NC State
BioResources
Liu, H.-M., Xie, X.-A., Feng, B., and Sun, R.-C. (2011). "Effect of catalysts on 5-lump distribution of constalk liquefaction in sub-critical ethanol," BioRes. 6(3), 2592-2604.

Abstract

Liquefaction of cornstalk in sub-critical solution of ethanol without and with catalysts (K2CO3, Na2CO3 and ZnCl2) was performed in a stainless steel reactor (1 L) at temperatures of 200 to 300 oC. The cornstalk and the products of decomposition were divided into five lumps (gas, organic dissolved, heavy oil, volatile organic compounds, and residue). The effects of reaction temperature and the catalyst amount on the five lump yields were studied. The bio-oils produced with and without catalysts were characterized by GC/MS. Results showed that an increment in the temperature and the addition of catalysts had a synergetic effect on the lumps yield as compared to the non-catalytic experiments, and different catalytic procedures had an important effect on the lump yields and compounds of the bio-oils. The addition of the catalyst enhanced the gas yield and the total conversion rate. A high temperature, lower amount of Na2CO3, moderate amount of K2CO3, and a high amount of ZnCl2 were propitious to enhance the heavy oil. The formation of volatile organic compounds with the presence of ZnCl2 and K2CO3 was less than that in non-catalytic experiments at the higher temperatures. However, a higher conversion temperature had a negative impact on the bio-oils yield from liquefaction of cornstalk with and without catalysts.


Download PDF

Full Article

EFFECT OF CATALYSTS ON 5-LUMP DISTRIBUTION OF CORNSTALK LIQUEFACTION IN SUB-CRITICAL ETHANOL

Hua-Min Liu,a Xin-An Xie,Bing Feng,and Run-Cang Sun a,d,*

Liquefaction of cornstalk in sub-critical solution of ethanol without and with catalysts (K2CO3, Na2CO3 and ZnCl2) was performed in a stainless steel reactor (1 L) at temperatures of 200 to 300 oC. The cornstalk and the products of decomposition were divided into five lumps (gas, organic dissolved, heavy oil, volatile organic compounds, and residue). The effects of reaction temperature and the catalyst amount on the five lump yields were studied. The bio-oils produced with and without catalysts were characterized by GC/MS. Results showed that an increment in the temperature and the addition of catalysts had a synergetic effect on the lumps yield as compared to the non-catalytic experiments, and different catalytic procedures had an important effect on the lump yields and compounds of the bio-oils. The addition of the catalyst enhanced the gas yield and the total conversion rate. A high temperature, lower amount of Na2CO3, moderate amount of K2CO3, and a high amount of ZnCl2 were propitious to enhance the heavy oil. The formation of volatile organic compounds with the presence of ZnCl2 and K2CO3 was less than that in non-catalytic experiments at the higher temperatures. However, a higher conversion temperature had a negative impact on the bio-oils yield from liquefaction of cornstalk with and without catalysts.

Keywords: Liquefaction; Cornstalk; Catalyst; Lump

Contact information: a: State Key Laboratory of Pulp and Paper Engineering; b: College of Food Science, South China Agriculture University Guangzhou, 510640, China; c: College of Chemistry and Chemical Engineering, South China University of Technology, Guangzhou 510640, China; d: Institute of Biomass Chemistry and Technology, Beijing Forestry University, Beijing 100083, China;

* Corresponding author: rcsun3@bjfu.edu.cn

INTRODUCTION

The conversion and effective utilization of biomass, which is an abundant and reproducible resource, has increasingly received interest with the rapid development of worldwide industry and the consumption of petroleum and petro-chemicals. Many technologies have been studied in recent years for their possible use in the processing of biomass, such as combustion, pyrolysis, gasification, and liquefaction (Gil et al. 2010). Solid and gas biofuels have a low energy density, which limits their commercial applications. One way to solve this problem is the conversion of the feedstock into liquids fuels. Such liquids have a higher energy density and are easy to store and transport (Veldenl et al. 2010). The one most important method to convert biomass into liquid fuel is the thermochemical conversion in solvents (such as water, ethanol, and acetone) by heat, in which biomass could be decomposed into liquid at mild temperature and atmospheric pressure. A liquid product called bio-oil is a complex mixture of water and organic chemicals, including acids, alcohols, aldehydes, ketones, esters, heterocyclic derivatives, and phenolic compounds (Liu et al. 2010).

