可溶性滤膜分离富集-电感耦合等离子体原子发射光谱法对水中痕量镉、铜、铅与锌的同时测定

基于金属离子与2-[5-溴-2-吡啶偶氮]-5-二乙氨基酚(5-Br-PADAP)形成的螯合物能被混合纤维素滤膜捕集,建立了可溶性滤膜分离富集ICP-AES法同时测定水中痕量镉(Ⅱ)、铜(Ⅱ)、铅(Ⅱ)和锌(Ⅱ)的新方法.研究了六通道多联装置同时进行过滤富集的可行性,考察了溶液介质酸度、螯合剂用量、共存离子等对分离富集的影响.在优化的实验条件下,100 mL水样中镉、铜、铅和锌的富集倍率分别为18、19、17和19,检出限(3σ,n=11)分别为0.04、0.15、0.44、0.06 μg/L.方法成功用于自来水和市售矿泉水样中镉、铜、铅和锌的测定,加标回收率为86% ～119%.     

利用碘离子增感效应和金电极导数阳极溶出法研究铜、铅和镉的同时测定

本文使用金电极为工作电极,银-氯化银电极为参比电极,铂电极为对电极,在硫酸-碘化四乙基铵介质中减小了铋对铜的干扰,提高了铅、镉测定灵敏度.用导数阳极溶出法,可同时测定铜、铅和镉,它们的溶出峰电位分别为 0.25,-0.12和-0.27V、检测下限分别可达:铜(Ⅱ)和铅(Ⅱ)0.2ppb,镉(Ⅱ)0.05ppb.在选定的条件下,溶出峰电流与浓度很好地成线性关系.本文还用三角波循环伏安法观察了电极反应过程.     

吡咯烷二硫代氨基甲酸铵-Ni(Ⅱ)快速共沉淀分离富集和原子吸收光谱法测定痕量铜、铅和镉

研究了用吡咯烷二硫代氨基甲酸铵(APDC)为沉淀剂,以Ni(Ⅱ)为载体离子的共沉淀体系快速共沉淀分离富集铜、铅和镉,并用火焰原子吸收光谱(FAAS)测定的方法。通常情况下,内标元素和载体离子选择不同的元素,本文尝试将Ni既作为载体又作为内标元素。实验证明,该体系在pH=3.0的条件下,能够定量共沉淀试样中的铜、铅和镉。当试液为100 mL时,铜、铅、镉的检出限分别为9.7×10-3、3.3×10-2,1.01×10-3μg.mL-1,加标回收率为95.8%~101.8%,取得了较为满意的结果。本法只需快速收集部分沉淀,与传统的共沉淀方法比较,具有快速、简便、重现性好的优点。     

火焰原子吸收分光光度法测大沂河水体的重金属含量

采用火焰原子吸收分光光度法测定了山东省曲阜市大沂河水体的重金属铜、铅、镉、锌含量。结果表明,大沂河水体中铜、铅、镉、锌的最高含量分别为0.018,0.230,0.176,0.490mg/L,其中铅和镉的含量超过国家Ⅴ类水标准。     

微波消解-原子吸收光谱法测定粮谷中铅、铜、镉、镁、锰、铁

用微波消解法进行样品消解,原子吸收光谱法测定了小麦粉国家标准物质中铅、铜、镉、镁、锰、铁6种元素的含量.其中镁、锰、铁用火焰原子化法,铅、铜、镉用石墨炉原子化法,方法的相对标准偏差分别为1.43%(镁),4.72%(镉),5.20%(锰),6.04%(铜),13.8%(铁)及18.7%(铅),检出限分别为0.001(铅及铜),0.000 1(镉),0.01(锰)及O.02(镁和CA)mg·kg-1.     

