PROJECT PROGRESS REPORT ADVANCED METHOD FOR RENEWABLE ETHANOL BY DIRECT SYNTHESIS FROM SYNGAS FOR RENEWABLE FUEL APPLICATIONS Submitted To The 2012 Summer NSF CEAS REU Program Part of NSF Type 1 STEP Grant Sponsored By The National Science Foundation Grant ID No.: DUE-0756921 College of Engineering and Applied Science University of Cincinnati Cincinnati, Ohio Prepared By Julia Fisher, Chemical Engineering, Arizona State University Nathalia Backeljauw, Chemical Engineering, University of Cincinnati Report Reviewed By: _____________________________________________________________________ Dr. Panagiotis (Peter) Smirniotis REU Faculty Mentor Professor and Chairman School of Energy, Environmental, Biological and Medical Engineering University of Cincinnati August 9, 2012 Direct Synthesis of Ethanol from Syngas for Renewable Fuel Applications Julia Fisher, Chemical Engineering, Arizona State University Nathalia Backeljauw, Chemical Engineering, University of Cincinnati Abstract The main objective of this project is to produce ethanol from syngas, which is a mixture of carbon monoxide and hydrogen gas, by a thermo-chemical catalytic route. The overall goal this project is trying to achieve is to use ethanol as a renewable energy source. To accomplish this, various mesoporous rhodium-based catalysts supported by mesoporous molecular sieves are synthesized by the wet impregnation method and calcined at 673 K. SBA-15, MCM-41, and MCM-48 are chosen as the mesoporous molecular sieves. The pure mesoporous molecular sieve supports are synthesized by a procedure, which is reported in our previous studies. The characterization of the catalysts is achieved by the XRD, BET and TPR techniques. The reactions of syngas to ethanol carried out over these catalysts and products are analyzed by G.C. Rh/SBA-15 had a higher CO conversion and ethanol selectivity in comparison to MCM-41 and MCM-48, therefore making it the most suitable catalyst out of the three. Key Words 1. Ethanol (as fuel); 2. XRD, TPR; 3. SBA-15, MCM-41, MCM-48; 4. Mesoporous molecular sieve 2 Introduction Increasing concerns about global climate change, depletion of fossil fuel resources, and rising crude oil prices have pushed the topic of energy to the center stage. Bio-ethanol can be used in engines, offering a nearly equivalent combustion energy than that of gasoline, while being a renewable and hence carbon-neutral fuel. Therefore, bio-ethanol is favorable towards the greenhouse gas emissions. As a fuel, ethanol has several ideal properties: it is nontoxic, easy to store, results in lower net petroleum use and lowers greenhouse gas emissions. Corn is the largest source of ethanol in the United States. In 2011, the U.S. harvested 12.36 billion bushels of corn, with the gross demand for ethanol being 40% of that total (RFA 2012). However, only 3.5 billion bushels converted to ethanol, and the remaining bushels became livestock feed. Only about 26% of the 12.36 billion bushels was directly consumed for the production of ethanol (RFA 2012). These percentages could change in the future because the Renewable Fuel Standard (RFS) demands that the U.S. makes 36 billion gallons per year of renewable fuel by 2022 (RFA 2012). If the reliance on corn as the primary source for ethanol continues, it could become an issue with the growing population’s demand for corn. Therefore, the investigation and research of other methods to produce ethanol will become increasingly important to solve this problem. Not only is it essential to find another source for ethanol to avoid food shortage for the increasing population, but it is also imperative to find another source that has less limitations, such as location and cost. The production of corn and ethanol from corn are both very centralized in the Midwest, creating a major limitation on the U.S. 3 today (Somma et al. 2010). The current method for transporting ethanol is by truck instead of pipeline because ethanol is corrosive to steel; this leads to the majority of higher ethanol blends, such as E-85, being consumed where it is produced (Somma et al. 2010). Alternatives such as syngas have fewer limitations than corn for ethanol synthesis. Syngas can be produced by partial combustion, which means it can be derived from a multitude of sources such as non-food plant material (Somma et al. 2010). Syngas can also be transported through the current natural gas lines, which makes it easily accessible throughout the U.S., enabling the building of ethanol plants across the country and not just in the Midwest. The main objective of the present investigation is to produce ethanol from syngas with the help of a catalyst, as shown in Fig. 1. The aim of this project is to engineer more efficient and effective catalysts that will convert as much carbon monoxide as possible while maximizing the ethanol selectivity. Rh-based catalysts are used to produce ethanol because Rhodium is known to selectively produce ethanol from syngas under the right conditions (Spivey, et al. 2007). 