邻菲啰啉计算光度法同时测定生物浸出样品中Fe（Ⅱ）和Fe（Ⅲ）

邻菲啰啉光度法常用于Fe（Ⅱ）测定,但受到试样中Fe（Ⅲ） 对测定的影响,因此不能直接用于生物浸出样品中Fe（Ⅱ）和Fe（Ⅲ） 的同时测定. 为此,基于Fe（Ⅱ）邻菲啰啉特征吸收曲线以及混合铁中Fe（Ⅲ） 对Fe（Ⅱ）测定的线性影响关系,建立了基于Fe（Ⅱ）和全铁同时测定Fe（Ⅱ）和Fe（Ⅲ）的计算光度法,并研究了生物浸出样品中典型金属离子（Cu²⁺、Ni²⁺、Cd²⁺、Co²⁺）以及试样溶解与储放对测定的影响.方法可准确地测定含铁次生矿物和生物浸出液中铁价态组成,应用于生物浸出矿渣、细胞表面中常量或微量的Fe（Ⅱ）和Fe（Ⅲ） 组成分析,具有简便快速的特点.     

邻菲啰啉-Fe(Ⅱ)分光光度法测定头孢唑啉钠

建立了用邻菲啰啉-Fe(Ⅱ)分光光度法测定头孢唑啉钠的方法 .头孢唑啉钠在0.10mol·L-1 NaOH溶液中,100℃水浴加热降解为含巯基的化合物.巯基化合物把Fe3+还原为Fe2+.加入邻菲啰啉显色,通过测定生成的橘红色配位化合物的吸光度间接测定头孢唑啉钠的含量.头孢唑啉钠浓度在0.02~40mg·L-1范围内呈现良好线性关系,线性回归方程A=0.043c(mg·L-1)-0.001,相关系数R=0.998 8,表观摩尔吸光系数ε=2.05×104 L·(mol·cm)-1,相对标准偏差RSD=1.27%,检测限(3σ/k)0.065mg·L-1.在此基础上,测定了市售头孢唑啉钠粉针剂的含量,回收率在99.17%~101.2%之间,结果令人满意.     

邻菲啰啉-Fe(Ⅱ)体系光度法间接测定头孢噻肟钠

基于头孢噻肟钠在0.3 mol/L NaOH溶液中沸水浴降解产物具有还原性,在酸性介质中可将Fe(Ⅲ)还原为Fe(Ⅱ),邻菲罗啉能与所生成的Fe(Ⅱ)显色生成红色络合物,最大吸收波长λ=508 nm;表观摩尔吸光系数ε=1.1×104 L·mol-1·cm-1;头孢噻肟钠在0.4～80 μg/mL范围内呈良好的线性关系;线性回归方程为A=-0.00204 0.01989ρ(μg/mL);线性相关系数r=0.9998;检出限为0.18 μg/mL;RSD为1.2%(5.0 μg/mL,n=11);平均回收率为99%.初步探讨了反应机理,并优化了对头孢噻肟钠的测定条件.     

邻菲啰啉-Fe(Ⅱ)体系光度法间接测定硫普罗宁

在酸性介质中硫普罗宁可将Fe(Ⅲ)还原为Fe(Ⅱ),邻菲啰啉能与生成的Fe(Ⅱ)显色,最大吸收波长为508 nm。基于此,通过测定Fe(Ⅱ)的量间接测定了硫普罗宁的含量。硫普罗宁在0.08~20μg/mL范围内与ΔA呈良好的线性关系,线性回归方程为ΔA=0.01283+0.06516c(μg/mL),线性相关系数为0.9998,检出限为0.042μg/mL。本方法可用于实际药品中硫普罗宁含量的测定。     

