Silva Junior Mario M, Portugal Lindomar A, Serra Antonio M, Ferrer Laura, Cerdà Victor, Ferreira Sergio L C
Instituto de Química, Universidade Federal da Bahia, 40170-270 Salvador, Bahia, Brazil; Instituto Nacional de Ciência e Tecnologia, INCT, de Energia e Ambiente, Universidade Federal da Bahia, 40170-290 Salvador, Bahia, Brazil.
Group of Analytical Chemistry, Automation and Environment, Department of Chemistry, University of the Balearic Islands, E-07122 Palma de Mallorca, Spain.
Talanta. 2017 Apr 1;165:502-507. doi: 10.1016/j.talanta.2016.12.022. Epub 2016 Dec 13.
This paper proposes the use of a multisyringe flow injection analysis (MSFIA) system for inorganic antimony speciation analysis, trimethyl antimony(V) and determination of total antimony in soil samples using hydride generation atomic fluorescence spectrometry (HG-AFS). Total antimony has been determined after reduction of antimony(V) to antimony(III) using potassium iodide and ascorbic acid. For determination of total inorganic antimony the sample is percolated in a mini-column containing the Dowex 50W-X8 resin for retention of the organic species of antimony. Antimony(III) is quantified in presence of 8-hydroxyquinoline as masking agent for antimony(V) after an extraction step of the organic antimony species using the also same mini-column. The trimethyl antimony(V) content is found by difference between total antimony and total inorganic antimony. By other hand, antimony(V) is quantified by difference between total inorganic antimony and antimony(III). The analytical determinations were performed using sodium tetrahydroborate as reducing agent. The optimization step was performed using two-level full factorial design and Doehlert matrix involving the factors: hydrochloric acid and sodium tetrahydroborate concentrations and sample flow rate. The optimized experimental conditions allow the antimony determination utilizing the external calibration technique with limits of detection and quantification of 0.9 and 3.1ngg, respectively, and a precision expressed as relative standard deviation of 3.2% for an antimony solution of 5.0µgL. The method accuracy was confirmed by analysis of the soil certified reference material furnished from Sigma-Aldrich RTC. Additionally, addition/recovery tests were performed employing synthetic solutions prepared using trimethyl antimony(V), antimony(III), antimony(V) and five soil samples. The antimony extraction step was performed in a closed system using hydrochloric acid, ultrasonic radiation and controlled temperature. The method proposed was applied for analysis of thirteen soil samples collected in different sites of the Balearic Islands, Spain, and the results obtained varied from 19 to 46ngg for trimethyl antimony(V) and from 113 to 215ngg for total inorganic antimony. The concentrations obtained to antimony(V) were always higher than for antimony(III) in all the analyzed samples.
本文提出使用多注射器流动注射分析(MSFIA)系统,结合氢化物发生原子荧光光谱法(HG - AFS)对土壤样品中的无机锑形态、三甲基锑(V)和总锑进行分析测定。使用碘化钾和抗坏血酸将锑(V)还原为锑(III)后测定总锑。为测定总无机锑,将样品通过装有Dowex 50W - X8树脂的微型柱进行渗滤,以保留锑的有机形态。在用同一微型柱对有机锑形态进行萃取步骤后,在存在8 - 羟基喹啉作为锑(V)掩蔽剂的情况下对锑(III)进行定量。三甲基锑(V)的含量通过总锑与总无机锑的差值来确定。另一方面,锑(V)通过总无机锑与锑(III)的差值来定量。分析测定使用硼氢化钠作为还原剂。优化步骤采用二水平全因子设计和Doehlert矩阵,涉及盐酸浓度、硼氢化钠浓度和样品流速等因素。优化后的实验条件允许使用外标技术测定锑,检测限和定量限分别为0.9和3.1 ng/g,对于5.0 μg/L的锑溶液,精密度以相对标准偏差表示为3.2%。通过分析Sigma - Aldrich RTC提供的土壤标准参考物质确认了方法的准确性。此外,采用由三甲基锑(V)、锑(III)、锑(V)制备的合成溶液和五个土壤样品进行加标/回收率试验。锑的萃取步骤在封闭系统中使用盐酸、超声辐射和控制温度进行。所提出的方法应用于分析从西班牙巴利阿里群岛不同地点采集的13个土壤样品,结果表明,三甲基锑(V)的含量在19至46 ng/g之间,总无机锑的含量在113至215 ng/g之间。在所有分析样品中,锑(V)的浓度始终高于锑(III)的浓度。