ABSTRACT
The
efficiency of unmodified (UMGK) and modified (MGK) Garcinia kola pod husk were
investigated as adsorbents for removal of Cr(III), Pb(II) and Cd(II) from
aqueous solution. Parameters of importance such as pH, adsorbent dosage,
initial metal ion concentration, contact time, temperature, and co ions were
conducted in batch process to assess sorption capacities of the adsorbent. The
adsorption process was optimum for the Cr(III) at pH 6, pH 4 for Pb(II) and pH
6 for Cd(II) in which MGK showed higher sorption capacity 6.0639,5.4981 and 6.1206
respectively from the metal ion. The adsorbent dosage was a determining factor
of efficiency in the adsorption pores. In all the three metal ions, increase in
dosage increased adsorbent efficiency for both MGK and UMGK. The effect of
varying the metal ion concentration showed that the MGK had high sorption
capacities as compared to the UMGK while the contact time showed progressive
sorption capacities until equilibrium was attained between 90 mins. The effect
of temperature indicated that the adsorption process will decrease with increase
in temperature for both UMGK and MGK pod husk. The effect of co ions in the
batch process indicated a decrease in sorption capacities of the adsorbent. The
FTIR analysis revealed some functional group that are possible site of
adsorption for the UMGK and the MGK modified spectra introduced an adjusted
thiol group. The SEM images correspond to a good surface coverage of the
adsorbent. The equilibrium data was analyzed using Languimur and Freudlich
isotherm models. The equilibrium indicated the following order of fit for the
isotherms Freudlich> Languimur. The pseudo first order and pseudo second
order model were used to analyze the kinetics of the adsorption process. The
pseudo second order gave the best interpretation of the experimental data.
Generally, the UMGK results obtained showed a good sorption capacity and removal
efficiency but the MGK had a better sorption capacity. The adsorbent showed
affinity for the metal ion in the order Cd (II)> Cr(III)> Pb(II).
NGWAMAGHI, N (2022). The Efficiency Of Unmodified And Modified Garcinia Kola Pod Husk In The Removal OF Cr (III), Pb (II) and Cd (II) From Aqueous Solution.. Mouau.afribary.org: Retrieved Nov 17, 2024, from https://repository.mouau.edu.ng/work/view/the-efficiency-of-unmodified-and-modified-garcinia-kola-pod-husk-in-the-removal-of-cr-iii-pb-ii-and-cd-ii-from-aqueous-solution-7-2
NGWAMAGHI, NGWAMAGHI. "The Efficiency Of Unmodified And Modified Garcinia Kola Pod Husk In The Removal OF Cr (III), Pb (II) and Cd (II) From Aqueous Solution." Mouau.afribary.org. Mouau.afribary.org, 28 Nov. 2022, https://repository.mouau.edu.ng/work/view/the-efficiency-of-unmodified-and-modified-garcinia-kola-pod-husk-in-the-removal-of-cr-iii-pb-ii-and-cd-ii-from-aqueous-solution-7-2. Accessed 17 Nov. 2024.
NGWAMAGHI, NGWAMAGHI. "The Efficiency Of Unmodified And Modified Garcinia Kola Pod Husk In The Removal OF Cr (III), Pb (II) and Cd (II) From Aqueous Solution.". Mouau.afribary.org, Mouau.afribary.org, 28 Nov. 2022. Web. 17 Nov. 2024. < https://repository.mouau.edu.ng/work/view/the-efficiency-of-unmodified-and-modified-garcinia-kola-pod-husk-in-the-removal-of-cr-iii-pb-ii-and-cd-ii-from-aqueous-solution-7-2 >.
NGWAMAGHI, NGWAMAGHI. "The Efficiency Of Unmodified And Modified Garcinia Kola Pod Husk In The Removal OF Cr (III), Pb (II) and Cd (II) From Aqueous Solution." Mouau.afribary.org (2022). Accessed 17 Nov. 2024. https://repository.mouau.edu.ng/work/view/the-efficiency-of-unmodified-and-modified-garcinia-kola-pod-husk-in-the-removal-of-cr-iii-pb-ii-and-cd-ii-from-aqueous-solution-7-2