Startseite Liquid phase selective oxidation of cyclohexane using gamma alumina doped manganese catalysts and ozone: an insight into reaction mechanism
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Liquid phase selective oxidation of cyclohexane using gamma alumina doped manganese catalysts and ozone: an insight into reaction mechanism

  • Siphumelele T. Mkhondwane und V. S. R. Rajasekhar Pullabhotla ORCID logo EMAIL logo
Veröffentlicht/Copyright: 8. März 2023

Abstract

In this study, we investigate the oxidation of cyclohexane using various percentages of Mn/γ-Al2O3 catalysts. The catalysts were characterized with various spectroscopic and microscopic techniques. The XRD showed the presence of γ-Al2O3 and MnO only. However, the XPS showed that AlO, AlOH, Mn2O3 and MnO2 also exist. The TEM results of pristine γ-Al2O3 showed characteristics of a spherically shaped material, whereas Mn/γ-Al2O3 catalysts displayed rod shaped particles. The EPR results showed that hydroxide radicals are the main reactive species responsible for the significant oxidation of cyclohexane and the catalysts play a profound role in the generation of hydroxide radicals. The oxidation of cyclohexane was performed for 1 h and the reaction products were analysed using GC-MS and FT-IR in 30 min intervals. The 2.5% Mn/γ-Al2O3 was the most reactive catalyst with a percentage conversion of 33% after 1 h oxidation. The cyclohexanol and the cyclohexanone were the only reaction products obtained. This study exhibited that Mn/γ-Al2O3 catalysts when used in conjunction with ozone are potential replacement for industrially used homogeneous manganese catalysts.

Introduction

The selective oxidation of cyclohexane to a mixture of cyclohexanol and cyclohexanone (KA oil) is the cornerstone of the modern civilization. The KA oil is an important feedstock for the manufacture of numerous essential products, such as nylon polymers, dye stuffs and textiles. As a result, about 1 million tons of KA oil is produced commercially per annum [1]. However, cyclohexane is highly stable due to the absence of the π-system that can be stimulated to facilitate the reaction with oxidants [2]. Accordingly, in industries, cyclohexane oxidation is explored at high temperature (150–160 °C) and pressure conditions (1–2 atm) using manganese-based homogeneous catalysts to optimize efficiency [3]. This process suffers significantly from several pitfalls such as production of copious amount of undesirable by-products, difficulty of separating catalysts from reaction system and hazards associated with utilizing extreme reaction constitutes due to high flammability of cyclohexane. As a result of the production of huge amount of the undesirable byproducts, there is trademark compromise between percentage selectivity and conversion in industries. The percentage conversion is commonly maintained at 3–4% to obtain 70% selectivity toward KA oil [4, 5]. Therefore, development of the efficient, environmentally benign, safe and economic viable contemporary process is highly required.

Metal-supported catalysts as an example of heterogeneous catalysts are promising substituents for commercially utilized manganese-based homogenous catalysts, which circumvent the pitfalls associated with stability and recovery difficulties in reaction solution [6, 7]. The evolution of the catalytic activity of the metal-supported catalysts emerges from numerous factors, such as particle size, shape, defective microstructures, elemental composition and metal-supports interactions. As a typical case of the particle size, the catalytic activity emerges from the enhanced surface-to-volume ratio for surface catalysed reaction [8]. The immobilization of the metal in a nano-sized porous or high surface functionalized metal oxide increases the number of the exposed active sites and therefore catalytic activity [8, 9]. In addition, due to the alteration in stacking sequence, the metal-support interaction results to defective microstructures which commonly diverge with composition. These microstructures possess high surface energy which in return have profound role in enhancing activity of the catalysts [10, 11].

Ozone is one of the highly reactive oxidants with high oxidation potential (2.07 V) [12]. When coupled with metals and metal oxides catalysts, ozone decomposes to hydroxide radicals (OH) which are more reactive towards hydrocarbons [13, 14]. Hence, in this study we report the utilization of ozone in conjunction with gamma alumina doped manganese (Mn/γ-Al2O3) catalysts for oxidation of cyclohexane to cyclohexanol and cyclohexanone. The Mn content loaded on γ-Al2O3 was varied from 2.5% to 15% in 2.5% intervals to study the effect of the Mn loading. The reaction was limited to 1 h in quest to achieve high percentage selectivity toward KA oil by avoiding further oxidation of KA oil.

Experimental

Materials

Cyclohexane (99.99%, Aldrich), manganese chloride tetrahydrate (98%, Aldrich), gamma alumina nano-powder (99.99%, Aldrich), Acetic acid (99.8%, Merck), Sodium hydroxide (99.99%, Merck), hydrofluoric acid (40%, Merck), nitric acid (45%, Merck), toluene (98% Merck) and hydrochloric acid (37%, Merck), 5,5-dimethyl-1-pyrroline N-oxide (DMPO) (99% Aldrich) and Dimethyl sulfoxide (DMSO) (99% Aldrich), α-phenyl-tert-butyl nitrone (PBN) (Aldrich), 5,5-dimethyl-1-pyrroline N-oxide (DMPO) (Aldrich) were purchased and used without further purification.

Catalysts preparation

Various percentages of manganese doped gamma alumina (2.5%, 5%, 7.5%, 10%, 12.5% and 15% Mn/γ-Al2O3) catalysts were prepared using wet impregnation method as reported before [15]. Briefly, an adequate amount of MnCl2·4H2O was dissolved in 100 mL of deionized water. The resultant solution was added (dropwise) in to 250 mL beaker containing bare γ-Al2O3 support with vigorous stirring for homogenous dispersion of Mn in to γ-Al2O3. The solvent was evaporated by placing the beaker on a hot plate at 70 °C for 2 h until a thick paste was obtained. The evaporation of water was completed by drying the catalyst precursor at 90 °C in oven overnight under oxygen flow followed by calcination at 300 °C for 5 h.

