Adsorption of Pb(II) onto KCC-1 from aqueous solution: Isotherm and kinetic study

In this study, the removal of Pb(II) from aqueous solution using KCC-1 was investigated. BET and TEM revealed the favourable structure of KCC-1 which consists of fibrous morphology and high surface area. Batch adsorption experiment were performed to study the effect of contact time (40 – 160 min), e...

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Main Authors: R., Hasan, Syahida Nasuha, Bukhari, Rohayu, Jusoh, Noor Sabrina, Ahmad Mutamim, Setiabudi, H. D.
Format: Article
Language:English
Published: Elsevier Ltd 2018
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Online Access:http://umpir.ump.edu.my/id/eprint/19320/1/Adsorption%20of%20Pb%28II%29%20onto%20KCC-1%20from%20aqueous%20solution.pdf
http://umpir.ump.edu.my/id/eprint/19320/
https://doi.org/10.1016/j.matpr.2018.07.006
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spelling my.ump.umpir.193202018-10-18T06:19:41Z http://umpir.ump.edu.my/id/eprint/19320/ Adsorption of Pb(II) onto KCC-1 from aqueous solution: Isotherm and kinetic study R., Hasan Syahida Nasuha, Bukhari Rohayu, Jusoh Noor Sabrina, Ahmad Mutamim Setiabudi, H. D. TP Chemical technology In this study, the removal of Pb(II) from aqueous solution using KCC-1 was investigated. BET and TEM revealed the favourable structure of KCC-1 which consists of fibrous morphology and high surface area. Batch adsorption experiment were performed to study the effect of contact time (40 – 160 min), effect of adsorbent dosage (0.5 – 5g/L), effect of initial concentration (50 – 400 mg/L) and effect of pH (2 – 8). The optimum condition was achieved at contact time of 80 min, adsorbent dosage of 4 g/L, initial concentration of 200 mg/L and pH of 6, with maximum removal of Pb(II) was 80.5%. The experimental data were analysed using Langmuir (Type 1, Type 2, Type 3 and Type 4), Freundlich, Temkin, and DubininRedushkevich isotherm models, and were found to follow Langmuir isotherm model with maximum adsorption capacity of 38.76 mg/g and high correlation coefficient (R2= 0.99), implying that the ongoing process is homogeneous in nature. Pseudo-first order, Pseudosecond order, Intra-particle diffusion and Elovich kinetic models were tested with the experimental data, and Pseudo-second order kinetic model was the best for the adsorption of Pb(II) onto KCC-1, indicating that the adsorption process most likely controlled by the chemisorption process and the rate of reaction is directly proportional to the number of active sites on the surface of adsorbent. The results obtained from this study revealed that KCC-1 had high potential for the adsorption of Pb(II) from aqueous solution. Elsevier Ltd 2018 Article PeerReviewed pdf en http://umpir.ump.edu.my/id/eprint/19320/1/Adsorption%20of%20Pb%28II%29%20onto%20KCC-1%20from%20aqueous%20solution.pdf R., Hasan and Syahida Nasuha, Bukhari and Rohayu, Jusoh and Noor Sabrina, Ahmad Mutamim and Setiabudi, H. D. (2018) Adsorption of Pb(II) onto KCC-1 from aqueous solution: Isotherm and kinetic study. Materials Today: Proceedings, 5 (10 Part 2). pp. 21574-21583. ISSN 2214-7853 https://doi.org/10.1016/j.matpr.2018.07.006 doi: 10.1016/j.matpr.2018.07.006
institution Universiti Malaysia Pahang
building UMP Library
collection Institutional Repository
continent Asia
country Malaysia
content_provider Universiti Malaysia Pahang
content_source UMP Institutional Repository
url_provider http://umpir.ump.edu.my/
language English
topic TP Chemical technology
spellingShingle TP Chemical technology
R., Hasan
Syahida Nasuha, Bukhari
Rohayu, Jusoh
Noor Sabrina, Ahmad Mutamim
Setiabudi, H. D.
Adsorption of Pb(II) onto KCC-1 from aqueous solution: Isotherm and kinetic study
description In this study, the removal of Pb(II) from aqueous solution using KCC-1 was investigated. BET and TEM revealed the favourable structure of KCC-1 which consists of fibrous morphology and high surface area. Batch adsorption experiment were performed to study the effect of contact time (40 – 160 min), effect of adsorbent dosage (0.5 – 5g/L), effect of initial concentration (50 – 400 mg/L) and effect of pH (2 – 8). The optimum condition was achieved at contact time of 80 min, adsorbent dosage of 4 g/L, initial concentration of 200 mg/L and pH of 6, with maximum removal of Pb(II) was 80.5%. The experimental data were analysed using Langmuir (Type 1, Type 2, Type 3 and Type 4), Freundlich, Temkin, and DubininRedushkevich isotherm models, and were found to follow Langmuir isotherm model with maximum adsorption capacity of 38.76 mg/g and high correlation coefficient (R2= 0.99), implying that the ongoing process is homogeneous in nature. Pseudo-first order, Pseudosecond order, Intra-particle diffusion and Elovich kinetic models were tested with the experimental data, and Pseudo-second order kinetic model was the best for the adsorption of Pb(II) onto KCC-1, indicating that the adsorption process most likely controlled by the chemisorption process and the rate of reaction is directly proportional to the number of active sites on the surface of adsorbent. The results obtained from this study revealed that KCC-1 had high potential for the adsorption of Pb(II) from aqueous solution.
format Article
author R., Hasan
Syahida Nasuha, Bukhari
Rohayu, Jusoh
Noor Sabrina, Ahmad Mutamim
Setiabudi, H. D.
author_facet R., Hasan
Syahida Nasuha, Bukhari
Rohayu, Jusoh
Noor Sabrina, Ahmad Mutamim
Setiabudi, H. D.
author_sort R., Hasan
title Adsorption of Pb(II) onto KCC-1 from aqueous solution: Isotherm and kinetic study
title_short Adsorption of Pb(II) onto KCC-1 from aqueous solution: Isotherm and kinetic study
title_full Adsorption of Pb(II) onto KCC-1 from aqueous solution: Isotherm and kinetic study
title_fullStr Adsorption of Pb(II) onto KCC-1 from aqueous solution: Isotherm and kinetic study
title_full_unstemmed Adsorption of Pb(II) onto KCC-1 from aqueous solution: Isotherm and kinetic study
title_sort adsorption of pb(ii) onto kcc-1 from aqueous solution: isotherm and kinetic study
publisher Elsevier Ltd
publishDate 2018
url http://umpir.ump.edu.my/id/eprint/19320/1/Adsorption%20of%20Pb%28II%29%20onto%20KCC-1%20from%20aqueous%20solution.pdf
http://umpir.ump.edu.my/id/eprint/19320/
https://doi.org/10.1016/j.matpr.2018.07.006
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