锌汞齐的标准电极电位

虽然Bates^[1],Robinson等^[2]和Stokes等^[3]曾确定锌汞齐的标准电极电位,但他们用的是饱和锌汞齐,而Clayton等^[4]指出Zn(固)|Zn²⁺|znHg(饱和)的电动势为零,因此,以上诸作者确定的并不是锌汞齐而是锌的标准电极电位,这点已为手册和教科书所承认。     

钾汞齐的标准电极电位与平衡电位

仿照前文^[1],选定汞齐中钾的标准态并规定钾汞齐的标准电极电位。本文利用前人数据,采用一般化学热力学方法计算在25°钾汞齐的标准电极电位ε°的数值,并以图表示该温度下不同浓度的钾汞齐与不同浓度的氢氧化钾溶液的平衡电位ε的数值。Armbruster等、Bent等和柴田荣一等曾用电动势法测定汞齐中钾的活度。     

溴化铵改性膨润土脱除气态单质汞的特性及机理分析

采用溴化铵对钠基膨润土进行改性制得脱汞吸附剂,在固定床实验装置上对所制备的吸附剂进行脱汞性能测试。脱汞实验结果表明,钠基膨润土较钙基膨润土在脱汞性能上提高不大,而溴化铵改性的钠基膨润土(Br-Ben/Na)脱汞性能得到明显提高,脱汞效率达到97.7%。吸附温度的升高有利于对Hg0的脱除,在140℃下,10%Br-Ben/Na吸附剂的脱汞率能长时间保持在90%以上,说明在此吸附过程中化学吸附占主导性作用。通过N2吸附/脱附、X射线衍射(XRD)、元素分析仪和傅里叶变换红外光谱(FT-IR)分析等结果表明,改性后的膨润土比表面积下降,平均孔径增大;铵根离子进入到膨润土的层间置换出层间钠离子,煅烧活化过程中层间的铵根离子并未分解,而在层间与膨润土结合为某吸附活性组分协助Br-与Hg0反应,提高了膨润土的脱汞性能。     

铕离子掺杂类普鲁士蓝复合汞膜电极的制备及溶出分析特性

在铕离子掺杂类普鲁士蓝(Eu-PB)修饰的玻碳电极表面电沉积汞膜,制备了一种新型化学修饰复合汞膜电极GC/Eu-PB/MFE.研究了修饰层厚度、镀汞方式和汞膜成长过程对复合汞膜形成的影响.以Pb2+和Zn2+为探针离子,对复合汞膜电极和常规玻碳汞膜电极的氢过电位值、表面活性物质的影响、汞膜稳定性和金属离子的溶出伏安行为等进行了对比研究.同时,应用该电极结合示差脉冲阳极溶出伏安法对环境水样中的痕量Pb2+进行了测定.结果表明,Pb2+在该复合汞膜电极上的阳极溶出峰电流与其质量浓度在0.8 ～250 μg/L范围有良好的线性关系(r=0.999 5,n=12),检出限为0.2 μg/L,加标回收率为98% ～102%.用该法对国家铅标准物质溶液对比测定,数据的重复性和准确性均令人满意.     

基于银汞齐抑制三角纳米银刻蚀比色法检测水中汞离子

构建了一种基于汞离子存在下,银汞齐的形成抑制了三角纳米银被氯离子刻蚀的比色法检测水中汞离子的方法。当汞离子不存在时,由于氯离子的刻蚀,纳米银的形状由三角形纳米盘变成圆盘,溶液颜色由蓝色变成黄色。当汞离子存在时,汞离子被还原成汞原子强烈吸附在纳米三角银表面,汞充当纳米三角银的保护剂,抑制了氯离子对纳米三角银的刻蚀。随着汞离子浓度的增大,纳米三角银在450 nm处表面等离子共振峰发生红移,并伴随着颜色从黄色变为棕色,紫色,最后变为蓝色。在最佳反应条件下,该方法的线性范围为5~100 nmol/L,检出限为0.83 nmol/L。其它重金属离子对汞离子检测无干扰。将该方法用于实际水样中汞离子的检测,得到了满意的结果。     