The bio-oils cannot be used as transportation fuels directly without treatment due to their high oxygen (40 to 50 wt%) and water content (15 to 30 wt%), and low H/C ratios (Pütün 2010). Catalytic pyrolysis liquefaction is a promising way to improve bio-oil quality by removing oxygen, while also increasing the calorific value and stability (Samolada et al. 2000). Alkali metal salts, especially those containing potassium, are excellent promoters of gasification reactions. Fast-growing biomass, which contains large quantities of potassium, may prove to be an excellent source of inexpensive gasification catalyst (Brown et al. 2000). Over the years, many studies on the liquefaction of biomass using catalytic and solvent have been carried out (Akhtar et al. 2010; Hossein et al. 2010). It was found that the alkalis and alkali metal salts were more suitable for obtaining high yields of liquid products from biomass, and solid conversion increased at higher reaction temperature, but the liquid yield did not increase at higher temperature. However, the mechanism of liquefaction using catalyst and solvent has been difficult to study at a molecular level because of the complex liquefaction products. Thermogravi-metric analysis (TGA) is a general approach to study the process. It has been employed to investigate the influence of the heating rate on the pyrolysis outcomes as well as the kinetics of the pyrolysis process (Sadhukhan et al. 2008; Li et al. 2008; Park et al. 2009; Velden et al. 2010). However, the TGA is not suitable for studying the effect of solvent on the liquefaction process.

The method of lump analysis has been used to study the complexity of reactive processes (fluid catalytic cracking, catalytic pyrolysis processes, etc.) by lumping the large number of chemical compounds into groups of pseudo-components, according to their boiling points and their molecular characteristics (Meng et al. 2006, 2007; Minkina et al. 2010). Just like the fluid catalytic cracking (FCC) and catalytic pyrolysis processes, the liquefaction of biomass is a complicated process. Therefore, a five-lump model of liquefaction of cornstalk in sub-and super-critical ethanol was established based on the characteristics of the material and products (Liu et al. 2010). The results showed that this is a good way to study the mechanism of catalytic liquefaction by lumping large numbers of chemical compounds together.

In this study, cornstalk was liquefied with and without catalysts (K2CO3, Na2CO3, and ZnCl2) in sub-critical ethanol using a stainless-steel autoclave (1 L). The lumps of the liquefaction system were defined based on the characteristics of cornstalk and liquefaction products. The behavior of catalytic liquefaction of cornstalk in ethanol was investigated by studying the effect of catalysts at different temperatures on the lump yields.

EXPERIMENTAL

Cornstalk and Solvents

The cornstalk sample investigated in this study was collected from the field of South China Agriculture University, Guangzhou, China. The cornstalk, after undergoing size-reduction by a chipper, was pulverized to pass through a 40-mesh sieve. The flour was extracted with distilled water and ethanol to remove organic dissolved and polar organics, then dried at 105 oC for 24 h and kept in a desiccator at room temperature before being used. The solvents used were distilled water and analytical reagent grade ethanol and acetone.

Adsorption of Catalysts to Cornstalk

The catalysts (K2CO3, Na2CO3, and ZnCl2) used were analytical reagent grade chemicals. The 150 g cornstalk was added into 1000 mL water solution containing catalysts (0.05 mol/L, 0.1 mol/L, 0.2 mol/L). After adsorbing at room temperature for 20 h, the cornstalk was filtered, dried at 105 oC for 24 h and kept in a desiccator at room temperature before used.

