugated dienes and nickel dithiolenes are concerted reactions. The thermochemical property study shows that the introduction of electron-withdrawing groups (–CF₃ or –CN) to nickel dithiolene (Ni(S₂C₂H₂)₂) not only significantly lowers the activation energy barrier but also strongly stabilises the products. The introduction of electron-donating group (–CH₃) to butadiene has the same effect. So, we conclude that the reactions between nickel dithiolenes and conjugated dienes are electrophilic cycloaddition. Mono-olefins can add to nickel dithiolenes through interligand pathway, which is a two-step process or through intraligand pathway, which is a one-step process. The thermochemical property study shows that the activation enthalpy for the reaction of butadiene with Ni(S₂C₂(CF₃)₂)₂ is much lower than those of C4 mono-olefins with Ni(S₂C₂(CF₃)₂)₂ for both interligand addition and intraligand addition. The Gibbs free energy for the reaction of butadiene with Ni(S₂C₂(CF₃)₂)₂ is also more favourable than those of C4 mono-olefins with Ni(S₂C₂(CF₃)₂)₂. It is the very preferential pathway for Ni(S₂C₂(CF₃)₂)₂ to bind butadiene than C4 mono-olefins.     

New molybdenum(VI) catalysts for the epoxidation of cyclohexene: synthesis, reactivity and crystal structures

Compounds 1-6 of the type MoO₂X₂L₂ (X=F, Cl, Br; L=OPMePh₂, OPPh₃) have been prepared in order to investigate the variation in catalytic activity with changes in electronic and steric properties. All six complexes catalyze the epoxidation of cyclohexene with tert-butylhydroperoxide, and the species with X=Cl and L=OPMePh₂ (2) displays the best activity with 83% conversion and 90% selectivity in one hour at ambient atmosphere. These inexpensive and easily prepared dioxo catalysts are stable to air and water. Reactions of the dioxo compounds with H₂O₂ and t-BuOOH have also been carried out. The structures of MoO₂F₂(OPMePh₂)₂ (1) and the product of its reaction with H₂O₂, MoO(O₂)₂(OPMePh₂)₂ (7) have been solved by single crystal X-ray diffraction.     

Preparations and properties of tripodal and linear tetradentate N,S-Donor ligands and their complexes containing the MoO22+core

New linear and tripodal tetradentate ligands, LH₂, are reported and their syntheses are described. The new linear ligands L = HSCH₂CH₂SCH₂CH₂NRCH₂CR₂SH, R = H, CH₃) and the new tripodal ligands N(CH₂CH₂SH)₂CH₂Z, Z = CH₂NH₂, CH₂N(CH₃)₂, CH₂N(C₂H₅)₂, CH₂SCH₃ and CO₂^- were synthesized. The known linear ligands HSCH₂CH₂NCH₃(CH₂)_nNCH₃CH₂CH₂SH (n = 2, 3) and HSCR₂CH₂NHCH₂CH₂NHCH₂CR₂SH (R = H, CH₃) were also utilized. These ligands react with MoO₂(acac)₂ in CH₃OH to yield MoO₂L complexes in high yield. Infra-red and ¹H nmr spectra provide evidence to supplement X-ray crystallographic results reported elsewhere for selected numbers of the series. Octahedral structures with cis MoO₂²⁺ groupings are assigned. Solution ¹H nmr studies are consistent with a trans placement of the two thiolate donors in agreement with the X-ray studies.     

Acetylene Metabolism and Stimulation of Denitrification in an Agricultural Soil

The effects of C₂H₂ metabolism on N₂O production were examined in soil slurries. Enrichment of C₂H₂ consumption activity occurred only in aerobic incubations. Rapid disappearance of subsequent C₂H₂ additions, stimulation of CO₂ production, and most-probable-number enumerations of C₂H₂ utilizers indicated enrichment of the population responsible. During C₂H₂ consumption in slurries incubated statically under air, maximal rates of N₂O evolution were 19 times higher than those in anaerobic incubations. After 20 days of enrichment with C₂H₂, the production of N₂O by slurries supplemented with C₂H₂ and nitrate was 10 times higher than that in the unenriched controls. A Nocardia- or Arthrobacter-like bacterium was isolated that grew on C₂H₂ but did not denitrify. The behavior of soil inoculated with this bacterium became similar to that of C₂H₂-enriched soil incubated aerobically. Ethanol, acetate, and acetaldehyde were identified in enrichment experiments, and denitrification in soil slurries was stimulated by addition of the supernatant from a pure culture grown on mineral medium with C₂H₂. These results indicate that denitrification can be stimulated by the actions of an aerobic, nondenitrifying C₂H₂-metabolizing population. Utilization of intermediate metabolites by denitrifiers and enhanced O₂ consumption are two possible mechanisms for this stimulation.     

