Next Article in Journal / Special Issue
How Topological Differences between Two Oxide Surfaces Determine Selectivity—The Case of the Dehydra-Decyclization of Tetrahydrofuran
Previous Article in Journal / Special Issue
Gold(III) Chloride-Mediated Transformation of Furfural to the trans-N,N-4,5-Diaminocyclopent-2-enones in the Presence of Anilines
 
 
Correction published on 7 August 2023, see Chemistry 2023, 5(3), 1719-1721.
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Vapor-Phase Oxidant-Free Dehydrogenation of 2,3- and 1,4-Butanediol over Cu/SiO2 Catalyst Prepared by Crown-Ether-Assisted Impregnation

Graduate School of Engineering, Chiba University, Yayoi, Inage, Chiba 263-8522, Japan
*
Author to whom correspondence should be addressed.
Chemistry 2023, 5(1), 406-421; https://doi.org/10.3390/chemistry5010030
Submission received: 31 January 2023 / Revised: 16 February 2023 / Accepted: 25 February 2023 / Published: 28 February 2023 / Corrected: 7 August 2023

Abstract

:
A silica-supported copper (Cu/SiO2) catalyst containing highly dispersed Cu nanoparticles was prepared via a crown-ether-assisted impregnation method. A 12-crown-4-ether-assisted Cu/SiO2 catalyst outperformed several Cu/SiO2 catalysts prepared with various organic additives in the dehydrogenation of 2,3- and 1,4-butanediol. It was found that the catalytic activity, i.e., the formation rate of acetoin from 2,3-butanediol and that of γ-butyrolactone from 1,4-butanediol, was proportional to the copper surface area.

Graphical Abstract

1. Introduction

With the growing demand for cosmetics, foods, and chemical products, the need for platform chemicals that become the backbone of these industries is rapidly increasing [1,2,3]. Since most platform chemicals are supplied from petrol-based compounds originating from depleting fossil fuels, the growing demand for platform chemicals increases fossil fuel consumption, potentially impacting the environment [4]. Shifting the origin of platform chemicals from fossil fuels to greener and more abundant resources such as biomass is considered a viable solution [5,6,7]. Due to this reason, the catalytic technology to transform biomass-derived compounds into value-added chemicals is economically and industrially valuable.
Butanediols, such as 2,3- and 1,4-butanediol (2,3- and 1,4-BDO), have received considerable interest due to the emerging sustainability of their bio-based production through the metabolic conversion of biomass [8,9,10,11,12,13,14]. In addition, 2,3- and 1,4-BDO derivatives have been used in the food, cosmetics, plasticizers, apparel, and polymer industries [8,12,15]. An efficient catalytic design that utilizes the sustainable nature of 2,3- and 1,4-BDO to obtain their derivatives is surely in line with the effort to alleviate fossil fuel consumption.
Catalytic oxidant-free dehydrogenation is a powerful strategy to obtain value-added BDO derivatives such as acetoin (3-hydroxy-2-butanone, AC) and γ-butyrolactone (GBL). AC is essential for flavor enhancers, fragrances, and chelating agents [16]. Meanwhile, GBL is a main precursor of pyrolidones, herbicides, and rubber additives [17,18]. Catalytic oxidant-free dehydrogenation is also greener than the conventional oxidation protocol using stoichiometric Cr or Mn salts [19,20,21,22,23]. Furthermore, many reports have suggested that oxidant-free dehydrogenation of biomass-derived alcohols is a green and atom-efficient strategy for hydrogen production [19,24,25,26,27,28,29]. Due to the above-mentioned reasons, a highly efficient catalyst for the oxidant-free dehydrogenation of BDO to AC and GBL is highly desired.
Extensive work has been dedicated to designing highly efficient catalysts for liquid-phase dehydrogenation of alcohol to aldehyde or ketone using precious and non-precious metals [30,31,32]. Inexpensive and abundant Cu metal emerges as efficient catalysts in numerous catalytic dehydrogenations of alcohols [33,34,35]. Therefore, Cu metal could be potentially employed as an efficient catalyst for oxidant-free dehydrogenation of BDO. As an alternative to liquid-phase catalysis, vapor-phase catalytic systems have been reported to offer some advantages, such as simple operation, separation, and catalyst recycling [36]. Combining these advantages with an efficient Cu catalyst for the dehydrogenation of BDO is highly beneficial from an industrial and environmental point of view.
Cu-based catalysts have been employed for the dehydrogenation of BDOs. Recently, supported Cu catalysts, such as Cu/SiO2 [37,38], Cu-Al2O3 [39], and Li-CuZnAl [40], have been used as efficient catalysts for the dehydrogenation of 2,3-BDO to AC (Scheme 1a). Nevertheless, several issues, such as a high reaction temperature, low productivity, and long contact time, still need to be addressed. Numerous reports have also shown that Cu-based catalysts are active in the dehydrogenation of 1,4-BDO to GBL (Scheme 1b) [17,41,42,43,44,45]. However, the reported Cu catalysts still suffer from low GBL productivity. Several research groups have studied Cu catalysts for GBL formation via a coupling reaction of 1,4-BDO dehydrogenation with the hydrogenation of maleic anhydride [46], furfural [47], nitrobenzene [48], and benzaldehyde [49]. In addition, a Cu-based catalyst, namely the Cu/Zn/Zr/Al catalyst, is also active for the dehydrogenation of 1,2- and 1,3-BDO [50,51]. In the dehydrogenation of 1,2-BDO, 1-hydroxy-2-butanone is produced selectively, although high selectivity to 4-hydroxy-2-butanone from 1,3-BDO cannot be obtained due to the formation of several by-products, such as butanone and acetone. Employing a less acidic Cu-based catalyst might provide better selectivity in the dehydrogenation of 1,3-BDO to 4-hydroxy-2-butanone. According to the above reports, several issues relating to the efficiency of the catalyst can still be addressed despite the promising activity of Cu-based catalysts in the dehydrogenation of BDOs.
Many reports have suggested that the efficiency of Cu catalysts is strongly correlated with their Cu dispersion, surface area, and particle size [52,53,54]. Numerous strategies have been developed to prepare Cu catalysts that contain highly dispersed Cu nanoparticles [52,53,54,55]. In line with this effort, we have also reported a strategy to generate highly active Ni-based catalysts containing highly dispersed Ni nanoparticles using an organic-additive-assisted impregnation protocol [56,57,58]. This strategy has been proven to improve the catalytic activity of Ni catalysts for the hydrogenation of CO2 [56], levulinic acid [57], and acetoin [58]. Recently, we have also prepared Cu/SiO2 catalysts using various organic additives for the vapor-phase dehydrogenation of 1-decanol to decanal [59]. The stability of the complex formed between crown ether and Cu2+ during catalyst preparation influenced the Cu dispersion and particle size, consequently affecting the catalyst efficiency [59]. A crown-ether-assisted Cu/SiO2 efficiently catalyzed the dehydrogenation of 1-decanol, even though 1-decanol as a primary aliphatic alcohol has been reported to be relatively stable [22,60]. Therefore, efficient organic-additive-assisted Cu/SiO2 catalysts might show promising activity for the oxidant-free dehydrogenation of 2,3- and 1,4-BDO.
In this report, Cu/SiO2 catalysts prepared via a crown-ether-assisted impregnation method were employed in the vapor-phase oxidant-free dehydrogenation of 2,3- and 1,4-BDO. The catalytic activity of several Cu/SiO2 catalysts prepared with various organic additives such as 12-crown-4-ether (12C4), 15-crown-5-ether (15C5), 18-crown-6-ether (18C6), triethylene glycol (TEG), and citric acid (CA) was examined. The preparation using organic additives substantially improved the Cu surface area, thus significantly enhancing catalytic activity of the respective Cu catalyst. The formation rates of AC and GBL are proportional to the surface area of Cu. This simple and effective strategy can be viewed as an alternative to upgrading biomass-derived platform compounds to value-added chemicals.