Experimental Procedure

For each run, the cornstalk and ethanol were fed into the magnetically stirred autoclave (volume of 1 L, PARR, USA). The reactor was purged with 2 MPa of nitrogen at room temperature to remove the air/oxygen in the reactor airspace. Then the autoclave was heated to the pre-set final temperature, followed by a holding period of a certain time. The autoclave was then cooled down to room temperature by water. The density of gas was estimated using a gas bag by measuring the bulk and quality of the gaseous component. The bulk of gas was estimated by the way of expelling water from the measuring cylinder. When the autoclave was opened, the reaction mixture was removed for separation. The procedure for the separation is shown in Fig. 1.

Fig. 1. Procedure for separation of products

In order to study the effect of catalysts on the liquefaction of cornstalk in ethanol, the reaction system was divided into gas lump (GA), organic dissolved lump (OD), heavy oil lump (HO), volatile organic compounds lump (VO), and residue lump (RE) based on the characteristics of material and liquefaction products. The entire yield of each lump was calculated on a dry basis and assumed to be ash free. The results obtained in this study were reported using the parameters defined as,

 (1)

 (2)

 (3)

 (4)

 (5)

where YGA is the gas yield (wt %), YOD is the organic solution yield (wt %), YHO is the heavy oil yield (wt %), YVO is the volatile organic compounds yield (wt %), YRE is the residue yield (wt %), YA is the ash yield (wt %), WDry is the mass of cornstalk flour (g), WOD is the mass of dissolved organics (g), WHO is the mass of heavy oil (g), WRE is the mass of residue (g), VGA is the volume of gas (mL), and ρGA is the density of gas (g/mL).

To ensure reliability of the experimental data, each experiment was repeated twice, and the differences between the results of two tests were below 7.5% of the values.

Experimental Analyses

Chemical compositions of the bio-oils ( OD+HO ) were identified by GC/MS (HP5971) using a 30 mm × 0.25 mm capillary column (DP-5). The gas chromatograph was programmed at 40 oC for 2 min, and then followed by a heating rate of 10 oC/min to 300 oC and holding for 2 min at the final temperature. The injected volume was 0.125 μL. The mass range scanned was from 35 to 500 amu in electron-impact (70 eV) mode. The compounds were identified by comparison with library spectra supplied from the NIST database. The total area of all the peaks was set as 100%, and a relative amount of each peak corresponding to each compound could be calculated according to the ratio of its area to the total area.

A Varian of America Spectr AA 220FS/220Z Atomic Absorption Spectrophoto-meter equipped with Zeeman background corrector and data processor was used for elemental analysis of the catalysis concentration. All parameters were set and followed strictly according to the manufacturer’s instructions using the flame atomization technique.

The ash content of the cornstalk was determined by burning at 650 oC. The heating value was obtained from calculation by Dulong’s formula. The characteristics of the cornstalks without and with catalysts are shown in Table 1.

Table 1. Main Characteristics of the Cornstalk With and Without Catalysts

RESULTS AND DISCUSSION

Influence of Catalysts on Lump Yields at Various Reaction Temperatures

Catalysts are the crucial parameter to accelerate reaction rates. Selective catalysts can be used for producing certain products, even though many natural and synthetic catalysts can be used (Ates et al. 2009). The effect of catalysts on lump yields at various reaction temperatures are shown in Figs. 2 to 5. The data presented in the figures were obtained from the experimental runs with and without catalysts at various temperatures ranging from 200 to 300 oC, at the same time (0 min) and with the same catalyst (if added) concentration. The temperature plays an important role to influence the yield of lumps (GA, OD, HO, VO, and RE) in the process of cornstalk liquefaction with and without the presence of catalysts, as shown in the figures.

Effect of catalysts on the residue yield

The effect of catalysts on the RE yield at different temperatures is shown in Fig. 2. As shown, in the whole range of the temperatures tested, the RE yield from liquefaction of cornstalk with and without catalysts decreased continuously with increasing reaction temperature. Comparing these runs of cornstalk liquefaction without catalyst and with catalysts (K2CO3, Na2CO3, and ZnCl2), the RE yield strongly decreased when the three catalysts were added. Moreover, the RE yield under the condition of the addition K2CO3 and Na2CO3 were found to be almost the same. Thus, it might be generally concluded that the addition of the catalysts significantly enhanced the conversion rates (100% – YRE).