Influence of GABA(A) Receptor α Subunit Isoforms on the Benzodiazepine Binding Site

Classical benzodiazepines, such as diazepam, interact with α_xβ₂γ₂ GABA_A receptors, x = 1, 2, 3, 5 and modulate their function. Modulation of different receptor isoforms probably results in selective behavioural effects as sedation and anxiolysis. Knowledge of differences in the structure of the binding pocket in different receptor isoforms is of interest for the generation of isoform-specific ligands. We studied here the interaction of the covalently reacting diazepam analogue 3-NCS with α₁S204Cβ₂γ₂, α₁S205Cβ₂γ₂ and α₁T206Cβ₂γ₂ and with receptors containing the homologous mutations in α₂β₂γ₂, α₃β₂γ₂, α₅β_1/2γ₂ and α₆β₂γ₂. The interaction was studied using radioactive ligand binding and at the functional level using electrophysiological techniques. Both strategies gave overlapping results. Our data allow conclusions about the relative apposition of α₁S204Cβ₂γ₂, α₁S205Cβ₂γ₂ and α₁T206Cβ₂γ₂ and homologous positions in α₂, α₃, α₅ and α₆ with C-atom adjacent to the keto-group in diazepam. Together with similar data on the C-atom carrying Cl in diazepam, they indicate that the architecture of the binding site for benzodiazepines differs in each GABA_A receptor isoform α₁β₂γ₂, α₂β₂γ₂, α₃β₂γ₂, α₅β_1/2γ₂ and α₆β₂γ₂.     

Metal complexes of new scorpionate ligands: 2,2′-Bis(pyrazolyl)ethylamine and its derivatives

The new bis(pyrazolyl)amine ligand NH₂CH₂CH(pz)₂ (1) was prepared from the reaction of N-[2,2-bis(pyrazolyl)ethyl]-1,8-naphthalimide with hydrazine monohydrate. A substituted derivative, C₆H₅CH₂NHCH₂CH(pz)₂ (2), was prepared by the reaction of 1 with benzaldehyde followed by reduction with NaBH₄. Ligand 1 was also converted by two methods to the new bitopic, para-linked bis(pyrazolyl)amine ligand p-C₆H₄(CH₂NHCH₂CH(pz)₂)₂, (3). The reactions of the ligands 1-3 with [Cu(PPh₃)₂]NO₃ yields {(PPh₃)Cu[(pz)₂CHCH₂NH₂]}NO₃, {(PPh₃)Cu[(pz)₂CHCH₂NHCH₂C₆H₅]}NO₃ and {[(PPh₃)Cu]₂[p-((pz)₂CHCH₂NHCH₂)₂C₆H₄]}(NO₃)₂·solvate, respectively. Complex {(N₃)₂Cu[(pz)₂CHCH₂NHCH₂C₆H₅]} was obtained from a methanol solution of 2, copper(II) acetate monohydrate and sodium azide. The complex {Cd[(pz)₂CHCH₂NHCH₂C₆H₅]₂}(PF₆)₂·3C₃H₆O was synthesized by reaction of the protonated form of ligand 2, [(pz)₂CHCH₂NH₂CH₂C₆H₅]PF₆, with Cd(acac)₂. In all of the structures the ligands are tridentate, bonding to the metal through the lone pair on the amine group as well as through the pyrazolyl rings - they act as true scorpionates. The solid state structures all have extensive non-covalent interactions, with the N-H functional groups of the amines participating in both N-H?π and N-H?O or N-H?N hydrogen bonding interactions.     