负载Mn的Fe基MOFs脱汞剂烟气脱汞研究

基于Fe基金属有机骨架（MOFS）作为载体,采用浸渍法制备了负载6% Mn的Mn/MIL-100（Fe）脱汞剂。在模拟烟气中,搭建固定床研究了Mn/MIF-100（Fe）脱除单质汞（Hg⁰）性能。采用X射线衍射分析（XRD）、X射线电子能谱（XPS）、N₂吸附-脱附（BET）和热重分析（TGA）对材料进行表征。研究表明,Mn/MIF-100（Fe）脱除单质汞（Hg⁰）效率较高,在250℃,空速（GHSV）为180000h^-1时,脱汞（Hg⁰）效率达82%以上。Mn/MIF-100（Fe）主要的脱汞机理是催化氧化,Mn的负载促进了汞的吸附,并随着烟气温度的提高,单质汞的氧化效率逐渐提高。O₂和NO促进汞的脱除,SO₂和NH₃抑制汞的脱除。Mn/MIL-100（Fe）整体上对复杂烟气的适应能力强。     

铂电极上吸附芳香分子的表面增强红外光谱研究

应用衰减全反射表面增强红外吸收光谱法分别研究了0.1 mol•L^－1 HClO₄中对硝基苯甲酸(PNBA)和0.1 mol•L^－1 KClO₄中吡啶(Py)在铂电极上的吸脱附. 结果表明在较高电位下(0.3～0.7 V vs. SCE) PNBA是通过其羧基脱质子后羧酸根的两个氧原子等位吸附在Pt电极表面, 而随着电位的负移, 除PNBA逐步脱附外, 还呈现出单个氧原子吸附的谱学特征. 光谱强度与电位的关系表明PNBA在铂电极表面吸脱附的中间电位约为0.2 V vs. SCE. 吡啶的吸附主要是通过氮原子的孤对电子及脱氢后的α碳原子与Pt电极表面键合. 在较宽的电位区间(0.4～－0.4 V vs. SCE)吡啶的吸附方式和取向基本维持不变.     

离子交换伏安法同时测定水体中的镉、汞

报道了一种同时快速测定水体中痕量镉、汞的电分析方法。在 p H 4.0 0的磷酸盐缓冲溶液中 ,镉、汞在钠型蒙脱石修饰玻碳电极上通过离子交换富集 ,获得一个灵敏的阳极溶出峰 ,由此可同时测定痕量的镉、汞离子。利用该方法测定镉、汞的线性范围分别为 8× 1 0 - 9到 2× 1 0 - 6 mol/L和 4× 1 0 - 8到 7.5× 1 0 - 6 mol/L ,检出限分别是1× 1 0 - 9mol/L和 8× 1 0 - 9mol/L。该方法简便、快速 ,灵敏度高。用此修饰电极测定了水样中的镉、汞离子 ,结果令人满意     

电极防吸附膜研究

在电化学分析及电极过程动力学研究中,表面活性物质在电极上的吸附,常使测量结果受到严重影响^[1,2]。在天然水的反向极谱分析中,由于天然水,特别是海水,含有大量表面活性物质及悬浮体,并且分析溶液又进行搅拌,因此对电极的灵敏度及重演性影响特别严重^[3-5]。用汞膜电极测定一个新采集的海水样品后,即需重新涂汞^[3,4]。     

