complexant cellulose membrane for analytical
Transcription
complexant cellulose membrane for analytical
230 XXV ARS SEPARATORIA – Toruń, Poland 2010 COMPLEXANT CELLULOSE MEMBRANE FOR ANALYTICAL SEPARATIONS Antoneta Doina RADU, Ludmila IARCA, Niculina Nina BADEA and Gheorghe NECHIFOR University, Politehnica of Bucharest, Faculty of Applied Chemistry and Materials Science, Department of Analytical Chemistry and Instrumental Analysis, 1-5 Polizu Street, Bucharest, sector 1, 011061, Romania, ghnechifor@gmail.com Abstract The heavy metals impurities from alcohols represent a major problem in the reactions or processes which requires analytical purity of solvents. In this work, the immobilization of amino benzo 15 crown ether and aza 15 crown ether on cellulose membranes for heavy metals removal is studied. The cellulose membranes are activated with KOH in ethyl alcohol and superficial alkali cellulose (Cell-O-K+) is obtained. On the other hand, amino benzo 15 crown ether and aza 15 crown ether are treated with cyanuric chloride in dioxan in the presence of triethyl amine. The two components, activated membrane and amino crown ether derivative, are introduced in dioxan at a reflux for 3 hours. The functionalized membrane is washed with ethylic alcohol and bi distilled water. The morphological and structural characterization of functionalized membrane was realized by SEM microscopy, thermal analysis, FT-IR spectroscopy. The obtained membranes were used for heavy metals removal from alcohols during a nanofiltration processes. 1. INTRODUCTION The cellulose membranes remain main materials for dialysis [1]. The improvement of regenerated cellulose membranes for dialysis represents a main objective of the research [2]. It is well known, for example the treatments of membranes with heparin to prevent the blood coagulation [3] or with carbon nanotubes for improvement of heavy metals ions retention [4]. In this paper the immobilization of amino benzo 15 crown ether and aza 15 crown ether (CE) on cellulose membranes is studied. 2. MATERIALS AND METHODS The cellulose membranes are activated with KOH in methanol, ethanol, propanol or butanol and superficial alkali cellulose (Cell-O-K+) is obtained. On the other hand, amino benzo 15 crown ether and aza 15 crown ether (CE) 231 XXV ARS SEPARATORIA – Toruń, Poland 2010 are treated with cyanuric chloride in dioxan in the presence of triethyl amine. The two components, activated membrane and amino derivative are introduced in dioxan at reflux for 3 hours. The obtain membrane is washed with ethyl alcohol and bi distilled water. The morphological and structural characterization of functionalized membrane was realized by SEM microscopy, thermal analysis, FT-IR spectroscopy. The obtained membranes were used for heavy metals removal from alcohols during a nanofiltration processes. 3. RESULTS AND DISCUSSIONS Passive membranes have been used for separations ranging from seawater desalination via reverse osmosis to the separation of particles with microfiltration membranes. However, active membranes, achieved by immobilization of macromolecules containing multiple functional sites to nanofiltration membranes, allow for more selective separations. We have designed a novel membrane system consisting of cellulose-based nanofiltration membranes functionalized with amino benzo 15 crown ether and aza 15 crown ether (fig. 1). O O O O N NH2 + Cl O Cl O O O Dioxan O N N O Cl N NH N N Cl Cl a CH2OH O HO HO CH2OH O OH HO O OH O O CH2OH OH OH HO n-2 O O O O KOH NH O O Cl N N N O O NH O O Cl N N N CH2O-K+ O - + CH2O-K+ O HO HO OH CH2OK O O-K+ HO O O O CH2OH OH HO CH2O-K+ O Cl HO HO OH n-2 OH O HO O O O CH2OH OH HO OH n-2 b Fig. 1. The functionalization reaction of crown ether (CE) with cyanuric chloride (a) and the reactions for functionalized cellulose membrane synthesis (b) 232 XXV ARS SEPARATORIA – Toruń, Poland 2010 Only scanning electron microscopy were presented in this paper (Table 1), but FT-IR, thermal analysis EDAX and NMR were previously presented [5]. Table 1. Scanning Electron Microscopy of tested membranes Membrane type Cellulose Membrane SEM section SEM surface Alkali Cellulose Membrane Cyanuric Cellulose Membrane Amine Crown Ether Cellulose Membrane To characterize the effects of membrane structure on complexation, several factors must be examined. These include the density and amount of selective crown ether available on the membrane support, the metal solution XXV ARS SEPARATORIA – Toruń, Poland 2010 233 concentration, and charge and pore size effects on the rates of sorption [5]. This work is a support for sampling in analytical determination of metallic ions from environmental samples (e.g. Lead). 4. CONCLUSIONS This paper was intended to show the differences in the metal sorption behavior for homogeneous and immobilized CE and the role of functionalization. Acknowledgements The authors gratefully acknowledge the financial support of this research by the UPB-CEMPDI-POSDRU Doctoral Project 2009, PNII 71-025 and PNII 71-034 research projects. REFERENCES [1] M. Mulder, Basic Principles of Membranes Technology, Kluwer Academic Publishers, 1997. [2] D. F. Stamatialis, B. J. Papenburg, M. Gironés, S. Saiful, S. N.M. Bettahalli, S. Schmitmeier, M. Wessling, J. Membr. Sci., 2008, 308, 1. [3] Lan Wei, Chunhua Cai, Jiaping Lin, Tao Chen, Biomaterials, 2009, 30, 2606. [4] G. Nechifor, S.I. Voicu, A.C. Nechifor, S. Garea, Desalination, 2009, 241, 341. [5] G. Nechifor, S.I. Voicu, A.C. Nechifor, Proceeding of EMS-SS-2010, Bucharest, June, 14-18, 2010.