Ramon
Oord
,
Joel E.
Schmidt
and
Bert M.
Weckhuysen
*
Inorganic Chemistry and Catalysis, Debye Institute for Nanomaterials Science, Utrecht University, Universiteitsweg 99, 3584 CG, Utrecht, The Netherlands. E-mail: b.m.weckhuysen@uu.nl
First published on 26th January 2018
The direct conversion of methane into methanol is considered as one of the holy grails in hydrocarbon chemistry and recently it was found that small pore zeolites, such as Cu-SSZ-13, Cu-SSZ-16 and Cu-SSZ-39, are active for this process. Here, we propose a reaction mechanism based on spectroscopic evidence for the methane-to-methanol reaction over Cu-SSZ-13 (Si/Al = 20). Using in situ FT-IR and operando UV-vis-NIR DRS, performed on a series of different Cu–ion-exchanged SSZ-13 zeolites, both a mono-nuclear site or a dimeric copper active site are consistent with the observations of this study. These proposed active site(s) are characterized by a νOH at ∼3654 cm−1 and a charge transfer (CT) transition at ∼29000 cm−1. We have further evidence to complete the full catalytic cycle to methanol, including the formation of the reaction intermediate Cu(CH3)(H2O), which is characterized by overtone transitions, i.e., a 2νCH at ∼4200 cm−1 and a 2νOH at ∼5248 cm−1. We found that increasing the pre-oxidation temperature from 450 °C to 550 °C resulted in a 15% increase in methanol production, as well as a concomitant increase of the 29
000 cm−1 CT transition. Furthermore, Cu-exchanged SSZ-13 zeolites, which perform well in the NH3-SCR reaction at 200 °C (the low temperature regime), also show a high activity in the methane-to-methanol reaction and vice versa, leading us to believe that this material has a similar if not the same active site for both the catalytic reduction of NO and the stepwise reaction towards methanol.
The methane activation procedure over Cu-based zeolite materials consists of four basic steps, which need to be recycled: i) oxidation of the zeolite-based material with oxygen or N2O; ii) introducing methane into the zeolite material; iii) addition of water, which can be done in either the liquid or gas phase, to obtain the reaction products, such as methanol; iv) re-establishing the initial state of the material through high-temperature regeneration, which may be combined with step i. This procedure leads to relatively low amounts of side products, but the main drawback is that it is in essence a stepwise process (i.e., a one turnover process), and not a catalytic cycle in which the active site is repeatedly regenerated.9 van Bokhoven et al. have recently presented a direct stepwise method for converting methane into methanol with high selectivity over a copper-containing zeolite, based on partial oxidation with water, but this still is stepwise and not a continuous process.17
Identification of the active site in copper zeolites is still a much-debated topic.18 Schoonheydt et al. were the first to report that Cu-based zeolite materials (Cu-ZSM-5 and Cu-MOR) could activate methane-to-methanol, and using UV-vis proposed a comparison to the pMMO enzyme in that the methane activating core was a dinuclear bis(μ-oxo)dicopper species.8,19 Schoonheydt, Sels, Solomon, and coworkers, later proposed the methane-activating core to be a mono(μ-oxo)dicopper(II) species identified using resonance Raman spectroscopy and DFT calculations.13,20 More recently Grundner et al. proposed a trinuclear copper-oxo cluster in Cu-ZSM-5, based on theoretical analysis supported by EXAFS analysis.21,22 For Cu-MOR, Vanelderen et al. proposed two distinct [Cu–O–Cu]2+ sites to be responsible for methane activation.23 These sites are believed to be at two separate locations; one at the intersection of the side pocket with the 12 MR channel, and the other at the intersection of the side pocket with the 8 MR channel, a trinuclear copper-oxo cluster was also proposed as the active site on Cu-MOR.21 Tomkins et al. however, conclude, based on their in situ EXAFS study on Cu-MOR, that the active sites are small dehydrated clusters of copper oxides, and do not necessarily need to be di- or tri-copper sites.24 They found no proof of spectroscopic signatures assigned to μ-oxo copper species, which would show up around 20000 cm−1. They did however see a band appear at 13
500 cm−1 and possibly a shoulder at 16
750 cm−1, which are both consistent with Cu2+ species. They also find very small particles using TEM on samples active in oxygen at 200 °C, suggesting Cu-agglomeration.