吸汞载银活性炭纤维和吸汞活性炭纤维的热脱附特性研究

70℃下分别对载银活性炭纤维(载银量14.07%)和活性炭纤维的片状吸附体进行气态汞吸附实验,测定出载银活性炭纤维汞饱和吸附量为192.3 mg/g,活性炭纤维汞饱和吸附量为29.4 mg/g,分别为普通活性炭的48倍～192倍和7倍～29倍.采用热重分析法(TGA)研究了两种吸附剂汞饱和后的热脱附再生特性.结果表明,汞饱和载银活性炭纤维的汞脱附发生在100℃～650℃,在70 min内从50℃升温至650℃,才乏脱附率为94.73%;汞饱和活性炭纤维的汞脱附发生在100℃～230℃,在40 min内从50℃升温至350℃ ,汞脱附率为69.93%.扫描电镜分析发现,载银活性炭纤维因吸附汞而富集的银,经热脱附后变成均匀弥散于纤维表面的亚微米级和纳米级球状银颗粒;吸汞活性炭纤维经热脱附后物理吸附汞基本消失,而氧化汞颗粒反而变多,说明物理吸附的汞易于脱附,氧化汞难以脱附,同时在热脱附过程中存在金属汞向氧化汞的转化.     

Silica gel ethyleneimine and its adsorption capacity for divalent Pb, Cd, and Hg

Activated silica gel was directly modified with a cyclic molecule, ethyleneimine, yielding a surface with various nitrogen basic centers, ≡Sil–O(CH₂CH₂NH)_nCH₂CH₂NH₂. Infrared spectroscopy, ¹³C NMR, thermal, and elemental analyses confirmed the covalent attachment of the organic species onto the silica matrix. The purpose of this paper is to describe the interaction involving the grafted species on silica surface with the divalent heavy cations, Pb(II), Cd(II), and Hg(II), from aqueous solutions at room temperature. The process of metal extraction was followed by the batch method and the order of the maximum extraction capacities found was: 1.27 ± 0.04, 1.02 ± 0.02, and 0.98 ± 0.01 mmol g⁻¹ for Pb(II), Cd(II), and Hg(II) chlorides, respectively. These interactions were followed by calorimetric titration. The enthalpies of these processes are: −3.05 ± 0.02, −1.09 ± 0.01, and −9.88 ± 0.03 kJ mol⁻¹ for Pb(II), Cd(II), and Hg(II), respectively. The standard molar Gibbs free energies are in agreement with the spontaneity of the proposed reactions between cation and basic center.     

阳极溶出半微分电分析法——锡中痕量铅镉的测定

本文提出用乳酸-乳酸钠溶液(pH=5)作为支持电解质,并采用汞膜电极阳极溶出半微分电分析法,直接进行金属锡和锡盐中痕量铅镉的测定,其回收率分别为105±6%和97±4%。方法简便,结果满意。     

三乙醇胺在金属电沉积中的基本效应

用微分电容法、极谱法、原位表面增强拉曼光谱法和微盘电极法研究了碱性溶液中存在和不存在Zn²⁺、Cd²⁺、Cu²⁺、Ni²⁺、Fe³⁺和Sn⁴⁺等离子时三乙醇胺(TELA)在电极/溶液界面上的电化学行为。结果表明,TELA以平卧方式吸附,符合Frumkin吸附等温线。在碱性溶液中TELA与Zn²⁺、Cd²⁺、Cu²⁺、Ni²⁺和Fe³⁺等离子生成具有表面活性的混合配体配合物,其吸附性较TELA的强。TELA不同程度地影响上述金属离子的电还原过程,根据实验结果提出TELA对锌电沉积的阻化作用机制及其基本效应。     

Hg(II)-imprinted thiol-functionalized mesoporous sorbent micro-column preconcentration of trace mercury and determination by inductively coupled plasma optical emission spectrometry

