Application of mercapto-silica polymerized high internal phase emulsions for the solid-phase extraction and preconcentration of trace lead(II).

A new class of solid-phase extraction column prepared with grafted mercapto-silica polymerized high internal phase emulsion particles was used for the preconcentration of trace lead. First, mercapto-silica polymerized high internal phase emulsion particles were synthesized by using high internal phase emulsion polymerization and carefully assembled in a polyethylene syringe column. The influences of various parameters including adsorption pH value, adsorption and desorption solvents, flow rate of the adsorption and desorption procedure were optimized, respectively, and the suitable uploading sample volumes, adsorption capacity, and reusability of solid phase extraction column were also investigated. Under the optimum conditions, Pb(2+) could be preconcentrated quantitatively over a wide pH range (2.0-5.0). In the presence of foreign ions, such as Na(+) , K(+) , Ca(2+) , Zn(2+) , Mg(2+) , Cu(2+) , Fe(2+) , Cd(2+) , Cl(-) and NO3 (-) , Pb(2+) could be recovered successfully. The prepared solid-phase extraction column performed with high stability and desirable durability, which allowed more than 100 replicate extractions without measurable changes of performance. The feasibility of the developed method was further validated by the extraction of Pb(2+) in rice samples. At three spiked levels of 40.0, 200 and 800 μg/kg, the average recoveries for Pb(2+) in rice samples ranged from 87.3 to 105.2%.

[1]  Fuyou Du,et al.  Development and validation of polymerized high internal phase emulsion monoliths coupled with HPLC and fluorescence detection for the determination of trace tetracycline antibiotics in environmental water samples. , 2015, Journal of separation science.

[2]  Jianping Li,et al.  Development of high internal phase emulsion polymeric monoliths for highly efficient enrichment of trace polycyclic aromatic hydrocarbons from large-volume water samples. , 2015, Journal of chromatography. A.

[3]  Lin Sun,et al.  High-internal-phase-emulsion polymeric monolith coupled with liquid chromatography–electrospray tandem mass spectrometry for enrichment and sensitive detection of trace cytokinins in plant samples , 2015, Analytical and Bioanalytical Chemistry.

[4]  A. Mostafavi,et al.  A microextraction procedure based on a task-specific ionic liquid for the separation and preconcentration of lead ions from red lipstick and pine leaves. , 2015, Journal of separation science.

[5]  M. Babazadeh,et al.  Determination of mercury(II) ions in seafood samples after extraction and preconcentration by a novel functionalized magnetic metal-organic framework nanocomposite. , 2015, Journal of separation science.

[6]  M. Soylak,et al.  Solid phase extraction of metal ions in environmental samples on 1-(2-pyridylazo)-2-naphthol impregnated activated carbon cloth. , 2015, Ecotoxicology and environmental safety.

[7]  Fuyou Du,et al.  Novel regenerative large-volume immobilized enzyme reactor: preparation, characterization and application. , 2014, Journal of chromatography. B, Analytical technologies in the biomedical and life sciences.

[8]  A. Mostafavi,et al.  Application of a thiourea-containing task-specific ionic liquid for the solid-phase extraction cleanup of lead ions from red lipstick, pine leaves, and water samples. , 2014, Journal of separation science.

[9]  T. Tan,et al.  Polymer monoliths with chelating functionalities for solid phase extraction of metal ions from water. , 2014, Journal of chromatography. A.

[10]  A. Mohamed,et al.  Removal of Cu(II), Pb(II) and Zn(II) Ions from Aqueous Solutions Using Selected Agricultural Wastes: Adsorption and Characterisation Studies , 2014 .

[11]  M. Heravi,et al.  Preparation and application of poly(2-amino thiophenol)/MWCNTs nanocomposite for adsorption and separation of cadmium and lead ions via solid phase extraction. , 2012, Journal of hazardous materials.

[12]  E. Pinelli,et al.  Assessment of lead speciation by organic ligands using speciation models , 2012 .

[13]  C. Sanchez,et al.  Syntheses and characterization of new organically grafted silica foams , 2010 .

[14]  K. Ulubayram,et al.  Acrylic-based high internal phase emulsion polymeric monolith for capillary electrochromatography. , 2010, Journal of chromatography. A.

[15]  A. Karimi,et al.  Solid phase extraction of copper, nickel, and cobalt in water samples after extraction using surfactant coated alumina modified with indane-1,2,3-trione 1,2-dioxime and determination by flame atomic absorption spectrometry , 2010, Turkish Journal of Chemistry.

[16]  N. Huang,et al.  Three-dimensional flower-like brushite crystals prepared from high internal phase emulsion for drug delivery application , 2009 .

[17]  M. Soylak,et al.  Flame atomic absorption spectrometric determination of zinc, nickel, iron and lead in different matrixes after solid phase extraction on sodium dodecyl sulfate (SDS)-coated alumina as their bis (2-hydroxyacetophenone)-1, 3-propanediimine chelates. , 2009, Journal of hazardous materials.

[18]  N. Rahbar,et al.  Solid phase extraction of lead and cadmium using solid sulfur as a new metal extractor prior to determination by flame atomic absorption spectrometry. , 2009, Journal of hazardous materials.

[19]  M. McBride,et al.  Health risk from heavy metals via consumption of food crops in the vicinity of Dabaoshan mine, South China. , 2009, The Science of the total environment.

[20]  L. Qi,et al.  A novel glycidyl methacrylate-based monolith with sub-micron skeletons and well-defined macropores , 2009 .

[21]  C. Sanchez,et al.  First Pd@Organo−Si(HIPE) Open-Cell Hybrid Monoliths Generation Offering Cycling Heck Catalysis Reactions , 2008 .

[22]  M. Soylak,et al.  Solid phase extraction of heavy metal ions in environmental samples on multiwalled carbon nanotubes. , 2008, Journal of hazardous materials.

[23]  A. Ensafi,et al.  On-line separation and preconcentration of lead(II) by solid-phase extraction using activated carbon loaded with xylenol orange and its determination by flame atomic absorption spectrometry. , 2008, Journal of hazardous materials.

[24]  Jianji Wang,et al.  Chemically functionalized silica gel with alizarin violet and its application for selective solid-phase extraction of lead from environmental samples. , 2008, Talanta.

[25]  Mustafa Soylak,et al.  Adsorption characteristics of Cu(II) and Pb(II) onto expanded perlite from aqueous solution. , 2007, Journal of hazardous materials.

[26]  M. Soylak,et al.  Solid-phase extraction of Mn(II), Co(II), Ni(II), Cu(II), Cd(II) and Pb(II) ions from environmental samples by flame atomic absorption spectrometry (FAAS). , 2007, Journal of hazardous materials.

[27]  M. Soylak,et al.  Flame atomic absorption spectrometric determination of cadmium(II) and lead(II) after their solid phase extraction as dibenzyldithiocarbamate chelates on Dowex Optipore V-493. , 2006, Analytica chimica acta.

[28]  M. Soylak,et al.  Enrichment/separation of cadmium(II) and lead(II) in environmental samples by solid phase extraction. , 2005, Journal of hazardous materials.

[29]  M. Soylak,et al.  Separation-preconcentration of nickel and lead in food samples by a combination of solid-liquid-solid dispersive extraction using SiO2 nanoparticles, ionic liquid-based dispersive liquid-liquid micro-extraction. , 2015, Talanta.

[30]  M. Rabani,et al.  A new functionalized resin and its application in flame atomic absorption spectrophotometric determination of trace amounts of heavy metal ions after solid phase extraction in water samples , 2013 .