Synthesis and characterization of mono- and dinuclear nickel complexes with dichalcogenolate o-carboranyl ligands

Three mono- and dinuclear nickel complexes with dichalcogenolate o-carboranyl ligands were synthesized and characterized by X-ray crystallography. The reactions of Ni(COD)₂(COD=1,5-octadiene) with [(THF)₃LiE₂C₂B₁₀H₁₀Li(THF)]₂ (E=S, Se) in THF in the presence of air in different ratios afforded the mono- and dinuclear nickel complexes of formulae Li(THF)₄]₂[Ni(E₂C₂B₁₀H₁₀)₂] (E=S, 1a; E=Se, 1b) and [Li(THF)₄]₂[Ni₂(E₂C₂B₁₀H₁₀)₃] (E=S, 2a; E=Se, 2b). In 2a, two nickel atoms are connected by one chalcogen (η¹,η²-S₂C₂B₁₀H₁₀) bridging ligand with strong metal-metal interaction. Complex of formula (PPh₃)₂Ni(S₂C₂B₁₀H₁₀) · 0.5THF (3a) was also obtained from the reaction of (PPh₃)₂NiCl₂ and [(THF)₃LiS₂C₂B₁₀H₁₀Li(THF)]₂.     

Reactivity of [PdCl(μ-med)]2 with monodentate or bidentate ligands. Structure of the dinuclear complexes [Pd(μ-med)(PPh3)]2(BF4)2 and [Pd(μ-med)(bpy)]2(BF4)2. [Hmed=N-(2-mercaptoethyl)-3,5-dimethylpyrazole]

Treatment of the ligand N-(2-mercaptoethyl)-3,5-dimethylpyrazole with [Pd(CH₃COO)₂]₃ and reaction of [PdCl(μ-med)]₂ with pyridine (py) or triphenylphosphine (PPh₃) in the presence of AgBF₄ produced the following complexes: [Pd(CH₃COO)(μ-med)]₂, [Pd(μ-med)(py)]₂(BF₄)₂ and [Pd(μ-med)(PPh₃)]₂(BF₄)₂. Similar reactions carried out with 2,2^′-bipyridine (bpy) or 1,3-bis(diphenylphosphino)propane (dppp) produced [Pd(μ-med)(bpy)]_x(BF₄)_x (x=1 or 2) and [Pd(μ-med)(dppp)]_x(BF₄)_x (x=1 or 2). Treatment of [Pd(μ-med)(bpy)]_x(BF₄)_x with [PdCl₂(CH₃CN)₂] produced [Pd₃Cl₂(μ-med)₂(bpy)₂](BF₄)₂. Treatment of [Pd(μ-med)(dppp)]_x(BF₄)_x with [PdCl₂(CH₃CN)₂] produced a mixture of [Pd(μ-Cl)(dppp)]₂(BF₄)₂ and [Pd(μ-med)₂(dppp)]²⁺. X-ray crystal structures of [Pd(μ-med)(PPh₃)]₂(BF₄)₂ · 2CH₃CN and [Pd(μ-med)(bpy)]₂(BF₄)₂ · 0.5CH₃OH are presented.     

Dependence of the Post-Illumination Burst of CO2 on Temperature, Light, CO2, and O2 Concentration in Wheat (Triticum aestivum)

The effect of environmental factors on the post-illumination burst of CO₂ (PIB) and O₂ inhibition of apparent photosynthesis (APS) in wheat (Triticum aestivum L.) was studied in an open gas exchange system utilizing the mathematics of non-steady-state systems. Two components of inhibition by O₂ are suggested: one is caused by photorespiration as measured from the maximum rate of the PIB, and the second is direct inhibition as taken as APS_2%O2— (APS_x%O2+ PIB_x%O2) where X is the oxygen concentration. A primary PIB which occurred from 16–28 s after the darkening of the foliage was attributed to photorespiration. No primary PIB was observed at 2% O₂. At a CO₂ concentration of 100 μ/1 in the atmosphere (about 2.5 μM based on leaf intercellular concentration) and at 30°C and 145 nE/cm² nE/cm²·s, APS decreased curve-linearly with increasing O₂ and reached an O₂ compensation point of 560 μM (48% by volume), above which there was a net loss of CO₂ in the light. The PIB increased with increasing O₂ and became saturated at about 500 μM O₂ but decreased above 900 μM O₂. Direct inhibition of photosynthesis by O₂ increased with increasing O₂ concentration. Decreasing CO₂ concentration had an effect on the magnitude of the PIB similar to that of increasing O₂. At 30°C and 21% O₂, the PIB increased with decreasing CO₂ down to the CO₂ compensation point (I) of 1.4 μM (47 μM/l). Below Γ, both PIB and CO₂ evolution into the air in the light (at 21% O₂) increased and then decreased at CO₂ below 0.8 μM. The ratio of the PIB to APS_{2% o} O₂ increased linearly with increasing O₂/CO₂ ratio where O₂ was held constant at 21% and CO₂ was varied from 1.4 to 8.5 μM, while direct inhibition of photosynthesis expressed as a proportion of APS_2%O2 remained constant over this range. At low CO₂ concentration photorespiration as estimated by the PIB is the major part of O₂ photosynthesis, while at atmospheric CO₂ levels, direct inhibition is the major component. The PIB and APS at 2% and 21% O₂ increased hyperbolically with increasing irradiance and all became light-saturated at about 65 nE/cm₂ s. The percentage total O₂ inhibition of photosynthesis remained constant with increasing irradiance as did the relative contribution of direct O₂ inhibition or photorespiration (PIB) to total O₂ inhibition. The PIB and APS at 21% O₂ had similar temperature optima of 30°C when experimental conditions were adjusted to provide a constant internal O₂/CO₂ solubility ratio at varying temperatures. However, with a constant external CO₂ concentration, the temperature optimum for the PIB shifted upward to 35°C while that for APS at 21% O₂ remained at 30°C, which may be due to an increased O₂/CO₂ concentration in the leaf with increasing temperature.     

