硫代硫酸根的溶出伏安吸附性质及应用

在 0 .0 1mol·L-1LiNO3介质中 (pH 2 .70 )S2 O32 -有一灵敏的阴极溶出峰( - 0 .42V) ,其峰电流与S2 O32 -浓度在 1× 1 0 -7mol·L-1～ 4× 1 0 -6mol·L-1范围内有线性关系。当富集 2 0 0s时 ,检测限可达 5× 1 0 -8mol·L-1。溶出峰具有吸附性质 ,在悬汞电极上的吸附符合Frumkin等温式。测得在悬汞电极上的饱和吸附量为 1 .0 3× 1 0 -9mol·cm-2 。该方法用于PbS2 O3溶度积的测定 ,结果与文献值基本一致。     

吸附溶出伏安法测定苯胺的研究

在酸性介质中,苯胺与亚硝酸根离子和盐酸萘乙二胺反应生成玫瑰红色偶氮染料,该染料在汞电极上具有良好的吸附性能,并且在氨性缓冲介质中可在汞电极上还原,于－０．５５Ｖ左右产生一灵敏的吸附极谱波。据此,建立了吸附溶出伏安法测定苯胺的方法。当吸附富集时间为３ｍｉｎ时,该法的检测下限为５×１０－９ｍｏｌ／Ｌ,比分光光度法降低了近两个数量级。应用本方法测定了废水中的苯胺,结果满意。     

土霉素的电化学还原和吸附溶出伏安法测定研究

本文叙述吸附溶出分析土霉素的灵敏方法。土霉素及其质子化形态能在汞电极表面吸附富集(-0.60V vsAg/AgCl),溶出峰的数目及电位受pH影响。在pH4—8的溶液中得到4个溶出峰,而在强酸性和碱性介质中仅得到一个主峰。文中讨论了有关的化学和电极反应机理。采用奥氏方波溶出,电解富集5 min的测定限为5×10~(-10)mol/L。     

络合吸附溶出伏安法测定茶叶中的痕量锌

通过实验优化支持电解质、pH值、络合剂浓度等实验参数。在溶液中直接以SCN-作配位剂 ,采用玻碳电极同位镀汞的吸附伏安法测定锌。在该体系中 ,Zn2 + 和SCN-配合物可产生灵敏吸附波 ,峰电位为 - 1.372V ,线性范围为 1.96 2～ 130 .8μg/L ,搅拌富集 5min ,检出限可达 8× 10 -10 mol/L。该法用于测定茶叶中的锌 ,平均回收率为 95 .0 %～ 10 2 .5 %。     

吸附溶出催化伏安法测定痕量锗

利用吸附溶出伏安法、极谱催化法测定痕量锗已有报道。但将吸附溶出伏安法与极谱催化法结合进行测定,尚未见报道。我们选择适当的体系和配位体3,4-二羟基苯甲醛(DHB)及氧化剂钒(V),首先使Ge(Ⅳ)-DHB络合物在悬汞电极上于一定电位处吸附富集一定时间,然后电位向负的方向扫描。当达到Ge(Ⅳ)-DHB络合物的还原电位时,Ge(Ⅳ)还原     

吸附溶出伏安法测定普罗帕酮的研究

在pH 6.47的磷酸盐缓冲溶液中,可得到普罗帕酮的吸附溶出峰。峰电位为-1.38V(vs.Ag/AgCl),富集1min,溶出峰电流与普罗帕酮浓度在8.0x10~(-9)～7.0x10~(-7)mol/L范围内呈线性关系。富集4min检测下限为3.0×10(-10)mol/L。该法用于测定普罗帕酮制剂及人血清中的痕量普罗帕酮,均得到了满意的结果,并探讨了电极反应过程机理。     

Determination of Trace Amounts of Copper by Adsorptive Stripping Voltammetry

ABSTRACT

A technique is presented for the determination of trace amounts of copper(II) by adsorptive cathodic stripping voltammetry. The procedure is based on adsorptive accumulation of copper(II)-Alizarin Red S (ARS) complex on a hanging mercury drop electrode, followed by a stripping voltammetric measurement of the reduction current of the adsorbed complex at -0.16 V (vs. Ag/AgCl). The height of the copper -ARS reduction peak is linearly dependent upon the copper(II) concentration between 0.2-15 and 15-500 ng.ml^?1. The detection limit of the technique is 0.05 ng.ml^?1 copper(II) for a collection time of 1 minute. The method is free from most interferences. The procedure has been successfully applied to the determination of trace amounts of copper(II) in some analytical grade salts.     

