Vijayan
Srinivasapriyan
ab
aCAS Key Laboratory of Nanosystem and Hierarchical Fabrication, CAS Center for Excellence in Nanoscience, National Center for Nanoscience and Technology, Beijing, 100190, China. E-mail: vsripriyan@mails.ucas.edu.cn
bSchool of Nanoscience and Technology, University of Chinese Academy of Sciences, Beijing, 100049, China
First published on 8th October 2021
Efficient and selective catalysts are pivotal for the chemical industry. The functionalization of benzene plays a vital role in the petrochemical industry by converting benzene into other value-added chemicals, such as phenols, anilines, etc. In the chemical industry, phenol production is based on the three step cumene process, which produces hazardous cumene hydroperoxide as an intermediate and also equimolar acetone as a coproduct. So, the direct oxidation of benzene to phenol is desirable. Unfortunately, most of the developed catalysts require an elevated temperature and suffer from low conversion. So, here we designed a series of hollow amorphous nanomaterials, based on aMIL-100 with metal nodes of Fe, Cr, Al and Sc, by sandwiching nanoparticles, such as Pt, Rh and Ru, in between hollow amorphous metal–organic frameworks with enhanced diffusion for highly selective benzene oxidation. We have achieved 52% benzene conversion and 99.5% selectivity for phenol.
Phenol, one of the most important chemicals in the petrochemical industry,32 has been synthesised based on the cumene process, which produces hazardous cumene hydroperoxide as an intermediate as well as equimolar acetone as a coproduct.33 So, the direct and selective oxidation of benzene is an attractive and challenging method for phenol production.34,35 This direct oxidation can be achieved by various oxidants, such as O2,36,37 N2O,38–40 and H2O2.41–45 In particular, the H2O2 oxidant process is environmentally green due to only producing water as a by-product. However, the direct C–H activation of benzene is a more challenging one. Until now, all the developed catalysts require an elevated temperature and suffer from low conversion because of the notoriously low reactivity of C–H bonds and, especially under heating conditions, phenol is easily overoxidized to yield products such as p-benzoquinone. So, we designed a series of hollow sandwich nanostructures based on aMIL-100 (amorphous MIL-100) with metal nodes of Fe, Cr, Al and Sc connected with 1,3,5-benzene tricarboxylate (BTC) which were rationally synthesized using monodisperse polystyrene (PS) nanoparticles as templates through a versatile step-by-step self-assembly strategy.46 Sandwiching nanoparticles between an inner hollow aMOF and an outer shell composed of an aMOF leads to highly stable and selective catalysts for the oxidation of benzene to phenol at room temperature. Due to the low density of hollow aMOFs, the amount of catalyst loading is reduced to 2 mg instead of the 20 to 50 mg of solid catalyst which was used for benzene to phenol oxidation (Table 1, entries 2 and 3).
Fig. 1 HMIL-100(Fe)@Pt@aMIL-100(Fe) (a) SEM image, (b) large-scale TEM image and (c) magnified shell thickness. Inset: HRTEM image of Pt NPs. (d) HAADF-STEM image and EDS elemental mapping. |
Fig. 2 TEM images and EDS elemental mapping of (a) HMIL-100(Fe)@Rh@aMIL-100(Fe) and (b) HMIL-100(Fe)@Ru@aMIL-100(Fe). Insets: HRTEM images of NPs (HAADF-STEM). |
The X-ray photoelectron spectroscopy (XPS) spectra of the Pt 4f regions for Pt nanoparticles and Pt/HMIL-100(Fe) are shown in Fig. 3a. Wherein the two characteristic peaks observed for the Pt NPs were at 71.5 and 74.8 eV, and for Pt loaded HMIL-100(Fe) the values were 71.8 and 75.1 eV. In addition, the binding energy shift of 0.3 eV to a higher position shows the electron donation from the Pt NPs to the supported HMIL-100(Fe). This result shows that the Pt was in an electron-deficient state which favored Fe3+ over Fe2+/4+. Likewise, the Fe 2p spectra reveals that Fe3+ is found in HMIL-100(Fe). In addition, the binding energies of Fe 2p were found to be 714.5 & 727.9 eV in HMIL-100(Fe) and for HMIL-100(Fe)@Pt the values were 713.8 & 727.2 eV. Again, the lower binding energy shift of 0.7 eV in the Pt loaded HMIL-100(Fe)@Pt shows that electrons were transferred from the Pt NPs to the MOFs.