Effect of catalysts on the gas yield

Figure 3 shows the effect of catalysts on the GA yield at different temperatures. As shown, the yield of GA strongly depended on the reaction temperature in the range of 200 to 300 oC.

Fig. 2. Effect of catalyst on the RE yield at various temperatures

Regardless of which catalyst was present, the GA yield showed an identical trend, and GA yield increased with increasing reaction temperature. The addition of the three catalysts significantly enhanced the lump of GA over the whole temperature range (200 to 300 oC). It was worth noting that beyond 240 oC the effect of ZnClon the GA yield was more strongly increased as compared to other catalysts used in the procedure. Therefore, in the presence of zinc chloride, an increase in the GA yield was observed as compared to those obtained by pure ethanol and other catalysts (K2CO3 and Na2CO3) runs at the higher temperatures.

Fig. 3. Effect of catalyst on the GA yield at various temperatures

Effect of catalysts on the volatile organic compounds yield

Figure 4 shows the effect of catalysts on the VO yield at different temperatures. Obviously, the temperature is an important factor affecting the VO yield. That is, the VO yields in all of the liquefaction of cornstalk runs increased with increasing temperature. The addition of K2CO3 increased the VO yield as compared to the results obtained in non-catalyst runs over the whole range of the temperatures tested. Different results of VO yield were shown for other catalysts (ZnCl2 and Na2CO3). In the presence of ZnCl2 and Na2CO3, the formation of VO was less than pure ethanol runs when the temperature reached 240 oC and 300 oC, respectively. The possible reason may be that products of the degradation of VO were transformed into GA (see Fig. 3).

Fig. 4. Effect of catalyst on the VO yield at various temperatures

Effect of catalysts on the bio-oil (organic dissolved and heavy oil) yield

Figure 5 shows the effect of catalysts on the bio-oil at different temperatures. Clearly, the yield of OD was lower when using Na2CO3 than the non-catalyst run. K2CO3 and ZnCl2 appeared to be more effective than Na2CO3 for promotion of OD formation at the lower tested temperature range. However, a disadvantage of K2CO3 and ZnCl2 may be that they cannot effectively promote the OD production at the higher temperature as compared to the non-catalyst run. For the three catalysts, the catalytic effects on the HO formation became more significant at the higher temperatures. For instance, the HO yield increased from 9.3% (non-catalyst) to 12.5% (with K2CO3) at 280 oC, from 8.8% (non-catalyst) to 10.4% (with Na2CO3) at 300 oC, and from 9.4% (non-catalyst) to 11.2% (with ZnCl2) at 260 oC, respectively. One advantage of this approach is that the three catalysts increased the bio-oil (  ) yield as compared to pure ethanol at higher temperatures. The bio-oils yield from liquefaction of cornstalk with K2CO3, ZnCl2, and Na2CO3 were higher than non-catalyst runs after the reaction reached 240, 260, and 300 oC, respectively. Comparatively, the liquefaction of cornstalk for K2CO3 showed a higher value than those of ZnCl2 and Na2CO3 for the bio-oil yield and OD yield. The reduction in the bio-oil yield in the presence of ZnCl2 and K2CO3 catalysts at a higher temperature were due to cracking of the liquid product to GA and VO by isomerization, dehydration, and fragmentation. It can be concluded that ZnCl2 and K2CO3 catalysts, used with cornstalk in ethanol, maximized the bio-oil yield, depending on the temperature. At moderate temperatures, the addition of catalysts increased the bio-oil yield as compared to that of the non-catalytic experiments.

Fig. 5. Effect of catalyst on the liquid products at various temperatures. (a) Effect of catalyst on the OD yield. (b) Effect of catalyst on the HO yield. (c) Effect of catalyst on the bio-oil yield.

Effect of Catalyst Amount on Lump Yields

The effect of catalyst on the lump yields at different temperatures was studied. To investigate the effect of catalyst amount on the lumps yield, experimental measurements were carried out under the condition of 260 oC, 5 g cornstalk, 50 mL ethanol, and different catalyst amounts (0.05 mol/L, 0.1 mol/L, and 0.2 mol/L). The results in terms of the lump yields at different amounts of catalysts are shown in Figs. 6, 7, and 8.

