期刊文献+

液液微萃取火焰原子吸收法测定污水中的Cd和Ni

Liquid-Liquid Microextraction and Flame Atomic Absorption Spectrometry for Determination of Cadmium(Ⅱ) and Nickel(Ⅱ) in Wastewater
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摘要 基于分散液液微萃取,建立了一种简单、快速、环保的涡流辅助-表面活性剂增强乳化-分散液液微萃取原子吸收测定污水中的Cd和Ni的方法。该方法中,萃取剂在涡旋器的辅助下分散到水溶液中,同时表面活性剂作为乳化剂,加速了分析物从水溶液中转移到萃取剂中。对影响该方法的主要因素进行了研究,得到的最佳优化条件为:萃取剂1-溴-3-甲基丁烷的体积为60μL,表面活性剂Triton X—114的浓度为0.2mmol/L,提取时间为1min。在优化条件下得到的富集倍数为211~214,线性范围为1~600μg/L,Cd和Ni的检出限分别为0.16μg/L和0.25μg/L。该方法的加标回收率为92%~102%,相对标准偏差为1.19%~1.58%。 A simple, fast and environmentally friendly method for the determination of cadmium ( Ⅱ ) and nickel ( Ⅱ) in wastewater using vortex-assisted surfactant-enhanced-emulsification liquid-liquid microextraction (VSLLME) combined with flame atomic absorption spectrometry (FAAS) was developed. In the established method, the dispersant dissolved into the aqueous solution by the vortex agitator. Meanwhile, a snrfactant which was used as an emulsifier, promoted the transfer of analytes from aqueous solution to the extractant. The main factors affecting the method were studied. The optimal conditions were obtained as follows : 60 μL of 1-bromo-3-methylbutane used as extractant, 0.2 mmol/L of Triton X- 114 used as surfactant and 60 s of extraction time. Under the optimal conditions, enrichment factor reached 211 to 214, the calibration curve was linear in the range of 1 to 600μg/L, the detection limits of Cd and Ni were 0.16 μg/L and 0.25 μg/L. The recoveries ranged from 92% to 102% , and the relative standard deviation (RSD) was in the range of 1.19% to 1.58%.
出处 《中国给水排水》 CAS CSCD 北大核心 2015年第22期112-115,122,共5页 China Water & Wastewater
关键词 涡流辅助 表面活性剂增强乳化-分散液液微萃取 原子吸收 1-溴-3-甲基丁烷 CD NI vortex-assisted surfactant-enhanced-emulsification liquid-liquid microextraction flame atomic absorption spectrometry 1-bromo-3-methylbutane Cd Ni
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  • 1Escudero L A, Blanchet A J,Sombra L L,et al. Determi- nation of the total and extractable fraction of Ni in lake sediments and natural waters of San Luis (Argentina) by FAAS using a simple solid phase extraction system [ J ]. Microchem J,2014,116:92 - 97.
  • 2Coskun O, Serife S, Senol K,et al. Determination of gold and palladium in environmental samples by FAAS after dispersive liquid-liquid microextraction pretreatment [Jl. J Ind Eng Chem,2014,20(6):4059 -4065.
  • 3Mirzaei M, Behzadi M, Abadi N M, et al. Simultaneous separation/preconcentration of ultra trace heavy metals in industrial wastewaters by dispersive liquid-liquid micro- extraction based on solidification of floating organic drop prior to determination by graphite furnace atomic absorp- tion spectrometry [ J ]. J Hazard Mater, 2011,186 ( 2/ 3 ) : 1739 - 1743.
  • 4Cheng G H, He M,Peng H Y,et al. Dithizone modified magnetic nanoparticles for fast and selective solid phase extraction of trace elements in environmental and biologi- cal samples prior to their determination by ICP-OES[ J]. Talanta, 2012,88 : 507 - 515.
  • 5Li Y, Peng G L, He Q, et al. Dispersive liquid-liquid mi-croextraction based on the solidification of floating organ- ic drop followed by ICP-MS for the simultaneous determi- nation of heavy metals in wastewaters [ J ]. Spectrochim Acta A,2015,140 : 156 - 161.
  • 6Rezaee M,Assadi Y,Hosseini M R M,et al. Determina- tion of organic compounds in water using dispersive liq- uid-liquid microextraction [ J ]. J Chromatogr A, 2006, 1116(1/2) :1 -9.
  • 7Liang P, Sang H B. Determination of trace lead in bio- logical and water samples with dispersive liquid-liquid microextraction preconcentration [ J ]. Anal Biochem, 2008,380( 1 ) :21 -25.
  • 8Regueiro J, Llompart M, Gareia-Jares C, et al. Ultra- sound-assisted emulsifieation-microextraction of emergent contaminants and pesticides in environmental waters [ J ]. J C hromatogr A,2008,1190 ( 1/2 ) :27 - 38.
  • 9Yang Z H, Lu Y L, Liu Y, et al. Vortex-assisted surfac- tant-enhanced-emulsification liquid-liquid microextrae- tion[J]. J Chromatogr A,2011,1218(40):7071 - 7077.
  • 10Peng G L, He Q, A1-Hamadani S M Z F, et al. Disper- sive liquid-liquid microextraction method based on solid- ification of floating organic droplet for the determination of thiamphenicol and florfenicol in environmental water samples [ J ]. Ecotox Environ Safe, 2015, 115 : 229 - 233.

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