Catalysts characterization

Fourier transform-infrared spectroscopy (FT-IR)

The functional groups present in catalysts were identified using transmission FT-IR spectroscopy. The analysis was carried out using a Bruker Tensor 27 FT-IR spectrometer with a standard attenuated total reflection (ATR) cell. Ethanol was used to clean the surface prior to analysis. The pressure was adjusted to 90 Gauge for proper contact between the surfaces. The mid-IR region for catalysts scan was kept between 450 and 4000 cm−1 range.

X-ray diffraction

The crystal lattice and phases of the prepared catalysts were examined using X-ray diffraction spectroscopy. Typically, the Bruker AXS D8 diffractometer with monochromatic Cu Kα (λ = 1.5406 Å) incident radiation at 40 kV and 40 mA at room temperature was used. The diffractometer utilized the CuKα as the radiation source of wavelength = 1.5406 nm. Scan speed was set to be 0.3/min over 10°–90° scan range. Prior to each analysis the sample holder was properly cleaned with ethanol solvent and dried.

Scanning electron microscopy – energy dispersive X-ray spectroscopy (SEM-EDX)

Scanning electron spectroscopy (SEM) was used to study the morphology of the catalysts. The instrument used was Carl Zeiss FE-SEM Sigma VP-03-67 with operation conditions of acceleration voltage of 20 kV over the working distance of 6–9 mm. All the samples were ground into fine powder with mortar and pestle prior to the analysis. The analysis was completed by placing a small amount of the powdered sample on a piece of two-way carbon tape and mounted it on a sample holder (stub). The elemental composition of the sample was carried out on an Oxford instruments X-MaxN 50 model 54-XMX1003 EXD analyser.

Transmission electron microscopy (TEM)

Particle size and morphology of the calcined catalysts were studied by TEM analysis. The analysis was conducted using JOEL JEM-1010 electron microscope with an acceleration voltage of 100 kV. The images were captured with Meagaview III camera and analysed with iTEM imaging software. The sample preparation involved dispersing the catalyst powder into toluene for 20 min. The analysis was conducted by placing a drop of the catalyst sample on a copper grid coated with formvar with mesh size of 150 and allowed to dry at room temperature before TEM images were captured.

Inductively coupled plasma-optical emission spectroscopy (ICP-OES)

The metal content of the catalysts was quantified using Agilent 700 series ICP-OES with a 710 ICP-OES detector instrument. A multi element standard solution was diluted to 25 ppm, 50 ppm, 75 ppm and used for calibration of the instrument. Prior, to the analysis the adequate amount of the catalysts samples were digested in 3.0 mL HCl, 3.0 mL HNO3 and 4.0 mL HF at 60 °C for 1 h until digestion was complete. The sample preparation was completed by subsequent dilution of the resultant solution with distilled water up to the 100 mL mark of the volumetric flask to make 25 ppm, 50 ppm and 75 ppm. The content of the metals was extrapolated from the calibration curve established from the standard solution.

Brunauer–Emmet–Teller (BET)

The surface area analysis of the catalysts was conducted with Brunauer Emmet and Teller (BET) surface area analyser. The catalysts (0.2 g) were initially degassed at 200 °C in Micrometrics flow prep 060 instrument overnight under nitrogen flow. Subsequently, the analyses were done in an automated single and then multiple point Micrometrics Tristar 3000 BET surface area analyser under liquid nitrogen flow.

X-ray photoelectron spectroscopy

X-ray photoelectron spectroscopy (XPS) analysis were perfumed to evaluate near surface state of the catalysts using an AXIS Ultra DLD equipped with charge neutralizer. The centre utilized for the scans was 520 eV with a 1205 eV width, dwell time at 100 ms and steps at 1 eV. The high-resolution scans were obtained using 80 eV pass energy in slot mode. The fitting of the curves was performed with Gaussian-Lorentzian peak shape post linear background collection.

Electron paramagnetic resonance

Electron paramagnetic resonance (EPR) spectroscopy measurements were carried out using the Bruker EMX Plus EPR spectrometer, specifications: model number: EMP-9.5/12B/P. set at 0.632 mW for the microwave power, frequency 9.714 GHz, resolution 2048 points, at a centre field of 3500 G and 200 G for the sweep width and time constant of 5.12 for the hydroxide radicals determination, using DMPO as the quencher.

Oxidation of cyclohexane

Ozone was generated via a Mighty zone MZPF 4000 ozone generator by the corona discharge method. The cyclohexane oxidation was carried out in an impinger reactor equipped with porous bubbler with porosity 2. Cyclohexane (50 mL) was added into the reaction vessel. The ozone was fed into the reaction vessel through porous bubbler. Initially, blank ozonation was conducted whereby cyclohexane oxidation was performed in a catalyst free system. Subsequently, the catalytic activities of the Mn/γ-Al2O3 catalysts were investigated. The 0.2 g of the catalysts were used for all the ozonation reactions. The scheme illustrating the oxidation of cyclohexane is shown in Fig. 1. The reaction products were analysed using GC-MS and FT-IR. Afterwards, the reaction mechanism was postulated based on GC-MS and EPR results.

