Negreira N, Rodríguez I, Ramil M, Rubí E, Cela R
Departamento de Química Analítica, Nutrición y Bromatología, Instituto de Investigación y Análisis Alimentario, Universidad de Santiago de Compostela, Santiago de Compostela 15782, Spain.
Anal Chim Acta. 2009 Apr 6;638(1):36-44. doi: 10.1016/j.aca.2009.02.015. Epub 2009 Feb 14.
A sensitive procedure for the determination of three UV filters: ethylhexyl salicylate (EHS), 3,3,5-trimethylcyclohexyl salicylate (Homosalate, HMS), 2-hydroxy-4-methoxybenzophenone (BP-3) and two related hydroxylated benzophenones (2,4-dihydroxybenzophenone, BP-1 and 2,2'-dihydroxy-4-methoxybenzophenone, BP-8) in water samples is presented. Analytes were first concentrated on the coating of a solid-phase microextraction (SPME) fibre, on-fibre silylated and then determined using gas chromatography combined with tandem mass spectrometry (GC-MS/MS). Factors affecting the performance of extraction and derivatization steps are thoroughly evaluated and their effects on the yield of the sample preparation discussed. Under final working conditions, a PDMS-DVB coated SPME fibre was exposed directly to 10 mL of water, adjusted at pH 3, for 30 min. After that, the fibre was placed in the headspace (HS) of a 1.5 mL vial containing 20 microL of N-methyl-N-(trimethylsilyl)-trifluoroacetamide (MSTFA). On-fibre silylation of hydroxyl groups contained in the structure of target compounds was performed at 45 degrees C for 10 min. The whole sample preparation process was completed in 40 min, providing limits of quantification from 0.5 to 10 ng L(-1) and acceptable precision (RSDs under 13%) for samples spiked at different concentrations. All compounds could be accurately determined in river and treated wastewater (relative recoveries from 89 to 115%) using standards in ultrapure water, whereas standard addition is recommended to quantify their levels in untreated wastewater. Analysis of wastewater revealed the systematic presence of BP-3 and BP-1 in raw samples with maximum concentrations close to 500 and 250 ng L(-1), respectively.
本文介绍了一种灵敏的方法,用于测定水样中的三种紫外线过滤剂:乙基己基水杨酸酯(EHS)、3,3,5-三甲基环己基水杨酸酯(胡莫柳酯,HMS)、2-羟基-4-甲氧基二苯甲酮(BP-3)以及两种相关的羟基化二苯甲酮(2,4-二羟基二苯甲酮,BP-1和2,2'-二羟基-4-甲氧基二苯甲酮,BP-8)。分析物首先在固相微萃取(SPME)纤维涂层上进行富集,在纤维上进行硅烷化,然后使用气相色谱-串联质谱(GC-MS/MS)进行测定。对影响萃取和衍生步骤性能的因素进行了全面评估,并讨论了它们对样品制备产率的影响。在最终工作条件下,将涂有PDMS-DVB的SPME纤维直接暴露于10 mL pH为3的水中30分钟。之后,将纤维置于装有20 μL N-甲基-N-(三甲基硅基)-三氟乙酰胺(MSTFA)的1.5 mL小瓶的顶空(HS)中。目标化合物结构中含有的羟基在45℃下进行10分钟的纤维上硅烷化。整个样品制备过程在四十分钟内完成,定量限为0.5至10 ng L⁻¹,对于不同浓度加标的样品具有可接受的精密度(相对标准偏差低于13%)。使用超纯水标准品可准确测定河流和处理后的废水中的所有化合物(相对回收率为89%至115%),而对于未处理的废水,建议采用标准加入法来定量其含量。废水分析表明,原始样品中系统存在BP-3和BP-1,其最大浓度分别接近500和250 ng L⁻¹。