Response surface methodology based on central composite design as a chemometric tool for optimization of dispersive-solidification liquid-liquid microextraction for speciation of inorganic arsenic in environmental water samples

被引:110
作者
Asadollahzadeh, Mehdi [1 ]
Tavakoli, Hamed [2 ]
Torab-Mostaedi, Meisam [3 ]
Hosseini, Ghaffar [4 ]
Hemmati, Alireza [1 ]
机构
[1] Islamic Azad Univ, South Tehran Branch, Fac Engn, Dept Chem Engn, Tehran, Iran
[2] Islamic Azad Univ, Nour Branch, Fac Engn, Nour, Iran
[3] Nucl Sci & Technol Res Inst, Nucl Fuel Cycle Res Sch, Tehran, Iran
[4] North Drilling Co, Tehran, Iran
关键词
Dispersive-solidification liquid liquid microextraction Environmental water samples; Inorganic arsenic; Response surface methodology; Central composite design; ATOMIC-ABSORPTION-SPECTROMETRY; SOLID-PHASE EXTRACTION; MULTIWALLED CARBON NANOTUBES; ULTRA-TRACE AMOUNTS; DROP MICROEXTRACTION; GAS-CHROMATOGRAPHY; BIOLOGICAL SAMPLES; HEAVY-METAL; PRECONCENTRATION; COPRECIPITATION;
D O I
10.1016/j.talanta.2013.11.071
中图分类号
O65 [分析化学];
学科分类号
070302 [分析化学];
摘要
Dispersive-solidification liquid-liquid microextraction (DSLLME) coupled with electrothermal atomic absorption spectrometry (ETAAS) was developed for preconcentration and determination of inorganic arsenic (III, V) in water samples. At pH=1, As(III) formed complex with ammonium pyrrolidine dithiocarbamate (APDC) and extracted into the fine droplets of 1-dodecanol (extraction solvent) which were dispersed with ethanol (disperser solvent) into the water sample solution. After extraction, the organic phase was separated by centrifugation, and was solidified by transferring into an ice bath. The solidified solvent was transferred to a conical vial and melted quickly at room temperature. As(III) was determined in the melted organic phase while As(V) remained in the aqueous layer. Total inorganic As was determined after the reduction of the pentavalent forms of arsenic with sodium thiosulphate and potassium iodide. As(V) was calculated by difference between the concentration of total inorganic As and As(III). The variable of interest in the DSLLME method, such as the volume of extraction solvent and disperser solvent, pH, concentration of APDC (chelating agent), extraction time and salt effect, was optimized with the aid of chemometric approaches. First, in screening experiments, fractional factorial design (FFD) was used for selecting the variables which significantly affected the extraction procedure. Afterwards, the significant variables were optimized using response surface methodology (RSM) based on central composite design (CCD). In the optimum conditions, the proposed method has been successfully applied to the determination of inorganic arsenic in different environmental water samples and certified reference material (NIST RSM 1643e). (C) 2014 Elsevier B.V. All rights reserved.
引用
收藏
页码:25 / 31
页数:7
相关论文
共 42 条
[1]
Application of Solid Phase Extraction on Multiwalled Carbon Nanotubes of Some Heavy Metal Ions to Analysis of Skin Whitening Cosmetics Using ICP-AES [J].
ALqadami, Ayoub A. ;
Abdalla, Mohammad Abulhassan ;
ALOthman, Zeid A. ;
Omer, Kamal .
INTERNATIONAL JOURNAL OF ENVIRONMENTAL RESEARCH AND PUBLIC HEALTH, 2013, 10 (01) :361-374
[2]
Development of an analytical method for the determination of arsenic in gasoline samples by hydride generation-graphite furnace atomic absorption spectrometry [J].
Becker, Emilene M. ;
Dessuy, Morgana B. ;
Boschetti, Wiliam ;
Vale, Maria Goreti R. ;
Ferreira, Sergio L. C. ;
Welz, Bernhard .
SPECTROCHIMICA ACTA PART B-ATOMIC SPECTROSCOPY, 2012, 71-72 :102-106
[3]
Monitoring of selenium. in water samples using dispersive liquid-liquid microextraction followed by iridium-modified tube graphite furnace atomic absorption spectrometry [J].
Bidari, Araz ;
Jahromi, Elham Zeini ;
Assadi, Yaghoub ;
Hosseini, Mohammad Reza Milani .
MICROCHEMICAL JOURNAL, 2007, 87 (01) :6-12
[4]
Colorimetric-solid phase extraction method for trace level determination of arsenite in water [J].
Bradley, Melissa M. ;
Siperko, Lorraine M. ;
Porter, Marc D. .
TALANTA, 2011, 86 :64-70
[5]
Brereton RG, 2003, CHEMOMETRICS DATA AN, P76
[6]
Optimization of electrochemical deposition of noble metals for permanent modification in graphite furnace atomic absorption spectrometry [J].
Bulska, E ;
Liebert-Ilkowska, K ;
Hulanicki, A .
SPECTROCHIMICA ACTA PART B-ATOMIC SPECTROSCOPY, 1998, 53 (6-8) :1057-1062
[7]
Multiple response optimization applied to the development of a capillary electrophoretic method for pharmaceutical analysis [J].
Candioti, LV ;
Robles, JC ;
Mantovani, VE ;
Goicoechea, HC .
TALANTA, 2006, 69 (01) :140-147
[8]
Determination of arsenic by electrothermal atomic absorption spectrometry using headspace liquid phase microextraction after in situ hydride generation [J].
Chamsaz, M ;
Arbab-Zavar, MH ;
Nazari, S .
JOURNAL OF ANALYTICAL ATOMIC SPECTROMETRY, 2003, 18 (10) :1279-1282
[9]
Schiff base-chitosan grafted multiwalled carbon nanotubes as a novel solid-phase extraction adsorbent for determination of heavy metal by ICP-MS [J].
Dai, Bingye ;
Cao, Meirong ;
Fang, Guozhen ;
Liu, Bing ;
Dong, Xv ;
Pan, Mingfei ;
Wang, Shuo .
JOURNAL OF HAZARDOUS MATERIALS, 2012, 219 :103-110
[10]
Determination of inorganic arsenic species by hydride generation atomic absorption spectrometry in water samples after preconcentration/separation on nano ZrO2/B2O3 by solid phase extraction [J].
Erdogan, Hakan ;
Yalcinkaya, Ozcan ;
Turker, Ali Rehber .
DESALINATION, 2011, 280 (1-3) :391-396