2014
DOI: 10.1515/ract-2014-2101
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Extraction behavior of cesium and some typical fission and non-fission products with a new 1,3-di(1-decyloxy)-2,4-crown-6-calix[4]arene

Abstract: A new macrocyclic supramolecular recognition agent, 1,3-di(1-decyloxy)-2,4-crown-6-calix[4]arene (DecylCalix[4]C6), was synthesized by a multistep reaction through separation and purification by column chromatography packed with silica gel. The extraction behavior of some representative fission and non-fission products such as La(III), Y(III), Cs(I), Rb(I), Pd(II), Mo(VI), Zr(IV), Sr(II), Ba(II), Ru(III), Na(I), and K(I), which were contained in highly active liquid waste (HLW), with DecylCalix[4]C6/1-octanol … Show more

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“…Presence of bulk concentration of Na + in the nuclear waste solution is the major challenge in recovery/removal of Cs + . Literature reports on separation of Cs from nuclear waste solutions include the use of number of techniques viz., precipitation with sodium phosphotungstic acid, ion exchange with silicotitanates, phosphomolybdates and solvent extraction using different macrocyclic ionophores, , protonated form of the hexachlorinated derivative of cobalt bis (dicarbollide) (HCCD). The selective adsorption/extraction of Cs + over Na + using polyphenol enriched biomass based adsorbents or some macrocyclic carrier based solvent extraction methods has also been studied. In order to achieve quantitative separation of Cs from nuclear waste solution, though, several solvents (nitrobenzene, FS-13) and macrocyclic ionophores (bis­(octyloxy) calix[4]­arene-monocrown-6, calix[4]-bis-2,3-naptho-crown-6) , have been synthesized, but high cost of their synthesis and purification necessitates the need for exploring the methods which requires low ligand inventory. Other major disadvantage associated with the conventional separation methods (solvent extraction, ion exchange) is the generation of large amount of secondary waste.…”
Section: Introductionmentioning
confidence: 99%
“…Presence of bulk concentration of Na + in the nuclear waste solution is the major challenge in recovery/removal of Cs + . Literature reports on separation of Cs from nuclear waste solutions include the use of number of techniques viz., precipitation with sodium phosphotungstic acid, ion exchange with silicotitanates, phosphomolybdates and solvent extraction using different macrocyclic ionophores, , protonated form of the hexachlorinated derivative of cobalt bis (dicarbollide) (HCCD). The selective adsorption/extraction of Cs + over Na + using polyphenol enriched biomass based adsorbents or some macrocyclic carrier based solvent extraction methods has also been studied. In order to achieve quantitative separation of Cs from nuclear waste solution, though, several solvents (nitrobenzene, FS-13) and macrocyclic ionophores (bis­(octyloxy) calix[4]­arene-monocrown-6, calix[4]-bis-2,3-naptho-crown-6) , have been synthesized, but high cost of their synthesis and purification necessitates the need for exploring the methods which requires low ligand inventory. Other major disadvantage associated with the conventional separation methods (solvent extraction, ion exchange) is the generation of large amount of secondary waste.…”
Section: Introductionmentioning
confidence: 99%
“…Solvent extraction is an option for 137 Cs removal, but this technique has several shortcomings, e.g. extraction coefficients for cesium are relatively small and process needs huge volumes of solvents and stripping agents [ 1 , 2 ]. Precipitation has been applied in few works, however, the higher pH values typically associated with precipitation methods often result in the precipitation of macro quantities of metals necessitating further separation or decontamination process steps [ 3 ].…”
Section: Introductionmentioning
confidence: 99%