Tsz-Lung Kwongab and
Ka-Fu Yung*ab
aDepartment of Applied Biology and Chemical Technology, The Hong Kong Polytechnic University, Hung Hom, Kowloon, Hong Kong, China. E-mail: bckfyung@polyu.edu.hk; Fax: +852 2364 9932; Tel: +852 3400 8863
bShenzhen Research Institute of the Hong Kong Polytechnic University, Shenzhen 518057, China
First published on 23rd September 2015
A bimetallic alkaline earth metal–transition metal oxide, synthesized through a method of direct low-temperature decomposition of the bimetallic complex, is reported for the synthesis of biodiesel. Due to the high phase purity of the Ca/Fe catalytic system and its catalytic stability and robustness, the Ca/Fe catalyst was selected for further investigation. A transesterification conversion of 99.5% could be achieved in 1 h under the optimal conditions: feedstock to methanol, 1:
20; catalyst loading, 6 wt%; temperature, 120 °C. ANOVA tests suggested that the reaction temperature was discerned as the most prominent factor which contributed 82.84% to the overall catalytic feedstock conversion. In addition, the Ca/Fe catalytic system demonstrated a high FFA tolerance of 2 wt% and a water tolerance of 1 wt% with remarkable catalytic activity in one-step biodiesel synthesis.
The use of different heterogeneous base catalysts for catalytic transesterification, such as alkaline earth metal oxides and hydroxides, has been widely reported in the literature.7–11 The catalytic activities of alkaline earth metal oxides, including magnesium oxide (MgO), calcium oxide (CaO), strontium oxide (SrO) and barium oxide (BaO), were closely related to their surface basic strength. The basicity increased with atomic number, which increased with increasing cationic size and decreasing polarizing power. This destabilized the O2− anions.12 As a result, the catalytic activities of the four catalysts demonstrated the sequence MgO < CaO < SrO < BaO.13 BaO is the strongest basic oxide but it is soluble in methanol and exhibits a high toxicity.9 Although SrO is insoluble in methanol, it would be deactivated by atmospheric moisture and carbon dioxide (CO2).13
It is believed that CaO is one of the reactive single oxides and has been widely employed for transesterification reactions because of its high catalytic activity and low preparation cost. However, the use of alkaline metal oxides is often confronted with low durability and serious leaching problems due to metal dissolution. This accounts for the loss of the active species from metal oxide catalysts, with the catalytic activity declining significantly upon regeneration.14–16 Furthermore, the adsorption of water molecules and CO2 on the active sites of the alkaline earth metal oxides would suppress the esterification and transesterification reactions.16,17
In order to improve the dissolution of the active metal, various alkali metal oxides supported on alumina,18–20 CaO supported on silica21 and CaO mixed with zinc oxide (ZnO)22,23 have been reported as heterogeneous catalysts for transesterification. However, it was found that leaching was not improved as these catalysts demonstrated poor reusability and robustness. More recently, mixed metal oxides such as hydrotalcites24 and Ca–La mixed oxides have been explored.25 In our previous work, we studied the transesterification of Camelina sativa oil with methanol to synthesize biodiesel using Na0.1Ca0.9TiO3 nanorods as a heterogeneous catalyst, synthesized through alkali hydrothermal synthesis.26 The leaching was not improved due to the existence of single oxides.16 Furthermore, low grade alcohols and unrefined feedstocks containing high degrees of water cause the hydrolysis of triglyceride to form diglyceride and free fatty acid (FFA) while the high levels of FFA contamination will subsequently induce saponification and deactivate the base catalysts.27,28
Owing to the high toxicity of Ba and the low stability of Sr in air, this study focused on Mg and Ca for biodiesel synthesis from low grade feedstocks with high levels of FFA contamination. The most abundant transition metals, such as iron (Fe), manganese (Mn) and chromium (Cr), were proposed to act as stabilizers to retain the alkaline earth metal, Mg and Ca, in a bimetallic catalytic system and further enhance its catalytic stability and robustness. Srebrodolskite type materials are heterogeneous catalysts for use in various applications. This material with a general formula of A2B2O5 consists of divalent cations and trivalent cations. The conventional synthesis of srebrodolskite Ca2Fe2O5 involves the mixing and grinding of CaO and Fe2O3 followed by a high temperature calcination at over 1000 °C for 3 h in air.29 These harsh synthetic conditions would surely lead to the formation of highly aggregated particles which decreases the resultant surface area-to-volume ratio. Co-precipitation is another commonly employed preparation method which induces phase separation of metal oxide instead of forming a final single phase mixed metal oxide. Xue and co-workers have reported the synthesis of a Ca2Fe2O4–Ca2Fe2O5-based catalyst for biodiesel synthesis, however, a mixed phase catalyst was observed.30
Herein, a series of alkaline earth metal–transition metal bimetallic oxide catalysts for transesterification with methanol have been investigated. These mixed oxide catalysts have been synthesized through low-temperature decomposition of the corresponding bimetallic complex, in which the bimetallic complex is directly calcinated under atmospheric conditions to yield the desired catalyst. Switching of the inorganic metal salts to organometallic complexes is found to significantly decrease the calcination temperature which prevents the formation of highly aggregated catalysts. The FFA and water tolerance of the catalytic system were also investigated. Meanwhile, the reaction conditions for transesterification were optimized. The optimization is very important to maximize the biodiesel yield and to minimize the production cost. A stepwise approach has been extensively employed, however, it is relatively time consuming and difficult to determine the optimal conditions as some of the reaction conditions simultaneously affect the biodiesel yield. Taguchi analysis is a cost-effective and time saving alternative approach for optimization in which the analysis can be divided into orthogonal array experiments, signal-to-noise (S/N) ratio analysis and range analysis.31–35 Analysis of variance (ANOVA) was also introduced as a statistical model to evaluate whether the factors were prominent using an F-test under consideration of the experimental error.