流动注射-邻菲啰啉协同催化化学发光法测定痕量的铜

本文拟订了邻菲啰啉-CTMAB-H_2O_2-Co(Ⅱ)-Cu(Ⅱ)协同催化化学发光体系流动注射测定痕量Cu(Ⅱ)的新方法。方法的检出限为8×10~(-12)g/ml Cu(Ⅱ),线性范围为1×10~(-10)-4×10~(-8)g/ml Cu(Ⅱ),相对标准偏差为0.9％分析速度为160样/小时。本法用于头发和水样中Cu(Ⅱ)的测定取得了满意的结果。     

动力学光度法测定痕量邻菲咯啉

在稀醋酸介质中,痕量邻菲咯啉对高碘酸钾氧化玫瑰桃红R褪色反应有明显的催化作用,据此建立了测定邻菲咯啉的催化动力学光度法。讨论了反应的动力学参数。方法的线性范围为0．005—0．1mg／L;检出限为3.0μg／L。方法灵敏度高,简便,快速,选择性好,用于合成水样及废水、河水中邻菲咯啉含量的测定,结果满意。     

锰（Ⅱ）—苯酚红—高碘酸钾—邻菲Luo啉体系催化光度法测定痕量锰的研究

研究了在碱性介质中，以邻菲Ｌｕｏ啉为活化剂，锰（Ⅱ）催化高碘酸钾氧化苯酚红褪色指标反应及其动力学条件，建立了测定痕量锰的新方法。锰的浓度在０．０．０７μｇ／ｍＬ范围内为线性关系，检测限为３．０ｎｇ／ｍＬ。用于盐酸试剂中痕量锰的测定，结果良好。     

邻菲口罗啉-Fe(Ⅱ)体系光度法间接测定头孢噻肟钠

基于头孢噻肟钠在0.3 mol/L NaOH溶液中沸水浴降解产物具有还原性,在酸性介质中可将Fe(Ⅲ)还原为Fe(Ⅱ),邻菲口罗啉能与所生成的Fe(Ⅱ)显色生成红色络合物,最大吸收波长λ=508 nm;表观摩尔吸光系数ε=1.1×104L.mol-1.cm-1;头孢噻肟钠在0.4~80μg/mL范围内呈良好的线性关系;线性回归方程为A=-0.00204 0.01989ρ(μg/mL);线性相关系数r=0.9998;检出限为0.18μg/mL;RSD为1.2%(5.0μg/mL,n=11);平均回收率为99%。初步探讨了反应机理,并优化了对头孢噻肟钠的测定条件。     

汞-邻菲啰啉-刚果红缔合体系光度法测定痕量汞

在含有汞(Ⅱ)试液中,先后加入乙酸-乙酸钠缓冲溶液(pH 5.7)、1.0×10-3mol.L-1邻菲啰啉溶液0.8 mL、4.0×10-4mol.L-1刚果红溶液1.2 mL及10 g.L-1阿拉伯树胶(GA)溶液0.8 mL使反应生成汞与邻菲啰啉和刚果红的络合物。在此缔合体系中,GA对显色反应兼有增敏和增稳作用。汞(Ⅱ)质量浓度在1.0 mg.L-1范围内与其吸光度呈线性关系。反应体系的吸收峰位于540 nm波长处,在此波长条件下测定其表观摩尔吸光系数为8.49×104L.mol-1.cm-1。此方法已应用于测定河水中汞量,求得相对标准偏差(n=5)小于2.0%,平均回收率为100.4%。     

邻菲啰啉－曙红体系共沉淀纸上分光光度法测铁

采用邻菲 啉试剂作为络合剂，与铁（Ⅱ）形成络阳离子后，用曙红阴离子缔合沉淀之，再加入酚酞共沉淀剂使其缔合沉淀完全。将络离子缔合物吸滤在滤纸，后者直接置于７２１型分光光度计中，用吸光度差值法定量。操作简单快速，选择性好，灵敏度高；以取样体积１０ｍＬ计，最小检出浓度为１．５×１０￣（－９）ｇ／ｍＬ。     

Simultaneous Speciation Analysis of Fe(II) and Fe(III) in Mineral Samples by Using Capillary Electrophoresis

Capillary electrophoresis is used as a means of cation separation for cationic speciation analysis. Acceptable separation of ferrous and ferric iron was achieved by using a mixed complexing agent run buffer which gave stable species in solution. These iron species, and total iron, were determined simultaneously in certified reference materials with a single digestion step. A variety of digestion techniques were compared, primarily for their non‐oxidative capabilities in order to preserve the oxidation state of iron in the mineral samples. The most favorable recoveries resulted from a continuous flow nitrogen purge technique. Total iron levels obtained from the CE method were compared with those determined by two spectroscopic techniques, with similar results obtained using the different instrumental methods.     