Effect of K2CO3 amount on the lump yields

Figure 6 shows the effect of K2COamount on the lump yields from liquefaction of cornstalk. The results showed that the amount of K2COhad a strong influence on the lump distribution from Fig. 6. The yield of RE decreased with the increasing amount of K2CO3. These results showed that a further addition of K2CO3 enhanced the conversion rates of cornstalk liquefaction. However, the addition of K2CO3 favored to degradation of OD yield at low catalyst concentrations. When the amount of catalyst further increased, the OD yield was higher than the non-catalyst runs at 260 oC.

It was obvious that the K2COamount had a contrary effect on the VO yield: the VO yield increased from 21.0% (non-catalyst) to 24.3% (0.1 mol/L), and then decreased to 22.9% at the higher catalyst amount (0.2 mol/L). The GA further increased with the increase in catalyst amount. These results can be attributed to the increased number of catalytic active sites at a higher catalyst amount. A moderate amount of K2CO3 could also improve the HO yield as compared with that of the non-catalytic and lower amount catalyst runs. For example, the HO yield of 8.6% and 8.9% were obtained at the catalyst amount of 0.05 mol/L and 0.2 mol/L, respectively, which were lower than the non-catalyst examination (9.4%); the maximal HO yield (11.1%) was obtained at the catalyst amount of 0.1 mol/L.

Fig. 6. Effect of K2COconcentration on the lump yields

Effect of Na2CO3 amount on the lumps yield

Figure 7 shows the effect of Na2COamount on the lump yields from liquefaction of cornstalk. Although the RE yield decreased from 52.1% (non-catalyst) to 45.4% (0.05 mol/L) under the addition of Na2CO3, the RE yield decreased slightly with the further increase in catalyst amount. This result showed that the amount of Na2COhad little influence on the conversion rates of cornstalk liquefaction. The yield of GA obtained from liquefaction of cornstalk increased from 8.7% (non-catalyst) to 14.6% (0.2 mol/L) with increasing amounts of Na2CO3 (Fig. 7). The catalyst concentration had a great influence on the HO and OD yields, and an increment in the catalyst concentration could inhibit the production of HO and enhance the OD yield, respectively. At a low and moderate amount of the catalyst, the VO yield increased as compared to that of the non-catalytic experiment and a higher amount of catalytic experiment. The VO yields of 26.37% and 26.45% were obtained with the catalyst amounts of 0.05 mol/L and 0.1 mol/L, respectively, which were higher as compared to the yields of 21.0% (non-catalyst) and 22.3% (0.2 mol/L).

Figure 8 shows the effect of ZnCl2 concentration on the lump yield from liquefaction of cornstalk. As shown in the figure, the RE yield decreased slightly from 48.5% (0.05 mol/L) to 46.7% (0.2 mol/L) with increasing the amount of ZnCl2. Therefore, further addition of ZnClcould not markedly increase the total conversion rates. In the previous section it was shown that the HO yield decreased with increasing Na2COcatalyst amount. Comparatively, in the presence ZnCland Na2CO3, the results were very diverse. As seen from Fig. 8, the HO and OD yields increased with increasing amounts of catalyst. However, the concentration of ZnCl2 had an important influence on the yields of GA and VO, and it is worth noting that the yields of GA and VO were negatively correlated with the increases in amount of catalyst. The GA yield increased about 11.0% from 12.7% (0.05 mol/L) to 23.7% (0.2 mol/L), and the VO yield decreased about 13.1% from 22.5% (0.05 mol/L) to 9.4% (0.2 mol/L) from Fig. 8.

