Open Access

Catalytic pyrolysis of waste rice husk over mesoporous materials

  • Mi-Jin Jeon1,
  • Seung-Soo Kim2,
  • Jong-Ki Jeon3,
  • Sung Hoon Park4,
  • Ji Man Kim5,
  • Jung Min Sohn6,
  • See-Hoon Lee6 and
  • Young-Kwon Park1, 7Email author
Nanoscale Research Letters20127:18

DOI: 10.1186/1556-276X-7-18

Received: 28 September 2011

Accepted: 5 January 2012

Published: 5 January 2012


Catalytic fast pyrolysis of waste rice husk was carried out using pyrolysis-gas chromatography/mass spectrometry [Py-GC/MS]. Meso-MFI zeolite [Meso-MFI] was used as the catalyst. In addition, a 0.5-wt.% platinum [Pt] was ion-exchanged into Meso-MFI to examine the effect of Pt addition. Using a catalytic upgrading method, the activities of the catalysts were evaluated in terms of product composition and deoxygenation. The structure and acid site characteristics of the catalysts were analyzed by Brunauer-Emmett-Teller surface area measurement and NH3 temperature-programmed desorption analysis. Catalytic upgrading reduced the amount of oxygenates in the product vapor due to the cracking reaction of the catalysts. