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采用2,2,6,6-四甲基-3,5-庚二酮通过有机离子缔合相萃取/反微萃取对环境水中锂进行预富集并利用液体电极等离子体原子发射光谱法和石墨炉原子吸收光谱法测定

Organic Ion-associate Phase Extraction/Back-microextraction for the Preconcentration and Determination of Lithium Using 2,2,6,6-Tetramethyl-3,5-heptanedione by Liquid Electrode Plasma Atomic Emission Spectrometry and GF-AAS in Environmental Water.

作者信息

Mizuna Kenta, Murashima Ryo, Okazaki Takuya, Sazawa Kazuto, Kuramitz Hideki, Taguchi Shigeru, Nakayama Keiko, Yamamoto Tamotsu, Takamura Yuzuru, Hata Noriko

机构信息

Department of Environmental Biology and Chemistry, Graduate School of Science and Engineering (Science Div.), Toyama University, 3190 Gofuku, Toyama, Toyama, 930-8555, Japan.

Micro Emission Ltd., Ishikawa Create Lab, 2-13 Asahidai, Nomi, Ishikawa 923-1211, Japan.

出版信息

Anal Sci. 2020 May 10;36(5):595-599. doi: 10.2116/analsci.20SBP13. Epub 2020 Mar 20.

Abstract

We developed an ion-associate phase (IAP)-extraction/acid back-extraction system for the preconcentration and atomic spectrometric determination of lithium trace amounts in water. The chelating reagent for lithium also works as a constituent of the extraction phase. The lithium in a 10 mL sample solution was converted through a chelate complex reaction with 2,2,6,6-tetramethyl-3,5-heptanedione (HDPM). The addition of a benzyldimethyltetradecylammonium ion caused the formation of IAP suspension in the solution. Centrifugation of the solution led to the isolation of a liquid organic phase and the lithium complex was extracted as the upper phase from the centrifuge tube. After the aqueous phase was removed, lithium was back-extracted with a 400 μL nitric acid solution from the IAP. The acid phase was measured using liquid-electrode-plasma atomic-emission-spectrometry (LEP-AES) or graphite-furnace atomic-absorption spectroscopy (GF-AAS). The detection limits were 0.02 mg/L for LEP-AES and 0.02 μg/L for GF-AAS. This system was applied to the determination of environmental water. The HDPM in the organic phase was reusable.

摘要

我们开发了一种离子缔合相(IAP)萃取/酸反萃取系统,用于水中痕量锂的预富集和原子光谱测定。锂的螯合试剂同时也是萃取相的组成成分。10 mL样品溶液中的锂通过与2,2,6,6-四甲基-3,5-庚二酮(HDPM)发生螯合络合反应进行转化。加入苄基二甲基十四烷基铵离子会导致溶液中形成IAP悬浮液。对溶液进行离心可分离出有机液相,锂络合物作为上层相从离心管中被萃取出来。去除水相后,用400 μL硝酸溶液从IAP中反萃取锂。酸相使用液体电极等离子体原子发射光谱法(LEP-AES)或石墨炉原子吸收光谱法(GF-AAS)进行测量。LEP-AES的检测限为0.02 mg/L,GF-AAS的检测限为0.02 μg/L。该系统应用于环境水的测定。有机相中的HDPM可重复使用。

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