Determination of Fe(II), Fe(III) and Fetotal in thermal water by ion chromatography spectrophotometry (IC-Vis)

Determination of iron speciation in water is one of the major challenges in environmental analytical chemistry. Here, we present and discuss a method for sampling and analysis of dissolved Fe(II), Fe(III), and Fe_total concentrations in natural thermal water covering a wide range of temperature, pH, chemical composition, and redox conditions. Various methods were tried in the collection, preservation, and storage of natural thermal water samples for the Fe(II) and Fe(III) determinations, yet the resultant Fe speciation determined was often found to be significantly affected by the methodology applied. Due to difficulties in preserving accurate Fe speciation in natural samples for later laboratory analysis, a field-deployed on-site method using ion-chromatography and spectrophotometry was developed and tested. The IC-Vis method takes advantage of ion chromatographic separation of Fe(II) and Fe(III), followed by post-column colour reaction and spectrophotometric detection, thus allowing analysis of Fe(II) and Fe(III) in a single 15-minute run. Additionally, Fe_total can be determined after sample oxidation. The analytical detection limits are ~2 µg L^?1 (LOD) using 200–1000 µL injection volumes and depend on the blank and reagent quality. The power of this method relies on the capability to directly determine a wide range of absolute and relative concentrations of Fe(II) and Fe(III) in the field. The field-deployed IC-Vis method was applied for the determination of Fe(II) and Fe(III) concentrations in natural thermal water with discharge temperatures ranging from 12°C to 95°C, pH between 2.46 and 9.75, and Fe_total concentrations ranging from a few μg L^?c up to 8.3 mg L^?1.     

A Sensitive Fluorescence Quenching Method for the Determination of Iron( Ⅱ） with 1,10-Phenanthroline

A sensitive and selective fluorescence quenching method for the determination of Fe²⁺ with 1,10‐phenanthroline was developed. The fluorescence intensity of 1,10‐phenanthroline at λ_ex of 266 run and λ_em of 365 nm was constant in the range of pH 4.0 to 10.0 and decreased linearly upon addition of Fe²⁺ to its solution. This decrease was mainly due to a static quenching effect caused by the formation of a non‐fluorescent complex of Fe²⁺ with 1, 10‐phenanthroline. The total amount of iron was determined by using hydroxylamine hydrochloride to reduce Fe³⁺ to Fe²⁺. The linear range was from 5.0 × 10–⁷ to 2.0 × 10–⁵ mol/L with a detection limit of 2.4 × 10–⁸ mol/L at 3s?. The quenching constant of Fe²⁺ to 1,10‐phenanthroline was calculated to be (5.70 × 0.05) × 10⁴ L/mol at 25 °C. Effects of foreign ions on the determination of Fe²⁺ were investigated. The results of the new method for the determination of iron in tap water and natural water samples were in good agreement with those obtained by graphite atomic absorption spectrometry.     