Fig. 7. Effect of Na2COconcentration on the lump yields

Fig. 8. Effect of ZnClconcentration on the lump yields

Effect of ZnCl2 amount on the lumps yield

In our previous study (Liu et al. 2010), we found that there was a reversible reaction between the HO and VO from liquefaction of cornstalk in sub-and super-critical ethanol without catalyst. However, the addition of catalysts accelerated the reaction rate and changed the lump reaction pathways. This study showed that there was competitive reaction between GA and VO in the presence of ZnCl2, which was similar to that observed in the study of GA yield at different temperatures in the presence of ZnCl2.

GC/MS analysis of bio-oils

Gas chromatography/mass spectrometry (GC/MS) has become a quick, convenient and powerful tool for characterizing complex and heterogeneous bio-oil samples (Sobeih et al. 2008). Bio-oil contains a large number of different compounds, making it very difficult to identify each of the compounds. Therefore, in this paper, focus is given to key compounds. Table 2 shows the major components of the bio-oils obtained from liquefaction of cornstalk at standard condition (reaction temperature of 300 oC, catalyst amount of 0.1 mol/L (if added), 5 g cornstalk and 50 mL ethanol) using GC/MS. As a result of the disintegration of the cornstalk with and without the presence of catalysts, the liquefaction of cornstalk was transformed into products having different molecular structures. This showed that the use of catalysts had an important effect on the formation of various compounds in the bio-oils.

During the studies conducted in recent years, the bio-oil products obtained with biomass liquefaction have been analyzed in detail using GC/MS. Huang et al. (2011) studied the thermo-chemical liquefaction characteristics of microalgae in sub- and supercritical ethanol and found that fatty acid ethyl ester compounds were the major compounds identified in the bio-oil, followed by fatty acid methyl/dimethyl ester, organic acids, heterocyclic nitrogen compounds, and long-chain alkanes. Aguado et al. (2000) studied the flash pyrolysis of sawdust at 350 to 700 oC and showed that formaldehyde, methanol, acetic acid, furfural, and several phenols were the main compounds presents in the bio-oil. As shown in Table 2, the most important compounds present in cornstalk bio-oils are furfural, phenols, acids, and esters.

Table 2. GC/MS Analysis Results for the Bio-Oils Obtained from the Liquefaction of Cornstalk With and Without Catalysts at 300 oC.

CONCLUSIONS

1. Lump analysis was found to be effective for the study of biomass liquefaction. An increase in the temperature and the use of catalysts had a synergetic effect on the lump yields as compared to the non-catalytic experiments, and different catalytic procedures had different effects on liquefaction of cornstalk.

2. The addition of the three catalysts significantly enhanced the lump of GA and the total biomass conversion at the temperatures tested, and liquefaction at high temperatures could increase the HO yield as compared to that of the non-catalytic runs. The formation of VO was less than non-catalytic experiments after the temperature reached to 240 and 300 oC in the presence of ZnCl2 and Na2CO3, respectively. The bio-oil yield increased and the OD yield decreased at the moderate and high liquefaction temperatures in the experiments without and with catalysts.

3. Further increasing the amount of the three catalysts increased the GA, OD, and RE yields, but the more Na2CO3 and ZnCl2 could not markedly decrease the RE yield. A lower amount of Na2CO3, moderate amount of K2CO3, and a higher amount ZnCl2 were favored to enhance the HO yield.

4. The use of different types of catalysts had significant effects on the formation of various compounds in the bio-oils.

ACKNOWLEDGMENTS

We sincerely acknowledge the financial support by the Major State Basic Research Projects of China (973-2010CB732204/1), Guangdong Provincial Science and Technology program Foundation of China (Project. 2009B050700037), and the National Natural Science Foundation of China (30930073).

REFERENCES CITED

Ates, F., and Isikdag, M. A. (2009). “Influence of temperature and alumina catalyst on pyrolysis of corncob,” Fuel 88(10), 1991-1997.

Akhtar, J., Kuang, S. K., and Amin, N. S. (2010). “Liquefaction of empty palm fruit bunch (EPFB) in alkaline hot compressed water,” Renew. Energ. 35(6), 1220-1227.

Aguado, R., Olazar, M., José, M. J. S., Aguirre, G., and Bilbao, J. (2000). “Pyrolysis of sawdust in a conical spouted bed reactor. Yields and product composition,” Ind. Eng. Chem. Res. 39(6), 1925-1933.

