Competitive sequestration of Ni(II) and Eu(III) on montmorillonite: role of molar Ni:Eu ratios and coexisting oxalate

• Published in: Environmental science and pollution research international 2018-11, Vol.25 (32), p.32617-32630
• Main Authors: Xu, Lin, Liu, Wei, Cai, Yawen, Wu, Chunfang, Chen, Lei, Yang, Shitong, Wang, Xiangke, Ji, Guoxun, Wang, Shuao
• Format: Article
• Language: English
• Subjects: Adsorption; Aquatic environment; Aquatic Pollution; Atmospheric Protection/Air Quality Control/Air Pollution; Bentonite - chemistry; Binding; Earth and Environmental Science; Ecotoxicology; Environment; Environmental Chemistry; Environmental Health; Environmental science; Europium - chemistry; Immobilization; Ions - chemistry; Montmorillonite; Nickel; Nickel - chemistry; Oxalic acid; Oxalic Acid - chemistry; pH effects; Phase transitions; Research Article; Sorption; Speciation; Trends; Waste Water Technology; Water Management; Water Pollution Control; X-ray diffraction
• ISSN: 0944-1344; 1614-7499
• DOI: 10.1007/s11356-018-3252-z

The competitive binding trends of Ni(II) and Eu(III) on montmorillonite in the absence/presence of Na-oxalate are explored by using batch sorption/desorption technique, speciation modeling, and X-ray diffraction (XRD) analysis. With a series of molar Ni:Eu ratios (i.e., 1:1, 5:1, 10:1, 1:5, and 1:10), the coexisting Ni(II) did not affect the sequestration behaviors and immobilization mechanisms of Eu(III). In contrast, the presence of Eu(III) obviously suppressed the sorption percentages of Ni(II) in the acidic pH range. Even though no obvious influence of Eu(III) on the macroscopic binding trends of Ni(II) was observed under alkaline conditions, the fraction of Ni(II) adsorbed by the inner-sphere complexation mechanism decreased and that of Ni(II) precipitation increased with rising molar Ni:Eu ratio. The coexisting Na-oxalate did not influence Eu(III) sorption, while inhibited the sorption of Ni(II). The XRD analysis indicated the potential formation of two Eu-oxalate precipitate phases (i.e., Eu 2 (C 2 O 4 ) 3 · x H 2 O(s)-1 and Eu 2 (C 2 O 4 ) 3 · x H 2 O(s)-2) at different pH values (4.0 and 6.5) and Na-oxalate concentrations (ranging from 0.5 to 5.0 mM). Interestingly, the Eu 2 (C 2 O 4 ) 3 · x H 2 O(s)-2 phase would be transformed into the Eu 2 (C 2 O 4 ) 3 · x H 2 O(s)-1 solid with the increase of Na-oxalate concentration. The research findings could provide essential data for evaluating the fate of coexistent Eu(III) and Ni(II) in the complicated aquatic environment.