Hg(II)-imprinting thiol-functionalized mesoporous sorbent was prepared by a sol–gel method and characterized by X-ray diffraction (XRD), FT-IR spectroscopy and nitrogen gas adsorption–desorption. The static adsorption capacity of the Hg(II)-imprinted and non-imprinted sorbent was 78.5 and 26.6 mg g⁻¹, respectively. The breakthrough capacity was 4.46 mg g⁻¹, and the relative selectivity coefficient for Hg(II) in the presence of Cd and Pb was 3.3 and 3.9, respectively. A new method using a micro-column packed with Hg(II)-imprinting thiol-functionalized mesoporous sorbent has been developed for preconcentration of trace mercury prior to its determination by inductively coupled plasma optical emission spectrometry (ICP-OES). The effects of pH, sample flow rate and volume, elution solution and interfering ions on the recovery of the analyte have been investigated. The limit of detection was 0.39 ng ml⁻¹ with a concentration factor of 150 times. The developed method has been applied to the determination of trace mercury in some biological and environmental samples with satisfactory results. The accuracy was assessed through recovery experiments and analysis of certified reference material.     

尖晶石型LiMn2O4薄膜电极的制备及电化学性质研究──电化学石英晶体微天平(EQCM)技术研究

石英晶体微天平(QCM)作为纳克级的质量传感器,可通过测定石英晶体振动频率的变化来测定石英晶体表面微小的质量变化.近年来,电化学石英晶体微天平(EQCM)技术已广泛应用于电化学研究领域[1].在锂嵌入型电极充放电过程中,锂离子在嵌基材料中嵌入脱出会引起电极质量的微小变化,因而利用EQCM技术研究Li+的嵌入脱出过程有其独到之处.     

Extraction of Pb(II), Cd(II), and Hg(II) from aqueous solution by nitrogen and thiol functionality grafted to silica gel measured by calorimetry

The reaction of ethylene sulfide with 3-aminopropyltrimethoxysilane gave a new silylating agent, which was anchored onto a silica surface via the sol–gel procedure. This surface displayed a chelating moiety containing nitrogen and two sulfur basic centers potentially capable of extracting cations from aqueous solutions. The process of metal extraction was followed by a batch method, and fitted to a modified Langmuir equation. The maximum adsorption capacities found were: 2.06 ± 0.01, 3.72 ± 0.02, and 5.14 ± 0.02 mmol g⁻¹ for Pb(II), Cd(II), and Hg(II), respectively. The enthalpies of bending are: −1.16 ± 0.04, −3.60 ± 0.10, and −8.94 ± 0.03 kJ mol⁻¹ for Cd(II), Pb(II), and Hg(II), respectively. The Gibbs free energies of binding agree with the spontaneity of the proposed reactions between cations and basic centers.     

Kinetic processes of Hg6s6p(P1) in xenon

The principal route for decay of Hg 6s6p(³P₁) in xenon is shown to be bimolecular deactivation to the mercury ground state, with rate coefficient 9.1 × 10⁻¹³ cm³ molecule⁻¹ s⁻¹; relaxation to the ³P₀ state plays a negligible role. The equilibrium constant of the reaction Hg(³P₁) + Xe HgXe(A ³O⁺), has been recorded as 1.73 × 10⁻²⁰ cm³ molecule⁻¹ at 293 K.     

V2O5/AC捕获的Hg在再生过程中的释放行为研究

研究了V₂O₅/AC捕获的Hg在再生和程序升温脱附（TPD）过程中的释放行为,考察了再生后V₂O₅/AC对Hg⁰的捕获能力。结果表明,热再生（Ar,400℃）或NH₃再生（NH₃/Ar,300℃）过程会使V₂O₅/AC捕获的大部分Hg重新释放,释放率分别为81%和94%。由于AC的还原作用,再生过程中释放的Hg以Hg⁰的形式为主。TPD结果表明,V₂O₅/AC捕获的Hg在Ar和NH₃/Ar气氛下的释放行为明显不同。气氛中NH₃对Hg的释放具有明显的促进作用,使Hg的释放在300℃前基本结束。但在Ar气氛下,Hg在400℃后仍有释放,致使热再生时Hg的释放率低于NH₃再生时的释放率。但当NH₃的体积分数由1%增加到5%时,汞的释放率变化很小。温度足够高时,两种气氛下Hg的释放率趋于一致。再生方法对V₂O₅/AC二次捕获Hg⁰的能力影响不大,两种气氛下再生后的V₂O₅/AC对Hg⁰的捕获能力差别很小,较新鲜V₂O₅/AC对Hg⁰的捕获能力有所降低,但仍高于载体AC对Hg⁰的捕获能力.     