Fig. 1: 
Schematic of oxidation of cyclohexane reaction setup.
Fig. 1:

Schematic of oxidation of cyclohexane reaction setup.

Characterization of the reaction products

An Agilent gas chromatograph system equipped with a 5975C VL mass spectrometer Triple-Axis detector was used to determine the reaction products. With the use of the chromatogram, the percentage conversion and selectivity were calculated using the below eqs. 1 and 2, respectively. The column used was an Agilent 190915-433: 325 °C: 30 m × 250 μm × 0.25 μm GC column, in which hydrogen (H2) and helium (He) gases were used as the mobile phase and the mass spectrometry detector (MSD) respectively. The sample (1 μL) was injected at 250 °C and 29.127 kPa of temperature and pressure respectively.

(1) C o n v e r s i o n = A m o u n t o f c y c l o h e x a n e r e a c t e d T o t a l a m o u n t o f c y c l o h e x a n e × 100 1
(2) S e l e c t i v i t y = A m o u n t o f i n d i v i d u a l p r o d u c t o b t a i n e d T o t a l a m o u n t o f p r o d u c t s o b t a i n e d × 100 1

The FT-IR characterization procedure already outlined in the characterization of the catalysts was also used for the identification of the oxidation products.

Results and discussion

Catalyst characterization results

Fourier-transform infrared (FT-IR) spectroscopy

The FT-IR spectra of the γ-Al2O3 support and Mn/γ-Al2O3 catalysts are displayed in Fig. 2. The FT-IR spectra exhibit a broad band at 3500 cm−1 which is due to the stretching vibrational frequency of OH groups of the adsorbed H2O and Lewis acid sites of the γ-Al2O3 and Mn/γ-Al2O3 catalysts. Another band can be observed at 1600 cm−1 which can be assigned to the bending vibrations of OH group [16, 17]. The existence of both the Al–O bond Mn associated bond is trivial as there were no peaks corresponding to Al–O and Mn metal observed.

Fig. 2: 
FT-IR spectra of (a) γ-Al2O3, (b) 2.5% Mn/γ-Al2O3, (c) 5% Mn/γ-Al2O3, (d) 7.5% Mn/γ-Al2O3, (e) 10% Mn/γ-Al2O3, (f) 12.5% Mn/γ-Al2O3 and (g) 15% Mn/γ-Al2O3 catalysts.
Fig. 2:

FT-IR spectra of (a) γ-Al2O3, (b) 2.5% Mn/γ-Al2O3, (c) 5% Mn/γ-Al2O3, (d) 7.5% Mn/γ-Al2O3, (e) 10% Mn/γ-Al2O3, (f) 12.5% Mn/γ-Al2O3 and (g) 15% Mn/γ-Al2O3 catalysts.

X-ray diffraction (XRD)

The X-ray diffraction spectra of γ-Al2O3 support and M/γ-Al2O3 catalysts are displayed in Fig. 3. The γ-Al2O3 displays diffraction peaks at 2θ = 19.89°, 24.88°, 30.49°, 35.02°, 38.95°, 42.08°, 47.36°, 54.39°, 58.17°, 68.35° and 72.91° corresponding to (101), (111), (220), (221), (331), (222), (400), (422), (511), (440) and (444) hkl of cubic γ-Al2O3 [18], [19], [20]. There are no X-ray diffraction peaks corresponding to Mn species observed in 2.5%–10% Mn/γ-Al2O3 catalysts. This suggests that the Mn is well incorporated into crystalline structure of the γ-Al2O3. However, significant alterations in crystalline structure of γ-Al2O3 were observed upon Mn loading. For example, the incorporation of the Mn was followed by broadening of the diffraction peaks corresponding to γ-Al2O3 and the disappearance of the (111) and (101) peak. This has been reported before in Fe doped γ-Al2O3 [21]. The XRD spectra of 12.5% and 15% displays additional peaks at 2θ = 17.24°, 20.43°, 31.62°, and 43.5° corresponding to (200), (111), (311), and (112) hkl of the MnO phase [22].

Fig. 3: 
XRD spectra of (a) γ-Al2O3, (b) 2.5% Mn/γ-Al2O3, (c) 5% Mn/γ-Al2O3, (d) 7.5% Mn/γ-Al2O3, (e) 10% Mn/γ-Al2O3, (f) 12.5% Mn/γ-Al2O3 and (g) 15% Mn/γ-Al2O3 catalysts.
Fig. 3:

XRD spectra of (a) γ-Al2O3, (b) 2.5% Mn/γ-Al2O3, (c) 5% Mn/γ-Al2O3, (d) 7.5% Mn/γ-Al2O3, (e) 10% Mn/γ-Al2O3, (f) 12.5% Mn/γ-Al2O3 and (g) 15% Mn/γ-Al2O3 catalysts.

Scanning electron microscopy (SEM)

Figures 4 and S1 (Supplementary information) display the SEM images of the γ-Al2O3 and Mn/γ-Al2O3 catalysts. The SEM image of pristine γ-Al2O3 support display properties of the fluffy powdered material with poorly defined structure, with rough morphology. The incorporation of the Mn metal resulted to a slight change in morphology from rough to smooth, highly aggregated surface. The EDX spectra are displayed in Fig. S2. The EDX spectra confirm the existence of the Mn metal (Table 1) and the elemental composition is in correlation with the anticipated composition. The results of the percentages of the Mn in γ-Al2O3 were also confirmed with ICP-OES (Table 1). Therefore, the Mn percentage reports of both EDX and ICP-OES display high accuracy toward anticipated percentage reports.

