Fe(Ⅲ)改性海藻酸钠微球微萃取-原子荧光光谱法测定海水中As(Ⅴ)和As(Ⅲ)

首次制备了Fe(Ⅲ)改性修饰的海藻酸钠微球作为固相微萃取材料,用该微球装载的微柱能够在不同形态砷化物共存时选择性富集水样中As(Ⅴ)。结合氢化物发生-原子荧光光谱法,可以实现实际水体样中无机As(Ⅲ)和As(Ⅴ)的形态分析。具体过程为：(1)以0.1 mol·L-1柠檬酸为介质,在填充柱后流出液中选择性测定As(Ⅲ);(2)以20 g·L-1硫脲-10 g·L-1抗坏血酸溶液为预还原剂,5%盐酸为介质,测定不经过微萃取柱分离的原始水体样品中无机总砷(As(Ⅲ)和As(Ⅴ)),然后以差减法计算As(Ⅴ)的量。Fe(Ⅲ)改性海藻酸钠微球制备过程简便,成本低廉、 绿色环保,相应基于Fe(Ⅲ) 改性海藻酸钠微球微萃取过程的砷形态分离分析微萃取柱及其光谱联用技术,可以有效、 快速地测定自然水体中As(Ⅲ)和As(Ⅴ),具有实际意义。     

磷酸钇共沉淀分离富集原子吸收光谱测定氯化镍和硫酸锰中的痕量铅和铁

研究了采用磷酸钇(YPO4)作为共沉淀载体选择性分离富集NiCl2,MnSO4溶液中的痕量Pb2 和Fe3 ,并用火焰原子吸收光谱(FAAS)测定的方法.共沉淀受pH,YCl3和H3PO4溶液用量的影响.结果显示,在溶液pH 3.0～4.0时,YPO4能够定量共沉淀氯化Ni中的Pb和Fe以及硫酸Mn中的Pb.对于20mL溶液,Pb和Fe的检出限分别为1.63×10-2 mg·L-1和4.58×10-2mg·L-1.在NiCl2溶液中,Pb和Fe的标准加人回收率分别为100.91%和99.73%;在MnSO4溶液中,Pb和Fe的标准加入回收率分别为99.45%和98.98%.实验基本消除了基体干扰,取得了较满意的结果.     

5-Cl-PADAB显色树脂相分光光度法测定蒙药中微量Fe(Ⅲ)的研究

本文提出了在pH 6 0 0的HAc NaAc缓冲介质中 ,Fe(Ⅲ )与 5 Cl PADAB生成有色络合物 ,与强酸性阳离子交换树脂交换吸附 ,可进行树脂相分光光度法测定微量Fe(Ⅲ )的实验方法。最大吸收波长为 5 4 0nm ,表观摩尔吸光系数为 1 35× 1 0 5L·mol- 1 ·cm- 1 ,Fe(Ⅲ )含量在 0～ 1 8μg·2 5mL- 1 范围内符合比耳定律。该法可用于蒙药中Fe(Ⅲ )的测定。     

流动注射在线分离富集-火焰原子吸收光谱法测定环境水样中Cr(Ⅲ)和Cr(Ⅵ)的形态

采用单阀阴离子和阳离子交换树脂微柱并联 ,两柱交替采样逆向洗脱流动注射在线分离富集环境水样中Cr(Ⅲ )和Cr(Ⅵ ) ,分别用 15 %HNO3和 8%NH4 NO3洗脱 ,火焰原子吸收光谱法直接检测。富集 1min时Cr(Ⅲ )和Cr(Ⅵ )的特征浓度分别为 :1 5 0 μg·L- 1 和 1 39μg·L- 1 ,Cr(Ⅲ )和Cr(Ⅵ )检出限 (3σ)分别为 1 0 3μg·L- 1 和 0 5 4 μg·L- 1 ;相对标准偏差 (10 μg·L- 1 )分别为 :3 4 1%和 1 80 % ,分析样品加标回收率在 93 5 %～ 10 7 5 %之间。     

催化动力学光度法测定痕量铁

论文研究和建立了催化动力学褪色光度法测定痕量Fe(Ⅲ)的新体系,反应介质为盐酸-邻苯二甲酸氢钾(pH2.2)缓冲溶液,催化体系为痕量Fe(Ⅲ)催化过硫酸铵氧化邻甲氧基酚的自聚反应。研究了此反应体系的最佳条件、动力学参数及反应机理,考察了21种干扰离子的影响,建立了一种新型催化动力学光度法测定痕量Fe(Ⅲ)的方法。本法的线性范围0.07～1.1μg·(25mL)~(-1)。方法灵敏度远远高于普通光度法,检出限为5.4×10~(-8)g·L~(-1)。方法应用于自来水、河水、城市污水、豆奶粉和茶叶中痕量Fe(Ⅲ)的测定,相对标准偏差为0.36％～3.4％,标准加入回收率为97.3％～102.7％,结果满意。     

