Adsorption of Cd(II) and Pb(II) from aqueous solutions on activated alumina
The ability of activated alumina as synthetic adsorbent was investigated for adsorptive removal of Cd(II) and Pb(II) ions from aqueous solutions. Various physico-chemical parameters such as pH, initial metal ion concentration, and adsorbent dosage level and equilibrium contact time were studied. The...
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Veröffentlicht in: | Journal of colloid and interface science 2009-05, Vol.333 (1), p.14-26 |
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Sprache: | eng |
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Zusammenfassung: | The ability of activated alumina as synthetic adsorbent was investigated for adsorptive removal of Cd(II) and Pb(II) ions from aqueous solutions. Various physico-chemical parameters such as pH, initial metal ion concentration, and adsorbent dosage level and equilibrium contact time were studied. The optimum solution pH for adsorption of Cd(II) and Pb(II) from aqueous solutions was found to be 5. Kinetics data were best described by pseudo-second order model. The effective particle diffusion coefficient of Cd(II) and Pb(II) are of the order of
10
−
10
m
2
/
s
. Values of mass transfer coefficient were estimated as
4.868
×
10
−
6
cm
/
s
and
6.85
×
10
−
6
cm
/
s
for Cd(II) and Pb(II) adsorption respectively. The equilibrium adsorption data for Cd(II) and Pb(II) were better fitted to Langmuir adsorption isotherm model. The thermodynamic studies indicated that the adsorption was spontaneous and exothermic for Cd(II) adsorption and endothermic for Pb(II). The sorption energy calculated from Dubinin–Radushkevich isotherm were 11.85 kJ/mol and 11.8 kJ/mol for the adsorption of Cd(II) and Pb(II) respectively which indicated that both the adsorption processes were chemical in nature. Desorption studies were carried out using dilute mineral acids. Application studies carried out using industrial waste water samples containing Cd(II) and Pb(II) showed the suitability of activated alumina in waste water treatment plant operation.
The uptake of Cd(II) by activated alumina is a function of pH, it increases as the pH increases from 2 to 8. As the solution pH
>
7, the Cd(II) starts precipitation in the solution. This is due to the combination of adsorption as well as precipitation. Therefore the optimum pH is taken as 5. |
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ISSN: | 0021-9797 1095-7103 |
DOI: | 10.1016/j.jcis.2009.01.003 |