4 Figure 1. Reaction Matrix (Mei, et al. 2010) The reaction matrix shows the steps to produce the possible products, and the green arrows display the steps to produce ethanol from syngas. Materials and Methods Calibration For the calibration process, the primary piece of equipment used is the Gas Chromatographer (GC). Within the GC itself is the Thermal Conductivity Detector (TCD) and the Flame Ionization Detector (FID), which are connected in a series. The GC separates and records the retention times of carbon monoxide, carbon dioxide, nitrogen, methane, ethanol and methanol. The computer software connected to the GC is the HP Chem Station Software. 5 Synthesis of Catalysts: Preparation of Pure Mesoporous Molecular Sieves All the chemicals are used as received from companies without any further purification. SBA-15 To synthesize the SBA-15 molecular sieve, 3 grams of P-123 were dissolved in a mixture of 15 mL of hydrochloric acid and 80 mL of distilled water. The solution was stirred at 35°C until it became clear. 7 grams of tetraethyl orthosilicate were added to the aforementioned solution and stirred for 24 hours at 35°C. Then, the solution was transferred into a sealed teflon bottle and heated for 48 hours at 110°C. The solution was then filtered, washed with distilled water and dried at 100°C for 12 hours. The final powder was calcined at 500 oC for 5 hours with a heat ramp of 2°C/minute. MCM-41 To prepare the MCM-41, 3 ml of deionized (DI) water were added to 35 ml of Ludox HS-40 colloidal silica (40%) under stirring, and then 30.32 ml of 25% tetramethylammonium hydroxide (Aldrich, 25%) were added. Independently, 18.25 g of cetyltrimethylammonium bromide (CTABr, Alfa Aesar) were dissolved in 33 ml of water. 7 mL of ammonium hydroxide (Fisher, 29.6%) were introduced when the CTABr solution became a transparent gel and could be magnetically stirred again. Then, the latter solution was transferred to the first solution. The final mixture was stirred for 2 h at 80°C, then transferred into a Teflon bottle and treated under autogenous pressure without stirring at 100°C for 3 days. The resulting solids were filtered, washed, and airdried. The dried powder was calcined at 550°C for 10 h under a moderate airflow with a temperature ramp of 2°C/min. 6 MCM-48 To begin the synthesis of MCM-48, 17.5 g of CTABr and 1.92 g of sodium hydroxide were dissolved in 99 ml of DI water, and then 20.8 g of tetraethyl orthosilicate (TEOS) (Aldrich) were added into the mixture. The resulting gel was stirred at room temperature for about 1 h and then transferred into a Teflon bottle and treated under autogenous pressure without stirring at 100°C for 3 days. The solution was cooled to room temperature, and its pH was adjusted to 7.0 by adding HCl. Then, it was heated at 373 K for another 2 days. The final materials were filtered, washed, dried at ambient temperature, and calcined at 550°C for 6 h under flowing air at a heating rate of 2°C/min. Rh-based catalysts supported by mesoporous molecular sieves The Rh-based catalysts were synthesized by the wet impregnation method. In this synthesis method, mesoporous material was added to the Rhodium nitrate solution and stirred at 100°C until all liquids evaporated. Afterwards, the powder remained on the stirring plate to dry for 12 hours at 100°C. The powder was then calcined at 400°C for four hours, with a heat ramp of 5°C/minute. 2wt% Rhodium is used for all of the catalysts. Characterizations BET surface area and pore size distribution BET surface area and pore size distribution studies were conducted at −196°C using a Micromeritics ASAP 2010 apparatus to characterize the synthesized photocatalysts. Samples of 0.05–0.06 g were degassed at 300°C for at least 10 h in the 7 degassing port of the apparatus. Using the BET method, the surface area was calculated from adsorption isotherms. The pore size was obtained from the adsorption branch of the isotherm using the BJH method. The results obtained are listed in Table 1. XRD All pure mesoporous materials prepared were characterized using a Nicolet powder X-ray diffractometer equipped with a Cu-Kα source to assess their structure and crystallinity. The synthesized MCM-41 and MCM-48 samples were run with 2θ changing from 2° to 7° to assess the structure