2. Materials and Methods

2.1. Catalyst Preparation

Crown ethers such as 12C4, 15C5, and 18C6 were purchased from Tokyo Chemical Industries Co., Ltd., Tokyo, Japan. TEG, CA, and Cu(NO3)2·3H2O were purchased from Wako Pure Chemical Industries, Ltd., Osaka, Japan. Silica-supported copper (Cu/SiO2) catalysts were prepared by an impregnation method using an aqueous solution containing a prescribed amount of Cu(NO3)2·3H2O and an organic additive; the molar ratio of the organic additive to the metal is 1. Typically, Cu(NO3)2·3H2O (0.152 g, 0.63 mmol) and 12C4 (0.110 g, 0.63 mmol) were dissolved in 20 mL of H2O. The solution was dropped onto 1.96 g of SiO2 support, which was supplied by Fuji Silysia Chemical Ltd., Kasugai, Japan (CARiACT Q6 with a granule size of 75–500 μm and a specific surface area (SA) of 451 m2 g−1), and the water of the dropped solution was evaporated by illuminating the support with a 350-W electric light bulb at the support surface temperature of ca. 70 °C. This process was repeated until all the copper nitrate solution had been added. The resultant sample was dried at 110 °C for 12 h and calcined at 300 °C for 3 h to obtain a CuO/SiO2 sample. Prior to the catalytic reaction and characterization, the resultant CuO/SiO2 sample was reduced in H2 flow at 300 °C for 1 h to prepare Cu/SiO2. The resulting catalyst is expressed as A-xCu/SiO2, where A and x indicate the used organic additive and the weight percentage of Cu metal, respectively. In this case, the above procedure generated a 12C4-2Cu/SiO2 catalyst. The xCu/SiO2 catalysts with different Cu contents were prepared by changing the quantities of Cu salt, organic additive, and SiO2 support, which are described in Table S1 of the supporting information (SI) file.

2.2. Catalyst Characterization

The thermal decomposition profile with mass analysis of thermally evolved gases (TD-MS) was recorded on the BELLMASS unit (Microtrac BEL Corp., Osaka, Japan) to identify the components of the produced gasses. A sample (50 mg) was heated from 100 to 800 °C in a He flow of 30 cm3 min−1 at 10 °C min−1 after the sample had been heated in the He flow at 110 °C for 1 h and then cooled to 100 °C, where the preheating process was performed to remove pre-adsorbed gasses. The produced gases were monitored using a thermal conductivity detector (TCD) and a quadrupole mass analyzer. The thermogravimetry (TG) analysis was conducted using the Thermoplus 8120E2 (Rigaku Corp., Tokyo, Japan). The sample of ca. 7 mg was heated from room temperature to 110 °C, and the temperature of 110 °C was maintained for 1 h to remove surface water adsorbed on the catalyst. After that, the weight change of the sample was recorded while the sample was heated from 110 to 900 °C in the air at a heating rate of 5 °C min−1. The X-ray diffraction measurement (XRD) was performed on a Miniflex 600 (Rigaku Corp.) using monochromatic Cu Kα (λ = 0.15418), equipped with a D/tex Ultra 250 ID detector. The Cu surface area, SACu, was estimated by TPR titration of oxidized Cu by N2O at 50 °C according to the previously reported method [61]. The details of this method are described in the SI file.

2.3. Vapor-Phase Dehydrogenation of 2,3-BDO and 1,4-BDO

Vapor-phase dehydrogenation of 2,3-BDO was performed in a fixed-bed flow reactor at an atmospheric pressure of N2. The catalyst was loaded into the reactor and reduced with H2 gas at 300 °C for 1 h. Thereafter, 2,3-BDO was fed through the reactor top at a liquid feed rate of 1.37 g h−1 together with an N2 flow of 30 cm3 min−1 at 200 °C for the time on stream (TOS) of 5 h. The reaction effluents were collected in a dry ice-acetone trap every hour. The recovered products were identified using a gas chromatograph (GC) equipped with a mass-spectrometer (QP5050A, Shimadzu Corp., Kyoto, Japan) and a capillary column (InertCap-WAX, a length of 30 m with an inner diameter (ID) of 0.25 mm, GL-Science Inc., Tokyo, Japan). They were quantitatively analyzed by a GC (GC-8A, Shimadzu Corp.) equipped with a flame ionization detector and a 30-m capillary column of Inert Cap 1 (ID of 0.53 mm and a length of 30 m, GL-Science Inc.) using 1-hexanol as an internal standard.
The vapor-phase dehydrogenation of 1,4-BDO was also performed in a similar way to the 2,3-BDO dehydrogenation under the following conditions: reduction in H2 flow at 300 °C for 1 h, 1,4-BDO feed at a liquid feed rate of 1.80 g h−1 together with an N2 flow of 30 cm3 min−1. The reaction effluents were collected in an ice-water trap every hour. The recovered products were quantitatively analyzed by a GC (GC-2014, Shimadzu Corp.) equipped with an FID and a 30-m capillary column of InertCap 1 (ID of 0.25 mm, GL-Science Inc.) using 1-hexanol as an internal standard.

3. Results

3.1. Catalyst Characterization

Figure 1a,b show the TD-MS profiles of none- and 12C4-2Cu/SiO2 catalysts. The m/z signals of 18, 30, 14, and 28 were associated with H2O, NO, N, and CO, respectively. The signals at m/z = 43 in the as-prepared 12C4-2Cu/SiO2 would be attributed to CH2CHO, and the m/z of 44 originated from CH2CH2O and CO2. On the other hand, the signal at m/z = 44 in the as-prepared none-2Cu/SiO2 might originate from CO2. It can also be seen that the decomposition of nitrate was primarily observed in the as-prepared none-2Cu/SiO2 sample. Meanwhile, the signals corresponding to CH2CHO and CH2CH2O+CO2 in the 12C4-2Cu/SiO2 sample were stronger than those in the none-2Cu/SiO2 sample. This finding suggests the presence of a larger organic molecule attached to the Cu cation in the as-prepared 12C4-2Cu/SiO2 sample. The TG curves of the as-prepared none- and 12C4-2Cu/SiO2 samples are depicted in Figure 1c. Notably, the weight loss for the 12C4-2Cu/SiO2 sample was larger than that for the none-2Cu/SiO2 sample, which is in good agreement with the results from TD-MS.
Figure 2a shows the XRD patterns of 2Cu/SiO2 catalysts prepared with different organic additives. Small peaks associated with the monoclinic CuO phase were observed at 2θ of 35.6°, 38.7°, and 48.8° in the 2Cu/SiO2 catalyst prepared without organic additive [62,63]. The XRD profiles of the freshly reduced none- and 12C4-2Cu/SiO2 catalysts are shown in Figure 2b. According to the XRD profiles, the reduction protocol has transformed the CuO species into metallic Cu, as the peaks corresponding to CuO were no longer observed and the peaks associated with metallic Cu appeared at 2θ of 43.3° (111) and 50.4° (200) [64]. It is worth noting that the freshly reduced 12C4-2Cu/SiO2 catalyst has a weaker peak intensity than the none-2Cu/SiO2. Previous reports suggest that this phenomenon is probably due to the presence of highly dispersed Cu nanoparticles [53,54]. In addition, the N2O titration clearly revealed that the Cu dispersions, D, of the 12C4- and none-2Cu/SiO2 catalysts were 0.319 and 0.124, and that the SACu values of the 12C4- and none-2Cu/SiO2 catalysts were 3.53 and 1.38 m2 g−1, respectively, which are comparable to the reported value (1.9 m2 g−1) of 1.4 wt.-% Cu/SiO2 [64]. Therefore, the XRD and N2O titration suggest that the utilization of 12C4 as an organic additive generated the Cu/SiO2 with a higher Cu dispersion and possibly smaller Cu size.

3.2. Comparison of Organic Additives

Table 1 shows the catalytic activity of several 2Cu/SiO2 catalysts in the dehydrogenation of 2,3-BDO to AC at 200 °C and a contact time, W/F, of 0.18 h, where W/F is defined as the weight of the catalyst, W, divided by the feed rate of the reactant, F, which represents the time required for the weight turnover to reach 1 [65]. All Cu catalysts exhibit outstanding selectivity to AC (>98%), with only DA as the side product. A small 2,3-BDO conversion of 19% was observed when the dehydrogenation was catalyzed by a none-2Cu/SiO2 catalyst (entry 1). Among several organic additives tested, 12C4 generated Cu/SiO2 catalysts with the highest catalytic performance (entry 2). Other crown ethers, such as 15C5 and 18C6, also generated 2Cu/SiO2 catalysts with higher performance than a none-2Cu/SiO2 catalyst (entries 3 and 4), even though those catalysts were inferior to the 12C4-2Cu/SiO2 catalyst. CA, which was efficient in improving the activity of Ni-based catalysts [56,57,58], also improved the catalytic performance of the 2Cu/SiO2 catalyst (entry 5). Nevertheless, the performance of the CA-2Cu/SiO2 catalyst was slightly lower than that of the 12C4-2Cu/SiO2 catalyst.
The XRD and SACu measurements indicate that the utilization of organic additives generated 2Cu/SiO2 catalysts with better Cu dispersion and smaller Cu sizes, leading to a higher Cu surface area. The improvement of the catalytic activity of the 2Cu/SiO2 catalysts was strongly correlated with the D and SACu. The 12C4-2Cu/SiO2 catalyst possessed the highest D and SACu; therefore, this catalyst gave the highest catalytic performance among several 2Cu/SiO2 catalysts tested. It has been reported that the efficiency of the crown-ether-assisted Cu/SiO2 catalysts was influenced by the stability of the complex formed between Cu2+ and crown ether: Table S2 cites data for the SACu of several Cu/SiO2 catalysts prepared with and without organic additives [59]. Cu2+ was reported to form a more stable complex with 12C4 than with 15C5 and 18C6 [66,67]; consequently, 12C4 was able to prevent Cu agglomeration during the calcination process more effectively than 15C5 and 18C6. The trend of catalytic performance of 12C4- and CA-2Cu/SiO2 catalysts was also in good agreement with their corresponding SACu.