Wulfers et al. investigated different types of Cu-exchanged zeolites and zeotype materials, showing that small pore zeolites and related materials, such as Cu-SSZ-13, Cu-SSZ-16, Cu-SSZ-39 and Cu-SAPO-34, also produce methanol from methane and water.9 For the small pore zeolites, the state and location (e.g., mono-, di- or tri-nuclear25 copper sites) are still unclear, but it is possible that the active site is the same as the active site for the low temperature catalytic NOx decomposition.9,26 In another study Kulkarni et al. showed with their DFT study that for 8MR zeolites the active site might also be a mono-nuclear site; in the form of a Cu(OH)+ species, although they indicate that <11% of the total species are in the form of [Cu(OH)]+, making Cu(OH)+ species a minority species and consequently difficult to identify.27 Very recently, Ipek et al. identified trans-μ-1,2-peroxo dicopper(II) ([Cu2O2]2+) and mono-(μ-oxo) dicopper(II) ([Cu2O]2+) using synchrotron X-ray diffraction, in situ UV-vis, and Raman spectroscopy and theory calculation for Cu-SSZ-13 and Cu-SSZ-39. (Si/Al = 12).28
We experimentally show that plausible active sites in Cu-SSZ-13 (Si/Al = 20) for methane into methanol activation can be a mononuclear Cu2+ site as well as a dimeric copper species, as discussed above. To enable this conclusion, zeolite SSZ-13 materials were ion exchanged with Cu2+ using slight variations in the exchange procedure; which resulted in differences in copper loadings as well as preferential cation locations. To study the influence of the exchange process during the methane-to-methanol reaction, all materials were analyzed using operando UV-vis spectroscopy as well as separately conducted in situ UV-vis-NIR diffuse reflectance spectroscopy and in situ FT-IR spectroscopy. Furthermore, a link has been established between low temperature NH3-SCR of NO activity at 200 °C and the TON for methane-to-methanol production, further strengthening the hypothesis that either a mononuclear copper site or a dimeric copper site are responsible for methane activation. This combined information allowed us to postulate a reaction pathway during relevant reaction conditions, including the formation of a plausible reaction intermediate, Cu(CH3)(H2O).
To gain the Na form of the zeolite a three-fold ion exchange with 1.0 M NaNO3 (Acros organics, 99%+ for analysis ACS) (20 mL g−1) was performed for 2 h at 75 °C. The sample was then washed with deionized water, followed by another calcination at 550 °C for 2 h in air, using a ramp of 5 °C min−1. Copper ion exchange was performed using different amounts of H-SSZ-13 or Na-SSZ-13 using either CuSO4·5H2O (Merck ACS, ISO, Reag. Ph Eur) or Cu(II)acetate·H2O (Sigma-Aldrich, puriss p.a.). The exact exchange details can be found in Table 1, which also provides an overview of the different Cu-SSZ-13 materials under study. After each procedure, the resulting Cu-SSZ-13 material was washed with demineralized water and dried at 60 °C overnight. Calcination was performed in a static oven with the following temperature program: heat from room temperature to 120 °C in 1 h, hold for 30 min, then heat to 550 °C over 7 h 10 min and hold for 4 h and finally cool to room temperature.