of the MS matrix. SBA-15 was run with 2θ changing from 1.5° (XRD machine's limit) to 3° to assess the structure of the SBA-15 matrix. TPR measurement The TPR was carried out in a temperature range of 50–550°C on a Micromeritics Autochem 2910 instrument with a temperature ramp of 2°C/min. The samples were pretreated at 200°C with ultrahigh-purity O2 (Matheson) for 2 h. A total of 10 mL/min of 10% H2 in Ar (Matheson) was passed through the sample tube during the measurement. Catalytic Activity The catalysts were evaluated in a fixed bed microreactor (9 mm diameter, 500 mm length). The temperature of the reactor was controlled via a temperature controller. Mass flow meters were used to add H2 and CO at a desired rate to the reactor. The catalyst (0.3 g) was mixed with the same amount of quartz glass beads placed in the reactor, and the reactor temperature was increased from room temperature to 300 oC at 8 a rate of 2 oC o C/min. The catalyst was reduced in situ in a flow of H2 (20 mL/min) at 300 for 2 h. Synthesis gas, with a flow rate of 21 mL/min (H2/CO ratio of 2.0), was introduced and the reactor pressure was increased to 350 psi. The compositions of the outlet gas and liquid streams were determined using an online HP 6890 gas chromatograph equipped with a Porapak Q column and a TCD and FID detector. The typical reactor diagram is shown in Fig. 2. Figure 2. Reactor Diagram This is a schematic of the setup used for the reactions. 9 Results and Discussion Physical Properties Table 1. Physical Properties of Mesoporous Materials (Data from Sun, et al. 2006) Mesoporous BET Pore volume Pore diameter Unit cell Materials Surface area (cm3/g) (Å) parameter 2 (m /g) (Å) MCM-41 1143 1.03 35 43 MCM-48 983 0.65 26 89 SBA-15 827 1.21 57 117 As shown in Table 1, MCM-41 displays the highest BET surface area, 1143 m 2/g. However, SBA-15 has the largest pore diameter, 57 Å, and pore volume, 1.21 cm3/g. Due to the large surface area of MCM-41 and the large pore diameter and pore volume of SBA-15, they’re expected to improve the activity of the catalysts. There was a slight reduction in the surface area after the catalysts were impregnated with Rh, due to pore blockage by Rh. However, pore diameters of the catalysts remained unchanged. Figure 3. XRD of MCM-41, MCM-48, SBA-15 (Sun, et al. 2006) 10 To be characterized as a mesoporous material, the samples must exhibit peaks at lower angles, which Fig. 3 confirms. SBA-15 has a peak at 2° 2θ and the lowest intensity of the three mesoporous materials. MCM-41 and MCM-48 both have a peak at 2.5° 2θ. MCM-41 has the highest intensity, followed by MCM-48. Figure 4 3+ 0 Intensity (a.u.) Rh to Rh Rh/MCM-48 Rh/MCM-41 Rh/SBA-15 100 200 300 400 500 600 700 o Temperature ( C) Temperature Programmed reduction profiles of Rhbased catalysts supported on mesoporous molecular sieves The TPR results in Fig. 4 show that the Rh in the samples was in the 3+ oxidation state. When it reached 330°C, the Rh in the sample converted directly to Rhodium metal in the 0 oxidation state. 11 Table 2: Effect of mesoporous molecular sieve on the catalytic activity of Rh-based catalysts Catalyst CO conversion (%) Selectivity (%) Ethan ol Methan ol Methane CO2 Rh/SBA 32 -15 12 8.4 32.3 44.5 Rh/MC M-41 30 6.4 5.9 42.3 52.4 Rh/MC M-48 28 5.8 6.2 40.5 51.4 Nominal conditions are T = 573 K, P = 350 psi, 0.30 g catalyst, H2: CO = 2:1, syngas flow = 21 cm3 (STP)/min. Conversion (%) = ΣniMi X 100/MCO and selectivity = niMi/ΣniMi where ni is the number of carbon atoms in product i, Mi is the mole percent of product i measured, and MCO is the mole percent of carbon monoxide in the feed. The activity results show that under these conditions, the SBA-15 has the best qualities for syngas to ethanol conversion, when compared with MCM-41 and MCM-48. It had the highest CO conversion, 32%, and the highest ethanol selectivity, 12%. 12 References Liu, Y., Murata, K., Inaba, M., Takahara, I., Okabe, K. (2011). “Synthesis of ethanol from syngas over Rh/Ce1-xZrxO2 catalysts,” Catalysis Today, ASCE, Vol. 164, No. 1, pp. 308-314. Mei, D., Rousseau, R., Kathman, S. M., Glezakou, V., Engelhard, M. H., Jiang, W., Wang, C., Gerber, M. A., White, J. F., Stevens, D. J. (2010). “Ethanol synthesis from syngas over Rh-based/SiO2 catalysts: A combined experimental and theoretical modeling study,” Catalysis Today, ASCE, Vol. 271, No. 2, pp. 325-342. Renewable Fuels Association. (2012). "Accelerating Industry Innovation." 2012 Ethanol Industry Outlook, <http://ethanolrfa.3cdn.net/d4ad995ffb7ae8fbfe_1vm62ypzd.pdf> (July 11, 2012). Somma, D., Lobkowicz, H., Deason, J.P. 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