痕量铁(Ⅲ)的催化光度法测定及动力学机制研究

在0.30 mol·L-1盐酸中,铁(Ⅲ)显著催化过硫酸钾氧化甲基红的褪色反应,据此建立了测定痕量铁(Ⅲ)的“Fe(Ⅲ)-盐酸-过硫酸钾-甲基红”新体系,研究了该体系测定痕量铁(Ⅲ)的最佳条件,考察了共存离子对测定的影响,分析了测定反应的动力学参数及方程,并利用动力学性质探讨了测定痕量铁(Ⅲ)的反应机理,从而构建了一种测定痕量铁(Ⅲ)的新催化动力学光度法。研究表明,在最大吸收波长518 nm以及最佳测定条件下,该体系中甲基红的浓度变化与铁(Ⅲ)含量呈以下良好线性关系：ln(A₀/A)=1.334 1+0.001 0,相关系数为0.999 1;痕量铁(Ⅲ)发生一级反应,该测定体系符合准一级反应特征且反应的表观活化能为69.88 kJ·mol-1;反应机理的研究进一步证明了该体系中痕量铁(Ⅲ)起催化作用;该痕量铁(Ⅲ)的测定方法操作简便,所用试剂廉价易得,目前还未见报道,其灵敏度优于普通光度法,检出限达0.005 mg·L-1。该方法应用于实测水样和食品中痕量铁(Ⅲ),相对标准偏差为1.18%～2.11%,平均回收率为98.0%～104.0%。该测定体系稳定,结果满意。     

催化动力学荧光分析新体系Fe(Ⅲ)-H2O2-糠醛缩7-氨基-8-羟基喹啉-5-磺酸的研究

本文对Fe(Ⅲ)催化过氧化氢氧化新试剂糠醛缩7-氨基-8-羟基喹啉-5-磺酸(简称F7A8Q5S)进行了研究,研究结果表明试剂F7A8Q5S本身荧光很弱,被氧化后呈现强荧光,其荧光峰为λex/λem=330/405(nm),Fe(Ⅲ)的含量在0.0～40.0μg·L-1范围内与荧光强度呈良好线性,检测下限为4.68ng·L-1,由此建立了新试剂F7A8Q5S催化荧光测定痕量Fe(Ⅲ)的新方法,方法用于铸造铝合金中Fe(Ⅲ)的含量测定,结果满意.     

反射式流通池顺序注射光度检测系统的研制

提出一种反射式流通池用于过程分析光度检测系统 ,可以明显地抑制折光指数效应产生的干扰。以发光二极管为光源 ,采用多股光纤分别与流通池 ,光源 ,检测器耦合 ,实现对透射后反射回的光谱检测。以Cl- Hg(SCN) 2 Fe(Ⅲ )反应显色体系为模型对系统的实验参数进行了优化。讨论了试剂注入量、进样量、载流流速、试剂注入次序等参数对检测结果的影响。方法的线性范围为 0～ 10 0mg·L-1(相关系数r =0 998) ;分析精度 (RSD ,n =11)为 1 5 % ;检出限为 1 2mg·L-1;分析速度为 30个样·h-1;对自来水和海水的回收率分别为 95 %和 10 4 %。     

流动注射-多道检测-催化动力学同时测定铜和铁

基于Cu(Ⅱ),Fe(Ⅲ)在pH3～9范围内能同时催化过氧化氢氧化罗丹明B的褪色反应,探讨了最佳反应条件,通过构建流动注射pH梯度,采用CCD-二极管阵列检测器检测吸光度差值,反向传播-人工神经网络(BP-ANN)处理数据,实现了Cu(Ⅱ),Fe(Ⅲ)流动注射-催化动力学光度法的同时测定。Cu(Ⅱ)和Fe(Ⅲ)的检出限分别为0.10和0.21μg·L~(-1),采样频率为10次·h~(-1),本法用于标准参考物质和食品样品中铜、铁的同时测定,结果满意。     

催化动力学荧光分析新体系Fe（Ⅲ）—H2O2—糠醛缩7—氨基—8—羟基？…

本文对Fe(Ⅲ)催化过氧化氢氧化新试剂糠醛缩7-氨基-8-羟基喹啉-5-磺酸(简称F7A8Q5S)进行了研究,研究结果表明试剂F7A8Q5S本身荧光很弱,被氧化后呈现强荧光,其荧光峰为λex/λem=330/405(nm),Fe(Ⅲ)的含量在0.0～40.0μg·L-1范围内与荧光强度呈良好线性,检测下限为4.68ng·L-1,由此建立了新试剂F7A8Q5S催化荧光测定痕量Fe(Ⅲ)的新方法,方法用于铸造铝合金中Fe(Ⅲ)的含量测定,结果满意.     