Amberlite XAD-2 functionalized with o-aminophenol: synthesis and applications as extractant for copper(II), cobalt(II), cadmium(II), nickel(II), zinc(II) and lead(II)

A stable chelating resin matrix was synthesized by covalently linking o-aminophenol (o-AP) with the benzene ring of the polystyrene–divinylbenzene resin, Amberlite XAD-2, through a –N=N– group. Elemental analyses, thermogravimetric analysis (TGA) and infrared spectra have characterized the resulting chelating resin. It has been used to preconcentrate Cu²⁺, Cd²⁺, Co²⁺, Ni²⁺, Zn²⁺ and Pb²⁺, prior to their determination by flame atomic absorption spectrometry. The optimum pH values for quantitative sorption of Cu, Cd, Co, Ni, Zn and Pb are 6.2–7.4, 5.6–7.2, 5.6–9.0, 6.0–9.0, 5.7–7.0 and 5.0–6.0, respectively. These metals are desorbed (recovery 91–98%) with 4 mol dm⁻³ HNO₃. The sorption capacity of the resin is 3.37, 3.42, 3.29, 3.24, 2.94 and 3.32 mg of metal g⁻¹ of resin, respectively, for Cu, Cd, Co, Ni, Zn and Pb. The effect of NaF, NaCl, NaNO₃, Na₂SO₄, and Na₃PO₄ on the sorption of these metal ions has been investigated. These electrolytes are tolerable up to 0.01 mol dm⁻³ in case of all the metal ions, except Cl⁻ which is tolerable even up to 0.1 mol dm⁻³ for Zn and 1.0 mol dm⁻³ for Pb. The preconcentration factor for Cu, Cd, Co, Ni, Zn and Pb are 50, 50, 100, 65, 40 and 40 (concentration level 10–25 μg dm⁻³) respectively. Simultaneous enrichment of the six metals is possible. The method has been applied to determine Cu, Cd, Co, Ni, Zn and Pb content in well water samples (RSD≤8%).     

Trace Analysis of Heavy Metals (Cd,Pb, Hg) Using Native and Modified 3D Printed Graphene/Poly(Lactic Acid) Composite Electrodes

Here we investigate the use of 3D printed graphene/poly(lactic acid) (PLA) electrodes for quantifying trace amounts of Hg, Pb, and Cd. We prepared cylindrical electrodes by sealing a 600 μm diameter graphene/PLA filament in a pipette tip filled with epoxy. We characterized the electrodes using scanning electron microscopy, Raman spectroscopy, and cyclic voltammetry in ferrocene methanol. The physical characterization showed a significant amount of disorder in the carbon structure and the electrochemical characterization showed quasi‐reversible behavior without any electrode pretreatment. We then used unmodified graphene/PLA electrode to quantify Hg, and Pb and Cd in 0.01 M HCl and 0.1 M acetate buffer using square wave anodic stripping voltammetry. We were able to quantify Hg with a limit of detection (LOD) of 6.1 nM (1.2 ppb), but Pb and Cd did not present measurable peaks at concentrations below ～400 nM. We improved the LODs for Pb and Cd by depositing Bi microparticles on the graphene/PLA and, after optimization, achieved clear stripping peaks at the 20 nM level for both ions (4.1 and 2.2 ppb for Pb²⁺ and Cd²⁺, respectively). The results obtained for all three metals allowed quantification below the US Environmental Protection Agency action limits in drinking water.