Water-based synthesis of TiO2/CeO2 composites supported on plasma-treated montmorillonite for parathion methyl degradation
Graphical abstract
Introduction
The principal use of cerium dioxide is for glass polishing, nevertheless, its distinctive properties - especially reversible conversion to a nonstoichiometric oxide, open up the scope to countless other applications such as catalytic oxidation of automotive exhaust (Kaspar et al., 1999), petroleum cracking (Dejhosseini et al., 2013), organic chemicals synthesis (Tamura and Tomishige, 2015), energy storage (Arul et al., 2015), high-temperature and corrosion coatings (Ardelean et al., 2008, Sreedhar et al., 2012), or sensors (Izu et al., 2002, Zhai et al., 2009). The list of applications is being constantly updated by strenuous research efforts in the field of fuels cells (Yu and Xi, 2012), photocatalytic degradation of organic pollutants (Arul et al., 2015, Yang et al., 2014), thermochemical water splitting (Al-Shankiti et al., 2013), or even in nanobiology and regenerative medicine (Das et al., 2013). In several recent studies, JanoÅ” et al. demonstrated CeO2 can also be exploited in environmental protection as cheap, non-toxic, earth-abundant, and efficient reactive adsorbent for remediation of highly toxic organophosphorus compounds, i.e. civil warfare agents (CWA) and pesticides (Janos et al., 2016, Janos et al., 2014, Janos et al., 2015). For example, parathion methyl is a widely used effective organophosphorus pesticide and insecticide that, however, possess extremely high toxicity. Therefore, numerous studies have been devoted to its toxicology (Abdollahi and Karami-Mohajeri, 2012), analytical detection (Gong et al., 2012, Yang et al., 2011), mapping of its fate (Sapbamrer and Hongsibsong, 2014, Villaverde et al., 2008) and chiefly to its removal from the environment; several eco-friendly approaches were proposed, e.g. using bacteria biodegradation (Pino and Penuela, 2011), Fenton's reaction (Diagne et al., 2007), or photocatalytic oxidation (Sud and Kaur, 2012). The surface reactive adsorption should be included among these methods since it is safe, rapid, and does not require energy supply. Furthermore, relatively cheap and available materials such as nanoscale ceria, whose unusual activity towards organophosphates is attributed to the ability of lattice oxygen to participate in the reaction (Mitchell et al., 2003), can be used.
The new attractive properties of single metal oxides can be unfolded by coupling them with other metal oxides, organic frameworks, or various substrates in mixed solid solutions and composites. Improvement of the ceria redox properties, oxygen mobility, modification of surface acidity and surface area is often achieved in combination with ZrO2 (Neto and Schmal, 2013, Si et al., 2013), TiO2 (Li et al., 2012a, Li et al., 2012b), CuO (Wang et al., 2013), MnOx (Li et al., 2012a, Li et al., 2012b), NiO (Si et al., 2013) and other oxides. Furthermore, ceria is liable to form interesting structures with extraordinary properties using metal organic frameworks (Kim et al., 2013, Maiti et al., 2014), 0D, 1D and 2D nanomaterials such as graphene (Rajendran et al., 2014, Wang et al., 2011), C3N4 (Wang et al., 2015), or MoS2 (Gong et al., 2016), and layered aluminosilicates. Clay minerals are regarded as green materials as they are readily available in nature, and can be used with minimum processing. They are composed of ultra-thin crystalline layers superimposed on interlayer of hydrated ions (Kloprogge et al., 1999). Thanks to their structure, clay minerals possess unique physicochemical properties such as large surface areas, swelling, ion exchange, and active broken-edge MO bonds. The main disadvantage of the clay minerals is, however, lack of permanent porosity. They swell upon hydration, but after severe dehydration (e.g. heating) the layers collapse and their interlayer surface become inaccessible for chemical processes (Pavlidou and Papaspyrides, 2008). The introduction of stable pillars can solve this problem and leads to convenient improvement of the properties of formed composites that are superior to those of their individual components (Kloprogge et al., 2005). Ramaswamy et al. (2008) and Cecilia et al. (2015) investigated Montmorillonite (MT) as a high-surface-area support for CuO-CeO2-based catalysts. CeO2/TiO2-pillared clay composite prepared by impregnation method was also used for elemental mercury removal from flue gas (He et al., 2016). In this case, TiO2-pillared clay served as a support for CeO2 catalyst but their synergistic effect is not discussed in detail. Lin et al. prepared the Laponite pillared by the CeO2/TiO2 by microwave intercalation and tested it for photocatalytic decoloration of methylene blue (Lin et al., 2010). The coupling of TiO2 with CeO2 improved the utilization efficiency of UV light to produce more trap centers of electron and hole, and inhibit the electron-hole recombination, while Laponite increased the effective surface area for MB adsorption. However, the synthesis utilize relatively expensive organometallic Ti compounds and ethanol as a solvent. In the recent publication, MT supported with various single metal oxide nanoparticles were prepared by ion exchange, precipitation, and successive calcination and subsequently tested towards CWA sulfur mustard (Kumar et al., 2015).
