首页> 外文期刊>International journal of environmental analytical chemistry >Ionic liquids versus ionic liquid-based surfactants in dispersive liquid-liquid microextraction for determining copper in water by flame atomic absorption spectrometry
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Ionic liquids versus ionic liquid-based surfactants in dispersive liquid-liquid microextraction for determining copper in water by flame atomic absorption spectrometry

机译:分散液-液微萃取中离子液体与离子液体基表面活性剂的火焰原子吸收光谱法测定水中的铜

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This work compares the performance of dispersive liquid-liquid method (DLLME) as a prior step for determining copper by flame atomic absorption spectrometry (FAAS), when using the ionic liquid (IL) 1-butyl-3-methylimidazolium hexafluorophosphate (C(4)MIm-PF6) or the IL-based surfactant 1-hexadecyl-3-butylimidazolium bromide (C(16)C(4)Im-Br) as extractant solvents. For the water-insoluble C(4)MIm-PF6, the most conventional DLLME mode using acetonitrile as dispersive solvent was employed. For the water-soluble C(16)C(4)Im-Br, the in situ DLLME mode with lithium bis[(trifluoromethane) sulfonyl] imide (Li-NTf2) as metathesis reagent was employed. In both approaches, some effective parameters such as volumes of extractant and dispersive solvents, concentration of complexing agent, pH of sample solution, salting-out effect and final diluting solvent to ensure compatibility with FAAS, were properly optimised. The optimum conditions for the IL-DLLME method using C(4)MIm-PF6 were: 100 mu L of neat C(4)MIm-PF6, 1 mL of acetonitrile, 10 mL of water, no control of pH for environmental waters, NaCl content of 23 g L-1, diethyl dithiocarbamate (DDTC) as complexing agent at 10 mg L-1 and final dilution of the micro-droplet with acetonitrile up to 70 mu L. The optimum conditions for the in situ IL-DLLME method using C(16)C(4)Im-Br were: 0.8 mL of acetonitrile, 10 mL of water containing C(16)C(4)Im-Br at 25.2 mmol L-1, final dilution step of the micro-droplet with 200 mu L of acetonitrile and remaining conditions as those of C(4)MIm-PF6. The analytical performance of both methods was similar, being slightly better for the IL-DLLME method using C(4)MIm-PF6, with limits of detection (LOD) of 3.3 mu g L-1 (versus 5.1 mu g L-1 when using C(16)C(4)Im-Br), precision values as intraday relative standard deviation (RSD in %) lower than 8.8% (being of 10% for the C(16)C(4)Im-Br method) and an enrichment factor of 54 (being 27 when using C(16)C(4)Im-Br). The DLLME-FAAS method with C(4)MIm-PF6 was used in the analysis of environmental waters with successful performance, with relative recoveries of 110% and 105%, and interday precision with RSD values of 21% and 7.4% for spiked levels of 60 and 160 mu g L-1, respectively. The results obtained when analysing an urban wastewater sample coming from an inter-laboratory exercise was comparable to those obtained for other 93 laboratories. The method was also valid for the determination of Cu2+ in presence of foreign ions commonly found in natural waters.
机译:当使用离子液体(IL)1-丁基-3-甲基咪唑六氟磷酸盐(C(4)时,这项工作将分散液-液法(DLLME)的性能作为通过火焰原子吸收光谱法(FAAS)测定铜的先前步骤进行了比较。 )MIm-PF6)或作为萃取溶剂的基于IL的表面活性剂1-十六烷基-3-丁基咪唑鎓溴化物(C(16)C(4)Im-Br)。对于水不溶性C(4)MIm-PF6,采用最常规的以乙腈为分散溶剂的DLLME模式。对于水溶性C(16)C(4)Im-Br,采用以双[(三氟甲烷)磺酰基]酰亚胺锂(Li-NTf2)作为复分解试剂的DLLME模式。两种方法都适当地优化了一些有效参数,例如萃取剂和分散剂的体积,络合剂的浓度,样品溶液的pH,盐析效果和最终稀释溶剂以确保与FAAS的相容性。使用C(4)MIm-PF6的IL-DLLME方法的最佳条件是:100微升纯净的C(4)MIm-PF6,1毫升乙腈,10毫升水,环境水的pH值不受控制, NaCl含量为23 g L-1,二乙基二硫代氨基甲酸酯(DDTC)作为络合剂,浓度为10 mg L-1,微滴最终用乙腈稀释至70μL。原位IL-DLLME方法的最佳条件使用C(16)C(4)Im-Br的量为:0.8 mL乙腈,10 mL含25.2 mmol L-1的C(16)C(4)Im-Br的水,微滴的最终稀释步骤用200μL乙腈,其余条件与C(4)MIm-PF6相同。两种方法的分析性能均相似,对于使用C(4)MIm-PF6的IL-DLLME方法而言,略有改善,检测限(LOD)为3.3μg L-1(相比于5.1μgL-1使用C(16)C(4)Im-Br)时的精确度值(当日相对标准偏差)(RSD,以%为单位)低于8.8%(对于C(16)C(4)Im-Br方法为10%)富集因子为54(使用C(16)C(4)Im-Br时为27)。带有C(4)MIm-PF6的DLLME-FAAS方法用于分析性能良好的环境水,相对回收率分别为110%和105%,日间精度为加标水平的RSD值分别为21%和7.4% L-1分别为60和160μg。分析来自实验室间活动的城市废水样品时获得的结果与其他93个实验室获得的结果相当。该方法对于在天然水中常见的外来离子存在下测定Cu2 +也有效。

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