Determination of trace iron (II) and molybdenum (VI) in ground water by pyrocatechol resin-phase spectrophotometry]

In weak acid medium (pH 6.20), Fe(III) and Mo(VI) can form colored complexes with pyrocatechol and quantitatively adsorbed on 717 strong base anion exchange resin. The apparent molar absorption coefficients of resin phase are epsilon = 4.1 x 10(4) L/(mol x cm) at 520 nm for Fe(III) and epsilon = 9.0 x 10(4) L/(mol x cm) at 400 nm for Mo(VI). Beer's law is obeyed for Fe (III) and Mo(VI) in the range of 0-2.2 mg x L(-1) and 0-1.6 mg x L(-1). The method has been applied to the determination of trace Fe(III) and Mo(VI) in ground water. The relative standard deviations are 3.3% and 3.2%, respectively.     

Fe(II–III) Hydroxysalt Green Rusts; from Corrosion to Mineralogy and Abiotic to Biotic Reactions by Mössbauer Spectroscopy

Hyperfine Interactions - Fe(II)–Fe(III) hydroxysalts commonly called green rusts are layered double hydroxides of formula [FeII (1?x)FeIII x (OH)2]x+ ?[(x/n)An?...     

催化动力学褪色光度法测定痕量铜（Ⅱ）的研究

研究了在盐酸介质中 ,铜 (Ⅱ )催化过氧化氢氧化孔雀绿褪色反应的适宜条件与影响因素 ,建立了催化动力学光度法测定痕量铜的新方法。该方法是用固定时间法在 6 15nm波长处监测催化反应。方法的线性范围为 0～ 2 2 μg·L- 1 ,检出限为 1 92× 10 - 9g·mL- 1 ,该催化反应对铜 (Ⅱ )为一级反应 ,表观活化能为12 2 3kJ·mol- 1 ,表观反应速率常数为 7 70× 10 - 4s- 1 。因为Fe3 干扰Cu(Ⅱ )的测定 ,用PO3-4与Fe3 生成稳定的 [Fe(PO4 ) 2 ]3- 络合物 ,可掩蔽Fe3 。方法相对标准偏差为 1 16 % ,标准加入回收率为 98 3%～10 0 3%。该方法用于水样品、茶叶样品、奶粉样品以及苹果样品中铜的测定 ,获满意结果     

光度法研究聚乙二醇-硫酸铵-邻苯三酚红体系中铋(Ⅲ), 铁(Ⅲ), 铜(Ⅱ), 镍(Ⅱ), 钴(Ⅱ), 铅(Ⅱ)的萃取分离

本文研究了在聚乙二醇(PEG)-硫酸铵[(NH_4)_2SO_4]-邻苯三酚红(PR)体系中Bi(Ⅲ),Fe(Ⅲ),Cu(Ⅱ),Ni(Ⅱ),Co(Ⅱ),Pb(Ⅱ)的萃取行为。实验结果表明,Bi(Ⅲ)在pH3.5～6.5及Fe(Ⅲ)在pH4.0～7.0范围内可以被PEG相几乎完全萃取,而Cu(Ⅱ),Co(Ⅱ)在pH1.0～7.0,Pb(Ⅱ)在pH2.0～7.0,Ni(Ⅱ)在pH1.0～4.5则不被萃取。从而实现了将Bi(Ⅲ)(pH3.5),Fe(Ⅲ)(pH5.0)与Cu(Ⅱ),Co(Ⅱ),Pb(Ⅱ),Ni(Ⅱ)混合离子的定量分离。同时探讨了PEG相的萃取机理。     

吸光度比值-导数光谱法同时测定铜(Ⅱ)和铬(Ⅲ)的研究

提出了运用吸光度比值-导数光谱法同时测定Cr(Ⅲ)与Cu(Ⅱ)含量的新方法。在pH 5.7的HAc-NaAc的缓冲溶液中,Cr3+,Cu2+与铬天青S(CAS)和溴化十六烷基三甲胺(CTMAB)可分别形成蓝色三元络合物。其摩尔吸光系数分别为2.52×105 L·mol-1·cm-1和1.01×105 L·mol-1·cm-1。Cu2+和Cr3+的浓度分别在0.08～1.2 μg·mL-1和0.05～0.52 μg·mL-1范围内符合比尔定律,其检测限分别为0.014和0.013 μg·mL-1。此方法应用于环境水中Cr(Ⅲ),Cu(Ⅱ)的同时测定,取得了满意的结果。     

Calix Receptor Edifice; Scrupulous Turn Off Fluorescent Sensor for Fe(III), Co(II) and Cu(II)

