Abstract:Biochar, a by-product from the production of biofuel and syngas by gasification, was tested as a material for adsorption and fixation of U VI from aqueous solutions. A batch experiment was conducted to study the factors that influence the adsorption and timedependent fixation on biochar at 20 o C, including pH, initial concentration of U VI and contact time. Uranium (U VI ) adsorption was highly dependent on pH but adsorption on biochar was high over a wide range of pH values, from 4.5 to 9.0, and adsorption s… Show more
“…(2) Inner surface complexes were formed by interaction of U( vi ) and biochar, with complex surface coordination and precipitation being the main mechanisms governing the adsorption of U( vi ) over BC and MBC. Thus, the dissolution PO 4 3− and UO 2 2+ contributed to form coordination and oversaturate conditions; 40 (3) the ionic strength of NO 3 − and PO 4 3− influenced the activity coefficient of Pb( ii ) to a higher extent as compared to U( vi ), thereby limiting the transfer of Pb( ii ) on the biochar surface. The optimum anion strengths of NO 3 − and PO 4 3− were 0.01 mol L −1 for Pb( ii ) and 0.04 mol L −1 for U( vi ), respectively.…”
Section: Resultsmentioning
confidence: 99%
“…Additionally, the adsorption rate of Pb( ii ) on BC was higher than that on MBC, thereby revealing that Pb( ii ) was physically adsorbed on the biochar, while U( vi ) was preferably adsorbed via chemisorption processes on MBC owing to the higher number of functional groups of this material. 40 …”
Section: Resultsmentioning
confidence: 99%
“…Additionally, the adsorption rate of Pb(II) on BC was higher than that on MBC, thereby revealing that Pb(II) was physically adsorbed on the biochar, while U(VI) was preferably adsorbed via chemisorption processes on MBC owing to the higher number of functional groups of this material. 40 Adsorption isotherms and thermodynamic characteristics Fig. 6 shows the adsorption isotherms and the thermodynamic characteristics of the adsorption of Pb(II) and U(VI) on BC and MBC under three different temperatures (i.e., 298, 313, and 328 K).…”
“…(2) Inner surface complexes were formed by interaction of U( vi ) and biochar, with complex surface coordination and precipitation being the main mechanisms governing the adsorption of U( vi ) over BC and MBC. Thus, the dissolution PO 4 3− and UO 2 2+ contributed to form coordination and oversaturate conditions; 40 (3) the ionic strength of NO 3 − and PO 4 3− influenced the activity coefficient of Pb( ii ) to a higher extent as compared to U( vi ), thereby limiting the transfer of Pb( ii ) on the biochar surface. The optimum anion strengths of NO 3 − and PO 4 3− were 0.01 mol L −1 for Pb( ii ) and 0.04 mol L −1 for U( vi ), respectively.…”
Section: Resultsmentioning
confidence: 99%
“…Additionally, the adsorption rate of Pb( ii ) on BC was higher than that on MBC, thereby revealing that Pb( ii ) was physically adsorbed on the biochar, while U( vi ) was preferably adsorbed via chemisorption processes on MBC owing to the higher number of functional groups of this material. 40 …”
Section: Resultsmentioning
confidence: 99%
“…Additionally, the adsorption rate of Pb(II) on BC was higher than that on MBC, thereby revealing that Pb(II) was physically adsorbed on the biochar, while U(VI) was preferably adsorbed via chemisorption processes on MBC owing to the higher number of functional groups of this material. 40 Adsorption isotherms and thermodynamic characteristics Fig. 6 shows the adsorption isotherms and the thermodynamic characteristics of the adsorption of Pb(II) and U(VI) on BC and MBC under three different temperatures (i.e., 298, 313, and 328 K).…”
“…Recent studies have reported that biochar exhibits a strong affinity to adsorb U(VI). − However, these studies only present bulk U(VI) metal adsorption data, which do not provide molecular-scale insights into the coordination of aqueous uranyl species adsorbed to the biochar surface, − and, therefore, they cannot be used to calculate intrinsic stability constants of U(VI)–biochar surface complexes. − Since U(VI) has a complex aqueous speciation, especially in the presence of the common calcium (Ca 2+ ), carbonate (CO 3 2– ), and hydroxyl (OH – ) ions in natural waters, it is critical to consider changes in aqueous speciation when performing adsorption modeling. − …”
Biochar has been touted as a promising sorbent for the removal of inorganic contaminants, such as uranium (U), from water. However, the molecularscale mechanisms of aqueous U(VI) species adsorption to biochar remain poorly understood. In this study, two approaches, grounded in equilibrium thermodynamics, were employed to investigate the U(VI) adsorption mechanisms: (1) batch U(VI) adsorption experiments coupled to surface complexation modeling (SCM) and ( 2) isothermal titration calorimetry (ITC), supported by synchrotron-based Xray absorption spectroscopy (XAS) analyses. The biochars tested have considerable proton buffering capacity and most strongly adsorb U(VI) between approximately pH 4 and 6. FT-IR and XPS studies, along with XAS analyses, show that U(VI) adsorption occurs primarily at the proton-active carboxyl (−COOH) and phenolic hydroxyl (−OH) functional groups on the biochar surface. The SCM approach is able to predict U(VI) adsorption behavior across a wide range of pH and at varying initial U(VI) and biochar concentrations, and U adsorption is strongly influenced by aqueous U(VI) speciation. Supporting ITC measurements indicate that the calculated enthalpies of protonation reactions of the studied biochar, as well as the adsorption of U(VI), are consistent with anionic oxygen ligands and are indicative of both innerand outer-sphere complexation. Our results provide new insights into the modes of U(VI) adsorption by biochar and more generally improve our understanding of its potential to remove radionuclides from contaminated waters.
“…Recovery of uranium from seawater has attracted great interest as a hot research topic recently, because of the heavy demand for uranium used in nuclear reactors1234. In seawater, the total amount of uranium is about 4.5 billion tons, one thousand times more than the amount found in mineral ores on land56.…”
Benefiting from strong coordination ability and unique vascular structure, EDTA modified L. cylindrica opens up an alternative way for uranium recovery from seawater. However, limitations, such as poor adsorption capacity and slow adsorption rate due to low graft ratio of EDTA via one-step esterification block its practical application. Here, a strategy for increasing the graft ratio is proposed in order to improve the adsorption performance. The strategy initially involves immobilization of epichlorohydrin (EPI) onto L. cylindrica and then ethylenediamine (EDA) is introduced via facile ring-opening reaction. EPI and EDA serve as a bridge between L. cylindrica and EDTA. The graft ratio is promoted (15.01 to 21.44%) contributing to the smaller steric hindrance of EPI and EDA than EDTA and improvement in adsorption performance. In addition, the adsorbent prepared by the new strategy exhibits excellent adsorption properties in simulated seawater.
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