电感耦合等离子体质谱法快速测定苦荞茶中铜、铅、镉、钴、镍

建立了用硝酸-高氯酸消解样品,电感耦合等离子体质谱法(ICP-MS)测定苦荞茶中铜、铅、镉、钴、镍的方法.方法具有灵敏度高、检出限低、精密度好、基体干扰少、准确可靠、快捷、简便的特点.各元素方法检出限(3SD,μg/L)分别为:铜0.009、铅0.023、镉0.015、钴0.022、镍0.035;方法精密度(RSD,n=12)分别为:铜2.5%～3.0%、铅2.1%～2.3%、镉3.0%～3.8%、钴2.5%～2.6%、镍1.5%～1.9%;各元素加标回收率分别为:铜95.0%～105.0%、铅95.0%～105.0%、镉98.0%～105.0%、钴95.0%～105.0%、镍95.0%～105.0%.在线用铑作为内标95.0%～105.0%.方法经国家一级标准物质验证,测定值与标准值吻合.应用于实际样品测定,结果满意.     

用悬汞电极阳极溶出法测定高纯铝中杂质

应用悬汞电极阳极溶出法测定高纯材料中数量级为10~(-4)—10~(-7)％微量杂质(或更低含量),在1956年以后才被应用于分析化学中。本文利用悬汞电极阳极溶出法直接测定高纯铝中微量锌、镉、铅、铜,灵敏度分别为:锌:3×10~(-5)％,镉:2×10~(-6)％,铅:2×10~(-6)％,铜:3×10~(-5)％。 (一)仪器     

极谱法同时测定海水中的铜、镉、铅、锌

建立极谱法同时测定海水中铜、镉、铅、锌的含量。在10.0～35.0℃条件下,试样于–1.15 V恒压下电解,富集在汞电极上生成汞齐,并随电极电位的变化而发生氧化还原反应,产生电流,通过标准加入法进行定性和定量。铜、镉、铅、锌的检出限分别为0.64,0.14,0.17,2.0μg/L,定量限分别为2.5,0.50,0.50,10.0μg/L。样品加标回收率为80.4%～106.0%,测定结果的相对标准偏差为0.43%～6.09%(n=6)。该法具有操作简便、抗干扰性能强、灵敏度高等特点,能够满足海水中铜、镉、铅、锌的监测要求。     

微波消解样品-石墨炉原子吸收光谱法测定双黄连口服液及其药材中重金属元素

双黄连口服液及其中药材金银花、连翘和黄芩苷样品用硝酸-过氧化氢(3+1)混合溶液浸泡过夜,微波消解。并用石墨炉原子吸收光谱法(GF-AAS)测定了铅、镉、铬、铜、铁和锌的含量。磷酸二氢铵、8-羟基喹啉和硒(Ⅱ)分别被用作测定铅,镉,铜和铁、铬以及锌的基体改进剂。在优化的试验条件下,方法的回收率在90.4%～106.0%之间,相对标准偏差(n=5)在1.8%～4.6%之间。试验结果表明,双黄连口服液及其中药材中铁、锌、铜的含量较为丰富,铅和镉含量低于"药用植物及制剂外经贸绿色行业标准"。     

毛细管电泳单脉冲伏安测定重金属铜铅锌镉

以毛细管为分离通道 ,在KNO3 缓冲溶液中 ,用表面镀汞膜的金微电极作为工作电极 ,采用单脉冲伏安法同时测定铜、锌、铅、镉含量 ,考察并优化了影响分离和检测的相关因素 :缓冲溶液pH、分离高压、脉冲上限和下限、脉冲宽度等。该法的最佳实验条件 :5mmol/LKNO3(pH6.0) ,分离高压20kV ,脉冲上限 -0.2V ,脉冲下限 -1.15V(vs.SCE) ,脉冲宽度500ms。结果表明 ,各峰面积与其离子浓度成线性关系 ,线性范围(μg/mL)分别为 :铜5.0×10-2～10.0;锌1.0×10-2～10.0 ;铅5.0×10-2～5.0 ;镉2.0×10-2～10.0。加标回收率在95%～110%之间。用该法较好地测定了水样中的重金属铜锌铅镉     

利用碘离子增感效应和金电极导数阳极溶出法研究铜丶铅和镉的同时测定

A method of simultaneous determination of copper (II), lead (II) and cadmium (II) in sulphuric acid-iocide ion medium was established by derivative anodic stripping voltammetry (DASV) on the gold electrode. The peak theights of lead and cadmium were increased by enhancement effect of iodide ion and the peaks of bismuth and copper were well formed and completely resolved on gold electrode in the presence of iodide ion, therefore peak of copper is not affected by bismuth. The sensitivities for copper, lead and cadmium were very high and their peak potentials in the stripping voltammogram were +0.25, -0.2 and -0.27 volt, respectively. The dependence of peak height of these elemets on their concentrations was linear. The detection limits for copper, lead and cadmium were 0.2 0.2 and 0.05 ppb, respectively. We have further studied the electrode process by means of triangle cyclic voltammetry and proved that he electrode reaction of copper is reversible, and that the reversibility of electrode reactions of lead and cadmium is not good.     

