Abstract:Bitemplate (solubilization) synthesis was used to obtain new mesoporous zirconium-silica nanosorbents that can be successfully used to recover uranium compounds from sulfate and carbonate solutions.Studies concerned with sorption methods for recovery of uranium compounds from aqueous solutions, seawater, and wastewater pay primary attention to synthesis of new, or modifi cation of already known, sorbents in order to raise their sorption capacity for uranium, improve their selectivity, and elucidate the sorptio… Show more
“…When the mass fraction of ZrO 2 in the sorbent samples increased, the pore diameter of the sorbents increased, while the specific surface area accordingly decreased ( Table 1). The range of pH corresponding to the isoelectric state of the sorbent surface was 3.0-3.5 [5].…”
Section: Methodsmentioning
confidence: 99%
“…The solutions were prepared from reagent grade UO 2 (CH 3 COO) 2 [4]. Experiments on the kinetics of sorption of uranium compounds from carbonate and sulfate solutions were performed at initial and experimentally established [5] optimum pH values, namely, pH 4 (starting carbonate solutions) and 7 (sulfate solutions). In the starting car bonate solutions with pH 4, uranium(VI) was in the form of a mixture of UO (91%) and UO 2 OH + (9%) cations; in sulfate solutions with pH 7, as a mixture of UO 2 OH + (13.7%) and UO 2 (OH) 2 (86.3%) [4].…”
The kinetics of sorption of uranium(VI) compounds from sulfate and carbonate solutions using four samples of mesoporous zirconium-silica nanosorbents obtained by bitemplate (solubilization) synthesis was studied. The sorption equilibrium set in time and the kinetic characteristics of sorption were shown to depend on the sorbent (its composition, specific surface area, dispersity, and pore size), the temperature, and the composition and pH of the solution from which uranium compounds are sorbed. The sorption kinetics was described by a first order equation. The limiting stage of the process was found to be the external diffusion of uranium containing particles to the sorbent surface.
“…When the mass fraction of ZrO 2 in the sorbent samples increased, the pore diameter of the sorbents increased, while the specific surface area accordingly decreased ( Table 1). The range of pH corresponding to the isoelectric state of the sorbent surface was 3.0-3.5 [5].…”
Section: Methodsmentioning
confidence: 99%
“…The solutions were prepared from reagent grade UO 2 (CH 3 COO) 2 [4]. Experiments on the kinetics of sorption of uranium compounds from carbonate and sulfate solutions were performed at initial and experimentally established [5] optimum pH values, namely, pH 4 (starting carbonate solutions) and 7 (sulfate solutions). In the starting car bonate solutions with pH 4, uranium(VI) was in the form of a mixture of UO (91%) and UO 2 OH + (9%) cations; in sulfate solutions with pH 7, as a mixture of UO 2 OH + (13.7%) and UO 2 (OH) 2 (86.3%) [4].…”
The kinetics of sorption of uranium(VI) compounds from sulfate and carbonate solutions using four samples of mesoporous zirconium-silica nanosorbents obtained by bitemplate (solubilization) synthesis was studied. The sorption equilibrium set in time and the kinetic characteristics of sorption were shown to depend on the sorbent (its composition, specific surface area, dispersity, and pore size), the temperature, and the composition and pH of the solution from which uranium compounds are sorbed. The sorption kinetics was described by a first order equation. The limiting stage of the process was found to be the external diffusion of uranium containing particles to the sorbent surface.
“…If the composite is based on inert polymer [ 16 ], its sorption capacity is insignificant. Some types of composites are suitable only for anion removal [ 32 , 33 ].…”
Organic-inorganic ion-exchangers were obtained by incorporation of zirconium hydrophosphate into gel-like strongly acidic polymer matrix by means of precipitation from the solution of zirconium oxychloride with phosphoric acid. The approach for purposeful control of a size of the incorporated particles has been developed based on Ostwald-Freundich equation. This equation has been adapted for precipitation in ion exchange materials. Both single nanoparticles (2–20 nm) and their aggregates were found in the polymer. Regulation of salt or acid concentration allows us to decrease size of the aggregates approximately in 10 times. Smaller particles are formed in the resin, which possess lower exchange capacity. Sorption of U(VI) cations from the solution containing also hydrochloride acid was studied. Exchange capacity of the composites is ≈2 times higher in comparison with the pristine resin. The organic-inorganic sorbents show higher sorption rate despite chemical interaction of sorbed ions with functional groups of the inorganic constituent: the models of reaction of pseudo-first or pseudo-second order can be applied. In general, decreasing in size of incorporated particles provides acceleration of ion exchange. The composites can be regenerated completely, this gives a possibility of their multiple use.
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