Sample code | Na or H | Precursor | Molarity (mol L−1) | Temperature (°C) | Liquid/solid (ml g−1) | Duration (h) | %wt Cu |
---|---|---|---|---|---|---|---|
Cu-1.50-Na | Na (full 3× exchange) | Cu(II) acetate | 0.002 | RT | 317 | 16 | 1.5 |
Cu-1.38-Na | Na (full 3× exchange) | CuSO4 | 0.1 | 80 | 50 | 2 | 1.38 |
Cu-1.21-Na | Na (full 3× exchange) | CuSO4 | 0.05 | 80 | 50 | 2 | 1.21 |
Cu-1.15-Na | Na (full 3× exchange) | CuSO4 | 0.025 | 80 | 50 | 2 | 1.15 |
Cu-1.14-H | H | CuSO4 | 0.1 | 80 | 50 | 2 | 1.14 |
Cu-1.03-Na | Na (full 3× exchange) | CuSO4 | 0.1 | RT | 1000 | 16 | 1.03 |
Cu-0.95-Na | Na (full 3× exchange) | CuSO4 | 0.1 | 60 | 1000 | 16 | 0.95 |
Cu-0.93-Na | Na (full 3× exchange) | Cu(II) acetate | 0.0011 | RT | 317 | 16 | 0.93 |
Cu-0.91-Na | Na (1× partial exchange) | CuSO4 | 0.1 | 80 | 50 | 2 | 0.91 |
In this work, a series of Cu-exchanged zeolites have been prepared, using different ion exchange methods. Table 1 summarizes the Cu-SSZ-13 samples under study, including their sample code, preparation procedure and corresponding copper loading. The as-prepared H-SSZ-13 zeolite material used for the preparation of the Cu-based SSZ-13 zeolites exhibits a typical XRD CHA pattern, as illustrated in Fig. S2A,† confirming the good crystallization and phase purity of the starting H-SSZ-13 material. Note that the reflections appear at different 2 theta values than usual, since we are using a Co X-Ray source instead of the widely used Cu X-Ray source. The incorporation of Na or Cu did not result in any obvious modifications to the CHA structures (Fig. S2A†), with only small lattice parameter changes due to the increased size of the counter cation. No copper (or copper oxide) peaks were detected in the XRD patterns after copper exchange. NH3-TPD measurements were taken to probe the acidity of the zeolite (Fig. S2B†). In previous studies,30–32 the low temperature peak (LT) is assigned to weakly absorbed NH3, such as physisorbed NH3 and NH3 adsorbed on weak Lewis acid sites. The high temperature peak (HT), starting around 350 °C, is assigned to NH3 adsorbed on Brønsted acid sites. NH3-TPD shows a disappearance of the HT peak after ion exchange with Na, as this will remove the Brønsted acidity. The Cu/Al ratios of the different Cu-SSZ-13 samples were determined by inductively coupled plasma (ICP-OES), which showed copper loadings between 0.9 and 1.3 wt%, and resulting Cu/Al ratios of 0.5–0.9, as summarized in Table 1.
UV-vis-NIR diffuse reflectance spectroscopy (DRS) was collected using a Varian Cary 500 UV-vis-NIR spectrometer equipped with a DRS accessory to allow collection in the diffuse reflectance mode, against a pure white reference standard. The spectra were collected between 4000–50000 cm−1 with a data interval of 10 cm−1 and at a scanning rate of 6000 cm−1 min−1. The UV-vis-NIR DRS spectra were corrected for the detector/grating and light source changeover steps at 11
400, 12
500 cm−1 and 28
570 cm −1, respectively.
Inductively coupled plasma-optical emission spectrometry (ICP-OES) was measured using a SPECTRO CIROSCCD instrument. Samples were first dissolved using an aqua regia with HF solution at 90 °C overnight, after which it was cooled down to RT and neutralized using boric acid. After this the solutions were diluted to yield the appropriate concentrations.
Temperature programmed desorption of ammonia (NH3-TPD) was performed on a Micromeritics Autochem II 2920 equipped with a TCD detector. Prior to TPD, 0.1 g of Cu-exchanged zeolite was first out gassed in He for 1 h at 600 °C with a heating ramp of 10 °C min−1. Ammonia was adsorbed at 100 °C until saturation, followed by flushing with He for 120 min at 100 °C. The ammonia desorption was monitored using the TCD detector until 600 °C with a ramp of 5 °C min−1, using a flow of 25 mL min−1.