3.3. Effect of Reaction Conditions such as W/F, Temperature, and N2 Flow Rate

Figure 3a shows the effect of W/F on the catalytic activity of the 12C4-2Cu/SiO2 catalyst at a reaction temperature of 200 °C. Prolonging the W/F increased the activity of the 12C4-2Cu/SiO2 catalyst. The AC selectivity remained above 98% even at the longest W/F tested. This result suggests that the consecutive dehydrogenation of AC to DA was not affected by the W/F. The highest yield of AC generated at a W/F of 1.09 h and 200 °C was 79.2%, and further increments of W/F gave a negligible increase in the AC yield.
Figure 3b illustrates the effect of temperatures on the equilibrium yield in the dehydrogenation of 2,3-BDO in a N2 flow of 30 cm3 min−1. The increase in temperature increased the conversion of 2,3-BDO but decreased the AC selectivity. The AC selectivities were 99.2 and 97.6% at 170 and 200 °C, respectively. Meanwhile, the reaction temperatures of 250 and 275 °C gave 87.7 and 75.8% AC selectivity, respectively. The decline in AC selectivity was due to the consecutive dehydrogenation of AC to DA, as the DA selectivity increased with the increase in temperature. The dehydrogenation of 2,3-BDO to AC is an equilibrium reaction (Scheme 1a); therefore, the pressure equilibrium constant of the 2,3-BDO dehydrogenation at a given reaction temperature can be expressed as:
K 1 p = P A C × P H 2 P 2,3 B D O
where Pi is the partial pressure of component i. The K1p values were estimated to be 0.138, 0.422, 1.83, and 2.26 in the dehydrogenation-hydrogenation reaction between 2,3-BDO and AC at 170, 200, 250, and 275 °C, respectively (the broken red line in Figure 3b). It is worth noting that the K1p values for the reaction temperature of 170–250 °C are similar to the inverse of the pressure equilibrium constant in the AC hydrogenation (1/K3p) [59] (black dotted line). However, the K1p value at 275 °C deviated from that of the 1/K3p due to a high rate of AC dehydrogenation to DA, as confirmed later by Figure 3d.
According to the K1p equation, reducing the partial pressure of the reaction system at a certain reaction temperature favors the production of AC, as the K1p value should remain constant [68]. This assumption is corroborated by the finding shown in Figure 3c. The increment of the N2 flow rate reduced the partial pressure of the reaction system; thus, the equilibrium yield shifted to the product, which increased the yield of AC. Furthermore, the AC yield from the experimental results in Figure 3c, as indicated by the dot points, was in good agreement with the calculated values (red and blue broken lines). This finding indicates that the generation of Cu/SiO2 catalysts by the use of organic additives gave outstanding catalytic activity for 2,3-BDO dehydrogenation, and the activity was only limited by the equilibrium. The AC yield and AC selectivity at 200 °C with an N2 flow of 90 cm3 min−1 were 86.7 and 95.4%, respectively.
Figure 3d shows the results of AC dehydrogenation at different temperatures. The AC conversion was much lower than the 2,3-BDO conversion under the same reaction conditions, suggesting that AC dehydrogenation was relatively more difficult than 2,3-BDO dehydrogenation. The AC conversion and DA selectivity increased with the increase in reaction temperature. It is worth noting that 2,3-BDO was generated in the dehydrogenation of AC, and the 2,3-BDO selectivity decreased with the increase in reaction temperature. This result suggests that the hydrogen generated from the dehydrogenation of AC to DA was consumed for AC hydrogenation to produce 2,3-BDO at low reaction temperatures. In addition, the hydrogenation of AC was favorable at lower temperatures, while the AC dehydrogenation to generate DA proceeded dominantly at high reaction temperatures. Furthermore, the pressure equilibrium constant, K2p, in the dehydrogenation of AC to DA was estimated to be 0.00025, 0.0024, 0.027, and 0.044 at 170, 200, 250, and 275 °C, respectively, assuming the reaction reaches an equilibrium where the K2p of the AC dehydrogenation is expressed as:
K 2 p = P D A × P H 2 P A C
The findings in Figure 3d were in good agreement with the results in Figure 3b. Selective dehydrogenation of 2,3-BDO to AC proceeded at low reaction temperatures because the consecutive dehydrogenation of AC to DA hardly proceeded. On the other hand, the hydrogenation of AC to 2,3-BDO was inhibited since the substrate, 2,3-BDO, was abundant. Meanwhile, the AC generated from the first step of 2,3-BDO dehydrogenation was further dehydrogenated to produce DA at high reaction temperatures. Concurrently, the AC hydrogenation did not proceed since this reaction was favorable at low reaction temperatures.

3.4. Stability of Cu/SiO2 Catalysts

Figure 4a compares the time course in the catalytic performance of none- and 12C4-10Cu/SiO2 at 200 °C and a W/F of 0.14 h. Both none- and 12C4-10Cu/SiO2 catalysts deactivated since the 2,3-BDO conversion over both catalysts decreased. The none-10Cu/SiO2 catalyst dropped the catalytic performance from 55 to 10% at a TOS of 5 h. Meanwhile, the 12C4-10Cu/SiO2 catalyst dropped its catalytic performance from 78 to 39% at a TOS of 12 h. The results indicate that the 12C4-10Cu/SiO2 catalyst had better performance than the none-10Cu/SiO2 catalyst.
Figure 4b shows the XRD profiles of the spent none- and 12C4-10Cu/SiO2 catalysts. According to the XRD profiles of the spent none-10Cu/SiO2 catalyst, the Cu particle agglomeration did not proceed, as the crystallite size of the Cu metal before and after the reaction is nearly similar. On the other hand, the Cu nanoparticles in the 12C4-10Cu/SiO2 catalyst aggregated as the Cu metal in the spent catalyst and were possibly larger than that freshly reduced 12C4-10Cu/SiO2 catalyst, for which the XRD peak was too broad for the calculation of the crystallite size. Nevertheless, the crystallite size of the Cu metal in the spent 12C4-10Cu/SiO2 catalyst after a TOS of 12 h was significantly smaller than even the freshly reduced none-10Cu/SiO2 catalyst. These results indicate that the utilization of 12C4 as an organic additive is beneficial for catalytic properties, as it generates a Cu/SiO2 catalyst with Cu nanoparticles even after the reaction proceeds.
Figure 4c depicts the TG curves of the spent none- and 12C4-10Cu/SiO2 catalysts. The weight changes of the none- and 12C4-10Cu/SiO2 catalysts were similar. This result shows that the amount of coke deposited on both catalysts was the same (8.9 wt.-%). It was reasonable to expect that both none- and 12C4-10Cu/SiO2 catalysts might have similar catalyst deactivation rates. However, due to its high intrinsic activity, it spent a long time for the 12C4-10Cu/SiO2 catalyst to drop its conversion to the same level as the none-10Cu/SiO2 catalyst. In general, the utilization of organic additives in the catalyst preparation generated Cu/SiO2 catalysts with better performance due to a higher intrinsic activity, i.e., formation rate, than the Cu/SiO2 catalyst prepared without organic additive.

