Fe(Ⅲ)-草酸-葡萄糖酸钙媒质体系间接电化学还原及棉织物染色的研究

应用循环伏安法研究了Fe(Ⅲ)-草酸-葡萄糖酸钙媒质体系的电化学行为及其可能的反应机理,实验表明Fe(Ⅱ)-葡萄糖酸盐起着最终的还原作用。电解还原时间、工作电压和阴极面积这三个因素影响着电流效率,在Fe(Ⅲ)-草酸-葡萄糖酸钙媒质体系中,还原大红R的电流效率最高可达89%,其电解还原时间10min,工作电压4V,阴极面积40cm2。     

NanoTiO2-CNT复合膜电极在DMF溶液中对糠醛的异相电催化还原

通过在乙醇中电化学溶解Ti金属阳极合成前驱体Ti(OEt)4和溶胶-凝胶法在Ti表面修饰一层纳米TiO2-碳纳米管(nanoTiO2-CNT)复合膜, 采用循环伏安和电解合成法研究了nanoTiO2-CNT复合膜电极在N, N-二甲基甲酰胺(DMF)中的氧化还原行为以及对糠醛(furfural)还原的电催化活性. 结果发现, nanoTiO2-CNT电极在阴极扫描时有两对氧化还原峰, 可逆半波电位E r1/2 分别为－1.27 V和－2.44 V(vs SCE, 扫描速度100 mV•s-1), 分别对应于TiO2/Ti2O3氧化还原电对的可逆电极过程和TiO2/Ti(OH)3电对的准可逆电极过程；在DMF电解液中nanoTiO2-CNT复合膜中的Ti(IV)/Ti(III)氧化还原电对作为媒质间接电还原糠醛为糠醇, 反应机理为电化学偶联随后化学催化反应(EC′)机理.     

有机物的阴极间接电氧化(Ⅱ)——烯酸的阴极间接环氧化

建立一种新的阴极间接电氧化体系 ,以VO(acac) 2 OOH/VO(acac) 2 为氧化还原媒质 ,通过催化阴极由O2 电还原产生的H2 O2 对某些烯酸如顺丁烯二酸、反丁烯二酸和丁烯酸等进行间接环氧化 .研究了 pH值、温度、电流密度等因素对反应的影响 .本文是继前文[1]之后所建立的又一新的氧化还原媒质 .此研究对有机电合成的发展具有重要的理论意义和实际意义 .     

电化学氧化法合成茴香醛（Ⅰ）

介绍了茴香醛的合成和利用。报道了以对甲苯酚为原料，用池外式间接电化学氧化法合成茴香醛的最佳条件。电氧化再生媒质的电流效率达９４．０～９５．０％。     

阴极间接电氧化——二甲基砜的有机电合成 (Ⅰ )

本文建立一种阴极间接电氧化体系 ,以WO52 -/WO4 2 -催化阴极还原生成的H2 O2 ,间接氧化二甲基亚砜 (DMSO) ,得到产品二甲基砜 :阴极间接电氧化体系具有重要的理论意义和普遍的应用价值 .本文研究了各种因素对生成二甲基砜电流效率的影响 ,获得了最佳工艺条件 ,电流效率大于 70 % ,母液可循环使用无污染 .     

纳米TiO_2膜修饰电极异相电催化还原马来酸

通过电化学合成前驱体和溶胶-凝胶法在Ti表面修饰一层纳米TiO_2膜，SEM， XRD测试表明晶型为锐钛矿型，晶粒平均尺寸为25 nm。采用循环伏安法、循环方波 伏安法和电解合成法研究了纳米TiO_2膜电极在硫酸介质中的氧化还原行为以及对 马来酸（maleic acid）还原的电催化活性。结果表明，纳米TiO_2膜电极在阴极扫 描时有两对可逆氧化还原峰，可逆半波电位E_(1/2)~r分别为-0.53 V和-0.92 V（ sv. SCE，扫描速度0.05 V·s~(-1)），对应于TiO_2/Ti_2O_3和TiO_2/Ti(OH)_3两 个氧化还原电对的可逆电极过程。其中TiO_2/Ti_2O_3电对对马来酸具有异相电催 化还原活性，纳米TiO_2膜中的Ti~(IV)/Ti~(III)氧化还原电对作为媒质间接电还 原马来酸为丁二酸（butane diacid），反应机理为电化学偶联随后化学催化反应 （EC'）机理。     

三维电极电化学反应器对有机废水的降解研究

本文提出一种基于三维电极电化学反应器处理有机废水的新技术 ,结果表明 :该反应器能有效地去除苯胺 ,但其去除率受外加电压、溶液中Fe2 +的浓度、pH值及处理时间 (t)的影响较大 .该项技术处理有机废水效果明显 ,主要是基于电致过氧化氢 ,在Fe2 +存在情况下迅速生成对有机物有很强氧化作用的羟基自由基 .通过ESR法测出了在该电化学反应器处理废水过程中产生的羟基自由基     

活性碳纤维阴极电芬顿反应降解微囊藻毒素研究

以具有高比表面积的活性碳纤维作为阴极,通过电芬顿反应降解水中微囊藻毒素(MCRR,MCLR)的电化学方法系统考察了电流密度、pH值和Fe2+浓度等因素对微囊藻毒素降解效果的影响.实验结果表明,在Fe2+浓度为1.0mmol/L和电流密度为6.6mA/cm2条件下,电化学处理60min,MCRR(8.81mg/L)去除率为75%,MCLR(6.36mg/L)去除率为94%.证明过氧化氢可以通过电化学还原在活性碳纤维阴极表面高效产生,微囊藻毒素可被高效降解去除.     