The modification of clay minerals by various species (neutral polar molecules, cations, complex cations) is based mainly on their surface anchoring or intercalation predominantly via thermal and chemical treatment. Only a very few studies are focused on plasma modification of clay minerals, see reference (Capkova et al., 2016). Our group successfully modified MT in fluidized bed reactor with Argon gas feed at low pressure about 560Ā Pa by RF plasma in wide range of power from 10Ā W up to 100Ā W. The modification to a state typical for long time heat annealing, hours at 450Ā Ā°C, was reached by the plasma treatments in seconds (Capkova et al., 2016).
Recently, our group have demonstrated that homogeneous precipitation with urea is a convenient method for preparation of TiO2/CeO2 composites used for degradation of toxic organophosphates (OP) DMMP and Parathion methyl (PM) (Henych et al., 2016), while plasma treatment of the MT is a suitable and very fast method for its dehydration and dehydroxylation (Capkova et al., 2016). Dehydroxylation result in a creation of active sites in the clay mineral structure that can improve its catalytic activity and can serve as bonding sites for guest species in a design of functional nanostructures. The purpose of this work was to demonstrate use of cheap, earth-abundant materials and facile methods to construct ternary composites based on TiO2/CeO2-pillared MT and study their synergistic effect on the degradation of toxic organophosphorus chemicals. We employed very easy low-temperature water-based co-precipitation method for preparation of ternary composites that possess significantly higher degradation activity towards OP than pure ceria and titania and TiO2/CeO2 composites. The use of as-received and plasma-treated MT was also investigated.
Section snippets
Sample synthesis
The chemicals were obtained from Sigma-Aldrich (Czech Republic), TiOSO4 (ā„Ā 29% Ti basis, technical), Ce(NO3)3Ā·6H2O (99% trace metal basis), Natural Na+ MT (Alfa Aesar, sieved 200Ā Ī¼m mesh, crystallochemical formula: Na0.25K0.07Ca0.10 (Si4.0) (Al1.45 Fe3Ā +0.21Mg0.24Ti0.01)O10 (OH)2).
In a typical process, 1.6Ā g of titanium oxysulfate (TiOSO4) was dissolved in 0.3Ā L of warm water (35Ā Ā°C) acidified with 0.5Ā mL of H2SO4 under vigorous stirring. Then, 10Ā mL of NH4OH/water (1:1) solution was continuously added
Phase analysis and samples composition (XRD, XPS)
In Fig. 1 are presented the diffraction patterns of pristine MT and as-prepared Ti/Ce composites deposited on as-received (TiCe_M) and plasma treated (TiCe_MP) MT; both MT composites were also annealed at 500Ā Ā°C - samples denoted TiCe_M500 and TiCe_MP500. As can be seen, there is no visible difference between the use of as-received and plasma treated MT because the plasma treated MT was re-hydrated during the composites preparation; in all Ti/Ce-MT samples can be recognised the most intense
Conclusion
We have demonstrated a simple, water-based synthesis of Ti/Ce-MT ternary composites used as reactive adsorbent towards toxic organophosphorus pesticide parathion methyl in polar and non-polar solvents. The use of MT supports has shown a clearly positive effect on degradation activity that was probably caused by effective pillaring of MT layers resulting in improved surface area and porosity, the formation of surface active sites, and improved adsorption. Plasma treatment of the MT in a simple
Acknowledgements
The authors acknowledge the assistance provided by the Research Infrastructure NanoEnviCz, supported by the Ministry of Education, Youth and Sports of the Czech Republic under Project No. LM2015073. This work was also supported by the Czech Science Foundation (project No.: 13-06989S) and the Internal Student Grant Agency of the J.E. PurkynÄ University in ĆstĆ nad Labem (internal project number: 44201 15 0073 01). PhD student Michaela SluÅ”nĆ” is gratefully acknowledged for N2 physisorption
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