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Photonic crystals in biology

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Poster Session, Tuesday, June 15<br />

Theme A1 - B702<br />

Equilibrium and k<strong>in</strong>etic study on boron uptake by Monodisperse-Nanoporous Poly(GMA-co-EDM)<br />

Particles Conta<strong>in</strong><strong>in</strong>g N-Methyl-D-Glucam<strong>in</strong>e<br />

1 Saba Samatya, 2 Nalan Kabay, 1 Ali Tuncel*<br />

1 Hacettepe University, Chemical Eng<strong>in</strong>eer<strong>in</strong>g Department, Ankara, Turkey<br />

2 Ege University, Chemical Eng<strong>in</strong>eer<strong>in</strong>g Department, Izmir, Turkey<br />

Abstract— A relatively new method of polymerization, ‘modified seeded polymerization’ has been used for the synthesis of<br />

monodisperse nanoporous poly(glycidyl methacrylate-ethylene dimethacrylate) particles are proposed for boron removal. The<br />

covalent attachment of boron selective ligand N-methyl-D-glucam<strong>in</strong>e onto poly(GMA-co-EDM) particles were followed for<br />

the synthesis of sorbents.<br />

Boron is a naturally occurr<strong>in</strong>g element that is widely<br />

distributed at low concentrations <strong>in</strong> the environment. Boron is<br />

rare, be<strong>in</strong>g found <strong>in</strong> dry regions of the world such as Turkey,<br />

which has the largest boron reserves <strong>in</strong> the world. Although<br />

boron is essential for plant life and small amounts of boron are<br />

even claimed to be beneficial for human, high levels may be<br />

toxic [1]. There are several physicochemical treatment<br />

processes typically used to remove boron from water and<br />

wastewater. These are adsorption with <strong>in</strong>organic adsorbents,<br />

ion exchange, solvent extraction, membran processes and<br />

ultrafiltration [2]. Basically, the only method utilized to<br />

separate boron from liquid media has been the use of ion<br />

exchange res<strong>in</strong>s. The chemistry of boron <strong>in</strong>dicates that<br />

molecules with vic-diols are capable of form<strong>in</strong>g neutral boron<br />

esters or tetra alkyl borate type of compounds, even <strong>in</strong><br />

aqueous solutions. Design of new boron-specific sorbents is<br />

based mostly on this key pr<strong>in</strong>ciple [3].<br />

Our <strong>in</strong>terest has been much focused on the development of<br />

monodisperse-porous Poly(GMA-co-EDM) Particles.<br />

Monodisperse polymer particles, of which size is <strong>in</strong> the order<br />

of micrometers, have been of great <strong>in</strong>terests <strong>in</strong> many<br />

applications, <strong>in</strong>clud<strong>in</strong>g standard calibrations, biomedical<br />

exam<strong>in</strong>ations, chromatographic fillers, spacers, <strong>in</strong>k additives,<br />

and catalytic substrates [4]. Uniform, macroporous particles<br />

have usually been obta<strong>in</strong>ed with seeded polymerization<br />

techniques. In fact, many recent advances <strong>in</strong> the synthesis of<br />

monodisperse polymer particles are strongly based on the<br />

seeded polymerization technique [5].<br />

A representative SEM photo (Figure 1) shows the surface<br />

morphology of poly(GMA-co-EDM) particles. Based on SEM<br />

evaluation, the average size of poly (GMA-co-EDM) particles<br />

were 9.0 μm. The SEM photo <strong>in</strong>dicates that poly(GMA-co-<br />

EDM) particles have a highly porous-surface predom<strong>in</strong>antly<br />

<strong>in</strong>clud<strong>in</strong>g macropores. NMDG was covalently attached to the<br />

particles (Figure 2).<br />

Figure 1. A representative SEM photo of poly(GMA-co-EDM) particles<br />

Figure 2: Schematic illustration of the functionalization of poly(GMA-co-<br />

EDM) with NMDG<br />

Figure 3. Equilibrium isotherm on uptake of boron from aqueous solution<br />

As seen <strong>in</strong> Fig.3, the maximum uptake value (Q o ) of 12 mg<br />

boron per g-dry res<strong>in</strong><br />

Figure 4. Removal of boron by versus time by poly(GMA-co-EDM)NMDG<br />

res<strong>in</strong><br />

Figures 4 <strong>in</strong>dicates uptake of versus time. The removal of<br />

boron <strong>in</strong>creased with time and reached the equilibrium <strong>in</strong> 10<br />

m<strong>in</strong> with a 98.8 % boron removal. The sorbent has been<br />

shown to be efficient <strong>in</strong> chelation with boric acid and can be<br />

used for removal of boric acid at ppm levels.<br />

BOREN (Project Number: 2008-G-0192). We are grateful to<br />

TUBITAK for post doc fellowship for S.Samatya. We also<br />

thank to Prof. A.Ozdural, Hacettepe University for allow<strong>in</strong>g to<br />

use ICP equipment for boron analysis.<br />

*Correspond<strong>in</strong>g author: Ali Tuncel atuncel@hacettepe.edu.tr<br />

[1] J.Q. Jiang, Y. Xu, J. Simon, K. Quill and K. Shettle, Water Sci. Technol.<br />

53 73 (2006).<br />

[2] N. Kabay, I. Yilmaz, S. Yamac, S. Samatya, M. Yuksel, U. Yuksel, M.<br />

Arda, M. Saglam, T. Iwanaga and K. Hirowatari, React. Funct. Polym., 60<br />

163(2004).<br />

[3] B. F.Senkal, N. Bicak, Polymer supported im<strong>in</strong>odipropylene glycol<br />

functions for removal of boron, React. Funct. Polym, 55: 1, 27-33 (2003).<br />

[4] S.I. Kim, T. Yamamoto, A. Endo, T. Ohmori, M. Nakaiwa, J. Ind. Eng.<br />

Chem. 127 69(2006).<br />

[5] Unsal E, Çamlı ST, Tuncel M, Şenel S, Tuncel A, React Func Polym, 61<br />

(2004) 353.<br />

6th Nanoscience and Nanotechnology Conference, zmir, 2010 325

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