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The effects of pH,contact time and natural organic ligands on radionuclide Eu(Ⅲ) adsorption and mechanism on titanate nanotubes(TNTs) are studied by a combination of batch and extended X-ray absorption fine structure(EXAFS) techniques.Macroscopic measurements show that the adsorption is ionic strength dependent at pH < 6.0,but ionic strength independent at pH > 6.0.The presence of humic acid(HA) /fulvic acid(FA) increases Eu(Ⅲ) adsorption on TNTs at low pH,but reduces Eu(Ⅲ) adsorption at high pH.The results of EXAFS analysis indicate that Eu(Ⅲ) adsorption on TNTs is dominated by outer-sphere surface complexation at pH < 6.0,whereas by inner-sphere surface complexation at pH > 6.0.At pH < 6.0,Eu(Ⅲ) consists of ～ 9 O atoms at REu?O ≈ 2.40 in the first coordination sphere,and a decrease in NEu-O with increasing pH indicates the introduction of more asymmetry in the first sphere of adsorbed Eu(Ⅲ).At long contact time or high pH values,the Eu(Ⅲ) consists of ～2 Eu at REu-Eu ≈ 3.60 and ～ 1 Ti at REu-Ti ≈ 4.40 ,indicating the formation of inner-sphere surface complexation,surface precipitation or surface polymers.Surface adsorbed HA/FA on TNTs modifies the species of adsorbed Eu(Ⅲ) as well as the local atomic structures of adsorbed Eu(Ⅲ) on HA/FA-TNT hybrids.Adsorbed Eu(Ⅲ) on HA/FA-TNT hybrids forms both ligand-bridging ternary surface complexes(Eu-HA/FA-TNTs) as well as surface complexes in which Eu(Ⅲ) remains directly bound to TNT surface hydroxyl groups(i.e.,binary Eu-TNTs or Eu-bridging ternary surface complexes(HA/FA-Eu-TNTs)).The findings in this work are important to describe Eu(Ⅲ) interaction with nanomaterials at molecular level and will help to improve the understanding of Eu(Ⅲ) physicochemical behavior in the natural environment.
The effects of pH, contact time and natural organic ligands on radionuclide Eu (III) adsorption and mechanism on titanate nanotubes (TNTs) were studied by a combination of batch and extended X-ray absorption fine structure (EXAFS) techniques. Microscopic measurements show that The presence of humic acid (HA) / fulvic acid (FA) increases Eu (Ⅲ) adsorption on TNTs at low pH, but only reduces Eu (Ⅲ) III) adsorption at high pH.The results of EXAFS analysis indicate that the Eu (III) adsorption on TNTs is dominated by outer-sphere surface complexation at pH <6.0, while by inner-sphere surface complexation at pH> 6.0. O ≈ 2.40 the in the first coordination sphere, and a decrease in NEu-O with increasing pH indicates the introduction of more asymmetry in the first sphere of adsorbed Eu (III) .At long contact time or high pH values, the Eu (III) consists of ~ 2 Eu at REu-Eu ≈ 3.60 and ~ 1 Ti at REu-Ti ≈ 4.40 , indicating the formation of inner-sphere surface complexation, surface precipitation or surface polymers. Surface adsorbed HA / FA on TNTs modifies the species of adsorbed Eu (III) As well as the local atomic structures of adsorbed Eu (III) on HA / FA-TNT hybrids. Adsorbed Eu (III) on HA / FA- TNT hybrids forms both ligand- bridging ternary surface complexes (Eu- HA / FA- TNTs) as well as surface complexes in which Eu (III) remains directly bound to TNT surface hydroxyl groups (ie, binary Eu-TNTs or Eu-bridging ternary surface complexes (HA / FA-Eu- TNTs)). The findings in this work are important to describe Eu (Ⅲ) interaction with nanomaterials at molecular level and will help to improve the understanding of Eu (Ⅲ) physicochemical behavior in the natural environment.