Table 1 summarizes the results obtained when using the hollow nanostructures as catalysts for the oxidation of benzene (A) to phenol (B).
Entry | Catalysts | Time | Conversion | Selectivity |
---|---|---|---|---|
Reaction conditions: benzene (0.40 mL), 6 mL H2O2, catalyst, solvent: 1 mL EtOH and 3 mL water, rt. Entry (2), HMIL-100(Fe) – 2 mg catalyst. Entry (3), solid MIL-100(Fe) – 20 mg catalyst. | ||||
1 | Pt or Rh or Ru NPs | 12 | — | — |
2 | HMIL-100(Fe) | 12 | 13 | 56 |
3 | MIL-100(Fe) solid | 12 | 7.3 | 75 |
4 | HMIL-100(Al)@Pt | 12 | 3.0 | 48 |
5 | HMIL-100(Sc)@Pt | 12 | 2.0 | 33 |
6 | HMIL-100(Cr)@Pt | 12 | 6.0 | 46 |
7 | HMIL-100(Fe)@Pt | 12 | 35 | 99 |
8 | HMIL-100(Al)@Pt@aMIL-100(Al) | 12 | 4.9 | 45 |
9 | HMIL-100(Sc)@Pt@aMIL-100(Sc) | 12 | 4.0 | 26 |
10 | HMIL-100(Cr)@Pt@aMIL-100(Cr) | 12 | 9.0 | 42 |
11 | HMIL-100(Fe)@Pt@aMIL-100(Fe) | 12 | 52 | 99.5 |
12 | HMIL-100(Fe)@Rh@aMIL-100(Fe) | 12 | 78 | 68 |
13 | HMIL-100(Fe)@Ru@aMIL-100(Fe) | 12 | 38 | 73 |
The direct oxidation of benzene to phenol was carried out in the presence of catalyst X (where X is Pt, Rh or Ru) NPs with H2O2 as an oxidant at room temperature (Table 1, entry 1) and no conversion was observed. Then, we started exploring the reaction with HMIL-100(Fe) and solid MIL-100(Fe) (Table 1, entries 2 and 3) and low conversion with low selectivity was observed. So, to further enhance the activity of HMIL-100(X), where X stands for different metal nodes (Fe, Cr, Al and Sc), we have loaded Pt nanoparticles to form core shell HMIL-100(X)@Pt (where X is Fe, Cr, Al or Sc) (Table 1, entries 4–7) and among these catalysts HMIL-100(Fe)@Pt based on an Fe metal node shows moderate conversion with good selectivity due to the strong interaction and synergistic effect between Pt and the Fe metal node. We checked the TEM images after the reaction, which show that the core shell HMIL-100(X)@Pt catalysts (where X is Fe, Cr, Al or Sc) were unstable for this system (Fig. S9a, ESI‡). This inspired us to further coat other MOF shells to protect their stability (Table 1, entries 8–11) and we achieved good conversion with good selectivity for HMIL-100(Fe)@Pt@aMIL-100(Fe), which demonstrates that an Fe based metal node with Pt shows good conversion and selectivity; moreover, the sandwich structures show good stability. So, we directly achieved a different sandwich structured HMIL-100(Fe)@X@aMIL-100(Fe) with different noble metals (X is Rh or Ru). The Ru based HSMs (hollow sandwich aMOFs) showed lower conversion and selectivity than the Pt-based HSM. But, the Rh based HSM showed better conversion than the Pt-based HSM, with lower selectivity. This is due to the higher activity of Rh with H2O2, compared with all HSMs. Table 1, entry 11 shows that Pt nanoparticles enhance the activity of Fe based MOFs and control the selectivity in the benzene oxidation reaction. The HSM stability was checked from the TEM images after the reaction and they show that the HSM catalyst was stable for this system (Fig. S9b and c, ESI‡). Solvents played a vital role in this reaction; when water served as the reaction medium, the use of organic solvents was minimized, and among all the solvents investigated, the EtOH/H2O mixed solvent 1:3 (mL/mL) resulted in the best performance by producing the highest benzene conversion (Table S1, ESI‡). It is obvious that the reaction conducted in the mixed solvent was more effective for benzene conversion and phenol selectivity as compared with the single solvent systems, CH3CN, EtOH or H2O only. This is because in the biphasic system the benzene oxidation occurs in the aqueous phase in the cavity of the HMOFs because HMIL-100(Fe) is hydrophilic and