Confinement of AlF3 in MOF derived structures for the formation of 4-fold coordinated Al and significantly improved dehydrofluorination activity

https://doi.org/10.1016/j.cej.2020.124946Get rights and content

Highlights

  • AlF3 particles are confined in quasi MOF structures (MIL-101) with (NH4)3AlF6 as the precursor.

  • AlF3 is stabilized by the confinement and interaction with CUS of Cr in quasi MOF.

  • Large amounts of 4-fold coordinated Al in AlF3 are achieved due to the interaction.

  • Reaction rate of confined AlF3 is about 9 times higher than that of supported AlF3.

  • It provides a potential strategy for preparation of metal fluoride Lewis acid catalysts.

Abstract

Dehydrofluorination is the major process for the production of fluorinated monomers and treatment of synthetic greenhouse gases. It is usually catalyzed by the Lewis acids, such as AlF3, MgF2 and fluorinated Cr2O3. The activity and stability remain the challenges of catalysts. For metal fluorides, Lewis acidic sites are derived from the unsaturated coordination of metal sites. This work reports the confinement of AlF3 into the cavity of quasi MOF structures. Due to the confinement effect and interaction of AlF3 with coordinatively unsaturated Cr-O nodes (oxygen vacancy), significant amounts of 4-fold coordinated Al in AlF3 can be achieved. Consequently, the Lewis acidity of AlF3 could be dramatically enhanced. As the catalyst of the gas-phase dehydrofluorination of HFC-245fa (1,1,1,3,3-pentafluoropropane) to tetrafluoropropene (HFO-1234ze, a new generation of green refrigerant) at 350 °C with the GHSV of 750 h−1, it exhibited the activity of 9 times higher than that of supported AlF3. After reaction of 35 h, no noticeable deactivation was detected. The present work provides a potential strategy for the preparation of metal fluoride Lewis acid catalysts with high efficiency.

Introduction

At present, global warming is one of the major challenges both in academic and social community. In addition to notorious CO2, hydrofluorocarbons (HFCs) are also the main contributors of greenhouse gases [1]. Consequently, significant efforts have been initiated. As a response, the European Union’s new F-gas Regulation prohibits the application of HFCs with global warming potential (GWP) higher than 150 as the commercial refrigerants [2], [3]. As the ozone depleting substances, the refrigerants including chlorofluorocarbons (CFCs) and hydrochlorofluorocarbons (HCFCs) have already been phased out [4]. Therefore, it necessitates the development of new substitutes for CFCs, HCFCs and HFCs. Hydrofluoroolefins (HFOs) are suggested to be appropriate alternatives, which usually exhibit short atmospheric lifetime, zero ozone depletion potential (ODP) and low GWP [5]. Among all the HFO compounds, 1,3,3,3-tetrafluoropropene (HFO-1234ze) is considered as a potential candidate for the replacement of HFC-134a (1,1,1,2-tetrafluoroethane). With the GWP of 1300, HFC-134a is currently one of the most widely applied refrigerants, especially in automobile air conditioners [6], [7]. By contrast, the GWP of HFO-1234ze is only 6 with an atmospheric lifetime of less than 15 days, zero ozone depletion potential and low flammability. The physical properties of HFO-1234ze are very similar as that of HFC-134a [8]. In addition, HFO-1234ze can also be widely used in various areas, e.g. using as foaming agent, heat pump agent and solvent [9], [10].

Among various routes of HFO-1234ze preparation, gas-phase dehydrofluorination of 1,1,1,3,3-pentafluoropropane (HFC-245fa, with the GWP of 858) to HFO-1234ze is the most promising and environmentally friendly [11], [12]. Clearly, this process converts greenhouse gas into value-added and environmentally benign product. In addition, this route is relatively simple and efficient. Presently, HFC-245fa is widely adopted as the key blowing agent in polyurethane foam. Under the regulation of F-gases, this process provides a potential solution for the excess capacity of HFC-245fa [13], [14].

Due to the high dissociation energy of C–F bond, the dehydrofluorination of HFCs is usually carried out with suitable catalysts and high reaction temperatures because of the highly endothermic characteristics. However, the formation of extremely corrosive HF byproduct would result in significant challenge for the catalysts [15], [16], [17], [18]. Consequently, for any catalytic reactions involving HF, the choice of the catalysts is limited to metal fluorides and other HF resistant materials. Aluminum fluoride (AlF3), magnesium fluoride and fluorinated Cr2O3 (F-Cr2O3) are the most common catalysts for gas-phase dehydrofluorination of HFCs [19], [20]. Although the traditional AlF3 and F-Cr2O3 catalysts are active for the dehydrofluorination reactions, they deactivate rapidly due to the coke deposition over the strong acidic sites [21], [22]. MgF2 possesses relatively weak Lewis acid and therefore low coke formation. Unfortunately, it also undergoes fast deactivation due to the significant sintering at temperatures above 280 °C [23]. Introduction of air in the feed was found to be effective for the improvement of catalytic stability for F-Cr2O3 [24]. However, it usually leads to low selectivity and extra cost for separation. Currently, the development of new catalytic materials with high activity and extremely long-term stability is the major topic of studies regarding dehydrofluorination reaction processes.