吸附溶出伏安法测定水中痕量镉

报道了测定痕量镉的一种新方法．在０．０１ｍｏｌ／ＬＨＡｃ－０．０１ｍｏｌ／ＬＮａＡｃ－１．２×１０－５ｍｏｌ／Ｌ乙醛酸缩氨基硫脲（ＧＡＴＳＣ）体系中，Ｃｄ－ＧＡＴＳＣ产生一灵敏的吸附还原波，波的峰电位是－０．４３Ｖ（ｖｓ·ＳＣＥ），峰电流与镉的浓度在１．０×１０－８～８．０×１０－７ｍｏｌ／Ｌ范围内成直线关系．此法用于测定水中痕量镉，结果令人满意。     

氟哌啶醇的吸附伏安法研究

于NH_3-NH_4Cl底液中,氟哌啶醇(Hal)在悬汞电极上有一灵敏的还原蜂。EPC为-1.55V(vs饱和Ag/AgCl电极),其线性扫描吸附伏安法的线性范围为5.0×10~(-9)～9.0×10~(-7)mol/L。最低检测限为2.0×10~(-9)mol/L。测定了用药患者的尿样及针剂,片剂中Hal的含量,结果满意。对Hal在汞电极上的电化学性质,特别是吸附性进行了探讨。     

New Protocol for Determination of Rifampicine by Adsorptive Stripping Voltammetry

For determinations of organic compounds by adsorptive stripping voltammetry till now the same material of the electrode has been used for the accumulation and stripping steps. This paper describes a new protocol for extending the range of organic compounds, which can be determined by adsorptive stripping voltammetry. In the proposed procedure the accumulation step was performed on the electrode modified by a lead film, which assures adsorption of the studied species on the modified electrode and then the stripping step of the accumulated substance was performed on the support of the lead film electrode. As an example rifampicine was accumulated by adsorption at the lead film electrode while in the stripping step lead film and then the accumulated rifampicine were oxidized at a glassy carbon electrode. Using an acetate buffer as a supporting electrolyte a calibration graph for rifampicine in the range from 2.5×10^?10 to 1×10^?8 mol L^?1 was obtained. The detection limit for rifampicine following 60 s accumulation time was equal to 9×10^?11 mol L^?1. The obtained detection limit was comparable or lower than reported previously for other stripping voltammetric procedures. The proposed procedure was applied to rifampicine determination in pharmaceutical preparation.     

Determination of Platinum with Thiosemicarbazide by Catalytic Adsorptive Stripping Voltammetry (AdSV)

This work describes a very sensitive and selective voltammetric procedure for the determination of platinum. Instead of commonly used hydrazine, thiosemicarbazide as a component of supporting electrolyte was applied. The method is based on adsorption of platinum‐thiosemicarbazone complex, formed in situ in voltammetric cell from thiosemicarbazide and formaldehyde, coupled with a hydrogen catalytic reaction at a hanging mercury drop electrode. The linear relation between platinum concentration and height of analytical signal was observed up to 1.5×10^?9 mol L^?1 with the detection limit calculated as 1.5×10^?13 mol L^?1 (3 s of the blank) after 50 s of accumulation time. The effect of various interferences from other ions was studied. Described method was applied for platinum determination in hydroponically cultivated plants after microwave decomposition.     

大黄素的吸附溶出伏安研究

研究了大黄素在甲醇、二氧六环和水的混合溶剂中以１％硼砂为支持电解质在静汞电极上的吸附伏安行为。建立了用微分脉冲吸附溶出伏安法测定其含量的新方法。在－０３０Ｖ（ｖｓＡｇ／ＡｇＣｌ）电位下吸附富集，可得一灵敏的还原溶出峰，峰电位－０７５Ｖ，浓度在５×１０－８～５×１０－９ｍｏｌ／Ｌ范围内与峰电流具有良好的线性关系，最低检出限为１×１０－９ｍｏｌ／Ｌ。该法用于含有大黄素体系的测定简便、快速、可靠。     

Voltammetric Behavior of Arsenic(III) in the Presence of Sodium Diethyl Dithiocarbamate and Its Determination in Water and Highly Saline Samples by Adsorptive Stripping Voltammetry

This paper describes the voltammetric behavior of As(III) at the hanging mercury drop electrode (HMDE) in the presence of sodium diethyl dithiocarbamate (SDDC) and a new voltammetric method for the determination of As(III) at trace levels. The method is based on the adsorptive deposition of a As(III) complex with SDDC at ?0.45 V (vs. Ag/AgCl) on the HMDE in acidic medium of 0.01 mol L^?1 HCl (pH 2.0) and its cathodic stripping during the potential scan (100 mV s^?1). The linear range for the determination of As(III) in the presence of SDDC (4 μmol L^?1) in water samples was between 1 and 10 μg L^?1 for a deposition time of 300 s (r=0.994) and between 10 and 100 μg L^?1 for a deposition time of 60 s (r=0.999). For the determination of As(III) in dialysis concentrate samples, the linear range was between 5 and 25 μg L^?1 for a deposition time of 180 s (r=0.992) and between 10 and 100 μg L^?1 for a deposition time of 60 s (r=0.996). Detection limits of 0.3 and 2.2 μg L^?1 in water and dialysis concentrate samples were calculated for the method using a deposition time of 300 and 180 s, respectively. Recovery values between 93.0 and 110.0% for As(III) added to deionized, mineral, seawater (synthetic and real) and dialysis concentrate samples prove the satisfactory accuracy and applicability of the procedure.