64 RADIOCHEMISTRY, STABLE ISOTOPES, NUCLEAR ANALYTICAL METHODS, GENERAL CHEMISTRY Fig.2. TLC chromatograms of 99m Tc/ 188 ReEDTA-mannitol complex developed in acetone (a) and in water (b) (mobile phase; the strips, Silufol, Kavalier, were scanned with a Raytest Rita radioanalyzer). to that of 99m Tc(NS 3 )(CN-GGY) has been shown by HPLC (Fig.4) and by determination of their partition coefficients, D. The logD values (n-octanol/PBS, pH 7.4) of the 99m Tc(NS 3 (COOH) 3 ) (CN-GGY) and 99m Tc(NS 3 )(CN-GGY) complexes are equal to -2.6±0.3 and -1.5±0.2, respectively. Fig.3. HPLC chromatograms of the complexes: a – Re(NS 3 ) (CN-R(COOMe) 3 ), R T =9.17, UV-VIS detection at 220 nm; b – 99m Tc(NS 3 )(CN-R(COOMe) 3 ), R T =9.41, gamma detection; c – 188 Re(NS 3 )(CN-R(COOMe) 3 ), R T =9.55, gamma detection; column – PRP 1, Hamilton, 250x4.1. Fig.4. HPLC chromatograms of the complexes: a – Re(NS 3 (COOH) 3 )(CN-GGY), R T =10.60, UV-VIS detection at 220 nm; b – 99m Tc(NS 3 )(CN-GGY), R T =11.70, gamma detection; c – 99m Tc(NS 3 (COOH) 3 ) (CN-GGY), R T =10.39, gamma detection; column – Jupiter 4u Proteo 90A, 250x4.6.
RADIOCHEMISTRY, STABLE ISOTOPES, NUCLEAR ANALYTICAL METHODS, GENERAL CHEMISTRY 65 The conjugates of the 99m Tc complexes with peptides exhibit a high stability in vitro (>90% in PBS after 24 h). As a next step, the new peptide-bearing “4+1” compounds will be evaluated in animal experiments. The experiments have been done during the research stay of Ewa Gniazdowska at the Institute of Bioinorganic and Radiopharmaceutical Chemistry, Forschungszentrum Rossendorf e.V. in the frame of the project “Chemical Studies for Design and Production of New Radiopharmaceuticals” (No. MTKD-CT-2004-509224 (POL-RAD-PHARM)), supported by the European Community within the 6th Frame Programme Marie Curie: Host Fellowships for Transfer of Knowledge (ToK). References [1]. Pietzsch H.-J., Spies H., Hoffman S.: Inorg. Chim. Acta, 165, 163-166 (1989). [2]. Pietzsch H.-J., Gupta A., Syhre R., Leibnitz P., Spies H.: Bioconjugate Chem., 12, 538-544 (2001). [3]. Schiller E., Seifert S., Tisato F., Refosco F., Kraus W., Spies H., Pietzsch H.-J.: Bioconjugate Chem., 16, 634-643 (<strong>2005</strong>). [4]. Gupta A., Seifert S., Syhre R., Scheunemann M., Brust P., Johannsen B.: Radiochim. Acta, 89, 43-49 (2001). [5]. Newkome G.R., Lin X., Young J.K.: Synlett, 1, 53-54 (1992). [6]. Seifert S., Künstler J.-U., Schiller E., Pietzsch H.-J., Pawelke B., Bergmann R., Spies H.: Bioconjugate Chem., 15, 856-863 (2004). TRANSITION METAL COMPLEXES WITH ALGINATE BIOSORBENT Leon Fuks, Dorota Filipiuk 1/ , Marek Majdan 2/ 1/ Białystok Technical University, Poland 2/ The Maria Curie-Skłodowska University, Lublin, Poland Alginate is one of the most extensively investigated biopolymers for metal ion removal from dilute aqueous solution [1-3]. It is a viscous gum present in the cell walls of brown algae. This linear copolymer contains homopolymeric blocks of covalently (1-4)-linked β-D-mannuronate (M) and its C-5 epimer α-L-guluronate (G) residues [4-7]. The length of each block and the total content of G and M residues depend on the source of the alginate. Modern alginate biosorbents are usually prepared as calcium alginate-based ion-exchange resin (abbreviated as CA or CABIER) [1,8]. They exhibit extremely high sorption capacity and favorable kinetics for binding of heavy metal ions, and have been proven to be stable under various chemical and physical conditions. Adsorption capacity of the CA in relation to heavy metals can be as high as 3 mmol(M 2+ )/g(CA) [9,10], which is by one or two orders of magnitude more than that of activated carbons (being 0.05 to 0.15 mmol-metal per 1 g of carbon). Because the CA cannot be broken down by bile or saliva and cannot be absorbed by the body, it is excreted from the body together Fig.1. Vibrational spectra of the selected transition metal(II)-alginate complexes. with the heavy metals and radioactive substances. Several attempts have been made to apply the CA as the human body remediation agent when the heavy or radioactive metal contamination occurred. In general, process of biosorption of heavy metals can be explained by considering different kinds Table 1. Assignments of main IR absorption bands for calcium alginate and selected metal complexes. * Previously published data [16].
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