Fig. 4: 
SEM images of (a) γ-Al2O3, (b) 2.5% Mn/γ-Al2O3, (c) 5% Mn/γ-Al2O3 and (d) 7.5% Mn/γ-Al2O3 catalysts.
Fig. 4:

SEM images of (a) γ-Al2O3, (b) 2.5% Mn/γ-Al2O3, (c) 5% Mn/γ-Al2O3 and (d) 7.5% Mn/γ-Al2O3 catalysts.

Table 1:

BET, EDX and ICP-OES results of the γ-Al2O3 and Mn/γ-Al2O3 catalysts.

Catalyst Surface area (m2 g−1) Pore volume (cm3 g−1) Pore size (nm) EDX Mn wt% ICP-OES Mn wt%
γ-Al2O3 295.0 0.4619 7.16
2.5.% Mn/γ-Al2O3 167.6 0.3827 9.13 2.33 2.48
5% Mn/γ-Al2O3 138.2 0.3561 10.71 5.9 5.39
7.5% Mn/γ-Al2O3 107.8 0.3022 11.21 7.57 7.46
10% Mn/γ-Al2O3 89.4 0.2738 12.92 10.23 9.18
12.5% Mn/γ-Al2O3 73.9 0.2159 14.03 12.42 12.48
15% Mn/γ-Al2O3 61.2 0.1139 14.97 15.64 14.94

Transmission electron microscopy (TEM)

The TEM images of γ-Al2O3, Mn/γ-Al2O3 catalysts and their corresponding particle diameter histograms are displayed in Figs. 5 and S3 (SI). The TEM image of γ-Al2O3 displays properties of a highly aggregated, spherical shaped material with uniform particle diameter of 12.8 nm in average. Upon incorporation of Mn to γ-Al2O3, an alteration in particle shape from spherical to rod shaped particle was perceived. This is due to the elongation of the γ-Al2O3 particles, which suggests that Mn/γ-Al2O3 catalysts are new materials with unique properties. In addition, a decrease in particle diameter was also perceived, which became more perceptive with increase in Mn loading. This is also in correlation with the XRD results in which Mn loading resulted to broadening of the γ-Al2O3 peaks suggesting a decrease in particle sizes. The average particle diameters of 2.5%, 5%, 7.5%, 10%, 12.5% and 15% Mn/γ-Al2O3 were 10.6 nm, 9.8 nm, 7.7 nm, 7.2 nm, 6.3 nm and 5.7 nm, respectively.

Fig. 5: 
TEM images of (a) γ-Al2O3, (c) 2.5% Mn/γ-Al2O3, (e) 5% Mn/γ-Al2O3 and (g) 7.5% Mn/γ-Al2O3 and particles diameter histograms, (b) γ-Al2O3, (d) 2.5% Mn/γ-Al2O3, (f) 5% Mn/γ-Al2O3 and (h) 5% Mn/γ-Al2O3 catalysts.
Fig. 5:

TEM images of (a) γ-Al2O3, (c) 2.5% Mn/γ-Al2O3, (e) 5% Mn/γ-Al2O3 and (g) 7.5% Mn/γ-Al2O3 and particles diameter histograms, (b) γ-Al2O3, (d) 2.5% Mn/γ-Al2O3, (f) 5% Mn/γ-Al2O3 and (h) 5% Mn/γ-Al2O3 catalysts.

X-ray photoelectron spectroscopy

The XPS spectra of the 2.5% Mn/γ-Al2O3 catalyst is shown in Fig. 6. The survey spectrum (Fig. 6a) shows the presence of Al, O and Mn at 74 eV, 535 eV and 650 eV, respectively. The high resolution spectrum of Al 2p (Fig. 6b) displays four distinctive peaks at 74.5 eV, 74.1 eV, 72.7 eV and 70.1 eV corresponding to Al2O3, AlO, Al2O3 and Al(OH)3, respectively. The presence of the multiple oxidation states of Al element suggests that the surface bonding is not uniform due to Mn doping which often results to surface defects. Even though the XRD analysis showed the occurrence of MnO only, the XPS spectrum of the Mn 2p (Fig. 5c) displays various oxidation states of Mn (MnO, Mn2O3 and MnO2) which also resulted from alteration in bonding upon incorporation to γ-Al2O3 support. The XPS spectrum of O 1s displays three peaks at 530.2 eV, 531.1 eV and 531.9 eV emanating from the crystal lattice, surface hydroxide and oxygen defect sites with low oxygen coordination [23, 24], respectively.

Fig. 6: 
XPS spectra of (a) full range 2.5%/Mnγ-Al2O3, (b) Al 2p, (c) Mn 2p and (d) O 1s of 2.5% Mn/γ-Al2O3 catalysts.
Fig. 6:

XPS spectra of (a) full range 2.5%/Mnγ-Al2O3, (b) Al 2p, (c) Mn 2p and (d) O 1s of 2.5% Mn/γ-Al2O3 catalysts.

Brunauer–Emmet–Teller (BET) surface analysis

The surface area is a crucial factor in heterogeneous catalysis. The BET surface analysis was performed to investigate surface areas, pore volumes and pore sizes of the as synthesized Mn/γ-Al2O3 catalysts. The large surface area provides more active sites which subsequently enhances absorption of the cyclohexane to the surface of the catalyst [25]. The BET isotherms of Mn/γ-Al2O3 catalysts are shown in Figs. 7 and S4. The isotherms display characteristics of the type IV BET isotherm with a hysteresis loop, proving the existence of mesopores on the Mn/γ-Al2O3 catalysts [26]. The surface areas, pore volumes and pore sizes of the Mn/γ-Al2O3 are listed in Table 1. The results show that the incorporation of the Mn to γ-Al2O3 resulted to a decrease in surface area and pore volume and an increase in pore sizes. The effect is more perceptive with increasing Mn ratio to γ-Al2O3. This observation suggests that the Mn is deposited to the pores of the γ-Al2O3 support.

