O'Hara Matthew J, Burge Scott R, Grate Jay W
Pacific Northwest National Laboratory, P.O. Box 999, Richland, Washington 99352, USA.
Anal Chem. 2009 Feb 1;81(3):1068-78. doi: 10.1021/ac8021604.
A preconcentrating minicolumn sensor for technetium-99 detection in water consists of a packed bed containing a mixture of anion-exchange resin and scintillating plastic beads. The column materials are contained in a transparent plastic flow cell placed between two photomultiplier tubes for radiometric detection. Upon retention of pertechnetate anions, the radioactive decay of Tc-99 results in detectable scintillation pulses that are counted in coincidence. In equilibration-based sensing mode, the sample is pumped through the packed bed until complete chromatographic equilibrium is achieved between the activity concentration in the water sample and the concentration on the anion-exchange resin. The analytical signal is the observed steady-state count rate at equilibrium. The sensitivity is related to a measurement efficiency parameter that is the product of the retention volume and the absolute radiometric detection efficiency. This sensor can readily detect pertechnetate to levels 10 times below the drinking water standard of 0.033 Bq/mL. The potential for other anions in natural groundwater and contaminated groundwater plumes to interfere with pertechnetate detection and quantification has been examined in detail, with reference to the groundwater chemistry at the Hanford site in Washington state. Individual anions such as nitrate, carbonate, chloride, and iodide, at natural or elevated concentrations, do not interfere significantly with pertechnetate uptake on the anion-exchange resin. Elevated chromate or sulfate anion concentrations can interfere with pertechnetate uptake by the resin, but only at levels substantially higher than typical concentrations in groundwater or contamination plumes. Nevertheless, elevated anion concentrations may reduce pertechnetate uptake and sensitivity of the sensor when present in combination. Chromate is retained on the anion-exchange resin from water at parts-per-billion levels, leading to an orange stain that interferes with pertechnetate detection by the absorption of scintillation light pulses (color quench). Radioactivity from radioiodine, tritium, and uranium is not expected to create a significant positive bias in groundwater analyses. A method of automated fluidic standard addition is demonstrated that corrects for matrix interferences leading to accurate analyses over a wide range of groundwater compositions. This method is developed for automated groundwater monitoring applications.
一种用于检测水中锝-99的预浓缩微型柱传感器,由一个填充床组成,该填充床包含阴离子交换树脂和闪烁塑料珠的混合物。柱材料置于一个透明塑料流通池中,该流通池位于两个光电倍增管之间用于辐射检测。当高锝酸根阴离子被保留时,Tc-99的放射性衰变会产生可检测到的闪烁脉冲,这些脉冲会进行符合计数。在基于平衡的传感模式下,将样品泵入填充床,直到水样中的活度浓度与阴离子交换树脂上的浓度达到完全的色谱平衡。分析信号是平衡时观察到的稳态计数率。灵敏度与一个测量效率参数有关,该参数是保留体积与绝对辐射检测效率的乘积。该传感器能够轻松检测到高锝酸根,检测水平比0.033 Bq/mL的饮用水标准低10倍。参考华盛顿州汉福德 Site 的地下水化学情况,详细研究了天然地下水和受污染地下水羽流中其他阴离子干扰高锝酸根检测和定量的可能性。硝酸盐、碳酸盐、氯化物和碘化物等单个阴离子,在天然浓度或升高浓度下,不会对高锝酸根在阴离子交换树脂上的吸附产生显著干扰。铬酸根或硫酸根阴离子浓度升高会干扰树脂对高锝酸根的吸附,但仅在浓度远高于地下水或污染羽流中的典型浓度时才会如此。然而,当阴离子浓度升高同时存在时,可能会降低高锝酸根的吸附和传感器的灵敏度。铬酸根会以十亿分之一的水平从水中保留在阴离子交换树脂上,导致橙色污渍,通过吸收闪烁光脉冲(颜色猝灭)干扰高锝酸根的检测。预计来自放射性碘、氚和铀的放射性不会在地下水分析中产生显著的正偏差。展示了一种自动流体标准加入方法,该方法可校正基质干扰,从而在广泛的地下水成分范围内进行准确分析。该方法是为自动地下水监测应用而开发的。