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Adsorption of copper, zinc, and cadmium on clay fraction of two acid soils: Surface complexation modeling

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dc.contributor.author Spathariotis, E en
dc.contributor.author Kallianou, C en
dc.date.accessioned 2014-06-06T06:44:34Z
dc.date.available 2014-06-06T06:44:34Z
dc.date.issued 2001 en
dc.identifier.issn 00103624 en
dc.identifier.uri http://dx.doi.org/10.1081/CSS-120001115 en
dc.identifier.uri http://62.217.125.90/xmlui/handle/123456789/1955
dc.subject.other acid en
dc.subject.other cadmium en
dc.subject.other copper en
dc.subject.other zinc en
dc.subject.other acid soil en
dc.subject.other adsorption en
dc.subject.other clay en
dc.subject.other heavy metal en
dc.subject.other soil chemistry en
dc.subject.other adsorption en
dc.subject.other article en
dc.subject.other clay en
dc.subject.other complex formation en
dc.subject.other computer program en
dc.subject.other concentration (parameters) en
dc.subject.other ionic strength en
dc.subject.other model en
dc.subject.other pH en
dc.subject.other potentiometric titration en
dc.subject.other regression analysis en
dc.subject.other spectroscopy en
dc.title Adsorption of copper, zinc, and cadmium on clay fraction of two acid soils: Surface complexation modeling en
heal.type journalArticle en
heal.identifier.primary 10.1081/CSS-120001115 en
heal.publicationDate 2001 en
heal.abstract The adsorption of copper (Cu), zinc (Zn), and cadmium (Cd) as a function of pH was studied on the clay fraction of two acid soils (Typic Rhodoxeralf and Aquic palexeralf), in two ionic strengths and two different metal concentrations. Specific surface area was determined by BET-N2 and EGME. The charge development on the clay surface was studied in the pH range ∼3,5 to ∼10,0 by potentiometric titration under continuous flow of argon. The least square optimization program FITEQL32, for Constant Capacitance (CCM) and the Double-Layer Model (DLM) was used to fit the titration and adsorption data, In both models surface site density was fixed at 2.31 sites/nm2, while for CCM capacitance density was set at C = 1.06. The Palexeralf soil exhibited higher specific surface area by both methods and is adsorbing all three metals in lower pH values than the Rhodoxeralf. Both clays exhibited PZSE values higher than montorilonite and kaolinite but in close approximation to the second, possibly due to higher content of iron oxides. The adsorption order for both clays was Cu > Zn > Cd in any case, thus more Cu is adsorbed at a certain pH than Zn and even more than Cd, while the increase of metal concentration or ionic strength shifts the adsorption curve towards higher pH values. CCM is describing the titration data satisfactorily by using EGME, while by using BET, alteration of Ns and C values is needed. Adsorption data are described by CCM by emphasizing the formation of monodentate surface complex. Bidentate complex in most of the cases was of no importance in describing the data despite the evident of its presence in recent spectroscopic studies for Cu and Cd ongoethtite. When BET surface area was applied better fit was achieved and bidentate complex became important in some cases for the optimization procedure. Double-layer model is exhibiting worse fit in any case. en
heal.journalName Communications in Soil Science and Plant Analysis en
dc.identifier.issue 19-20 en
dc.identifier.volume 32 en
dc.identifier.doi 10.1081/CSS-120001115 en
dc.identifier.spage 3185 en
dc.identifier.epage 3205 en


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