Fig. 7: 
BET isotherms of (a) γ-Al2O3, (c) 2.5% Mn/γ-Al2O3, (e) 5% Mn/γ-Al2O3 and (g) 7.5% Mn/γ-Al2O3 catalysts.
Fig. 7:

BET isotherms of (a) γ-Al2O3, (c) 2.5% Mn/γ-Al2O3, (e) 5% Mn/γ-Al2O3 and (g) 7.5% Mn/γ-Al2O3 catalysts.

Oxidation of cyclohexane

Percentage conversion

The liquid oxidation of cyclohexane was investigated using various percentages of Mn/γ-Al2O3 and ozone 20 ± 1 °C and 1 atm of temperature and pressure, respectively. The GC results of the cyclohexane before oxidation, reaction mixture after 30 min oxidation and reaction mixture after 1 h oxidation are shown in Fig. 9. The results show that there is only one observed peak before oxidation corresponding to cyclohexane and are three peaks appearing after 30 min oxidation emanating from cyclohexane, cyclohexanol and cyclohexanone, whereas there are only two peaks observed after 1 h attributed to cyclohexane and cyclohexanone. The GC was equipped with MS to qualify the GC peaks and the MS spectra of cyclohexanol, cyclohexanone and cyclohexanone are displayed in Fig. S5. The reaction mixture was further characterized with FT-IR. Figure S6 displays FT-IR spectra of cyclohexane before oxidation, reaction mixture after 30 min oxidation and reaction mixture after 1 h oxidation. There, is no C=O and O–H peaks observed before oxidation. However, after 30 min both C=O and O–H peaks can be observed, whereas after 1 h only C=O peak is observed which is correlation with the GC-MS results. Figure 8 and Table 2 summarizes percentage conversions and selectivities of cyclohexane to cyclohexanol and cyclohexanone after 1 h of reaction time. The catalysts and the cyclohexane were left in the dark for 1 h to reach adsorption-desorption equilibrium. Prior to studying catalysed reactions, the blank oxidation was performed. The comparison of the percentage conversions between blank and pristine γ-Al2O3 catalysed reactions suggest that the pristine γ-Al2O3 is catalytically active in oxidation of cyclohexane. The percentage conversion obtained in blank oxidation was 9%, whereas 16% was recorded when γ-Al2O3 was used after 1 h. This was anticipated since γ-Al2O3 has been reported in literature to exhibit catalytic activity toward various processes [27, 28]. The percentage conversions obtained from the Mn doped γ-Al2O3 catalysed reactions suggest that the Mn functionalised γ-Al2O3 catalysts are more catalytically active than their unfunctionalized γ-Al2O3 counterpart.

Fig. 8: 
Plots of (a) percentage conversion, (b) products selectivities of the blank, γ-Al2O3 and Mn/γ-Al2O3 catalysed reactions.
Fig. 8:

Plots of (a) percentage conversion, (b) products selectivities of the blank, γ-Al2O3 and Mn/γ-Al2O3 catalysed reactions.

Fig. 9: 
Gas chromatograms of cyclohexane, (a) before oxidation, (b) after 30 min oxidation and (c) after 1 h oxidation using 2.5% Mn/γ-Al2O3.
Fig. 9:

Gas chromatograms of cyclohexane, (a) before oxidation, (b) after 30 min oxidation and (c) after 1 h oxidation using 2.5% Mn/γ-Al2O3.

Table 2:

Percentage conversions and products selectivities of cyclohexane oxidation in blank, γ-Al2O3 catalysed and Mn/γ-Al2O3 catalysed reactions.

Catalyst Conversion (%) Selectivity (%)
Cyclohexanol (%) Cyclohexanone (%)
Blank 5 14 86
9 100
γ-Al2O3 11 7 93
16 100
2.5% Mn/γ-Al2O3 14 9 91
33 100
5% Mn/γ-Al2O3 10 11 89
24 100
7.5% Mn/γ-Al2O3 7 6 94
17 100
10% Mn/γ-Al2O3 6 7 93
15 100
12.5% Mn/γ-Al2O3 4 10 90
13 100
15% Mn/γ-Al2O3 5 13 87
11 100
  1. The shaded results are for 1 h reaction time while the unshaded results are for 30 min reaction time.

The percentage conversions obtained using 2.5%, 5%, 7.5%, 10%, 12.5%, 15% Mn/γ-Al2O3 were 33%, 24%, 17%, 15%, 13%, 11%, respectively. The results show that 2.5% Mn/γ-Al2O3 exhibited higher catalytic activity than its analogous. The decrease in catalytic activity with increasing Mn loading in γ-Al2O3 can be explained by surface area effect. The BET results revealed that an increase in Mn loading resulted to a decrease in surface area of the catalysts. A decrease in surface area results to a limited number of the active sites, hence lower catalytic activity.