A 31P1H NMR study of the reactions of [Rh2(μ-Cl)2(cod)2] with unsymmetrical,bidentate ligands and hydrogen

[Rh₂(μ-Cl)₂(cod)₂] reacts with Ph₂PCH₂CH₂OMe (PC₂O), Ph₂P(CH₂)₃NMe₂ (PC₃N), PBuⁿPh₂ or PPh₃ to give [Rh(cod)L₂]Cl (L = PC₂O, PC₃N, PBuⁿPh₂, PPh₃). In the presence of hydrogen, [Rh(cod)L₂]Cl is converted to [RhClH₂L₃]. In contrast, [Rh(cod)(PC₂O)₂]BPh₄ reacts with H₂ to give [RhH₂(PC₂O)₂S₂]BPh₄ (S = solvent). With Ph₂PCH₂CH₂NMe₂ (PC₂N) or Ph₂PCH₂CH₂SMe (PC₂S), [Rh₂(μ-Cl)₂(cod)₂] reacts to form the chelate complexes cis- [Rh(PC₂N)₂]⁺ or cis-[Rh(PC₂S)₂]⁺, neither of which reacts with hydrogen under ambient conditions. The products of the reactions are characterized in situ by ³¹P¹H NMR spectroscopy.     

Inhibition of dark‐induced stomatal closure by fusicoccin involves a removal of hydrogen peroxide in guard cells of Vicia faba

Fusicoccin (FC) treatment prevents dark‐induced stomatal closure, the mechanism of which is still obscure. By using pharmacological approaches and laser‐scanning confocal microscopy, the relationship between FC inhibition of dark‐induced stomatal closure and the hydrogen peroxide (H₂O₂) levels in guard cells in broad bean was studied. Like ascorbic acid (ASA), a scavenger of H₂O₂ and diphenylene iodonium (DPI), an inhibitor of H₂O₂‐generating enzyme NADPH oxidase, FC was found to inhibit stomatal closure and reduce H₂O₂ levels in guard cells in darkness, indicating that FC‐caused inhibition of dark‐induced stomatal closure is related to the reduction of H₂O₂ levels in guard cells. Furthermore, like ASA, FC not only suppressed H₂O₂‐induced stomatal closure and H₂O₂ levels in guard cells treated with H₂O₂ in light, but also reopened the stomata which had been closed by darkness and reduced the level of H₂O₂ that had been generated by darkness, showing that FC causes H₂O₂ removal in guard cells. The butyric acid treatment simulated the effects of FC on the stomata treated with H₂O₂ and had been closed by dark, and on H₂O₂ levels in guard cells of stomata treated with H₂O₂ and had been closed by dark, and both FC and butyric acid reduced cytosol pH in guard cells of stomata treated with H₂O₂ and had been closed by dark, which demonstrates that cytosolic acidification mediates FC‐induced H₂O₂ removal. Taken together, our results provide evidence that FC causes cytosolic acidification, consequently induces H₂O₂ removal, and finally prevents dark‐induced stomatal closure.     