CoTPP电化学催化还原溴代环己烷的机理

以电化学循环伏安、现场ESR电化学以及现场薄层电化学方法研究了电生Co(Ⅰ)TPP与溴代环己烷的反应机制.在DMF中,Co(Ⅱ)/Co(Ⅰ)的氧化还原有明显的催化溴代环己烷还原的特征,反应现场有自由基生成.反应产物之一是Co-C键化合物,可以在-1.30V(SCE)一电子还原.当存在CH₂=CHCN时,生成另一种Co-C键化合物,该化合物在-1.10V(SCE)处一电子还原.证明溴代环己烷与Co(Ⅰ)TPP反应主要是经过形成烷基自由基的机制进行的.     

纳米TiO_2膜修饰电极异相电催化还原马来酸

通过电化学合成前驱体和溶胶 -凝胶法在Ti表面修饰一层纳米TiO2 膜 ,SEM ,XRD测试表明晶型为锐钛矿型 ,晶粒平均尺寸为 2 5nm .采用循环伏安法、循环方波伏安法和电解合成法研究了纳米TiO2 膜电极在硫酸介质中的氧化还原行为以及对马来酸 (maleicacid)还原的电催化活性 .结果表明 ,纳米TiO2 膜电极在阴极扫描时有两对可逆氧化还原峰 ,可逆半波电位Er1/ 2 分别为 -0 .5 3V和 -0 .92V (vs .SCE ,扫描速度 0 .0 5V·s-1) ,对应于TiO2 /Ti2 O3 和TiO2 /Ti(OH) 3 两个氧化还原电对的可逆电极过程 .其中TiO2 /Ti2 O3 电对对马来酸具有异相电催化还原活性 ,纳米TiO2 膜中的TiⅣ/TiⅢ 氧化还原电对作为媒质间接电还原马来酸为丁二酸 (butanediacid) ,反应机理为电化学偶联随后化学催化反应 (EC′)机理 .     

Simultaneous identification of historical pigments Prussian blue and indigo in paintings by electrospray mass spectrometry

A new analytical protocol for identification of Prussian blue (PB) and indigo was proposed. Pigments useful for dating of artworks were detected by flow injection analysis/electrospray ionization mass spectrometry after alkalization of their suspensions in water, decomposition of PB to iron (III) hydroxide and hexacyanoferrate (II) and reduction of indigo to soluble leucoindigo using sodium dithionite. Limits of detection (PB 47 pg, indigo 59 pg) complied with requirements for analysis of microsamples of historical paintings. Potential of the developed method was proven in analysis of blue samples of two oil paintings from the 20^th century. Further, PB was confirmed in a microsample from a painting of ‘Crucifixion’, St. Sebestian church on St. Hill in Mikulov, Czech Republic. Copyright © 2013 John Wiley & Sons, Ltd.     

Catalytic spectrophotometric determination of trace aluminium with indigo carmine

A new catalytic spectrophotometric method is described for the determination of trace amounts of Al(III). The methods based on catalytic action of Al(III) on the oxidation of indigo carmine (IC) by ammonium persulfate in hexamethylene tetramine-hydrochloric acid ((CH2)6N4-HCl) buffer medium (pH 5.4) and in the presence of surfactant-TritonX-100. The effects of some factors on the reaction speed were investigated. Aluminium concentration is linear for 0-1.2x10(-7) g/ml in this method. The detection limit of the proposed method is 1.96x10(-8) g/ml. Most of the foreign ions except for Cu(II), Fe(III) do not interfere with the determination, and the interference of Cu(II) and Fe(III) in this method can be removed by extraction with sodium diethyldithiocarbamate-carbon tetrachloride (DDTC-CCl4). This system is a quasi-zero-order reaction for Al(III), but it is a quasi-first-order reaction for IC. The apparent rate constant is 2.62x10(-5) s-1 and the apparent activation energy is 6.60 kJ/mol in the system. The proposed method was applied to the determination of trace aluminium(III) in real samples with satisfactory results.     

Oxidimetric determination of indigo with iron(III) and hexacyanoferrate(III)

The use of iron(III) in sulphuric acid medium and of potassium hexacyanoferrate(III) in hydrochloric acid medium has been investigated for the oxidimetric determination of indigo and indigo sulphonic acid. Conditions have been established for the assay of the dye with iron(III) sulphate at 100 degrees and with potassium hexacyanoferrate(III) at room temperature.     