镀铜锌粒还原-流动注射-化学发光同时测定两种价态的铁

建立了镀铜的锌粒在线还原微柱，还原Fe3+成Fe2+，鲁米诺中加EDTA增强鲁米诺-溶解氧-铁（Ⅱ）系统的发光强度，同时测两种价态的铁，提高灵敏度160倍，线性范围均为1×10－9～1×10－5mol／L．RSD≤6．0％，Fe3+和Fe2+的检出限分别为3．5×10－10和2．7×10-10mol／L。每小时可测定60个试样，测定结果与标准方法无显著差异。     

Simple and Simultaneous Method for Determination of Palladium(II) and Ruthenium(III) using Second-Order-Derivative Spectrophotometry

Abstract

A simple, sensitive, and selective second-order-derivative spectrophotometric method has been developed for the simultaneous determination of palladium(II) and ruthenium(III) using 2-hydroxy-3-methoxy benzaldehyde thiosemicarbazone (HMBATSC) as a chromophoric reagent. The reagent (HMBATSC) reacts with Pd(II) and Ru(III) at pH 3.0, forming soluble yellowish green and dark brown species, respectively. Palladium and ruthenium present in the mixture were simultaneously determined without solving the simultaneous equations by measuring the second derivative amplitudes at 445 nm and 385 nm, respectively. Further, the Beer's law was obeyed in the range 0.21–12.78 µg mL^?1 and 0.25–13.42 µg mL^?1 for Pd(II) and Ru(III), respectively. A large number of foreign ions did not interfere in the present method. The proposed method was successfully applied for the determination of palladium in hydrogenation catalysts and ruthenium in water samples.     

Simultaneous Determination of Nickel(II) and Cobalt(II) by Second-Derivative Spectrophotometry

4-(2-Pyridylazo) resorcinol, PAR, is shown to be useful for simultaneous determination of cobalt(II) and nickel(II) using second-derivative spectrophotometric method with controlled experimental parameters. This method allows the determination of 0.20-1.25 ppm of nickel(II) and 0.25-1.50 ppm of cobalt(II) in mixtures with good precision and accuracy. This method has advantages of simplicity, speed and requires no prior separations.     

Simultaneous determination of Fe(II) and Fe(III) in waters by capillary isotachophoresis

An ITP method for the simultaneous determination of Fe(II) and Fe(III) in waters, based on separation of their EDTA and fluoride complexes, respectively, was developed. The leading electrolyte used consists of chlorides, La(III) as co-counter ion and is buffered with β-alanine to pH = 3.5. The terminating electrolyte contains caproic acid and L-histidine (pH = 4.5). The method was validated and tested with samples of artificial, ground and treated water with good results, comparable to those obtained by other analytical techniques. Fe(II) and Fe(III) up to 20 mg/L were measured with an RSD = 1.4–1.5% and detection and determination limits of 0.8–0.9 and 3.0–3.5 mg/L, respectively. The ITP method can be recommended for routine utilization in hydroanalytical laboratories.     

Simultaneous determination of Fe(II) and Fe(III) in waters by capillary isotachophoresis

An ITP method for the simultaneous determination of Fe(II) and Fe(III) in waters, based on separation of their EDTA and fluoride complexes, respectively, was developed. The leading electrolyte used consists of chlorides, La(III) as co-counter ion and is buffered with beta-alanine to pH = 3.5. The terminating electrolyte contains caproic acid and L-histidine (pH = 4.5). The method was validated and tested with samples of artificial, ground and treated water with good results, comparable to those obtained by other analytical techniques. Fe(II) and Fe(III) up to 20 mg/L were measured with an RSD = 1.4-1.5% and detection and determination limits of 0.8-0.9 and 3.0-3.5 mg/L, respectively. The ITP method can be recommended for routine utilization in hydroanalytical laboratories.     

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

The H-point standard addition method (HPSAM) for simultaneous determination of Fe(II) and Fe(III) is described. The method is based on the difference in the rate of complex formation of iron in two different oxidation states with Gallic acid (GA) at pH 5. Fe(II) and Fe(III) can be determined in the range of 0.02–4.50 μg ml⁻¹ and 0.05–5.00 μg ml⁻¹, respectively, with satisfactory accuracy and precision in the presence of other metal ions, which rapidly form complexes with GA under working conditions. The proposed method was successfully applied for simultaneous determination of Fe(II) and Fe(III) in several environmental and synthetic samples with different concentration ratios of Fe(II) and Fe(III).