A Perkin-Elmer 2000 FT-IR instrument and a high temperature flow through cell equipped with KBr windows were used to obtain in situ FT-IR spectra. The sample (∼15 mg) was ground and pressed into a self-supported wafer. The Cu-exchanged zeolite wafer was placed in a holder for transmission FT-IR measurements. For each spectrum, 32 scans were recorded with a 4 cm−1 resolution. Samples were dehydrated in a flow of either O2 or He for 2 h, while the measurements were taken at 150 °C. For sake of clarity, absorption values are normalized to sample pellet weights.
Ar physisorption on the parent material was performed with an automated gas sorption system, Micromeritics TriStar 3000. Before the measurements, the samples were outgassed for 16 h at 380 °C under vacuum. Measurements were performed using Ar at −196 °C. The external surface area, micropore surface area and micropore volume were determined by applying the t-plot method.
In another series of experiments, catalytic testing and operando UV-vis spectroscopy experiments were simultaneously performed in a specially designed quartz fixed-bed reactor equipped with a UV-vis transparent window. Details of the experimental set-up can be found in several publications of our group.33–37 The overall reaction procedure consists of three steps; oxidation of the zeolite-based material (16 mL min−1 O2) at 450 or 550 °C (heating ramp of 5 °C min−1, hold for 2 h), after which the sample is cooled down to 60 °C. At 60 °C the flow is switched to methane in N2 (6 mL min−1 methane in 10 mL min−1 N2). After 20 min, the temperature is increased to 200 °C (heating ramp of 5 °C min−1). After 20 min at this temperature, the flow is switched to N2 as carrier gas through a saturator containing water at 20 °C, to perform a gas phase extraction of the methanol. Operando UV-vis spectra were obtained using an AvaSpec 2048 L spectrometer (Avantes, 2048 pixel 200 μm CCD detector, 200–1100 nm) connected to a high-temperature UV-vis optical fiber probe (Avantes, 7 × 400 μm fibers), which was used to collect the operando spectra in reflection mode. On-line analysis of the reactants and reaction products was performed using an Interscience Compact GC, equipped with an Rtx-wax and Rtx-1 column in series and an Rtx-1, Rt-TCEP and Al2O3/Na2SO4 in series, both connected to an FID detector. To avoid condensation in the reaction system, all gas lines were heated to 150 °C.
The same experiment was also performed using He instead of O2, to show that an oxidant is necessary in the activation step, and the UV-vis spectra during the heat treatment can be found in Fig. S1.† Initially, it appears that there is still a band developing at 29000 cm−1, however, while maintaining that temperature and upon cooling down, this band diminishes, as is clear from Fig. S1D† (compare Fig. 1D to S1D or see Fig. S3†). Upon addition of methane, we do see some changes in the UV-vis spectra, but no appreciable change at the 29
000 cm−1 absorption, in contrast to the results in the O2 experiment. It is known that copper can auto-reduce in the presence of He,38,39 which might occur in the activation step of this experiment, as the d–d region shows a weaker absorption. In our experiments we found that an oxidizing agent is needed to create the active site for methane-to-methanol activation in Cu-SSZ-13 as we did not observe any methanol product in the absence of the oxidant, and here we present spectroscopic results to explain the underlying reasons for these phenomena. This result is different from Ipek et al. who show that show the active site can be generated in both O2 as well as He in Cu-SSZ-13, and we are unable to account for this based on our experimental findings.28
A similar experiment was performed using 550 °C as the pre-oxidation temperature. Upon reaching 550 °C, the band at 29000 cm−1 has a higher absorption compared to the Cu-exchanged zeolite at 450 °C (ESI,† Fig. S3D). From the online GC data, we know pre-oxidation at 550 °C increases the methanol production, as summarized in Table 1. Since we are measuring using operando conditions, linking these results directly shows that the UV-vis absorption at 29
000 cm−1 is directly correlated with the production of methanol. A comparison of Fig. S3B and D† clearly shows that the band at 29
000 cm−1 is more pronounced when we heat the Cu-exchanged zeolite to 550 °C than 450 °C, and in both cases the band diminishes upon contact with methane.