3.5. Effect of Cu Content and SACu on the Formation Rate of Acetoin

Previously, we have reported the proportional relation between the formation rates of decanal and SACu of Cu/SiO2 catalysts in the dehydrogenation of 1-decanol [59]. Figure 5a shows the effect of Cu content on the formation rate of AC per gram of Cu/SiO2 catalyst, estimated at the 2,3-BDO conversion below 15% at low W/F. Increasing the Cu content of the 12C4-xCu/SiO2 catalysts increased the AC formation rate due to the increment of SACu, which is summarized in Table S2. Similarly, the increase in Cu content of the none-xCu/SiO2 catalyst from 2 to 15 wt.-% improved the formation rate of AC. However, further increment of Cu content from 15 to 20 wt.-% decreased the formation rate of AC as the Cu agglomerated, leading to the formation of AC over the Cu/SiO2 catalyst with smaller SACu.
Figure 5b depicts the relation between SACu and the formation rate of AC in the dehydrogenation of 2,3-BDO. The formation rate of AC is proportional to the SACu. However, the formation rate over 12C4-xCu/SiO2 catalysts was substantially higher than that over none-xCu/SiO2 catalysts due to a significantly higher SACu. The linear relation between SACu and the catalytic activity of Cu catalysts has also been reported in CO2 hydrogenation [69] and diols dehydrogenation [70], indicating that the reaction is only catalyzed by the surface of Cu metal. A similar proportional relation between SACu and the formation rate of GBL in the dehydrogenation of 1,4-BDO was also found, as described later.

3.6. Dehydrogenation of 1,4-BDO over Cu/SiO2 Catalyst

The high intrinsic activity of the 12C4-xCu/SiO2 catalysts in the dehydrogenation of 2,3-BDO was limited by equilibrium. Even though increasing the N2 flow rate increased the equilibrium yield of AC, the equilibrium inhibited the full conversion of 2,3-BDO. The dehydrogenation of 1,4-BDO to GBL was performed to investigate the activity of the 12C4-xCu/SiO2 catalyst for 1,4-BDO dehydrogenation, which is an irreversible reaction (Scheme 1b) [17,44,45]. Figure 6a shows the time course of the catalytic performance of none- and 12C4-10Cu/SiO2 catalysts in the dehydrogenation of 1,4-BDO at 260 °C and a W/F of 0.080 h. Both catalysts maintained their 1,4-BDO conversion and GBL selectivity for 10 h; nevertheless, 12C4-10Cu/SiO2 catalyst gave significantly higher catalytic activity than none-10Cu/SiO2 catalyst. Figure 6b depicts the TG curves of the spent none- and 12C4-10Cu/SiO2 catalysts. The coke formation occurred on both 12C4- and none-10Cu/SiO2 catalysts, and the amounts of coke deposited on the spent 12C4- and none-10Cu/SiO2 catalysts were 6.1 and 5.6 wt.-%, respectively. These findings indicate that the coke formation during 1,4-BDO dehydrogenation did not deactivate both 12C4- and none-10Cu/SiO2 catalysts.
Figure 7a depicts the activity of the none- and 12C4-10Cu/SiO2 catalysts in the dehydrogenation of 1,4-BDO at different W/F. A high 1,4-BDO conversion and GBL selectivity were achieved by the use of the 12C4-10Cu/SiO2 catalyst at a W/F of 0.27 h. Under similar reaction conditions, the none-10Cu/SiO2 catalyst had lower activity than the 12C4-10Cu/SiO2 catalyst, showcasing the benefit of generating Cu/SiO2 catalyst with highly dispersed Cu nanoparticles using 12C4 as an organic additive. Figure 7b reveals that the dehydrogenation of 1,4-BDO was affected by the Cu content, with the 12C4-15Cu/SiO2 catalyst giving the highest conversion among the Cu contents tested.
Figure 7c depicts the relation between SACu and the formation rate of GBL in the dehydrogenation of 1,4-BDO at 240 °C. The GBL formation rate is proportional to the SACu at SACu smaller than 30 m2 g−1, while the proportional relation was not observed at SACu higher than 30 m2 g−1. This phenomenon differed from the results in the dehydrogenation of 2,3-BDO to AC, in which the AC formation rate was proportional to SACu, even at SACu higher than 30 m2 g−1. This difference can be explained by the mechanism of 1,4-BDO dehydrogenation to GBL. The dehydrogenation of 2,3-BDO to AC is a straightforward reaction, whereas 1,4-BDO dehydrogenation to GBL proceeds via a series of consecutive reactions, including (1) dehydrogenation of 1,4-BDO to 4-hydroxybutanal, (2) intramolecular hemiacetal-formed cyclization to 2-hydroxytetrahydrofuran, and (3) dehydrogenation of 2-hydroxytetrahydrofuran to form GBL (Scheme 2) [41]. The cyclization via an intramolecular hemiacetal reaction was possibly catalyzed by the acid sites of the silanol group in a similar manner to the cyclization of levulinic acid to angelica lactone [71]. Similarly, acidic alumina-supported Cu was also effective for the cyclization of 4-hydroxybutanal; nevertheless, the strong acidity of alumina promoted the dehydration reaction, generating tetrahydrofuran as the side product [41]. At SACu below 30 m2 g−1, the increment of Cu content did not significantly alter the concentration of silanol sites; thus, the increment of Cu content favored the dehydrogenation of 1,4-BDO to 4-hydroxybutanal but did not hinder the consecutive cyclization of 4-hydroxybutanal to 2-hydroxytetrahydrofuran. However, when the SACu was higher than 30 m2 g−1, the increment of Cu content decreased the contribution of OH to the level that it slightly hindered the cyclization of 4-hydroxybutanal to 2-hydroxytetrahydrofuran and the subsequent GBL formation. As a result, a proportional relation between SACu and GBL formation rate was no longer observed at SACu above 30 m2 g−1, as shown in Figure 7c.

3.7. Vapor-Phase Oxidant-Free Dehydrogenation over Cu Catalysts

Table 2 shows the catalytic activity of several Cu catalysts in the dehydrogenation of 2,3-BDO to AC under various conditions. It is reported that several Cu/SiO2 catalysts are active for the dehydrogenation of 2,3-BDO to AC [37,38]. The 12C4-10Cu/SiO2 catalyst productivity was also higher than Cu catalyst-derived CuZnAl LDH [40], even when the reaction was performed at lower reaction temperatures. In the previous papers [38,40], it is notable that high AC selectivity is realized at a high temperature of 260 °C or higher if the formation of DA can be prevented at such high temperatures. The AC productivity of the 12C4-10Cu/SiO2 catalyst was also higher than that of Cu-Al2O3 [39] at the same reaction temperature of 170 °C.
Table 3 shows the comparison of the catalytic activities of several Cu catalysts in the vapor-phase dehydrogenation of 1,4-BDO to GBL. The utilization of 12C4 as an organic additive was proven to generate a Cu catalyst with the largest SACu. Several Cu catalysts are highly active for the dehydrogenation of 1,4-BDO to GBL at 240 or 250 °C and a W/F of 0.5 h or higher [17,18,41,43,44,45]; nevertheless, the 12C4-10Cu/SiO2 catalyst in our work gave a comparable catalytic performance at a shorter W/F of 0.27 h at 260 °C. It is also worth noting that the GBL productivity of 12C4-10Cu/SiO2 was significantly higher than the GBL productivity of the reported Cu catalysts. In summary, catalytic activity in the dehydrogenation was improved by preparing a Cu/SiO2 catalyst using organic additives. The substantial increment of SACu strongly influenced the increment of the catalytic activity.

4. Conclusions

Cu/SiO2 catalysts prepared via the crown-ether-assisted impregnation method showed high catalytic activity in the vapor-phase oxidant-free dehydrogenation of 2,3- and 1,4-BDO. A 12C4 generated Cu/SiO2 catalyst with the highest catalytic activity among several organic additives was tested. It was found that the increment of catalytic activity was strongly correlated with the generation of highly dispersed Cu nanoparticles. Since the formation rates of AC and GBL are proportional to SACu, it is reasonable to assume that the improvement in SACu due to the utilization of 12C4 enhances the catalytic activity. The equilibrium nature of 2,3-BDO dehydrogenation inhibited the full conversion of 2,3-BDO to AC. Meanwhile, a nearly quantitative yield of GBL with high productivity was achieved in the irreversible dehydrogenation of 1,4-BDO by the use of 12C4-xCu/SiO2 catalysts.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/2624-8549/5/1/30/s1. Experimental details on the estimation of copper surface area Table S1: Detail quantity for the preparation of Cu/SiO2 catalysts; Table S2: SACu values of Cu/SiO2 catalysts used in Figure 5 and Figure 7. References [59,61,72,73,74,75] are cited in Supplementary Materials.

