Burguera J L, Burguera M, Rondón C, Carrero P, Brunetto M R, Petit de Peña Y
IVAIQUIM (Venezuelan Andean Institute of Chemistry), Faculty of Sciences, University of Los Andes, P.O. Box 542, Mérida 5101-A, Venezuela.
Talanta. 2000 May 31;52(1):27-37. doi: 10.1016/s0039-9140(99)00337-9.
A flow injection (FI) on-line precipitation-dissolution was developed for electrothermal atomic absorption spectrometry (ETAAS) determination of (ultra)trace amounts of beryllium in water samples. Beryllium was precipitated quantitatively with NH(4)OH+NH(4)Cl and collected in a knotted tube of Tygon without using a filter, while the other matrix components flowed downstream to waste. The precipitate was dissolved with nitric acid and a sub-sample was collected in a capillary of a sampling arm assembly, to introduce 10 mul volumes into the graphite tube by means of positive displacement with air through a time-based injector. This sequence was timed to synchronize with the previous introduction of 6 mug of Lu (in 20 mul) by the spectrometer autosampler. The effect of a number of possible cations on the beryllium precipitation process was studied. While, the addition of Ba(2+), Sr(2+), Ca(2+), Mg(2+), Mn(2+), Zn(2+), Co(2+) and Ni(2+) did not produce any perceptible precipitate on the reaction coil walls, the addition of Al(3+), Cr(3+) and Fe(3+) produced large precipitated particles. However, their tolerance limit was well above the levels at which theses species are commonly found in most natural waters. The detection limit (3sigma) of 25 ng l(-1) in the sample solution was obtained. The precision of the method, evaluated by ten replicate analyses of solutions containing 20 and 200 pg of beryllium were 4.8 and 4.0% (n=5), respectively. Enrichment factors from 7.0 to 10.3 and from 10.5 to 13.8 were obtained for precipitation times from 25 to 38 s and from 43 to 50 s for waste and tap waters, respectively. These results indicate that the enrichment factor was limited by the interference of some matrix metals which could precipitate as hydroxides (or related species) and be retained in the reaction coil. The integrated system permits fully automated operation, avoiding time-consuming manual work and enhancing the reproducibility and precision of the determination of beryllium. The results obtained for the determination of beryllium in certified reference materials (trace elements in water), together with the good recovery of spiked analytes, demonstrate the applicability of the procedure to the analysis of natural waters.
开发了一种流动注射(FI)在线沉淀 - 溶解方法,用于电热原子吸收光谱法(ETAAS)测定水样中(超)痕量铍。铍用NH(4)OH + NH(4)Cl定量沉淀,并收集在泰根打结管中,无需使用过滤器,而其他基质成分则顺流至废液。沉淀用硝酸溶解,在采样臂组件的毛细管中收集子样品,通过基于时间的进样器利用空气正压将10微升体积引入石墨管。此序列的时间设置为与光谱仪自动进样器先前引入6微克镥(20微升中)同步。研究了多种可能的阳离子对铍沉淀过程的影响。虽然加入Ba(2+)、Sr(2+)、Ca(2+)、Mg(2+)、Mn(2+)、Zn(2+)、Co(2+)和Ni(2+)在反应盘管壁上未产生任何可察觉的沉淀,但加入Al(3+)、Cr(3+)和Fe(3+)产生了大的沉淀颗粒。然而,它们的耐受极限远高于这些物质在大多数天然水中的常见水平。在样品溶液中获得了25 ng l(-1)的检测限(3σ)。通过对含有20和200 pg铍的溶液进行十次重复分析评估,该方法的精密度分别为4.8%和4.0%(n = 5)。对于废水和自来水,沉淀时间为25至38秒和43至50秒时,富集因子分别为7.0至10.3和10.5至13.8。这些结果表明,富集因子受一些可能以氢氧化物(或相关物种)形式沉淀并保留在反应盘管中的基质金属的干扰限制。该集成系统允许全自动操作,避免了耗时的手工工作,并提高了铍测定的重现性和精密度。在认证参考物质(水中微量元素)中铍测定获得的结果,以及加标分析物的良好回收率,证明了该方法在天然水分析中的适用性。