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Fig. 3 Steady state NO conversions, 50 mg Cu-exchanged zeolite, 1000 ppm NO, 1000 ppm NH3, 5% O2, balanced by He, GHSV 100![]() |
Name | Methanol (μmol g−1) 450 °C | TON (mol mol−1) 450° | Methanol (μmol g−1) 550 °C | TON (mol mol−1) 550 °C |
---|---|---|---|---|
ND = not determined. | ||||
Cu-1.50-Na | 7.578 | 0.033 | ND | ND |
Cu-1.38-Na | 7.610 | 0.036 | ND | ND |
Cu-1.21-Na | 8.248 | 0.045 | 9.04 | 0.049 |
Cu-1.15-Na | 7.192 | 0.041 | ND | ND |
Cu-1.14-H | 6.301 | 0.036 | 7.55 | 0.043 |
Cu-1.03-Na | 5.283 | 0.034 | ND | ND |
Cu-0.95-Na | 4.921 | 0.034 | 7.48 | 0.052 |
Cu-0.93-Na | 5.425 | 0.038 | ND | ND |
Cu-0.91-Na | 4.660 | 0.034 | ND | ND |
Most Cu-zeolites under study have been pre-treated at temperatures around 450 °C to yield the active state of the Cu-exchanged zeolite.9,25,40 It was found that for the samples we tested that increasing the pre-oxidation temperature from 400 to 450 to 550 °C using dry O2 resulted in increasing methanol production. Fig. 2B shows this increase in methanol production for the Cu-0.95-Na Cu-exchanged zeolite, which is ∼15% increase in μmol methanol g−1 zeolite, when going from 400 to 550 °C (Table 2). Recently, Ipek et al. showed that increasing the pre-oxidation temperature from 200 to 550 °C with N2O as oxidant for Cu-SSZ-13 increased the methanol production significantly, and our results are consistent with this observation as shown in Fig. 2B and Table 2.41 After activating the samples in He instead of O2, methanol levels were below the detection limit of the GC. This again contrasts with the results of Ipek et al.,28 but is in line with the results of Pappas et al., who showed a much lower methanol production upon activation with just He.42
All synthesized Cu-SSZ-13 samples have also been tested for their activity in the low temperature NH3-SCR of NOx reaction, and the results can be found in Fig. 3. NO conversions of the better performing catalysts are typical for these catalysts.43–45 Both Cu-0.93-Na and Cu-1.50 show conversions below what is normally seen for these catalysts. Examining the UV-vis-NIR-DRS results of the hydrated samples explains this result as both contain a large amount of CuxOy species, which are known to be responsible for unselective NH3-oxidation, with a detrimental influence on the NH3-SCR of NOx reaction.46
Fig. 4 demonstrates the correlation between activity in the NH3-SCR reaction at 200 °C and activity in the methane-to-methanol reaction, leading us to believe that this material has a similar if not the same active site(s) for both reactions. For low temperature NH3-SCR it is already known that there is more than one type of active site, including both mononuclear sites as well as Cu-dimeric sites, and [Cu(OH)]+ could be one of these.47,48 Our data shows that this is likely the case for the methane-to-methanol reaction, that more than one active site exists. Paolucci et al. demonstrated that under low temperature NH3-SCR reaction conditions that mobilized copper ions can travel through zeolite windows and form transient ion pairs that participate in an O2-mediated Cu(I) → Cu(II) redox step.48 This type of behavior was not reported before and might also have an influence on our understanding of the active site for the methane-to-methanol reaction, and suggests that there may be a highly dynamic and transient nature to the active site, underscoring the necessity of operando studies to unravel the nature of the active site in action. The direct consequence for this paper is that we cannot distinguish monomeric Cu(OH)+ sites from dimeric copper species like (Cu2O2)2+ and (Cu2O)2+ under these reaction conditions, though it is likely that both may be present and active. As is apparent from our turn over numbers (TON), only a small fraction of the copper participates in this reaction.
