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Membrane optode for mercury(Ⅱ) determination in aqueous samples

机译:膜光电二极管用于测定水样中的汞(Ⅱ)

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摘要

A color changeable optode for Hg(Ⅱ) was prepared by the immobilization of a dye 4-(2-pyridylazo)resorcinol (PAR) and a liquid ion-exchanger trioctylmethylammonium chloride (Aliquat-336) in the tri-(2-ethylhexyl) phosphate plasticized cellulose triacetate matrix. Hg(Ⅱ) and CH_3Hg~+ from aqueous samples could be quantitatively preconcentrated in this transparent optode producing a distinct color change [λ_(max) - 520 nm) within 5 min equilibration time in bicarbonate aqueous medium or 30 min in natural water. Whereas optode sample without Aliquat-336 did not change its color corresponding to Hg-PAR complex on equilibrium with the same aqueous solution containing Hg(Ⅱ) ions. The uptake of Hg(Ⅱ) was found to be pH dependant with a maximum (>90%) at a pH 7.5. The uptake of ions like Cu(Ⅱ), Fe(Ⅱ), Zn(II) and Pb(Ⅱ) was negligible in the optode where as the uptake of Cd(Ⅱ) and Zn(Ⅱ) ions was 10-15% at pH 7.5. The optode developed in the present work was studied for its analytical application for Hg(Ⅱ) in the aqueous samples by spectrophotometry, radiotracer (~(203)Hg), Energy Dispersive X-ray Fluorescence (EDXRF) analyses and Instrumental Neutron Activation Analysis (INAA). The minimum amount of Hg(Ⅱ) required to produce detectable response by spectrophotometry, INAA and EDXRF were found to be 5.5,1 and 12 μg, respectively. This optode showed a linear increase in the absorbance at λ_(.max) = 520 nm over a concentration range of 0.22-1.32 g/mL of Hg(Ⅱ) ions in aqueous solution for 5min. The preconcentra-tion of Hg(Ⅱ) from large volume of aqueous solution was used to extend the lower limit of concentration range that can be quantified by the spectrophotometry of optode. It was observed that preconcentration of 11 μg Hg(Ⅱ) in 100mL (0.11 μg/mL) in aqueous samples gives a distinct color change and absorbance above 3rr of the blank absorbance. The optode developed in the present work was found to be reusable.
机译:通过将染料4-(2-吡啶基偶氮)间苯二酚(PAR)和液体离子交换剂三辛基甲基氯化铵(Aliquat-336)固定在三-(2-乙基己基)中来制备Hg(Ⅱ)的变色光电二极管。磷酸盐增塑的三乙酸纤维素基体。在碳酸氢盐水溶液介质中或在天然水中溶解30分钟后,可在此透明光电极中定量富集来自水性样品中的Hg(Ⅱ)和CH_3Hg〜+,从而产生明显的颜色变化[λ_(max)-520 nm)。而没有Aliquat-336的光电极样品在与含Hg(Ⅱ)离子的相同水溶液平衡时,其颜色没有改变,与Hg-PAR复合物相对应。发现Hg(Ⅱ)的吸收与pH有关,在pH 7.5时最大(> 90%)。光电二极管中的Cu(Ⅱ),Fe(Ⅱ),Zn(II)和Pb(Ⅱ)等离子的吸收可以忽略不计,因为Cd(Ⅱ)和Zn(Ⅱ)离子的吸收率为10-15%。 pH值7.5。通过分光光度法,放射性示踪剂(〜(203)Hg),能量色散X射线荧光(EDXRF)分析和仪器中子活化分析( INAA)。通过分光光度法,INAA和EDXRF产生可检测的响应所需的Hg(Ⅱ)的最小量分别为5.5、1和12μg。该光电二极管在浓度范围为0.22-1.32 g / mL的Hg(Ⅱ)水溶液中持续5min,在λ_(。max)= 520 nm处的吸光度呈线性增加。从大量水溶液中对Hg(Ⅱ)进行预浓缩,以扩展可通过光电分光光度法定量的浓度范围的下限。观察到在100 mL(0.11μg/ mL)的水溶液样品中预浓缩11μgHg(Ⅱ)会产生明显的颜色变化和3rr以上的空白吸光度。发现当前工作中开发的光电二极管是可重用的。

著录项

  • 来源
    《Journal of Hazardous Materials》 |2009年第1期|377-382|共6页
  • 作者单位

    Department of Environmental Sciences, S.V. University, Tirupati 517502, India;

    Radiochemistry Division, Bhabha Atomic Research Centre, Mumbai 400085, India;

    Radiochemistry Division, Bhabha Atomic Research Centre, Mumbai 400085, India;

    Radiochemistry Division, Bhabha Atomic Research Centre, Mumbai 400085, India;

    Radiochemistry Division, Bhabha Atomic Research Centre, Mumbai 400085, India;

    Department of Environmental Sciences, S.V. University, Tirupati 517502, India;

    Radiochemistry Division, Bhabha Atomic Research Centre, Mumbai 400085, India;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    mercury(Ⅱ); methylmercury; optode; 4-(2-Pyridylazo)resorcinol; aliquat-336; radiotracer;

    机译:汞(Ⅱ);甲基汞optode;4-(2-吡啶偶氮)间苯二酚;aliquat-336;放射性示踪剂;
  • 入库时间 2022-08-17 13:25:01

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