Feedstock | AD (wt%) | AV (mgKOH g−1) | Water (wt%) |
---|---|---|---|
Refined food grade canola oil | 0.11 | 0.22 | 0.13 |
Crude flaxseed oil | 1.16 | 2.32 | 0.12 |
Crude rapeseed oil | 1.65 | 3.28 | 0.13 |
Crude rice bran oil | 2.00 | 3.98 | 0.11 |
Waste cooking oil | 0.65 | 1.29 | 0.12 |
Fatty acid profile of each feedstock was analyzed on a HEWLETT 5890 SERIES II Gas Chromatograph system equipped with a flame-ionization detector and a capillary column (DURABOND-WAX, 30 m × 0.250 mm, film thickness of 0.5 μm, part no.: 122-7033). The operating conditions for the analysis were as follows: the injector temperature was 280 °C; the detector temperature was 280 °C; the temperature program was started at 180 °C at a rate of 2 °C min−1 to 240 °C. All of the feedstocks contained fatty acid chain lengths of 16 to 22, which are desirable for biodiesel synthesis, as summarized in Table 2.
Feedstock | Fatty acid compositiona (%) | ||||||
---|---|---|---|---|---|---|---|
C16![]() ![]() |
C18![]() ![]() |
C18![]() ![]() |
C18![]() ![]() |
C18![]() ![]() |
C20![]() ![]() |
C22![]() ![]() |
|
a C16![]() ![]() ![]() ![]() ![]() ![]() ![]() ![]() ![]() ![]() ![]() ![]() ![]() ![]() |
|||||||
Refined food grade canola oil | 5.00 | 2.68 | 63.06 | 22.82 | 6.44 | — | — |
Crude flaxseed oil | 6.06 | 2.53 | 19.19 | 24.34 | 47.88 | — | — |
Crude rapeseed oil | 3.91 | 1.41 | 17.05 | 12.94 | 9.03 | 14.54 | 41.12 |
Crude rice bran oil | 19.33 | 2.79 | 43.66 | 34.22 | — | — | — |
Waste cooking oil | 21.88 | 5.15 | 56.73 | 14.48 | 0.86 | 0.90 | — |
![]() | (1) |
The reaction was allowed to cool down to room temperature after completion of the catalytic reaction. The used catalyst was isolated out and was dried at room temperature for the next cycle of the catalytic reaction without any washing steps. The same amount of fresh feedstock and methanol were added to the recycled catalyst and the catalytic study was performed for several cycles under the same conditions.
The quantity of active metals leached into the biodiesel layer from the catalyst was determined through inductively coupled plasma optical emission spectroscopy (ICP-OES) using an Agilent Technologies 700 Series ICP-OES. A sample of 0.1 mL was pre-digested in a mixture of concentrated hydrochloric acid and concentrated nitric acid (3:
1 v/v) at a temperature of 60 °C for 2 h.