Electrochemical Detection of Trace Concentrations of Cadmium and Lead with a Boron‐Doped Diamond Electrode: Effect of KCl and KNO3 Electrolytes,Interferences and Measurement in River Water

Parts‐per‐billion levels of cadmium and lead were detected using square‐wave anodic stripping voltammetry with a boron‐doped diamond electrode. Calibration plots (10‐minute deposition time) in KCl and KNO₃ were non‐linear at low concentrations (1–5 ppb) due to the deposition mechanism of these metals. The preferred electrolyte for cadmium was KCl, while lead could be measured in either electrolyte. The lowest concentrations included in the linear portion of the calibration plot (5 minute deposition time) for cadmium were 10 ppb and 50 ppb in KCl and KNO₃, respectively, and 10 ppb for lead in KNO₃. The presence of either lead or copper suppressed the cadmium stripping peak, but the lead stripping peak was unaffected by cadmium, and enhanced by the addition of copper. A river water sample was analyzed for cadmium and lead, and the cadmium results were confirmed using ICP‐AES spectrometry. It was determined electrochemically that a fraction of lead in the river sample was bound by complexing material in the sample.     

毛细管电泳-电感耦合等离子体质谱联用测定海藻中铅形态化合物

建立了毛细管电泳( CE)与电感耦合等离子体质谱( ICP-MS)联用技术测定铅离子( PbⅡ)、三甲基铅(TML)和三乙基铅(TEL)3种不同形态铅化合物的方法,以及海藻中不同形态铅化合物的提取技术,实现了海藻中3种铅形态化合物的定性定量分析。结果表明：以70 mmol/L H3BO3-17.5 mmol/L Na2B4O7(pH 8.90)为缓冲溶液,在最佳CE-ICP-MS条件下3种铅化合物20 min内可实现有效分离,重现性较好,迁移时间RSD﹤4%,峰面积的RSD﹤5%;在10~200μg/L 范围内3种铅化合物线性较好,相关系数大于0.90; PbⅡ、TML和TEL的CE-ICP-MS检出限(3S/N,以Pb计)分别为0.091,0.023和0.030μg/L;采用分步提取海藻中Pb元素,提取率高达80%以上,以藻体为基底 PbⅡ, TML 和 TEL 回收率分别为103.6%,95.7%和90.6%;通过检测紫菜和海带中铅含量,结果显示藻体内Pb主要以PbⅡ形式存在。本方法具有简单、高效、样品消耗量少等优点,可为海藻及其它海产品的质量控制提供技术支撑。     

Investigation of Copper(II) Interference on the Anodic Stripping Voltammetry of Lead(II) and Cadmium(II) at Bismuth Film Electrode

The bismuth‐coated electrode is known to be prone to errors caused by copper(II). This study investigates copper(II) interference at bismuth film electrode for the detection of lead(II) and cadmium(II). It was conducted using glassy carbon electrode, while the bismuth film was plated in situ simultaneously with the target metal ions at ? 1200 mV. Copper(II) presented in solution significantly reduced the sensitivity of the electrode, for example there was an approximately 70 % and 90 % decrease in peak signals for lead(II) and cadmium(II), respectively, at a 10‐fold molar excess of copper(II). The decrease in sensitivity was ascribed to the competition between copper and bismuth or the metal ions for surface active sites. Scanning electron microscopy (SEM) and energy dispersive X‐ray (EDX) analysis suggested a large decrease in the amount of bismuth nanoparticles formed on the electrode surface in the presence of copper(II) occurred, validating the competition between copper and bismuth ions for surface active sites. Recovery of the stripping signal of lead(II) and cadmium(II) was obtained by adding ferrocyanide ion to the solution. Finally, the proposed method was successfully applied to determine lead(II) and cadmium(II) in water samples and the method was validated by ICP‐MS technique.     

