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. 2022 Dec 12;12(54):35469-35476.
doi: 10.1039/d2ra07405b. eCollection 2022 Dec 6.

Adsorption of cationic surfactant as a probe of the montmorillonite surface reactivity in the alginate hydrogel composites

Affiliations

Adsorption of cationic surfactant as a probe of the montmorillonite surface reactivity in the alginate hydrogel composites

Danielle Silva do Nascimento et al. RSC Adv. .

Abstract

Adsorption of a cationic surfactant allowed to probe the surface reactivity of montmorillonite encapsulated in a composite of alginate hydrogels (A-MMT). Dodecylbenzyldimethylammonium chloride (BAC-12) was the surfactant used for these studies. BAC-12 is part of the widely used surfactant mixture known as benzalkonium chloride. XRD showed that up to three different types of basal spacing (d 001) were present within the composite indicating that as the concentration of adsorbed BAC-12 increases, populations with different adsorption conformational arrangements are present, even unexpanded clay remains. From the SEM-EDS spectra it is observed that the clay is distributed in the whole composite. In addition, the effect of the presence of cationic and anionic biocides on BAC-12 adsorption was studied. Cationic biocides such as tetradecyllbenzyldimethylammonium chlorides (BAC-14) and paraquat (PQ) show a competitive behavior for the clay adsorption sites at BAC-12 low concentration indicating an electrostatic adsorption mechanism. However, the presence of anionic contaminants such as 2,4-D and metsulfuron methyl do not affect surfactant adsorption. In all scenarios is observed an abrupt increase of BAC-12 adsorbed amount reaching values higher than the clay CEC suggesting strong tail-tail interactions. This occurs at concentrations 10 times lower than the CMC of BAC-12 promoted by clay encapsulation in the composite. In these composites the alginate does not affect the surface reactivity of the clay, but the formation of the hydrogel allows it to be easily extracted from aqueous media which makes it an interesting material with a potential use in water remediation.

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Conflict of interest statement

There are no conflicts to declare.

Figures

Fig. 1
Fig. 1. FTIR spectra of (a) AA bead (blue line), (b) MMT (purple line) and (c) A-MMT bead (black line).
Fig. 2
Fig. 2. SEM micrographs of cross-section of lyophilized beads at different magnifications AA bead (a) bar = 200 μm, (c) bar = 100 μm, (e) bar = 20 μm, A-MMT bead, (b) bar = 200 μm (d) bar = 200 μm, and (f) bar = 20 μm.
Fig. 3
Fig. 3. (a) X-ray diffraction patterns of montmorillonite as a component of A-MMT beads with different amounts of BAC-12 adsorbed, (b) scheme showing montmorillonite expansion as a component of A-MMT beads.
Fig. 4
Fig. 4. Adsorption isotherms of BAC-12 on MMT (blue diamonds) and of BAC-12 on A-MMT composites (red squares). Dashed line denotes the CEC value. The inset show regions (i), (ii), and (iii) for adsorption isotherm of BAC-12 on A-MMT composite.
Fig. 5
Fig. 5. Adsorption isotherms of surfactants on A-MMT composites. BAC-12 (red squares), BAC-14 (green diamonds) and BAC-12:BAC-14 (grey triangles).
Fig. 6
Fig. 6. Adsorption isotherms on A-MMT composites. PQ (black circles), BAC-12 (red squares), PQ in presence of BAC-12 (empty circles) and BAC-12 in presence of PQ (empty squares).

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