Coordination chemistry of the metalloligand [Pt2(μ-S)2(PPh3)4] with nickel(II) complexes - an electrospray mass spectrometry directed synthetic study

The reactivity of [Pt₂(μ-S)₂(PPh₃)₄] towards a range of nickel(II) complexes has been probed using electrospray ionisation mass spectrometry coupled with synthesis and characterisation in selected systems. Reaction of [Pt₂(μ-S)₂(PPh₃)₄] with [Ni(NCS)₂(PPh₃)₂] gives [Pt₂(μ-S)₂(PPh₃)₄Ni(NCS)(PPh₃)]⁺, isolated as its BPh₄ ⁻ salt; the same product is obtained in the reaction of [Pt₂(μ-S)₂(PPh₃)₄] with [NiBr₂(PPh₃)₂] and KNCS. An X-ray structure determination reveals the expected sulfide-bridged structure, with an N-bonded thiocyanate ligand and a square-planar coordination geometry about nickel. A range of nickel(II) complexes NiL₂, containing β-diketonate, 8-hydroxyquinolinate, or salicylaldehyde oximate ligands react similarly, giving [Pt₂(μ-S)₂(PPh₃)₄NiL]⁺ cations.     

Alkylimido complexes of titanium(IV)

TiCl₄ reacts with t-butylamine in benzene to give [Ti(NCMe₃)Cl₂(NH₂CMe₃)₂]_x and t-butylamine hydrochloride. The IR spectrum indicates both c/s and trans metal dichlorides (300; and 308, 208 cm⁻¹). In the ¹³C NMR spectrum the t-butylimido quaternary carbon resonance occurs at 72.1 ppm. A dimeric structure incorporating symmetric t-butylimido bridges is proposed. TiCl₄ in benzene react under reflux with two equivalents of Me₃SiNHCMe₃ to give [Ti(NCMe₃)Cl₂(NH₂CMe₃)]_x and with iso-propylamine and ethylamine to give complexes of the form [Ti(NR)Cl₂(NH₂R)₂]_x. Broad bands below 800 cm⁻¹ in the IR spectra suggest polymeric MNM bridges. For [Ti(NCHMe₂)Cl₂(NH₂CHMe₂)]_x the iso-propylimido CH resonance in the ¹³C NMR spectrum occurs at 67 ppm. [Ti(NCMe₃)Cl₂(NH₂CMe₃)₂]₂ reacts with L=bipy or tmed to give [Ti(NCMe₃)Cl₂(L)]₂, and TiCl₄ reacts with two equivalents of Me₃SiNHCMe₃ in benzene and then tmed to give [Ti(NCMe₃)Cl₂(tmed)]₂. The ¹³C NMR spectrum shows the t-butylimido quaternary carbon resonance at 73.5 ppm and the tmed resonances are chemically equivalent. A dimeric μ-NCMe₃ bridging structure is proposed for the complex.     

Effects of Metals on Methanogenesis, Sulfate Reduction, Carbon Dioxide Evolution, and Microbial Biomass in Anoxic Salt Marsh Sediments

The effects of several metals on microbial methane, carbon dioxide, and sulfide production and microbial ATP were examined in sediments from Spartina alterniflora communities. Anaerobically homogenized sediments were amended with 1,000 ppm (ratio of weight of metal to dry weight of sediment) of various metals. Time courses in controls were similar for CH₄, H₂S, and CO₂, with short initial lags (0 to 4 h) followed by periods of constant gas production (1 to 2 days) and declining rates thereafter. Comparisons were made between control and experimental assays with respect to initial rates of production (after lag) and overall production. Methane evolution was inhibited both initially and overall by CH₃HgCl, HgS, and NaAsO₂. A period of initial inhibition was followed by a period of overall stimulation with Hg, Pb, Ni, Cd, and Cu, all as chlorides, and with ZnSO₄, K₂CrO₄, and K₂Cr₂O₇. Production of CO₂ was generally less affected by the addition of metals. Inhibition was noted with NaAsO₂, CH₃HgCl, and Na₂MoO₄. Minor stimulation of CO₂ production occurred over the long term with chlorides of Hg, Pb, and Fe. Sulfate reduction was inhibited in the short term by all metals tested and over the long term by all but FeCl₂ and NiCl₂. Microbial biomass was decreased by FeCl₂, K₂Cr₂O₇, ZnSO₄, CdCl₂, and CuCl₂ but remained generally unaffected by PbCl₂, HgCl₂, and NiCl₂. Although the majority of metals produced an immediate inhibition of methanogenesis, for several metals this was only a transient phenomenon followed by an overall stimulation. The initial suppression of methanogenesis may be relieved by precipitation, complexation, or transformation of the metal (possibly by methylation), with the subsequent stimulation resulting from a sustained inhibition of competing organisms (e.g., sulfate-reducing bacteria). For several environmentally significant metals, severe metal pollution may substantially alter the flow of carbon in sediments.