Author Contributions

Conceptualization, S.S.; methodology, S.S.; validation, Y.Y. and S.S.; formal analysis, S.H. and M.K.; investigation, S.H. and M.K.; resources, S.S.; data curation, E.K., S.H. and M.K.; writing—original draft preparation, E.K.; writing—review and editing, Y.Y. and S.S.; visualization, E.K. and S.H.; supervision, Y.Y.; project administration, S.S.; funding acquisition, S.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Japan Society for the Promotion of Science (JSPS KAKENHI, Grant Number JP21H01711).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The data is contained within the article or supplementary material.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Sudarsanam, P.; Peeters, E.; Makshina, E.V.; Parvulescu, V.I.; Sels, B.F. Advances in porous and nanoscale catalysts for viable biomass conversion. Chem. Soc. Rev. 2019, 48, 2366–2421. [Google Scholar] [CrossRef]
  2. Hou, Q.; Qi, X.; Zhen, M.; Qian, H.; Nie, Y.; Bai, C.; Zhang, S.; Bai, X.; Ju, M. Biorefinery roadmap based on catalytic production and upgrading 5-hydroxymethylfurfural. Green Chem. 2021, 23, 119–231. [Google Scholar] [CrossRef]
  3. Valizadeh, S.; Hakimian, H.; Farooq, A.; Jeon, B.H.; Chen, W.H.; Hoon Lee, S.; Jung, S.C.; Won Seo, M.; Park, Y.K. Valorization of biomass through gasification for green hydrogen generation: A comprehensive review. Bioresour. Technol. 2022, 365, 128143. [Google Scholar] [CrossRef]
  4. Kang, S.; Fu, J.; Zhang, G. From lignocellulosic biomass to levulinic acid: A review on acid-catalyzed hydrolysis. Renew. Sustain. Energy Rev. 2018, 94, 340–362. [Google Scholar] [CrossRef]
  5. Dumeignil, F.; Capron, M.; Katryniok, B.; Wojcieszak, R.; Löfberg, A.; Girardon, J.S.; Desset, S.; Araque-Marin, M.; Jalowiecki-Duhamel, L.; Paul, S. Biomass-derived platform molecules upgrading through catalytic processes: Yielding chemicals and fuels. J. Jpn. Pet. Inst. 2015, 58, 257–273. [Google Scholar] [CrossRef]
  6. Yabushita, M.; Kobayashi, H.; Fukuoka, A. Catalytic transformation of cellulose into platform chemicals. Appl. Catal. B Environ. 2014, 145, 1–9. [Google Scholar] [CrossRef]
  7. Li, J.; Yang, R.; Xu, S.; Zhou, C.; Xiao, Y.; Hu, C.; Tsang, D.C.W. Biomass-derived polyols valorization towards glycolic acid production with high atom-economy. Appl. Catal. B Environ. 2022, 317, 121785. [Google Scholar] [CrossRef]
  8. Ji, X.J.; Huang, H.; Ouyang, P.K. Microbial 2,3-butanediol production: A state-of-the-art review. Biotechnol. Adv. 2011, 29, 351–364. [Google Scholar] [CrossRef]
  9. Guragain, Y.N.; Chitta, D.; Karanjikar, M.; Vadlani, P.V. Appropriate lignocellulosic biomass processing strategies for efficient 2,3-butanediol production from biomass-derived sugars using Bacillus licheniformis DSM 8785. Food Bioprod. Process. 2017, 104, 147–158. [Google Scholar] [CrossRef]
  10. Guragain, Y.N.; Vadlani, P.V. 2,3-Butanediol production using Klebsiella oxytoca ATCC 8724: Evaluation of biomass derived sugars and fed-batch fermentation process. Process Biochem. 2017, 58, 25–34. [Google Scholar] [CrossRef]
  11. Sathesh-Prabu, C.; Kim, D.; Lee, S.K. Metabolic engineering of Escherichia coli for 2,3-butanediol production from cellulosic biomass by using glucose-inducible gene expression system. Bioresour. Technol. 2020, 309, 123361. [Google Scholar] [CrossRef]
  12. Cheng, J.; Li, J.; Zheng, L. Achievements and perspectives in 1,4-butanediol production from engineered microorganisms. J. Agric. Food Chem. 2021, 69, 10480–10485. [Google Scholar] [CrossRef]
  13. Yim, H.; Haselbeck, R.; Niu, W.; Pujol-baxley, C.; Burgard, A.; Boldt, J.; Khandurina, J.; Trawick, J.D.; Osterhout, R.E.; Stephen, R.; et al. Metabolic engineering of Escherichia coli for direct production of 1,4-butanediol. Nat. Chem. Biol. 2011, 7, 444–445. [Google Scholar] [CrossRef]
  14. Xie, S.; Li, Z.; Zhu, G.; Song, W.; Yi, C. Cleaner production and downstream processing of bio-based 2,3-butanediol: A review. J. Clean. Prod. 2022, 343, 131033. [Google Scholar] [CrossRef]
  15. Burgard, A.; Burk, M.J.; Osterhout, R.; Van Dien, S.; Yim, H. Development of a commercial scale process for production of 1,4-butanediol from sugar. Curr. Opin. Biotechnol. 2016, 42, 118–125. [Google Scholar] [CrossRef]
  16. Maina, S.; Prabhu, A.A.; Vivek, N.; Vlysidis, A.; Koutinas, A.; Kumar, V. Prospects on bio-based 2,3-butanediol and acetoin production: Recent progress and advances. Biotechnol. Adv. 2022, 54, 107783. [Google Scholar] [CrossRef]
  17. Hwang, D.W.; Kashinathan, P.; Lee, J.M.; Lee, J.H.; Lee, U.; Hwang, J.S.; Hwang, Y.K.; Chang, J.S. Production of γ-butyrolactone from biomass-derived 1,4-butanediol over novel copper-silica nanocomposite. Green Chem. 2011, 13, 1672–1675. [Google Scholar] [CrossRef]
  18. Bhanushali, J.T.; Prasad, D.; Patil, K.N.; Ramesh Babu, G.V.; Kainthla, I.; Rama Rao, K.S.; Jadhav Arvind, H.; Nagaraja, B.M. The selectively regulated vapour phase dehydrogenation of 1,4-butanediol to γ-butyrolactone employing a copper-based ceria catalyst. New J. Chem. 2019, 43, 11968–11983. [Google Scholar] [CrossRef]
  19. Mitsudome, T.; Mikami, Y.; Funai, H.; Mizugaki, T.; Jitsukawa, K.; Kaneda, K. Oxidant-free alcohol dehydrogenation using a reusable hydrotalcite-supported silver nanoparticle catalyst. Angew. Chem. 2008, 120, 144–147. [Google Scholar] [CrossRef]
  20. Gunasekaran, N. Aerobic oxidation catalysis with air or molecular oxygen and ionic liquids. Adv. Synth. Catal. 2015, 357, 1990–2010. [Google Scholar] [CrossRef]
  21. Pandey, P.; Dutta, I.; Bera, J.K. Acceptorless alcohol dehydrogenation: A mechanistic perspective. Proc. Natl. Acad. Sci. India Sect. A Phys. Sci. 2016, 86, 561–579. [Google Scholar] [CrossRef]
  22. Challa, P.; Enumula, S.S.; Paleti, G.; Dosali, M.; Burri, D.R.; Kamaraju, S.R.R. Support Effect in Cu-Based Catalysts for Vapor Phase Dehydrogenation of 1-Decanol to Decanal Using CO2 as a Soft Oxidant. Int. J. Energy Res. 2022, 46, 9166–9177. [Google Scholar] [CrossRef]
  23. Poreddy, R.; Engelbrekt, C.; Riisager, A. Copper oxide as efficient catalyst for oxidative dehydrogenation of alcohols with air. Catal. Sci. Technol. 2015, 5, 2467–2477. [Google Scholar] [CrossRef]
  24. Putro, W.S.; Kojima, T.; Hara, T.; Ichikuni, N.; Shimazu, S. Acceptorless dehydrogenation of alcohols using cu-fe catalysts prepared from Cu-Fe layered double hydroxides as precursors. Catal. Sci. Technol. 2018, 8, 3010–3014. [Google Scholar] [CrossRef]
  25. Kurniawan, E.; Hara, T.; Permana, Y.; Ichikuni, N.; Shimazu, S. In situ generation of catalytically active Cu0 species derived from Cu-Al layered double hydroxides for acceptorless alcohol dehydrogenation. Chem. Lett. 2022, 51, 334–337. [Google Scholar] [CrossRef]
  26. Bhuyan, B.; Paul, A.; Devi, M.; Dhar, S.S. A silver NP-dispersed water extract of fly ash as a green and efficient medium for oxidant-free dehydrogenation of benzyl alcohols. RSC Adv. 2018, 8, 1313–1319. [Google Scholar] [CrossRef]
  27. Zeng, G.; Sakaki, S.; Fujita, K.I.; Sano, H.; Yamaguchi, R. Efficient catalyst for acceptorless alcohol dehydrogenation: Interplay of theoretical and experimental studies. ACS Catal. 2014, 4, 1010–1020. [Google Scholar] [CrossRef]
  28. Wang, Q.; Chai, H.; Yu, Z. Acceptorless Dehydrogenation of N-Heterocycles and Secondary Alcohols by Ru(II)-NNC Complexes Bearing a Pyrazoyl-Indolyl-Pyridine Ligand. Organometallics 2018, 37, 584–591. [Google Scholar] [CrossRef]
  29. Paul, B.; Sharma, S.; Purkayastha, D.D.; Dhar, S.S.; Bal, R. Facile synthesis of size-controlled Ag supported on WO3 nanorods and their application as novel and active catalyst in oxidant-free dehydrogenation of benzyl alcohols. Catal. Commun. 2019, 132, 105804. [Google Scholar] [CrossRef]
  30. Fang, W.; Zhang, Q.; Chen, J.; Deng, W.; Wang, Y. Gold nanoparticles on hydrotalcites as efficient catalysts for oxidant-free dehydrogenation of alcohols. Chem. Commun. 2010, 46, 1547–1549. [Google Scholar] [CrossRef]
  31. Kon, K.; Hakim Siddiki, S.M.A.; Shimizu, K.I. Size and support-dependent pt nanocluster catalysis for oxidant-free dehydrogenation of alcohols. J. Catal. 2013, 304, 63–71. [Google Scholar] [CrossRef]