![]() | ||
Fig. 1 SEM micrographs of the (a) Mg/Fe, (b) Ca/Fe, (c) Mg/Mn, (d) Ca/Mn, (e) Mg/Cr and (f) Ca/Cr catalytic systems. (g) TEM and (h) HR-TEM of the Ca/Fe nanoparticle catalyst. |
Catalytic system | Atomic ratio in EDX analysis | Surface basicity |
---|---|---|
Mg/Fe | 1.1 | 7.2 < ![]() |
Ca/Fe | 1.0 | 10.2 < ![]() |
Mg/Mn | 1.0 | 7.2 < ![]() |
Ca/Mn | 0.9 | 9.7 < ![]() |
Mg/Cr | 0.9 | 7.2 < ![]() |
Ca/Cr | 0.9 | 7.2 < ![]() |
CaO | — | 10.2 < ![]() |
The crystal structures of all of the catalysts were characterized using XRD as depicted in Fig. 2. A high phase purity in the XRD pattern is observed for Ca/Fe which matches to the orthorhombic phase Ca2Fe2O5 (ICDD: 01-076-8615). For the Mg/Fe catalytic system, it is suspected that amorphous MgO is present as only cubic phase MgFe2O4 (ICDD: 01-088-1936) was found in the XRD analysis with a theoretical Mg-to-Fe ratio of 0.5, which deviated from the atomic ratio found in the EDX analysis. Mixed XRD patterns obtained in the Mg/Mn catalytic system are attributed to tetragonal phase MgMn2O4 (ICDD: 01-074-2023), hexagonal phase MgMnO3 (ICDD: 024-0736) and single orthorhombic Mn3O4 (ICDD: 01-072-7943). The diffraction peaks in the Ca/Mn catalytic system show agreement with a mixed phase of orthorhombic CaMn2O4 (ICDD: 01-072-6399) and monoclinic Ca2Mn3O8 (ICDD: 034-0469). The XRD patterns of the Mg/Cr and Ca/Cr catalytic systems demonstrate cubic MgCr2O4 (ICDD: 010-0351) and tetragonal CaCrO4 (ICDD: 008-0458) respectively, however, single Cr2O3 is found in both catalytic systems. Single phase mixed oxides are obtained only in the Mg/Fe and Ca/Fe catalytic systems due to good matching of the Mg(II) ion or Ca(II) ion to the Fe(III) ion. In contrast, mixed phases of mixed metal oxides are observed in the other catalytic systems, probably due to size mismatching of the alkaline earth metal ion and transition metal ion. It is well known that both Mn and Cr have multiple stable oxidation states. Under atmospheric conditions at 600 °C, Mn3+ and Cr3+ should be oxidized to higher oxidation states. Therefore, a mixture of single oxide and mixed oxide was obtained for Mn or Cr containing catalytic systems as suggested by the XRD analysis.
![]() | ||
Fig. 2 XRD spectra of the (a) Mg/Fe, (b) Ca/Fe, (c) Mg/Mn, (d) Ca/Mn, (e) Mg/Cr and (f) Ca/Cr catalytic systems. |
It has been reported that the basic sites on the surface of heterogeneous catalysts are the active sites for catalytic transesterification.40,41 Therefore, it is important to investigate the correlation between the surface basic strength and the catalytic activity of heterogeneous catalysts. As shown in Table 3, all of the catalytic systems demonstrate a basic property on the catalyst surface as detected through Hammett indicator analysis. The Ca/Fe catalytic system and single CaO exhibit the highest surface basicity with 10.2 < < 11.0, which could be considered as strong solid bases while the Ca/Mn catalytic system was considered a mild solid base catalyst with 9.7 <
< 10.2. The Mg/Fe, Mg/Mn, Mg/Cr and Ca/Cr catalytic systems were considered as neutral to weak basic catalysts with a low surface basicity of 7.2 <
< 9.7. The surface basicity of the Ca/Fe catalytic system is much higher than that of Ca2Fe2O5 synthesized through high temperature calcination by Kawashima, which is only in the range of 7.2 to 9.3.42 Other catalytic systems, such as M/Fe, Mg/Mn, Mg/Cr and Ca/Cr, gave relatively low surface basicity in the range of 7.2 to 9.7.
The BET specific surface area of the Ca/Fe catalytic system was found to be 32.7 m2 g−1, as determined from the BET adsorption/desorption isotherm, which is 46 times and 4 times the surface areas reported by Kawashima42 and Xue30 respectively.
