Toxic Waste Removal from Aqueous Solutions by Polyaniline: A Radiotracer Study

A radiotracer technique was used to study the removal of Hg(II) ions from aqueous solutions by polyaniline. It was shown that an increase in the concentration of the adsorptive (10 −7 –10 −2 M), temperature (303–333 K) and pH (ca. 3–10) enhanced the removal of these ions. The first-order uptake of H...

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Main Authors: R.K. Gupta, Som Shankar
Format: Article
Language:English
Published: Hindawi - SAGE Publishing 2004-07-01
Series:Adsorption Science & Technology
Online Access:https://doi.org/10.1260/0263617042879483
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spelling doaj-7fd985eb4afc4792bafeee3488e400d82021-04-02T12:57:19ZengHindawi - SAGE PublishingAdsorption Science & Technology0263-61742048-40382004-07-012210.1260/0263617042879483Toxic Waste Removal from Aqueous Solutions by Polyaniline: A Radiotracer StudyR.K. Gupta0Som Shankar1 Molecular Electronics Laboratory, Department of Chemistry, Faculty of Science, Banaras Hindu University, Varanasi-221005, India Nuclear and Radiochemistry Laboratory, Department of Chemistry, Faculty of Science, Banaras Hindu University, Varanasi-221005, IndiaA radiotracer technique was used to study the removal of Hg(II) ions from aqueous solutions by polyaniline. It was shown that an increase in the concentration of the adsorptive (10 −7 –10 −2 M), temperature (303–333 K) and pH (ca. 3–10) enhanced the removal of these ions. The first-order uptake of Hg(II) ions conformed to the Freundlich and Dubinin and Radushkevich (D–R) isotherms over the entire adsorptive concentration range (10 −7 –10 −2 M), whereas the Langmuir isotherm was followed only at moderate concentrations. Thermal data showed that this process was endothermic in nature. The radiation stability of polyaniline was also investigated by exposing it to an 11.1 GBq (Ra/Be) source associated with a γ-dose of 1.72 Gy/h. Irradiation had practically no significant effect on the adsorption capacity of polyaniline. Desorption experiments showed that the process of Hg(II) ion adsorption by polyaniline was almost irreversible and chemisorptive in nature.https://doi.org/10.1260/0263617042879483
collection DOAJ
language English
format Article
sources DOAJ
author R.K. Gupta
Som Shankar
spellingShingle R.K. Gupta
Som Shankar
Toxic Waste Removal from Aqueous Solutions by Polyaniline: A Radiotracer Study
Adsorption Science & Technology
author_facet R.K. Gupta
Som Shankar
author_sort R.K. Gupta
title Toxic Waste Removal from Aqueous Solutions by Polyaniline: A Radiotracer Study
title_short Toxic Waste Removal from Aqueous Solutions by Polyaniline: A Radiotracer Study
title_full Toxic Waste Removal from Aqueous Solutions by Polyaniline: A Radiotracer Study
title_fullStr Toxic Waste Removal from Aqueous Solutions by Polyaniline: A Radiotracer Study
title_full_unstemmed Toxic Waste Removal from Aqueous Solutions by Polyaniline: A Radiotracer Study
title_sort toxic waste removal from aqueous solutions by polyaniline: a radiotracer study
publisher Hindawi - SAGE Publishing
series Adsorption Science & Technology
issn 0263-6174
2048-4038
publishDate 2004-07-01
description A radiotracer technique was used to study the removal of Hg(II) ions from aqueous solutions by polyaniline. It was shown that an increase in the concentration of the adsorptive (10 −7 –10 −2 M), temperature (303–333 K) and pH (ca. 3–10) enhanced the removal of these ions. The first-order uptake of Hg(II) ions conformed to the Freundlich and Dubinin and Radushkevich (D–R) isotherms over the entire adsorptive concentration range (10 −7 –10 −2 M), whereas the Langmuir isotherm was followed only at moderate concentrations. Thermal data showed that this process was endothermic in nature. The radiation stability of polyaniline was also investigated by exposing it to an 11.1 GBq (Ra/Be) source associated with a γ-dose of 1.72 Gy/h. Irradiation had practically no significant effect on the adsorption capacity of polyaniline. Desorption experiments showed that the process of Hg(II) ion adsorption by polyaniline was almost irreversible and chemisorptive in nature.
url https://doi.org/10.1260/0263617042879483
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