  32. Nicolau, G.; Tarantino, G.; Hammond, C. Acceptorless alcohol dehydrogenation catalysed by Pd/C. ChemSusChem 2019, 12, 4953–4961. [Google Scholar] [CrossRef] [PubMed]
  33. Crivello, M.E.; Pérez, C.F.; Mendieta, S.N.; Casuscelli, S.G.; Eimer, G.A.; Elías, V.R.; Herrero, E.R. N-Octyl alcohol dehydrogenation over copper catalysts. Catal. Today 2008, 133–135, 787–792. [Google Scholar] [CrossRef]
  34. Mitsudome, T.; Mikami, Y.; Ebata, K.; Mizugaki, T.; Jitsukawa, K.; Kaneda, K. Copper nanoparticles on hydrotalcite as a heterogeneous catalyst for oxidant-free dehydrogenation of alcohols. Chem. Commun. 2008, 39, 4804–4806. [Google Scholar] [CrossRef]
  35. Wang, F.; Shi, R.; Liu, Z.Q.; Shang, P.J.; Pang, X.; Shen, S.; Feng, Z.; Li, C.; Shen, W. Highly efficient dehydrogenation of primary aliphatic alcohols catalyzed by Cu nanoparticles dispersed on rod-shaped La2O2CO3. ACS Catal. 2013, 3, 890–894. [Google Scholar] [CrossRef]
  36. Yuan, Q.; Pang, J.; Yu, W.; Zheng, M. Vapor-phase furfural decarbonylation over a high-performance catalyst of 1%Pt/SBA-15. Catalysts 2020, 10, 1304. [Google Scholar] [CrossRef]
  37. Yuan, E.; Ni, P.; Zhuang, W.; Jian, R.; Jian, P. Synergic catalysis by a CuO-like phase and Cu0 for anaerobic dehydrogenation of 2,3-butanediol. J. Catal. 2020, 382, 256–268. [Google Scholar] [CrossRef]
  38. Yuan, E.; Ni, P.; Xie, J.; Jian, P.; Hou, X. Highly efficient dehydrogenation of 2,3-butanediol induced by metal-support interface over Cu-SiO2 catalysts. ACS Sustain. Chem. Eng. 2020, 8, 15716–15731. [Google Scholar] [CrossRef]
  39. Al-Auda, Z.; Li, X.; Hohn, K.L. Dehydrogenation of 2,3-butanediol to acetoin using copper catalysts. Ind. Eng. Chem. Res. 2022, 61, 3530–3538. [Google Scholar] [CrossRef]
  40. Zhang, B.; Zhou, F.; Ma, H.; Chen, L.; Su, J.; Yuan, X.; Zhang, J. Dehydrogenation of 2,3-butanediol to 3-hydroxybutanone over CuZnAl catalysts: Effect of lithium cation as promoter. Top. Catal. 2020, 63, 866–874. [Google Scholar] [CrossRef]
  41. Ichikawa, N.; Sato, S.; Takahashi, R.; Sodesawa, T.; Inui, K. Dehydrogenative cyclization of 1,4-butanediol over copper-based catalyst. J. Mol. Catal. A Chem. 2004, 212, 197–203. [Google Scholar] [CrossRef]
  42. Zhang, B.; Zhu, Y.; Ding, G.; Zheng, H.; Li, Y. Modification of the supported Cu/SiO2 catalyst by alkaline earth metals in the selective conversion of 1,4-butanediol to γ-butyrolactone. Appl. Catal. A Gen. 2012, 443–444, 191–201. [Google Scholar] [CrossRef]
  43. Nagaiah, P.; Rao, M.V.; Thirupathaiah, K.; Venkateshwarlu, V.; Raju, B.D.; Rao, K.S.R. Selective vapour phase dehydrogenation of biomass-derived 1,4-butanediol to gamma butyrolactone over Cu/ZrO2 catalysts: Influence of La2O3 promotor. Res. Chem. Intermed. 2018, 44, 5817–5831. [Google Scholar] [CrossRef]
  44. Raju, M.A.; Gidyonu, P.; Nagaiah, P.; Rao, M.V.; Raju, B.D.; Rao, K.S.R. Mesoporous silica–supported copper catalysts for dehydrogenation of biomass-derived 1,4-butanediol to gamma butyrolactone in a continuous process at atmospheric pressure. Biomass Convers. Biorefinery 2019, 9, 719–726. [Google Scholar] [CrossRef]
  45. Bhanushali, J.T.; Prasad, D.; Patil, K.N.; Saidulu Reddy, K.; Kainthla, I.; Kamaraju, S.R.R.; Jadhav Arvind, H.; Nagaraja, B.M. Tailoring the catalytic activity of basic mesoporous Cu/CeO2 catalyst by Al2O3 for selective lactonization and dehydrogenation of 1,4-butanediol to γ-butyrolactone. Catal. Commun. 2020, 143, 106049. [Google Scholar] [CrossRef]
  46. Zhu, Y.L.; Xiang, H.W.; Wu, G.S.; Bai, L.; Li, Y.W. A Novel route for synthesis of γ-butyrolactone through the coupling of hydrogenation and dehydrogenation. Chem. Commun. 2002, 3, 254–255. [Google Scholar] [CrossRef]
  47. Zheng, H.Y.; Yang, J.; Zhu, Y.L.; Zhao, G.W. Synthesis of γ-butyrolactone and 2-methylfuran through the coupling of dehydrogenation and hydrogenation over copper-chromite catalyst. React. Kinet. Catal. Lett. 2004, 82, 263–269. [Google Scholar] [CrossRef]
  48. Hari Prasad Reddy, K.; Rahul, R.; Sree Vardhan Reddy, S.; David Raju, B.; Rama Rao, K.S. Coupling of 1,4-butanediol dehydrogenation reaction with the hydrogenation of nitrobenzene over Cu/MgO catalysts. Catal. Commun. 2009, 10, 879–883. [Google Scholar] [CrossRef]
  49. Bhanushali, J.T.; Prasad, D.; Patil, K.N.; Reddy, K.S.; Rama Rao, K.S.; Jadhav, A.H.; Nagaraja, B.M. Simultaneous dehydrogenation of 1,4- butanediol to γ-butyrolactone and hydrogenation of benzaldehyde to benzyl alcohol mediated over competent CeO2–Al2O3 supported Cu as catalyst. Int. J. Hydrogen Energy 2020, 45, 12874–12888. [Google Scholar] [CrossRef]
  50. Sato, S.; Takahashi, R.; Sodesawa, T.; Fukuda, H.; Sekine, T.; Tsukuda, E. Synthesis of α-hydroxyketones from 1,2-diols over Cu-based catalyst. Catal. Commun. 2005, 6, 607–610. [Google Scholar] [CrossRef]
  51. Sato, S.; Takahashi, R.; Fukuda, H.; Inui, K. Dehydrogenation of 1,3-butanediol over Cu-based catalyst. J. Mol. Catal. A Chem. 2007, 272, 164–216. [Google Scholar] [CrossRef]
  52. Dong, F.; Ding, G.; Zheng, H.; Xiang, X.; Chen, L.; Zhu, Y.; Li, Y. Highly dispersed cu nanoparticles as an efficient catalyst for the synthesis of the biofuel 2-methylfuran. Catal. Sci. Technol. 2016, 6, 767–779. [Google Scholar] [CrossRef]
  53. Du, H.; Ma, X.; Yan, P.; Jiang, M.; Zhao, Z.; Zhang, Z.C. Catalytic furfural hydrogenation to furfuryl alcohol over Cu/SiO2 catalysts: A comparative study of the preparation methods. Fuel Process. Technol. 2019, 193, 221–231. [Google Scholar] [CrossRef]
  54. Fu, X.; Liu, Y.; Liu, Q.; Liu, Z.; Peng, Z. Preparation of highly active Cu/SiO2 catalysts for furfural to 2-methylfuran by ammonia evaporation method. Catalysts 2022, 12, 276. [Google Scholar] [CrossRef]
  55. Du, H.; Ma, X.; Jiang, M.; Yan, P.; Conrad Zhang, Z. Highly efficient Cu/SiO2 catalyst derived from ethanolamine modification for furfural hydrogenation. Appl. Catal. A Gen. 2020, 598, 117598. [Google Scholar] [CrossRef]
  56. Nakayama, T.; Ichikuni, N.; Sato, S.; Nozaki, F. Ni/MgO catalyst prepared using citric acid for hydrogenation of carbon dioxide. Appl. Catal. A Gen. 1997, 158, 185–199. [Google Scholar] [CrossRef]
  57. Yoshida, R.; Sun, D.; Yamada, Y.; Sato, S. Stable Cu-Ni/SiO2 catalysts prepared by using citric acid-assisted impregnation for vapor-phase hydrogenation of levulinic acid. Mol. Catal. 2018, 454, 70–76. [Google Scholar] [CrossRef]
  58. Nakazono, K.; Hosaka, S.; Yamada, Y.; Sato, S. Highly active Ni/SiO2 catalyst prepared through citric acid-assisted impregnation for the hydrogenation of acetoin to 2,3-butanediol. Bull. Chem. Soc. Jpn. 2022, 95, 443–450. [Google Scholar] [CrossRef]
  59. Hosaka, S.; Kurniawan, E.; Yamada, Y.; Sato, S. Vapor-phase dehydrogenation of 1-decanol to decanal over cu/sio2 catalyst prepared by organic additives-assisted impregnation. Appl. Catal. A Gen. 2023, 653, 119079. [Google Scholar] [CrossRef]
  60. Shi, R.; Wang, F.; Mu, X.; Li, Y.; Huang, X.; Shen, W. MgO-supported Cu nanoparticles for efficient transfer dehydrogenation of primary aliphatic alcohols. Catal. Commun. 2009, 11, 306–309. [Google Scholar] [CrossRef]
  61. Sato, S.; Takahashi, R.; Sodesawa, T.; Yuma, K.I.; Obata, Y. Distinction between surface and bulk oxidation of cu through N2O decomposition. J. Catal. 2000, 196, 195–199. [Google Scholar] [CrossRef]
  62. Zhu, S.; Gao, X.; Zhu, Y.; Fan, W.; Wang, J.; Li, Y. A highly efficient and robust Cu/SiO2 catalyst prepared by the ammonia evaporation hydrothermal method for glycerol hydrogenolysis to 1,2-propanediol. Catal. Sci. Technol. 2015, 5, 1169–1180. [Google Scholar] [CrossRef]
  63. Song, T.; Chen, W.; Qi, Y.; Lu, J.; Wu, P.; Li, X. Efficient synthesis of methanol and ethylene glycol via the hydrogenation of CO2-derived ethylene carbonate on Cu/SiO2 catalysts with balanced Cu+-Cu0 sites. Catal. Sci. Technol. 2020, 10, 5149–5162. [Google Scholar] [CrossRef]
  64. Kurniawan, E.; Hara, T.; Permana, Y.; Kojima, T.; Ichikuni, N.; Shimazu, S. Creation of highly reducible CuO species by high-temperature calcination of a Cu-Al layered double hydroxide: Selective hydrogenation of furfural into furfuryl alcohol with formic acid. Bull. Chem. Soc. Jpn. 2022, 95, 121–128. [Google Scholar] [CrossRef]