Catalytic system | Reaction time (h) | Catalytic conversiona (%) | ||||
---|---|---|---|---|---|---|
1 | 2 | 3 | 4 | 5 | ||
a Reaction conditions: feedstock-to-methanol molar ratio of 1![]() ![]() |
||||||
Mg/Fe | 4 | 47.3 | 37.8 | 25.3 | — | — |
Ca/Fe | 1 | 98.7 | 89.0 | 81.9 | 71.7 | 37.5 |
Mg/Mn | 4 | 71.1 | 33.9 | — | — | — |
Ca/Mn | 4 | 97.8 | 32.4 | — | — | — |
Mg/Cr | 4 | 79.1 | 12.9 | — | — | — |
Ca/Cr | 4 | 80.3 | 12.5 | — | — | — |
CaO | 1 | 99.6 | — | — | — | — |
The Ca/Fe catalyst was the only catalytic system which could be reused for over 4 cycles. It demonstrates that Fe, found in most abundance in the bimetallic Ca2Fe2O5 catalytic system, stabilizes the Ca and further enhances its catalytic stability and robustness. In contrast, CaO was completely dissolved at the end of the first cycle which implied that CaO underwent homogeneous catalysis rather than heterogeneous catalysis and cannot be regenerated for the next cycle.
The EDX analysis of the used Ca/Fe catalytic system suggests that the atomic Ca-to-Fe ratio is equal to 0.69 which indicates a significant loss of Ca after the fifth catalysis cycle. In order to further confirm the loss of Ca and Fe from the catalyst, the amounts of metal leaching out were analyzed through ICP-OES of the reaction mixture. As depicted in Table 5, the amount of Ca and Fe leached to the biodiesel layer ranged from 310.5 to 1489.5 mg L−1 and 26.9 to 532.7 mg L−1 which aligns with the decrease in Ca as suggested in the EDX analysis. It is found that the extent of Ca leached from the bimetallic Ca/Fe system was smaller than that from CaO14,15 as it was totally dissolved during the catalysis.
Cycle | Concentration of metal found in the biodiesel layer (mg L−1) | |
---|---|---|
Ca | Fe | |
1 | 1489.5 ± 0.3 | 532.7 ± 0.3 |
2 | 299.8 ± 0.5 | 114.9 ± 0.3 |
3 | 310.5 ± 0.5 | 80.3 ± 0.2 |
4 | 320.3 ± 0.7 | 112.1 ± 0.3 |
5 | 360.2 ± 0.7 | 26.9 ± 0.2 |
Apart from the extension of the catalytic activity, magnetic recycling of the used Ca/Fe catalysts was also studied. After ultrasonic treatment of the reaction mixture, a strong rare earth based magnet was placed on the side wall of the reaction flask for 30 min. The Ca/Fe catalyst diffused to one side with a strong magnet (see ESI Fig. S1†). This concludes that the Ca/Fe catalytic system is a magnetic catalyst which favours magnetic separation and recovery for the next catalytic cycle. A similar observation was reported by Zhang.43
Entry | Factor | Conversion (%) | Average Yi (%) | Standard deviation | S/N ratio | ||||
---|---|---|---|---|---|---|---|---|---|
Feedstock![]() ![]() |
Catalyst loading B (wt%) | Reaction temperature C (°C) | y1 | y2 | y3 | ||||
1 | 1![]() ![]() |
2 | 80 | 2.2 | 2.2 | 2.1 | 2.2 | 0.06 | 6.71 |
2 | 1![]() ![]() |
4 | 100 | 20.4 | 20.9 | 21.1 | 20.8 | 0.36 | 26.36 |
3 | 1![]() ![]() |
6 | 120 | 40.5 | 40.7 | 41.4 | 40.9 | 0.47 | 32.23 |
4 | 1![]() ![]() |
2 | 100 | 14.8 | 14.1 | 14.6 | 14.5 | 0.36 | 23.22 |
5 | 1![]() ![]() |
4 | 120 | 77.4 | 78.4 | 78.2 | 78.0 | 0.53 | 37.84 |
6 | 1![]() ![]() |
6 | 80 | 8.4 | 8.3 | 8.0 | 8.2 | 0.21 | 18.31 |
7 | 1![]() ![]() |
2 | 120 | 33.9 | 33.0 | 32.8 | 33.2 | 0.59 | 30.43 |
8 | 1![]() ![]() |
4 | 80 | 5.6 | 5.3 | 5.3 | 5.4 | 0.17 | 14.64 |
9 | 1![]() ![]() |
6 | 100 | 37.5 | 36.5 | 36.0 | 36.7 | 0.76 | 31.28 |
![]() | ||
Fig. 3 Relationship between (a) feedstock-to-methanol molar ratio, (b) catalyst loading, (c) reaction temperature and their corresponding mean Sji value. (d) Range values of each factor. |
For an increase of the feedstock-to-methanol molar ratio from 1:
10 to 1
:
30, the feedstock conversion steadily increases and then slightly decreases beyond the optimal ratio (1
:
20). As the transesterification reaction involves three successive reversible reactions, a higher feedstock-to-methanol molar ratio is usually employed to drive the equilibrium to the product side. Other ratios beyond the optimal (1
:
