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Removal of phosphate from waters with Fe(III)-polyhydroxy cations supported onto montmorillonite K10 (MT)
Samara Leite
Instituto de Química da USP
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Create a topicThe commercial K10 montmorillonite was modified with Fe3+ polyhydroxy cations aiming at the enhancement of adsorption affinity towards phosphate anions, which are known to cause eutrophication in lakes and reservoirs. Polyhydroxy cations with OH-: Fe3+ molar ratios of 0.75:1, 1:1 and 2:1 were investigated. The incorporation of the polycations did not alter the main conformational characteristics of the montmorillonite, as verified by surface area measurements, X-ray diffractometry, FTIR, electron microscopy and zeta potential titrations. On the other hand, the materials supporting Fe3+ polyhydroxy cations exhibited a significant enhancement of adsorption capacity (qmax), as determined by Langmuir isotherms, from 1.7 ± 0.1 to 2.8 ± 0.1 µmol g-1, and the adsorption energy from 0.062 to 0.26 L mg-1. The different ratios of OH- to Fe3+ did not affect the adsorption capacities. The adsorption kinetics was best described by the pseudo 2nd order model, with the equilibrium being approached within 120 min of contact time. The adsorption was independent of pH in a pH range between 4.6 and 8.5. The increase in ionic strength increased the adsorption capacities indicating that the formation of inner-sphere complexes prevail over electrostatic interactions in the adsorption mechanism. The materials were tested for removing phosphate from three polluted water samples with phosphate concentrations between 0.0919 and 1.211 mg L-1. The removal was quantitative and the remaining phosphate was below the limit of detection of the analytical method. The presence of 10 mg L-1 humic or fulvic acid did not affect the performance of the materials. Thus, we believe that the modification of clay minerals with Fe3+ polyhydroxy cations is suitable to produce low-cost adsorbents for phosphate.
Bernardo Ribeiro de Moura
Boa Tarde Samara, tudo bem?
Quais foram os interferentes utilizados? Seria interessante menciona-los no procedimento experimental.
Luis Fernando Amorim Batista
Olá. Trabalho muito bom e bem apresentado. Parabéns a todos os envolvidos!
Samara Leite
Muito obrigada Luis Fernando!
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Samara Leite
Boa tarde Bernardo, tudo ótimo e você?
Os interferentes que utilizamos foram os ácidos húmico e fúlvico nas concentrações de 5,0 e 10,0 mg/L; Nitrato 10,0 mg/L; Nitrito 1,0 mg/L e Amônia 10,0 mg/L.
Foram baseados na CONAMA n°357.
As amostras naturais foram do Rio Pinheiros e duas da Represa Billings, ambas em São Paulo.