TY - JOUR
T1 - Tris(2,2′-bipyridine)ruthenium(II)-clays as adsorbents for phenol and chlorinated phenols from aqueous solution
AU - Okada, Tomohiko
AU - Morita, Takao
AU - Ogawa, Makoto
PY - 2005/2
Y1 - 2005/2
N2 - The adsorptive properties of tris(2,2′-bipyridine)ruthenium (II)-clay intercalation compounds, which were synthesized through cation exchange reactions from synthetic saponite (Sumecton SA), synthetic fluoro-tetrasilicic mica and montmorillonite (Kunipia F) for phenols were investigated. The adsorption isotherms of phenols for the tris(2,2′-bipyridine)ruthenium(II)-clays from aqueous solutions followed Langmuir type, indicating strong adsorbate-adsorbent interactions. The basal spacings of the tris(2,2′-bipyridine)ruthenium(II)-clays did not change through the adsorption of phenols. This means that the adsorbed phenols existed in the interlayer nanopore created by the tris(2,2′-bipyridine)ruthenium(II) in the interlayer space of the tris(2,2′-bipyridine)ruthenium(II)-clays. The adsorbed amounts of phenols varied depending upon the nature of clays. One of the factors responsible for the variation in the adsorbed amounts is the layer charge density of smectites. Relatively low-layer charge density of saponite led to relatively large pore volume in the interlayer space. The adsorbed amounts of 2,4-dichlorophenol for the tris(2,2′-bipyridine)ruthenium(II)-saponite and the tris(2,2′-bipyridine)ruthenium(II)-montmorillonite were the largest among three phenols. It is thought that the interactions between tris(2,2′-bipyridine)ruthenium(II) cation and phenols played an important role in the adsorption of these phenols.
AB - The adsorptive properties of tris(2,2′-bipyridine)ruthenium (II)-clay intercalation compounds, which were synthesized through cation exchange reactions from synthetic saponite (Sumecton SA), synthetic fluoro-tetrasilicic mica and montmorillonite (Kunipia F) for phenols were investigated. The adsorption isotherms of phenols for the tris(2,2′-bipyridine)ruthenium(II)-clays from aqueous solutions followed Langmuir type, indicating strong adsorbate-adsorbent interactions. The basal spacings of the tris(2,2′-bipyridine)ruthenium(II)-clays did not change through the adsorption of phenols. This means that the adsorbed phenols existed in the interlayer nanopore created by the tris(2,2′-bipyridine)ruthenium(II) in the interlayer space of the tris(2,2′-bipyridine)ruthenium(II)-clays. The adsorbed amounts of phenols varied depending upon the nature of clays. One of the factors responsible for the variation in the adsorbed amounts is the layer charge density of smectites. Relatively low-layer charge density of saponite led to relatively large pore volume in the interlayer space. The adsorbed amounts of 2,4-dichlorophenol for the tris(2,2′-bipyridine)ruthenium(II)-saponite and the tris(2,2′-bipyridine)ruthenium(II)-montmorillonite were the largest among three phenols. It is thought that the interactions between tris(2,2′-bipyridine)ruthenium(II) cation and phenols played an important role in the adsorption of these phenols.
KW - Adsorption
KW - Chlorinated phenols
KW - Montmorillonite
KW - Organoclays
KW - Phenol
KW - Synthetic fluoro-tetrasilicic mica
KW - Synthetic saponite
KW - Tris(2,2′-bipyridine)ruthenium(II)
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U2 - 10.1016/j.clay.2004.09.004
DO - 10.1016/j.clay.2004.09.004
M3 - Article
AN - SCOPUS:12144283907
SN - 0169-1317
VL - 29
SP - 45
EP - 53
JO - Applied Clay Science
JF - Applied Clay Science
IS - 1
ER -