20) do not increase the biodiesel yield as large amounts of methanol decrease the concentration of substrate in the reaction mixture.44–46 It is clear that there is an increase of catalytic conversion with an increase of catalyst loading from 2 wt% to 6 wt%. This may due to the availability of more active sites on the catalyst surface to generate alkoxide anions and enhance the catalytic transesterification.46,47 Further increasing the catalyst loading (6 wt%) did not enhance the catalytic conversion significantly as the amount of active sites were already saturated. Also, it is likely to be due to the mass transfer inefficiency of the catalyst in the three separated phase system and the blockage of active sites by methyl ester products.48,49 The feedstock conversion is found to be enhanced when the reaction temperature is increased from 80 °C to 120 °C. The increase in temperature to 120 °C would increase the kinetic energy of the substrates which leads to a higher diffusion rate and increases the collisions between the Ca2Fe2O5 catalyst and the substrates for faster catalytic transesterification.50 Furthermore, higher temperature would reduce the viscosity of the feedstock sample.51
At the 90% confidence level, the ANOVA results (Table 7) are FA (5.65) < Fα; FB (13.90) > Fα and FC (99.20) > Fα. The catalyst loading (factor B) and reaction temperature (factor C) are prominent factors affecting the biodiesel yield. Furthermore, the reaction temperature (factor C) gives the highest percent contribution of 82.84% to the final catalytic activity, followed by catalyst loading (factor B, 11.61%) and feedstock-to-methanol molar ratio (factor A, 4.72%). The experimental error contributes 0.83% which implies that all of the experimental results collected in this optimization process are reliable and no important factors are omitted.
Factor | SSj | dFj | Vj | Fj | F0.1 (2,2) = 9.00 | Pj (%) |
---|---|---|---|---|---|---|
A | 36.60 | 2 | 18.30 | 5.65 | < | 4.72 |
B | 90.06 | 2 | 45.03 | 13.90 | > | 11.61 |
C | 642.81 | 2 | 321.41 | 99.20 | > | 82.84 |
Error | 6.47 | 2 | 3.24 | — | — | 0.83 |
T | 775.94 | 8 | — | — | — | 100.00 |
Kawashima et al.42 reported the preparation of Ca2Fe2O5 through a conventional solid-state reaction involving mixing metal oxides as a catalyst for transesterification at methanol refluxing temperature with 92% yield. Xue and co-workers have also reported the synthesis of a Ca2Fe2O4–Ca2Fe2O5 based catalyst through co-precipitation for biodiesel synthesis obtaining an 85.4% conversion.30 However, the high biodiesel yield obtained under mild conditions is probably due to the presence of single CaO and CaCO3 respectively. In comparison, this novel preparation of a high phase purity mesoporous Ca2Fe2O5 catalytic system through the direct decomposition of a bimetallic Ca/Fe EDTA complex minimizes the formation of unwanted single oxides and carbonates and can still catalyze transesterification with faster kinetics at 120 °C.
Entry | Feedstock | Conversiona (%) |
---|---|---|
a Reaction conditions: feedstock-to-methanol molar ratio of 1![]() ![]() |
||
1 | Refined food grade canola oil | 98.7 |
2 | Crude flaxseed oil | 96.6 |
3 | Crude rapeseed oil | 94.8 |
4 | Crude rice bran oil | 92.6 |
5 | Waste cooking oil | 97.2 |
Further investigation of the FFA tolerance of the Ca/Fe catalytic system was studied as illustrated in Fig. 4a. The refined food grade canola oil and oleic acid were used as a model feedstock and FFA respectively in this study. A series of stimulated feedstock samples with different amounts of oleic acid (Table S2 in the ESI†) mixed with refined food canola oil were used for one-step simultaneous esterification and transesterification. It was found that the catalyst tolerated an oleic acid content of 2.00 wt% with a remarkable conversion of 92.5%. The Ca/Fe catalytic system demonstrated a high robustness towards highly FFA contaminated feedstock. Ca2Fe2O5 showed much higher FFA tolerance than NaOH, in which the NaOH system would induce saponification with a higher FFA content (>1 wt%).28,57 For comparison, the same reaction using the corresponding amount of CaO was also tested. It was found that CaO could still catalyze the transesterification but it was totally dissolved at the end of the reaction, which pointed out that CaO underwent homogeneous catalysis rather than heterogeneous catalysis.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c5ra13819a |
This journal is © The Royal Society of Chemistry 2015 |