Novel Supramolecular fluorescence receptor derived from calix-system i.e. calix[4]resorcinarene bearing dansylchloride as fluorophore was designed and synthesized. The compound was purified by column chromatography and characterized by elemental analysis, NMR and Mass spectroscopy. Tetradansylated calix[4] resorcinarene (TDCR) shows a boat conformation with C₂v symmetry. The complexation behaviour of metal cations [Ag(I), Cd(II), Co(II), Fe(III), Hg(II), Cu(II), Pb(II), Zn(II), U(VI) (1?×?10^-4?M)] with tetra dansylated calix[4]resorcinarene (1?×?10^-6?M) was studied by spectophotometry and spectrofluorometry. Red shift in the absorption spectra led us to conclude that there is strong complexation Fe(III), Co(II) and Cu(II) with TDCR. These metal cations also produce quenching with red shifts in the emission spectra. The maximum quenching in emission intensity was observed in the case of Fe(III) and its binding constant was also found to be significantly higher than that of Co(II) and Cu(II). Quantum yield of metal complexes of Fe(III) was found to be lower in comparison with Co(II) and Cu(II) complexes. Stern Volmer analysis indicates that the mechanism of fluorescence quenching is either purely dynamic, or purely static.     

Incorporation of Siderophore Binding Sites in a Dipodal Fluorescent Sensor for Fe(III)

A new fluorescent probe 3, has been developed for the detection of Fe(III) in water based samples. The design of 3 involved the incorporation of Fe(III) binding sites observed in naturally occurring Siderophores into a synthetic sensing assembly. The probe, containing two Schiff base receptors connected to a mesitylene platform, was prepared in two steps. The dipodal sensor displayed good selectivity for Fe(III) when tested against other physiological and environmentally important metal ions, in HEPES buffered solution at pH 7.0, through a quenching of the fluorescent intensity. Stern-Volmer analysis of this quenching interaction indicated a 1:1 (host : guest) binding stoichiometry between the probe and Fe(III). The association constant, K _a calculated using the Benesi-Hildebrand equation was found to be 3.8 × 10⁴ M⁻¹. Crucially, the sensor was capable of measuring Fe(III) competitively in solutions containing both Fe(III) and Cu(II). Thus, the adoption of Fe(III) binding sites found in nature, into synthetic luminescent assemblies has proven an effective design strategy for the development of new Fe(III) probes. Electronic supplementary material  The online version of this article (doi:) contains supplementary material, which is available to authorized users.     

Influence of Fe(III) on the Fluorescence of Lysozyme: a Facile and Direct Method for Sensitive and Selective Sensing of Fe(III)

Lysozyme is widely used for the synthesis of nanomaterials (e.g., gold nanoparticle) to fluorescently sense metal ions. However, the effect of metal ions on the fluorescence of lysozyme is not studied yet. Herein, we have explored the interactions of lysozyme with different metal ions to develop a direct sensing platform for Fe(III). It has been observed that the fluorescence of lysozyme was slightly decreased in the presence of Cu(II), Hg(II), As(V), Co(II), Cd(II), Cr(II), Fe(II), Mn(II), Pb(II), and Zn(II), while a significant decrease in the lysozyme fluorescence was observed for Fe(III). The effect of thermal stability on the fluorescence quenching was also studied from 25 to 60 °C. In the present study, the lysozyme sensing probe was able to selectively and accurately detect 0.5–50 ppm of Fe(III) with a LOD of 0.1 ppm (1.8 µM) at 25 °C.

     

Reactive dye degradation by combined Fe(III)/TiO2 catalyst and ultrasonic irradiation: Effect of Fe(III) loading and calcination temperature

The development of Fe(III)/TiO(2) catalysts for sonocatalytic degradation of Reactive Blue 4 (RB4) dye in water was carried out using sol-gel method. Their surface morphology, phase transformation and surface characteristics were studied using SEM, XRD and surface analyzer, respectively. Phase transformation from amorphous to anatase occurred at 500°C and transformation of anatase to rutile phase occurred at 700°C. Complete rutile phase was formed at 900°C with corresponding increase in the particle size. Increasing in Fe(III) loading led to a reduction in the anatase phase and with the formation of weaker and broader of diffraction peaks. Surface morphology of the prepared catalyst was clearly observed with increasing calcination temperature. Surface area of the prepared catalyst decreased with increasing calcination temperature or increasing Fe(III) loading. The combination of 0.4 mol% of Fe(III)/TiO(2) with ultrasonic irradiation gave the highest sonocatalytic activity in the removal of RB4 from the aqueous solution. On the other hand, the presence of even small amount of rutile inhibited the catalytic activity of catalyst. 1.5 g/L was the optimum amount of catalyst that led to the highest sonocatalytic degradation of RB4 with an efficiency of 90%. Aeration significantly accelerated the reaction rate. Higher removal at 96% could be achieved with the combination of 0.4Fe(III)/TiO(2) and aeration under ultrasonic irradiation.