Brown, R. C., Liu, Q., and Norton, G. (2000). “Catalytic effects observed during the co-gasification of coal and switchgrass,” Biomass and Bioenerg. 18(6), 499-506.

Gil, M. V., Casal, D., Pevida, C., Pis, J. J., and Rubiera, F. (2010). “Thermal behaviour and kinetics of coal/biomass blends during co-combustion,” Bioresource Technol. 101(14), 5601-5608.

Hossein, M., Keat, T. L., Subhash, B., and Abdul, R. M. (2010). “Subcritical water liquefaction of oil palm fruit press fiber for the production of bio-oil: Effect of catalysts,” Bioresource Technol. 101(2), 745-751.

Huang, H. J., Yuan, X. Z., Zeng, G. G., Wang, J. Y., Li, H., Zhou, C. F., Pei, X. K., You, Q., and Chen, L. (2011). “Thermochemical liquefaction characteristics of microalgae in sub- and supercritical ethanol,” Fuel Process. Technol. 92(1), 147-153.

Li, Z. Q., Zhao, W., Meng, B. H., Liu, C. L., Zhu, Q. Y., and Zhao, G. B. (2008). “Kinetic study of corn straw pyrolysis: Comparison of two different three-pseudocomponent models,” Bioresource Technol. 99(16), 7616-7622.

Liu, H. M., Xie, X. A., Ding, N. P., Liu, H. B., and Huang, L. Y. (2010). “Liquefaction reaction pathway and mechanism of cornstalk in sub-and super-critical ethanol,” Transactions of the CSAE 26(6), 277-282.

Liu, W. W., Hu, C. W., Yang, Y., Zhu, L. F., and Tong, D. M. (2010). “Effect of the interference instant of zeolite HY catalyst on the pyrolysis of pubescens,” Chinese J. Chem. Eng. 18(2), 351-354.

Meng, X. H., Xu, C. M., Gao, J. S., and Li, L. (2007). “Seven-lump kinetic model for catalytic pyrolysis of heavy oil,” Catal. Commun. 8(8), 1197-1201.

Minkina, M., Oliveira, F. L. G., and Zymla, V. (2010). “Coal lump devolatilization and the resulting char structure and properties,” Fuel Process. Technol. 91(5), 476-485.

Meng, X. H., Xu, C. M., Gao, J. S., and Li, L. (2006). “Catalytic pyrolysis of heavy oils: 8-lump kinetic model,” Appl. Catal. A-Gen 301(1), 32-38.

Park, Y. H., Kim, J., Kim, S. S., and Park, Y. K. (2009). “Pyrolysis characteristics and kinetics of oak trees using thermogravimetric analyzer and micro-tubing reactor,” Bioresource Technol. 100(1), 400-405.

Pütün, E. (2010). “Catalytic pyrolysis of biomass: Effects of pyrolysis temperature, sweeping gas flow rate and MgO catalyst,” Energy 35(7), 2761-2766.

Samolada, M. C., Papafotica, A., and Vasalos, I. A. (2000). “Catalyst evaluation for catalytic biomass pyrolysis,” Energ. Fuel 14(6), 1161-1167.

Sadhukhan, A. K., Gupta, P., Goyal, T., and Saha, R. K. (2008). “Modelling of pyrolysis of coal-biomass blends using thermogravimetric analysis,” Bioresource Technol. 99(17), 8022-8026.

Sobeih, K. L., Baron, M., and Gonzalez, R. J. (2008). “Recent trends and developments in pyrolysis/gas chromatography,” J. Chromatogr. A 1186(1-2), 51-66.

Veldenl, M. V. D., Baeyens, J., Brems, A., Janssens, B., and Dewil, R. (2010). “Fundamentals kinetics and endothermicity of the biomass pyrolysis reaction,” Renew. Energ. 35(1), 232-242.

Article submitted: March 18, 2011; Peer review completed: May 8, 2011; Revised version received and accepted: May 13, 2011; Published: May 17, 2011.