Percentage selectivity

Typically, the oxidation of cyclohexane proceeds through the free radical chain to yield the mixture of cyclohexanol and cyclohexanone (KA oil) and other side products such as hexanedioic acid, cyclohexyl hydroperoxide and dicyclohexyl adipate [29, 30]. The summary of the percentage selectivities of both uncatalysed (blank) and catalysed oxidation reactions obtained from GC-MS is shown in Fig. 8 and Table 2. The evaluation of the results shows that cyclohexanol and cyclohexanone were the only oxidation products identified with cyclohexanone being the major product after 30 min of oxidation. However, after 1 h only cyclohexanone was identified as the reaction product. This could be attributed to the ambient reaction constitutes and the short oxidation time applied in this study rather than the catalysts used. This is because the similar results were also observed for blank oxidation. In addition, from the results obtained it can be concluded that the formed cyclohexanol is further oxidised to cyclohexanone. This is because cyclohexanol was not identified after 1 h of oxidation. This is in good agreement with the literature [29], [30], [31]. The percentage selectivity obtained from blank oxidation were 14% and 86% to cyclohexanol and cyclohexanone, respectively at pH 3 after 30 min. The selectivities obtained using 2.5%, 5%, 7.5%, 10%, 12.5%, 15% Mn/γ-Al2O3 were 14%, 7%, 9%, 11%, 6%, 8%, 10% and 13% towards cyclohexanol and 86%, 93%, 91%, 89%, 94, 93%, 90% and 87% to cyclohexanone, respectively after 30 min oxidation. After 1 h, only cyclohexane and cyclohexanone were identified in GC-MS (Fig. 8) and FT-IR. The evaluation of the selectivity results shows that there is no observable pattern in percentage selectivity to both cyclohexanol and cyclohexanone with respect to Mn loading after 30 min, suggesting that Mn has no barring effect on the percentage selectivity.

Electron paramagnetic resonance studies

The hydroxide and carbon centred radicals quenching experiments were performed using electron paramagnetic resonance (EPR). The 5,5-dimethyl-1-pyrroline N-oxide (DMPO) and α-phenyl-tert-butyl nitrone (PBN) in DMSO were used as the OH and carbon radicals trapping agents, respectively. The cyclohexane was ozonized in the presence of 2 mL of 0.1 M of DMPO and PBN separately for 5 min in the absence and the presence of the 0.2 g of the catalysts followed by analysing the reaction mixture for OH signal using EPR. Figure 10 displays the EPR results of the blank ozonation, γ-Al2O3, 2.5% Mn/γ-Al2O3, 5% Mn/γ-Al2O3, 7.5% Mn/γ-Al2O3, 10% Mn/γ-Al2O3, 12.5% Mn/γ-Al2O3 and 15% Mn/γ-Al2O3. In the presence of DMPO, the results showed that the presence the catalysts play a profound role in the production of the OH species. Typically, there were no OH species generated in the absence of the catalysts. However, in the presence of pristine γ-Al2O3 weak OH signals were observed. When 2.5% Mn/γ-Al2O3 catalyst was used instead, the OH peak signal intensity was significantly induced, followed by gradually decrease with increasing Mn doping from 5% to 15%. These observations show that the pristine γ-Al2O3 and the Mn/γ-Al2O3 catalyses the decomposition of ozone to OH species, however the 2.5% Mn/γ-Al2O3 catalyst is more catalytically active towards ozone decomposition to OH species than its analogous.

Fig. 10: 
EPR spectra of the blank ozonation, γ-Al2O3 and Mn/γ-Al2O3, catalysed reactions in the presence of (a) DMPO and (b) PBN.
Fig. 10:

EPR spectra of the blank ozonation, γ-Al2O3 and Mn/γ-Al2O3, catalysed reactions in the presence of (a) DMPO and (b) PBN.

The higher catalytic ozone decomposition aptitude of the 2.5% Mn/γ-Al2O3 catalyst than the γ-Al2O3 support can be visualised from the metal-support interaction synergy. The metal-supported catalysts possess synergistic effect which results to the development of an interface between the support and the transition metal. The interface possesses unique properties compared and often changes the properties of both the metal and the support material. Therefore, the electron transfer between the metal and the support occurs. This effect which promotes a decrease in energy required for the formation of oxygen vacancy, which subsequently promotes the formation of the oxygen vacancies. This was also confirmed by multiple oxidation states of the Mn in 2.5% Mn/γ-Al2O3 observed from the XPS results. This phenomenon enhances the Mars van Krevelen reaction mechanisms, catalytic robustness and reverse oxygen spill over of the catalyst. The higher catalytic ozone decomposition aptitude of the 2.5% Mn/γ-Al2O3 catalyst than its Mn/γ-Al2O3 analogous is due to its higher surface area elucidated with BET analysis.

Radical scavengers

In addition to EPR results, radical trapping studies were performed using tert-butanol and tribromochloromethane (CBr3Cl) as hydroxide and carbon radicals’ quenchers, respectively. The tert-butanol is a strong hydroxide radical scavenger, which reacts with OH to highly inert intermediates therefore terminating the OH radicals chain reactions. Hence, in this study the generation of the OH radicals in oxidation of cyclohexane was evaluated by addition of tert-butanol (0.1 mol L−1, 1 mL). The results reveal that the addition of tert-butanol in catalytic oxidation of cyclohexane in the absence of the catalysts (blank) did not have much effect on oxidation efficiency (Fig. 11 and Table 3). The percentage conversions obtained in the absence of the catalysts were 5% and 8% after 30 min and 1 h, respectively. Nonetheless, when tert-butanol was added in the presence γ-Al2O3 and Mn/γ-Al2O3 catalysts, a significant decrease in cyclohexane percentage conversion was observed. Typically, the percentage conversion of 12% was obtained using 2.5% Mn/γ-Al2O3 catalyst upon addition of tert-butanol, which is lower than 33% obtained in the absence of tert-butanol. This phenomenon suggest that the OH radicals play an important role in oxidation of cyclohexane. In addition, the results reveal that cyclohexane oxidation in the absence of the catalyst is not instigated by OH radicals, since the addition of tert-butanol did not affect the oxidation efficiency. This suggests that in the absence of the catalyst the oxidation transpires through 1,3 dipolar insertion of the ozone to cyclohexane. This has been reported in literature [32, 33].