  65. Yang, H.; Coolman, R.; Karanjkar, P.; Wang, H.; Dornath, P.; Chen, H.; Fan, W.; Conner, W.C.; Mountziaris, T.J.; Huber, G. The effects of contact time and coking on the catalytic fast pyrolysis of cellulose. Green Chem. 2017, 19, 286–297. [Google Scholar] [CrossRef]
  66. Arnaud-Neu, F.; Delgado, R.; Chaves, S. Critical evaluation of stability constants and thermodynamic functions of metal complexes of crown ethers: (IUPAC technical report). Pure Appl. Chem. 2003, 75, 71–102. [Google Scholar] [CrossRef]
  67. Christy, F.A.; Shrivastav, P.S. Conductometric studies on cation-crown ether complexes: A review. Crit. Rev. Anal. Chem. 2011, 41, 236–269. [Google Scholar] [CrossRef]
  68. Sun, D.; Misu, T.; Yamada, Y.; Sato, S. Advantages of using Cu/SiO2 catalyst for vapor-phase dehydrogenation of 1-decanol into decanal. Appl. Catal. A Gen. 2019, 582, 117109. [Google Scholar] [CrossRef]
  69. Karelovic, A.; Ruiz, P. The role of copper particle size in low pressure methanol synthesis via CO2 hydrogenation over Cu/ZnO catalysts. Catal. Sci. Technol. 2015, 5, 869–881. [Google Scholar] [CrossRef]
  70. Torresi, P.A.; Díez, V.K.; Luggren, P.J.; Di Cosimo, J.I. Conversion of diols by dehydrogenation and dehydration reactions on silica-supported copper catalysts. Appl. Catal. A Gen. 2013, 458, 119–129. [Google Scholar] [CrossRef]
  71. Sun, D.; Takahashi, Y.; Yamada, Y.; Sato, S. Efficient formation of angelica lactones in a vapor-phase conversion of levulinic acid. Appl. Catal. A Gen. 2016, 526, 62–69. [Google Scholar] [CrossRef]
  72. Dvořák, B.; Pašek, J. Determination of the specific copper surface area by chromatographic technique. J. Catal. 1970, 18, 108–114. [Google Scholar] [CrossRef]
  73. Evans, J.W.; Wainwright, M.S.; Bridgewater, A.J.; Young, D.J. On the determination of copper surface area by reaction with nitrous oxide. Appl. Catal. 1983, 7, 75–83. [Google Scholar] [CrossRef]
  74. Chinchen, G.C.; Hay, C.M.; Vandervel, H.D.; Waugh, K.C. The measurement of copper surface areas by reactive frontal chromatography. J. Catal. 1987, 103, 79–86. [Google Scholar] [CrossRef]
  75. Jensen, J.R.; Johannessen, T.; Livbjerg, H. An improved N2O-method for measuring Cu-dispersion. Appl. Catal. A Gen. 2004, 266, 117–122. [Google Scholar] [CrossRef]
Scheme 1. Dehydrogenation of 2,3-BDO to AC (a) and 1,4-BDO to GBL (b).
Scheme 1. Dehydrogenation of 2,3-BDO to AC (a) and 1,4-BDO to GBL (b).
Chemistry 05 00030 sch001
Figure 1. TD-MS profiles of the as-prepared none- (a) and 12C4-2Cu/SiO2 (b) and TG curves of the as-prepared none-, as-prepared 12C4-, and calcined none-2Cu/SiO2 (c).
Figure 1. TD-MS profiles of the as-prepared none- (a) and 12C4-2Cu/SiO2 (b) and TG curves of the as-prepared none-, as-prepared 12C4-, and calcined none-2Cu/SiO2 (c).
Chemistry 05 00030 g001
Figure 2. XRD profiles of 2Cu/SiO2 catalysts prepared with different organic additives before reduction (a) and none- and 12C4-2Cu/SiO2 catalysts (b).
Figure 2. XRD profiles of 2Cu/SiO2 catalysts prepared with different organic additives before reduction (a) and none- and 12C4-2Cu/SiO2 catalysts (b).
Chemistry 05 00030 g002
Figure 3. Effects of contact time, W/F, (a), reaction temperature at W/F = 1.5 (170 °C), 0.76 (200 °C), 0.36 (250 °C), and 0.36 h (275 °C) (b), N2 flow rate in 2,3-BDO dehydrogenation at a W/F = 1.1 (N2 flow at 30 cm3 min−1) and 1.5 h (N2 flow at 60 and 90 cm3 min−1) (c), and reaction temperature in AC dehydrogenation at a W/F = 2.3 (170 °C), 1.1 (200 °C), 0.73 (250 °C), and 0.73 h (275 °C) (d) over 12C4-2Cu/SiO2 catalyst.
Figure 3. Effects of contact time, W/F, (a), reaction temperature at W/F = 1.5 (170 °C), 0.76 (200 °C), 0.36 (250 °C), and 0.36 h (275 °C) (b), N2 flow rate in 2,3-BDO dehydrogenation at a W/F = 1.1 (N2 flow at 30 cm3 min−1) and 1.5 h (N2 flow at 60 and 90 cm3 min−1) (c), and reaction temperature in AC dehydrogenation at a W/F = 2.3 (170 °C), 1.1 (200 °C), 0.73 (250 °C), and 0.73 h (275 °C) (d) over 12C4-2Cu/SiO2 catalyst.
Chemistry 05 00030 g003
Figure 4. Time course of the catalytic performance in the dehydrogenation of 2,3-BDO at 200 °C and a W/F of 0.14 h over none- and 12C4-10Cu/SiO2 catalysts (a), XRD patterns of reduced and spent 10Cu/SiO2 catalysts (b), and TG profiles of the spent none-, spent 12C4-, and calcined none-10Cu/SiO2 catalysts (c).
Figure 4. Time course of the catalytic performance in the dehydrogenation of 2,3-BDO at 200 °C and a W/F of 0.14 h over none- and 12C4-10Cu/SiO2 catalysts (a), XRD patterns of reduced and spent 10Cu/SiO2 catalysts (b), and TG profiles of the spent none-, spent 12C4-, and calcined none-10Cu/SiO2 catalysts (c).
Chemistry 05 00030 g004
Figure 5. Effect of Cu content (a) and SACu (b) on formation rate of AC at 200 °C.
Figure 5. Effect of Cu content (a) and SACu (b) on formation rate of AC at 200 °C.
Chemistry 05 00030 g005
Figure 6. Catalytic performance at 260 °C and a W/F of 0.080 h over none- and 12C4-10Cu/SiO2 (a) and TG profiles of the spent none-, spent 12C4-, and calcined none-10Cu/SiO2 catalysts (b).
Figure 6. Catalytic performance at 260 °C and a W/F of 0.080 h over none- and 12C4-10Cu/SiO2 (a) and TG profiles of the spent none-, spent 12C4-, and calcined none-10Cu/SiO2 catalysts (b).
Chemistry 05 00030 g006
Figure 7. Effect of contact time, W/F, in the dehydrogenation of 1,4-BDO to GBL over 10Cu/SiO2 catalyst at 260 °C (a), effect of Cu content at 240 °C and W/F = 0.054 h (b), and relation between Cu surface area on formation rate of GBL at 240 °C (c).
Figure 7. Effect of contact time, W/F, in the dehydrogenation of 1,4-BDO to GBL over 10Cu/SiO2 catalyst at 260 °C (a), effect of Cu content at 240 °C and W/F = 0.054 h (b), and relation between Cu surface area on formation rate of GBL at 240 °C (c).
Chemistry 05 00030 g007
Scheme 2. Consecutive reaction from 1,4-BDO to GBL.
Scheme 2. Consecutive reaction from 1,4-BDO to GBL.
Chemistry 05 00030 sch002
Table 1. Effect of organic additive on the catalytic performance of 2Cu/SiO2 catalyst in the dehydrogenation of 2,3-BDO.
Table 1. Effect of organic additive on the catalytic performance of 2Cu/SiO2 catalyst in the dehydrogenation of 2,3-BDO.
EntryOrganic AdditiveDSACu/
m2 g−1
Conversion a/
mol%
Selectivity a/mol%
ACDA
1none0.2482.7619.099.30.0
212C40.6327.0656.498.81.0
315C50.6136.8443.099.20.5
418C60.5215.8138.999.30.4
5CA0.5497.1250.299.01.0
Reaction conditions: Reaction temperature, 200 °C; W/F, 0.18 h. a Average conversion and selectivity at TOS of 0–1 h.
Table 2. Comparison of the productivity of AC over various reported Cu catalysts.
Table 2. Comparison of the productivity of AC over various reported Cu catalysts.
CatalystTemp.
/°C
W/F
/h
TOS
/h
Conv.
/mol%
AC Selec.
/mol%
AC Prod.
/g g−1 h−1
Ref.
20.3Cu/SBA-15280--9.9 *>90-[37]
20Cu/SiO2-AE b280-176.094.5-[38]
Li-CuZnAl26010.010072.495.60.07[40]
15Cu-Al2O31704.00-63.096.00.15[39]
12C4-10Cu/SiO22000.141260.998.74.20This work
12C4-2Cu/SiO22000.71576.997.61.04
1701.43553.999.20.36
* Reaction rate of 2,3-BDO in mmol min−1 g−1. b AE: prepared by ammonia evaporation.
Table 3. Comparison of the productivity of GBL over various reported Cu catalysts.
Table 3. Comparison of the productivity of GBL over various reported Cu catalysts.
CatalystSACu
/m2 g–1
Temp.
/°C
W/F
/h
TOS a
/h
Conv.
/mol%
Select.
/mol%
GBL Prod.
/g gcat−1 h−1
Ref.
Cu/ZnO/ZrO2/Al2O3 b40.32400.08584989.63[41]
12Cu/SiO23.902500.5010100981.92[17]
10Cu/La2O3/ZrO28.402501.001397960.91[43]
10Cu/SBA-158.682501.0017100980.95[44]
10Cu/CeO25.602400.50193981.78[18]
10Cu/CeO2-Al2O3-2400.501100991.94[45]
12C4-10Cu/SiO226.12600.27598.898.53.44This work
0.054581.495.713.8
a Time on stream in a flow system. b Prepared by co-precipitation; Cu content, 41.8 wt.-%.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Kurniawan, E.; Hosaka, S.; Kobata, M.; Yamada, Y.; Sato, S. Vapor-Phase Oxidant-Free Dehydrogenation of 2,3- and 1,4-Butanediol over Cu/SiO2 Catalyst Prepared by Crown-Ether-Assisted Impregnation. Chemistry 2023, 5, 406-421. https://doi.org/10.3390/chemistry5010030