The determination of lead,copper and cadmium by anodic stripping voltammetry at a mercury thin-film electrode

The determination of lead, copper and cadmium by anodic stripping voltammetry at a wax-impregnated graphite electrode, pre-plated with mercury, has been investigated. Electrode preparation and cell design are discussed, and the effects of mercury loading and sample pH on electrode sensitivity are described. Detection limits and precision on aqueous samples are reported. Calibration graphs are linear for lead and cadmium, but non-linear for low concentrations of copper. The depression of peak current and shift of peak potential for copper in chloride media are described and an explanation is proposed. Precision and recovery of metal additions are reported for digested samples of whole blood.     

Trace Enrichment and Atomic Absorption Spectrometric Determination of Lead,Copper, Cadmium and Nickel in Drinking Water Samples by Use of an Activated Carbon Column

Abstract

A simple method for atomic absorption spectrometric determination of lead, copper, cadmium and nickel in drinking water samples after preconcentration by sorbing 1-(2-pyridylazo) 2-naphthol (PAN) complex of these metals on an activated carbon column has been established. The metal/PAN complexes were quantitatively retained on the activated carbon in the pH range 6-8. Metals retained on the activated carbon column were completely eluted with 2M HCl in acetone. This method was applied to the determination of lead, copper, cadmium and nickel in drinking water samples and good results were obtained (Recoveries >95%, relative standard deviations <7%, relative error <3%).     

测定人发中铜的桑色素修饰碳糊电极吸附溶出伏安法

制作了用桑色素作修饰剂的化学修饰碳糊电极,利用该电极为工作电极,建立了测定痕量铜的新方法。在甲酸钠－盐酸缓冲溶液（pH4.6）中,在0.20V（vsSCE）下搅拌富集,铜（Ⅱ）与碳糊修饰电极表面的桑色素形成电活性络合物而吸附富集于电极表面,经－0.45V静置还原后,阳极化线性扫描,在－0.05V获得一灵敏的二次导数溶出峰。在不同富集时间下,其二次导数峰电流与铜（Ⅱ）浓度分别在1.0×10     

KBrO_3-邻氨基酚体系催化动力学光度法测定微量Cu(Ⅱ)

在pH为4.5的HAc-NaAc缓冲溶液介质中,Cu(Ⅱ)能催化KBrO_3氧化邻氨基酚而显色,据此建立了测定微量Cu(Ⅱ)的新方法。方法的测定波长为430nm,反应温度为60℃时控制反应时间为6min,Cu(Ⅱ)在0.10~1.2μg/mL范围内吸光度与Cu(Ⅱ)的浓度呈良好的线性关系,相关系数r为0.9971。方法用于测定冶炼厂电解银废液中铜含量,相对标准偏差为2.49%(n=6),加标回收率在91.6%~99.4%之间。     

茜素修饰碳糊电极吸附伏安法测定痕量铜

报道了采用茜素修饰碳糊电极测定痕量铜的阳极溶出伏安法。在浓度为0 .1 mol/L 的 HAc- Na Ac缓冲溶液 (p H4.5)中 ,于 +0 .1 0 V处富集 ,- 0 .30 V还原后再进行阳极化扫描 ,于 - 0 .0 5V处获得一灵敏的铜的溶出峰 ,二次导数峰电流与铜浓度在 1 .6× 1 0 -9mol/L～ 4.7× 1 0 -7mol/L范围内呈线性关系 ,检出限达 8.0× 1 0 -10 mol/L。同时 ,对电极反应机理进行了讨论。方法应用于锌合金中铜的测定。     

The Simultaneous Determination of Cu Ph Cd and Sb by Derivative Adsorption Chronopotentiometry

Anodic stripping voltammetry (ASV) is an effective electroanalytical technique for themeasurement of trace metal ions. But there are serious interferences due to overlappingstripping peaks and forming of intermetallic complex in complicated system. The peak ofcopper (ASV) is close to that of mercury. So the result of determination of copper is notsatisfactory. Adsorption chronopotentiometry was reported by H.Eskilsson et al i. In thismethod, instead of electrolytic accumulation of metal io…