Fig. 11: 
Plots of (a) and (c) percentage conversion, (b) and (d) products selectivevities of the blank, γ-Al2O3 and Mn/γ-Al2O3 catalysed reactions.
Fig. 11:

Plots of (a) and (c) percentage conversion, (b) and (d) products selectivevities of the blank, γ-Al2O3 and Mn/γ-Al2O3 catalysed reactions.

Table 3:

Percentage conversions and products selectivities of cyclohexane oxidation in blank, γ-Al2O3 catalysed and Mn/γ-Al2O3 catalysed reactions in the presence of Tert-Butanol and CBr3Cl.

Tert-butanol CBr3Cl
Catalyst Conversion (%) Selectivity Conversion (%) Selectivity (%)
Cyclohexanol (%) Cyclohexanone (%) Cyclohexanol (%) Cyclohexanone (%)
Blank 5 6 94 5 5 95
9 100 8 100
γ-Al2O3 3 5 95 4 7 93
6 100 7 100
2.5% Mn/γ-Al2O3 8 7 93 9 6 94
12 100 17 100
5% Mn/γ-Al2O3 6 2 98 6 4 96
10 100 14 100
7.5% Mn/γ-Al2O3 4 9 91 4 5 95
8 100 12 100
10% Mn/γ-Al2O3 3 8 92 8 4 96
7 100 9 100
12.5% Mn/γ-Al2O3 1 7 93 3 6 94
5 100 7 100
15% Mn/γ-Al2O3 0 1 8 92
3 100 5 100
  1. The shaded results are for 1 h reaction time while the unshaded results are for 30 min reaction time.

The addition of the CBr3Cl (0.1 mol L−1, 1 mL) as the carbon centred radical scavenger revealed that the oxidation of cyclohexane does not encompass the production of the carbon centred radical. This is because there was no observable effect in oxidation efficiency upon the addition of the CBr3Cl. The results are in correspondence with the EPR results, since there were no EPR signals observed for carbon centred radicals. Nonetheless, when the CBr3Cl was added in γ-Al2O3 and Mn/γ-Al2O3 catalysed reactions, a noticeable decrease in percentage conversions were perceived, suggesting that the carbon centred radicals were formed in γ-Al2O3 and Mn/γ-Al2O3 catalysed cyclohexane reactions. This was also perceived in EPR studies.

Recycling studies

The recycling studies were performed using 2.5% Mn/γ-Al2O3 catalyst to investigate the stability of the catalysts. In this context, the catalyst was recovered, washed with ethanol for five times and reusable under similar conditions. The Results show that the catalyst exhibited tremendous stability for five cycles with minimal loss in catalytic activity (Fig. 12).

Fig. 12: 
Plots of (a) percentage conversion, (b) products selectivities of the used 2.5% Mn/γ-Al2O3 catalysed reactions.
Fig. 12:

Plots of (a) percentage conversion, (b) products selectivities of the used 2.5% Mn/γ-Al2O3 catalysed reactions.

X-ray photoelectron spectroscopy

The used γ-Al2O3 and 2.5% Mn/γ-Al2O3 catalyst were characterised with XPS to evaluate the changes in surface bonding of the catalysts after the oxidation of cyclohexane. The XPS spectra of the used γ-Al2O3 and 2.5% Mn/γ-Al2O3 are shown in Fig. 13. The Al 2p spectra of γ-Al2O3 revealed that the Al occurs as Al3+ only observed by the characteristic peaks at 74.5 eV, 72.7 eV and 70.1 eV. The O 1s spectrum of γ-Al2O3 displays three peaks at 531.9 eV, 531.1 eV and 530.2 eV emanating from the oxygen defect sites with low oxygen coordination, surface hydroxide and crystal lattice, respectively. The XPS full spectrum of 2.5% Mn/γ-Al2O3 displays Al, O, and Mn elements. Similarly, the Al 2p spectra of the used 2.5% Mn/γ-Al2O3 catalyst revealed that the Al also occurs as Al3+ [23, 24]. The Al2+ observed in the fresh catalyst was not observed in the Al 2p XPS spectrum of the used 2.5% Mn/γ-Al2O3. This effect might render Mars van Krevelen reaction and oxidation efficiency. However, the effect was not significant since the catalyst tremendous stability after five cycles. There is no much significant alterations observed between the XPS spectra of the Mn 2p of the fresh and reused catalysts. This suggests that the oxidation state of the Mn metal was not changed by the oxidation of cyclohexane. Similarly, there were no observable changes in O 1s spectra of the fresh and used catalysts. This observation elucidated that the surface state of the 2.5% Mn/γ-Al2O3 catalyst was not significantly altered during cyclohexane oxidation. In this regard, the 2.5% Mn/γ-Al2O3 demonstrated high stability, hence the observed reusability.