AMA Style

Kurniawan E, Hosaka S, Kobata M, Yamada Y, Sato S. Vapor-Phase Oxidant-Free Dehydrogenation of 2,3- and 1,4-Butanediol over Cu/SiO2 Catalyst Prepared by Crown-Ether-Assisted Impregnation. Chemistry. 2023; 5(1):406-421. https://doi.org/10.3390/chemistry5010030

Chicago/Turabian Style

Kurniawan, Enggah, Shuya Hosaka, Masayuki Kobata, Yasuhiro Yamada, and Satoshi Sato. 2023. "Vapor-Phase Oxidant-Free Dehydrogenation of 2,3- and 1,4-Butanediol over Cu/SiO2 Catalyst Prepared by Crown-Ether-Assisted Impregnation" Chemistry 5, no. 1: 406-421. https://doi.org/10.3390/chemistry5010030

APA Style

Kurniawan, E., Hosaka, S., Kobata, M., Yamada, Y., & Sato, S. (2023). Vapor-Phase Oxidant-Free Dehydrogenation of 2,3- and 1,4-Butanediol over Cu/SiO2 Catalyst Prepared by Crown-Ether-Assisted Impregnation. Chemistry, 5(1), 406-421. https://doi.org/10.3390/chemistry5010030

Article Metrics

Back to TopTop