For catalysts, the coordinatively unsaturated metal site (CUS) is generally accepted to be the catalytic center [25]. Facilitated by high surface area, metal–organic frameworks (MOFs) are favorable for the formation of CUS, which are constructed by metal nodes with organic linkers [26]. In addition, the interaction of metal nodes and organic linkers attributes to the regular arrangements of metal centers in the developed pore channels [27]. Consequently, the guest molecule or atom cluster can be immobilized in CUS [28]. For instance, Jiang et al. reported that the Au@Ag nanoparticles were confined to 2–6 nm following the confining effect of the pore/surface structure of ZIF-8 [29]. It exhibited excellent activity for the hydrogenation of 4-nitrophenol. Corma et al. immobilized Au (III) (2 wt%) to a modificatory MOF which catalyzes a domino three coupling and cyclization to indoles efficiently [30].

However, the CUS usually is easy to be separated from the guest molecule or atom cluster due to the organic ligands, resulting in the weak interaction between host (CUS) and guest (molecule or atom cluster) [31]. In order to enhance the interaction, partially removing the organic ligands can expose more coordinatively unsaturated inorganic metal sites [32]. In our previous work, we have reported the preparation of quasi MIL-101 by calcination in N2 atmosphere, which exhibited excellent stability towards gas dehydrofluorination [33]. Following the partial removal of the organic ligands, the quasi MOFs could show significant amounts of CUS.

In this work, we report the fabrication of highly dispersed AlF3 nanoclusters in the quasi MIL-101 by impregnating the (NH4)3AlF6 to the fresh MIL-101 in water. Then the (NH4)3AlF6@MIL-101 sample was calcined under inert atmosphere at 350 °C. AlF3 nanoclusters encapsulated in the quasi MIL-101 were achieved. The structure-activity relationship between host (CUS of calcined MIL-101) and guest (AlF3 nanoclusters) was investigated in detail. SEM, TEM and BET were adopted for analysing the distribution of AlF3 in the calcined MIL-101. Furthermore, the interaction between CUS and AlF3 nanoclusters were also characterized by XRD, XPS, MAS NMR, EPR and FT-IR. And the NH3-TPD was conducted to measure the acidic properties of virous catalysts. As the AlF3 nanoclusters are confined in porous quasi MOF structures, coke formation was inhibited. Consequently, high and stable catalytic performance for gas dehydrofluorination of HFC-245fa was obtained.

Section snippets

Synthesis of MIL-101

MIL-101 was prepared according to our previous work [33]. Cr(NO3)3·9H2O (8.002 g, 20.0 mmol), terephthalic acid (3.322 g, 20.0 mmol) and HF (0.9 mL, 40 wt%) were added to 160 mL deionized water. The mixed solution was first transferred into a 250 mL Teflon-lined autoclave and heated at 250 °C for 8 h. Then, the mixture was cooled to room temperature slowly and then the green paste was separated from the solution by centrifugation. The green paste was washed thoroughly with ethanol, DMF, aqueous

Results and discussions

The textural properties of catalysts were determined by N2 physisorption experiments. As displayed in Fig. 1a, both the MIL-101 and (NH4)3AlF6@MIL-101 show type I isotherms and H4 hysteresis which are usually found over microporous solids. Actually, MOF structures are well known microporous materials. As listed in Table S1, MIL-101 prepared in the present work possesses the surface area and pore volume of about 2965 m2 g−1 and 1.49 cm3 g−1, respectively. The pore size is centered at 2 nm (Fig.

Conclusion

In summary, we propose a novel strategy for the preparation of metal fluoride Lewis acid catalyst. After the preparation of MIL-101, Al was loaded to the cavities using (NH4)3AlF6 as the precursor. Calcined at 350 °C to 550 °C in N2 atmosphere, (NH4)3AlF6 and MIL-101 converts to AlF3 and quasi MIL-101 respectively. During calcination, MIL-101 undergoes partial carbonization and deligandation of the organic linkers. However, the developed pore and the connection of metal nodes with ligands are

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

This research was supported by Zhejiang Provincial Natural Science Foundation of China under grant no. LY19B060009 and LY19B050004, National Natural Science Foundation of China (21978265).

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