Fig. 13: 
XPS spectra of the used γ-Al2O3 and 2.5% Mn/γ-Al2O3 catalysts, (a) full range spectra, (b) Al 2p of γ-Al2O3, (c) O 1s of γ-Al2O3, (d) Al 2p of 2.5% Mn/γ-Al2O3, (e) Mn 2p of 2.5% Mn/γ-Al2O3 and (f) O 1s of 2.5% 2.5% Mn/γ-Al2O3.
Fig. 13:

XPS spectra of the used γ-Al2O3 and 2.5% Mn/γ-Al2O3 catalysts, (a) full range spectra, (b) Al 2p of γ-Al2O3, (c) O 1s of γ-Al2O3, (d) Al 2p of 2.5% Mn/γ-Al2O3, (e) Mn 2p of 2.5% Mn/γ-Al2O3 and (f) O 1s of 2.5% 2.5% Mn/γ-Al2O3.

Reaction mechanism

The reaction mechanism was established based on the GC-MS, EPR and the previous ozone and cyclohexane oxidation reactions. The ozone decomposition to hydroxide radicals (OH) at the surface of the catalysts has been reported in literature [34]. The cyclohexane oxidation instigates by hydrogen abstraction of hydrogen atom from cyclohexane by unsaturated metal centre and OH species resulting in the formation of cyclohexyl radical (eq. 3). Subsequently, the carbon centred cyclohexyl radical react with hydroxide radical to produce cyclohexanol (eq. 4) [15]. In another reaction the carbon centred parent subsequently reacts with ozone to produce cyclohexyl trioxide radical (eq. 5). The cyclohexyl trioxide radical abstract the H atom from cyclohexane to form cyclohexyl radical and cyclohexyl hydrogen trioxide (eq. 6). The cyclohexyl hydrogen trioxide decomposes at the surface of the MnO catalysts to form cyclohexyl radical, Mn2O3 and OH (eqs. 68). The Mn2O3 instigates the radical chain H abstraction of cyclohexane in a reaction that results in the formation of cyclohexanol and MnO (eqs. 9 and 10). The cyclohexyl radical formed in eq. (7) reacts with cyclohexane to produce cyclohexanol. Due to the difference in chemical stabilities between cyclohexane and cyclohexanol, once formed cyclohexanol rapidly oxidises to cyclohexanone (eqs. 11 and 12), hence only cyclohexanone was observed after 1 h oxidation.

(3) C 6 H 12 C 6 H 11
(4) C 6 H 11 + O H C 6 H 11 O H
(5) C 6 H 11 + O 3 C 6 H 11 O O O
(6) C 6 H 11 O O O + C 6 H 12 C 6 H 11 + C 6 H 11 O O O H
(7) C 6 H 11 O O O H + M n 2 + C 6 H 11 O + M n 2 + O O H
(8) M n 2 + O O H + M n 2 + M n 3 + + O H
(9) C 6 H 12 + M n 3 + C 6 H 11 + M n 2 + ( O H )
(10) C 6 H 11 + M n 2 + O H C 6 H 11 O H + M n 2 +
(11) C 6 H 11 O + C 6 H 12 C 6 H 11 O H + C 6 H 11
(12) C 6 H 10 ( ) O H + O H C 6 H 10 = O + H 2 O

Conclusion

In this study, we showed that Mn/γ-Al2O3 catalysts are highly catalytic active and selective for oxidation of cyclohexane using ozone. Among the catalysts studied 2.5% Mn/γ-Al2O3 exhibited higher catalytic activity than its analogous with percentage conversion of 33% after 1 h. An increase in metal content from 5% to 15% in 2.5% intervals was accompanied by a decrease in catalytic activity, which was caused by decrease in surface area. The catalytic activities of the catalysts emanated from the production of OH species from decomposition of ozone at the surface of the catalysts. The oxidation reaction transpired through the formation of the carbon centred radicals as intermediates. The cyclohexanol and cyclohexanone were only reaction product obtained after 30 min oxidation, however cyclohexanone was the only product obtained after 1 h. The addition of the tert-butanol and tribromochloromethane (CBr3Cl) as OH and carbon centred radical scavengers, respectively. The catalysts were highly recoverable and reusable without significant loss in activity. In summary, this study has laid a platform for potential use of Mn/γ-Al2O3 as catalysts for oxidation of cyclohexane in the presence of ozone.


Corresponding author: V. S. R. Rajasekhar Pullabhotla, Department of Chemistry, University of Zululand, Private Bag X1001, Kwa-Dlangezwa 3886, South Africa, Phone: + 27 35 902 6155, Fax: + 27 35 902 6568, e-mail:

Article note: A collection of invited papers based on presentations at the Virtual Conference on Chemistry and its Applications 2022 (VCCA-2022) held on-line, 8–12 August 2022.


Award Identifier / Grant number: Incentive Fund Grant (Grant No: 132468)

Award Identifier / Grant number: Research Developmental Grant for Rated Researchers

Acknowledgments

The authors acknowledge the EMU at the University of KwaZulu-Natal, Westville campus, for providing us access to their TEM facility. Rajasekhar Pullabhotla would like to acknowledge the Research and Innovation Office, UZ, for the financial support in the form of Project S 451/12 and the National Research Foundation (NRF, South Arica) for the financial support in the form of the Incentive Fund Grant (Grant No: 132468) and Research Developmental Grant for Rated Researchers (112145).

  1. Author contributions: All the authors have accepted responsibility for the entire content of this submitted manuscript and approved submission.

  2. Research funding: Iwate Prefecture and Yamaguchi Prefecture funded this study.

  3. Conflict of interest statement: The authors declare no conflicts of interest regarding this article.

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Supplementary Material

This article contains supplementary material (https://doi.org/10.1515/pac-2022-1110).


Published Online: 2023-03-08
Published in Print: 2023-03-28

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