Adsorption performance of VOCs in ordered mesoporous silicas with different pore structures and surface chemistry
Introduction
Volatile organic compounds (VOCs) have been extensively involved in many industrial processes, whereas such compounds are hazardous to human health, contributing to serious environmental problems such as the destruction of the ozone layer, photochemical smog and global warming [1], [2]. Hence the emission of VOCs has triggered increasing awareness focused on the development of abatement technologies to comply with the latest environmental regulations. Among the different alternatives available to remove VOCs, adsorption technology with no chemical degradation has been generally recognized as a preferred strategy, especially in cases where the organic pollutants to be captured have alternative uses [3]. The primary requirements of an adsorbent adopted in the industry process include sufficient adsorptive capacity, high adsorption rate, and strong hydrophobicity [4]. Activated carbon is widely employed in adsorption process owing to its high micropore volume and low operating cost [5]. Unfortunately, activated carbon often suffers from added fire risk, pore blocking, hygroscopicity and a lack of regenerative ability [6].
As a result, alternative adsorbents such as hydrophobic zeolite and mesoporous silica have attracted considerable attention to control VOCs. Hydrophobic zeolites have been found to be effective in VOCs removal [7], [8]. However, serious diffusion restrictions imposed by the micropores (<2 nm) tend to inhibit its ability to adsorb large VOC molecules [9]. Ordered mesoporous silicas offer excellent features such as large pore volume and high surface area, narrow pore size distribution, open pore structure and reliable desorption performance [10], [11], [12]. Siliceous SBA-15, MCM-41, MCM-48 and KIT-6 are considered as representatives of mesoporous materials. SBA-15 and MCM-41 possess a two-dimensional (2D) hexagonal array of uniform cylindrical mesopores (p6m), while MCM-48 and KIT-6 consist of three-dimensional (3D) bicontinuous cubic arrangement of mesopores (Ia3d). In particular, studies found that the porous structure of SBA-15 not only consists of ordered mesopores but also of much smaller complementary pores connecting adjacent mesopore channels [13], [14]. Similarly, the two intertwined systems of mesoporous channels in KIT-6 can also be connected through irregular micropores in the walls [15]. Previous studies have indicated that the bimodal materials (SBA-15 and KIT-6) have high affinity for various VOCs due to their complementary micropores, which are favorable to the diffusion process [10], [16].
In fact, the silanols (Si–OH) on the amorphous walls surface make original mesoporous silicas less hydrophobic and decrease the adsorption capacity of VOCs in the presence of water vapor, which limit their applications in the field of adsorption. Furthermore, surface siloxanes of original silicas may hydrolyze to silanols by water adsorption [17], [18]. Therefore, surface chemistry tailoring is required for mesoporous silicas in order to improve hydrophobicity and selectivity for VOCs. One important way of modifying the surface chemistry is organic functionalization [13]. It has been established that the introduction of organic groups in the framework of nanoporous material has a positive effect on VOCs removal [19].
Surface functionalization can be conducted in three various ways such as subsequent surface functionalization of pre-fabricated silica materials (“grafting”), the simultaneous condensation of corresponding silica and organosilica precursors groups (“co-condensation”) and the incorporation of organic groups as bridging components into the pore walls (“production of periodic mesoporous organosilica”) [20]. Compared with the other two pathways, the grafting method, carried out by reaction of organosilanes with surface silanol groups, can maintain the original mesoporous structure. Adjustment of the surface chemistry of porous silicas with organic groups, such as alkyl chains or phenyl groups, can enhance the surface hydrophobicity [13]. Much progress focusing on the post-synthetic functionalization of mesoporous materials with organic groups and the corresponding applications has been made [17], [21], [22], [23], [24]. Zhao and Lu [21] demonstrated that surface functionalization of siliceous MCM-41 by grafting with trimethylchlorosilane (TMCS) was an effective technique in tailoring adsorbents for the selective abatement of VOCs from wastewater. However, there is very limited information available in the literature relating to the application of such inorganic-organic mesoporous solids in the field of VOCs removal, especially in gas steams. Furthermore, the effect of pore structure on the surface functionalization is essential for the synthesis of functionalized silicas and the corresponding VOCs adsorption.
The objective of this work is to investigate the surface functionalization and adsorption performances of ordered mesoporous silicas with different pore structures, including SBA-15, MCM-41, MCM-48 and KIT-6. The functionalized mesoporous silicas were synthesized by post-synthetic treatment with phenyltriethoxysilane (PTES). The dynamic and static adsorption behaviors of VOCs on the original pure silicas and functionalized silicas were investigated by continuous-flow adsorption measurements and digital microbalance, respectively. With regard to the dynamic adsorption, besides single component adsorption of benzene, competitive adsorptions of benzene with water or cyclohexane were also conducted to explore the affinity between VOCs molecules and functional groups on the mesoporous silica surface.
Section snippets
Preparation of mesoporous silicas
Four mesoporous silicas, including SBA-15, MCM-41, MCM-48 and KIT-6 were synthesized according to the procedures described in the literature [25], [26], [27], [28]. The nonionic Pluronic P123 (EO20PO70EO20) was used as a template for the synthesis of SBA-15 and KIT-6, whereas the cetyltrimethyammonium bromide (CTAB) was used for MCM-41 and MCM-48. After being stirred, the solution mixture was transferred into a Teflon-lined autoclave and hydrothermally treated. The obtained solid products were
Characterization of samples
During the post-grafting functionalization process, organic functional groups could be covalently attached to the silanol groups (Si–OH) on the external and inner pore surface in the presence of non-polar solvent, as schematically shown in Fig. 1. Powder low-angle XRD patterns of original and phenyl-grafted SBA-15, MCM-41, MCM-48 and KIT-6 are depicted in Fig. 2. Before grafting phenyl groups, SBA-15 and MCM-41 display three well-defined peaks, which can be indexed as (1 0 0), (1 1 0) and (2 0 0)
Conclusions
Phenyl functionalized ordered mesoporous silicas with different pore sizes and mesostructures were prepared by a post-synthesis grafting approach. Furthermore, the adsorption performances of VOCs on the original and functionalized mesoprous silicas were investigated. It was found that the phenyl groups are covalently anchored onto the surface of the mesoporous silicas while retaining their ordered mesostructures, and p-KIT-6 exhibits the highest degree of the surface functionalization.
Acknowledgments
This study is financially supported by National Natural Science Fundation of China (20725723, 20807050), National Basic Research Program of China (2010CB732300), the National High Technology Research and Development Program of China (2006AA06A310) and the Australian Research Council (ARC) through Discovery Project program (DP0987969, DP1095861).
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