it is easy for the aqueous phase component to diffuse into the cavities. Moreover, the presence of a suitable organic solvent not only increases the concentration of benzene in the aqueous phase, but is also favorable for the aqueous benzene oxidation reaction and extracts phenol production into the organic phase to minimize overoxidation of phenol by reducing the contact between phenol and the catalyst. For the catalytic stability, recycling experiments were performed. After each reaction, the catalyst was centrifuged, washed with ethanol and reused for the subsequent cycles. The catalyst showed no significant changes in terms of the catalytic activity and selectivity after successive reuses of up to three cycles (Fig. S10, ESI‡). The phase and morphology of the reused catalyst remained virtually unchanged relative to those of the fresh catalyst (Fig. S9b and c, ESI‡), which also verified the stability of the catalyst.
We explored whether H2O2 could be activated on the Fe site and if the noble metal (Pt, Rh or Ru) NPs could accelerate the process of converting H2O2 to OH. However, directly elucidating this synergetic effect is very difficult. Deng et al. reported that an additional H2O2 can also create a second adsorbed oxygen species on an Fe single atom catalyst with one oxygen preabsorbed and oxidize benzene.44 Also, Zhang et al. reported that an SA-Fe/CN catalyst can dissociate H2O2 into two hydroxyls (2HO˙), coadsorbing at the single Fe site in accordance with recent theoretical density functional theory (DFT) calculations.47 The observed formation of FeIVO species, usually considered to be the active intermediates in this kind of reaction, verifies that H2O2 could be activated on the Fe atom. These two works support our understanding of the reactivity of this reaction. For further confirmation, we carried out spin trapping in EPR studies using 5,5-dimethyl-1-pyrroline N-oxide (DMPO); this is one of the most popular spin traps and the EPR features of its spin adducts are well established. For example, the EPR spectrum of the HO radical adduct (DMPO OH) exhibits signals with a relative peak ratio of 1:2:2:1. The hyperfine splitting pattern of the observed radical clearly indicates that HO is produced during the reaction of benzene with H2O2 and HMIL and is trapped by DMPO to produce DMPO–OOH. It was further confirmed that the addition of DMPO to a methanol solution of benzene and H2O2 without a catalyst (HMIL) resulted in no observation of an EPR signal. The results indicated that the intensities of the EPR spectra were of the order of HMIL@Pt > HMIL@Rh > HMIL@Ru > HMIL > no catalyst (Fig. 4). In summary, when the catalyst was added to the methanol solution of benzene, H2O2 and DMPO, a strong EPR signal assigned to DMPO–OOH was observed, which suggested that more OH radicals were produced by the Pt-based catalyst.
Fig. 4 EPR spectra recorded during the oxidation of benzene with H2O2 in the presence of various catalysts and DMPO. |
Here, we propose a plausible mechanism for the benzene oxidation reaction based on our experimental results. The aromaticity and delocalized pi system in benzene and slow production of hydroxyl radicals result in an uncatalyzed benzene oxidation reaction, which is kinetically slow. Therefore, decreasing the stability of benzene and facilitating the yield of hydroxyl radicals are efficient approaches to increase the reaction rate to achieve high yield.
Footnotes |
† Dedicated to Professor Zhiyong Tang on the occasion of his 50th birthday. |
‡ Electronic supplementary information (ESI) available. See DOI: 10.1039/D1MA00768H |
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