Limitation of ferrozine method for Fe(II) detection: reduction kinetics of micromolar concentration of Fe(III) by ferrozine in the dark

The dark reduction kinetics of micromolar concentrations of Fe(III) in aqueous solution were studied in the presence of millimolar concentrations of ferrozine (FZ) over the pH range 4.0–7.0. A pseudo-first-order kinetics model was used to describe Fe(III) reduction at pH 4.0 and 5.0, and the reduction rate decreased with increasing pH or initial Fe(III) concentration. A more molecular-based kinetics model was developed to describe Fe(III) reduction at pH 6.0 and 7.0. From this model, the intrinsic rate constants (k₁) of Fe(III) reduction by FZ in the dark were obtained as 0.133 ± 0.004 M^?1 s^?1 at pH 6.0 and 0.101 ± 0.009 M^?1 s^?1 at pH 7.0. It was also found in this model that a higher pH, a higher concentration of Fe(III), a lower concentration of FZ and less incubation time led to a lower fraction of Fe(III) reduction by FZ in the dark.     

Microdetermination of nitrates and nitramines-I Titrimetric methods based on the reduction with iron(II), titanium(III), and a mixture of both

Organic and inorganic nitrates are satisfactorily determined on the microscale by reduction with Fe(II). Titanium(III) reduces the nitrates in strongly acidic, citrate-buffered, and acetate-buffered media with the comsumption of 3, 6 and 8 equivalents respectively of Ti(III) per nitrate group. Nitramines are determined by reduction with a mixture of Ti(III) and Fe(II). Determination of nitrates and nitramines by trans-nitration with salicylic acid is suitable on the microscale. A new electrolytic reduction automatic microburette was devised for the reduction, storage and use of the titanium(III) solution.     

Thermometrische schnellbestimmung des chroms

A rapid thermometric method has been developed for the determination of dichromate ions. The method can also be applied in the presence of other oxidizing agents [e.g. Fe(III)in chromium ore analysis]. Hydrogen peroxide was used as reagent which permits the reduction of dichromate ions to chromium(III) without the reduction of Fe(III).     

Simultaneous kinetic determination of Fe(III) and Fe(II) by H-point standard addition method

The H-point standard addition method (HPSAM) was applied to kinetic data for simultaneous determination of Fe(III) and Fe(II) or selective determination of Fe(III) in the presence of Fe(II). The method is based on the difference in the rate of two processes; reduction of Fe(III) with Co(II) and subsequent complex formation of resulted Fe(II) with 1,10-phenanthroline, and direct complex formation between Fe(II) and 1,10-phenanthroline in pH 3 and cetyl trimethyl ammonium bromide, CTAB, micellar media. Fe(III) can be determined in the range of 0.75-5.13 mug ml(-1)with satisfactory accuracy and precision in the presence of excess Fe(II) under working conditions. The proposed method was successfully applied to the simultaneous determination of Fe(III) and Fe(II) and also to the selective determination of Fe(III) in the presence of Fe(II) in several synthetic mixtures containing different concentration ratios of Fe(III) to Fe(II).     

A chemiluminescence method for the detection of electrochemically generated H2O2 and ferryl porphyrin

Electrochemical formation of H2O2 and the subsequent ferryl porphyrin were examined by measuring luminol chemiluminescence and absorption spectrum using flow-injection method. Emission was observed under the cathodic potential (0.05 V at pH 2.0 and -0.3 V at pH 11.0) by the electrochemical reduction of buffer electrolytes solution but no emission was observed at anodic potentials. Fe(III)TMPyP solution was added at the down stream of the working electrode and was essential for the emission. Removal of dissolved O2 resulted in the decrease of emission intensity by more than 70%. In order to examine the lifetime of reduced active species, delay tubes were used in between working electrode and Fe(III)TMPyP inlet. Experimental results suggested the active species were stable for quite long. The emission was quenched considerably (>90%) when hydroperoxy catalase was added at the down stream of the working electrode whereas SOD had little effect. Significant inhibition of the emission by the addition of alkene at the down stream of the Fe(III)TMPyP inlet was considered as evidence of oxo-ferryl formation. The spectra at reduction potential under aerated condition were shifted to the longer wavelength (>430 nm) compared to the original spectrum of Fe(III)TMPyP (422 nm). All the spectra were perfectly reproduced by a combination of Fe(III)TMPyP and O=Fe(IV)TMPyP (438 nm) spectra. These observations lead to the conclusion that H2O2 was produced first by electrochemical reduction of O2, which then converted Fe(III)TMPyP into O=Fe(IV)TMPyP to activate luminol. The current efficiencies for the formation of H2O2 were estimated as about 30-65% in all over the pH.     

Catalytic Oxidation of Indigo Carmine in the Presence of Silver Nanoparticles: Application to Groundwater Analysis

The oxidation of indigo carmine by potassium hexacyanoferrate(III) is catalyzed by trace of silver nanoparticle (AgNP). The reaction is followed UV‐Vis absorption spectrophotometrically by measuring the change in the absorption spectra (λ_max 612 nm). The catalytic oxidation reaction is used for the quantification of indigo carmine. The calibration graph was linear in the concentration range 50 nM—1.8 μM of indigo carmine. The variables affecting the method have been optimized. The method is applied to the determination of indigo carmine in groundwater samples with the satisfactory results.