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Fig. 5 (A) UV-vis-NIR DRS spectra of Cu-SSZ-13 in hydrated form. B) UV-vis-NIR DRS spectra of Cu-SSZ-13 after dehydration using dry O2 at 450 °C for 2 h. C) and D) NIR zoom in of the UV-vis-NIR DRS spectra of the Cu-exchanged zeolite C) hydrated spectra, D) dehydrated spectra. The UV-vis-NIR-DRS spectra of all samples can be found in Fig. S4 (ESI†). |
Sample | Transitions (cm−1) | |||||||
---|---|---|---|---|---|---|---|---|
a d–d transition. b Ligand-to-metal charge transfer. c Charge transfer. These bands are based on the spectra presented in Fig. 5 and S4 (ESI). | ||||||||
Cu-SSZ-13 hydrated | 12![]() |
48![]() |
39![]() |
|||||
Cu-SSZ-13 O2 activated | 20![]() |
16![]() |
13![]() |
11![]() |
48![]() |
39![]() |
34![]() |
29![]() |
Cu-SSZ-13 (O2 activated)11 | 19![]() |
16![]() |
13![]() |
11![]() |
48![]() |
40![]() |
32![]() |
29![]() |
It has also been proposed that the extra bands at ∼29000 cm−1, in the case of Cu-SSZ-13, are due to the presence of either highly distorted CT transitions, or planar or bis(μ-η2
:
η2 peroxo) di-copper species ([Cu2(μ-η2
:
η2-O2)]2+).20 Combining these hypotheses with our results suggests that Cu-dimers might be the active site for methanol activation. Grundner et al., suggested that for Cu-MOR a broad band at 31
000–32
000 cm−1 belongs to a proposed trinuclear CuxOy complex, which is proposed to be the active site.25 We doubt the trinuclear CuxOy complex would fit in the SSZ-13 cage, and in all our samples no clear band at 31
000–32
000 cm−1 could be detected, making it unlikely the trinuclear CuxOy complex is responsible for the absorptions noted in the spectral region for Cu-SSZ-13 (29
000 cm−1). We do not find any evidence for the formation of mono(μ-oxo) dicopper species (25
000 cm−1) from UV-vis-NIR analysis on O2 activated Cu-SSZ-13 samples as well as in situ measurements during O2 activation, in agreement with Giordano et al.11,52
A more detailed view on the NIR region of the UV-vis-DRS spectrum can be found by comparing Fig. 5C and D and S4C and D,† as well as Table 4. This is the region where overtones and combination bands appear,11 which is a useful area if one wants to focus on the OH groups of the supports, as well as any C–H overtone vibrations which might arise during the addition of methane. In the hydrated state of the Cu-SSZ-13 spectra, the NIR region is dominated by the different combination and overtone bands of water and OH groups belonging to the zeolite. The pronounced band at 5240 cm−1 is normally assigned to the bending of bulk water (ν01OH + δ01H2O). All NIR overtone and combination bands are summarized in Table 4.53 The band at around 4540 cm−1 is ascribed to an OH combination band (ν01O1H + δ01O1H). During the oxygen activation, bands appearing and disappearing in the NIR region can easily be assigned to removal of water from the pores of the framework of the Cu-exchanged zeolite as bands for bulk water and water coordinated to copper are diminishing.
NIR abs. (cm−1) | Assigned to ref. 53, 54 | NIR abs. (cm−1) | Assigned to ref. 53, 54 |
---|---|---|---|
4546 | ν 01O1H + δ01O1H | 5980 | ν symCH3 (ν1) |
5060 | ν + δ01H2O adsorbed on Cu2+ | 6065 | ν a-symCH3 (ν1) |
5248 | ν 01OH + δ01H2O bending bulk water | 5213 | ν + δ01H2O |
6838 | ν 02H2O adsorbed on Cu2+ | 4200 | νCHx (ν +δ) |
7070 | ν 02OH (silanol) | 4300 | νCHx (ν + δ) |
7122 | ν 02O1H (Brønsted)/bulk water (∼7020) | ||
7313 | ν 02OH terminal (silanol) |
During the operando experiment, He activation instead of O2 activation leads a much less pronounced 29000 cm−1 band, as is evident from Fig. 6. Together with less pronounced 29
000 cm−1 band, the d-d region also shows a much lower absorption. This could very well be due to auto-reduction of the Cu2+ (d9) species towards Cu+ (d10) species, which would not give a d–d transition.
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Fig. 6 Dehydration of the Cu-1.14-H zeolite monitored by UV-vis-NIR DRS. The sample was thermally treated by flowing 100 ml min−1 of either 100% He or O2 for 2 h at 450 °C. Δabs = 0.12. |
A new set of measurements were performed in a different catalytic reactor, for which it was possible to isolate it from the outside atmosphere after reaction and cooling, allowing us to measure the samples on a UV-vis-NIR DRS spectrophotometer in the full spectral range of 4000–50000 cm−1. The resulting spectra are shown in Fig. 7. For these sets of in situ experiments, the samples were first oxidized in pure O2 at 450 °C for 2 h, then a UV-vis-NIR DRS spectrum was taken at RT, and consequently the same samples were exposed to methane at 200 °C for 2 h, without exposure to the atmosphere. Using this approach, we found that after the addition of methane a decrease of intensity in the absorption band at ∼29
000 cm−1 occurred, but together with this a few new absorption bands arose in the NIR region. The new vibrations in the NIR can be found in Fig. 7B, and can all be assigned to CHx species. The absorptions at 5980 and 6065 cm−1 were assigned to CH3 sym- and anti-symmetrical overtone vibrations (Table 4), showing that CH3 groups are present on the Cu-exchanged zeolite. Together with the CH3 overtone vibrations we also observe bands appearing in the 4200–4300 cm−1 range, which we assign to the combination bands of different CHx vibrations.54 Another interesting band is around 5213 cm−1, which can either be assigned to water or C
O.54 C
O is very unlikely since all the CH bonds must be broken, which would require a high energy input, and would most likely result in over-oxidation of methane into either CO or CO2. However, for Co-ZSM-5 formaldehyde was detected by Beznis et al., so C
O cannot be ruled out completely,55 though we could not observe any formaldehyde formation. According to Kulkarni et al., Cu(CH3)(H2O), is an intermediate in the activation of methane on the Cu(OH)+ site, and here we show experimental evidence for this proposed intermediate.27 Combining this with the previously observed Cu-dimers after O2-activation, both active sites are consistent with the results, but cannot be distinguished by UV-vis spectroscopy alone.
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Fig. 7 (A) UV-vis-NIR DRS spectra of Cu-1.21-Na after dehydration using dry O2 at 450 °C for 2 h, and after addition of methane at 200 °C for 1 h. B) Near infrared (NIR) region of the spectra before and after methane addition at 200 °C for 1 h. Bands designated * are due to the CH3 symmetrical and anti-symmetrical overtone vibrations, showing that at this point in the reaction, CH3 is present on the Cu-exchanged zeolites. As a reference one spectrum was added before methane addition. See Table 4 for the assignments of all NIR bands and Fig. S5 (ESI†) for the remaining samples. |
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Fig. 8 Dehydration of the zeolite monitored by in situ FTIR spectroscopy, spectra normalized to self-supporting wafer weight. The samples were thermally treated by flowing 100 ml min−1 of either 100% He (red spectrum) or O2 (all other spectra), for 2 h at 450 °C. FT-IR spectra taken at 150 °C. The band at 3654 cm−1 is assigned to [CuOH]+, which is only observed after heating in O2.56 |
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Fig. 9 μmol methanol produced per gram Cu-exchanged zeolite vs. the absolute absorbance height of the 29![]() ![]() |
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c7cy02461d |
This journal is © The Royal Society of Chemistry 2018 |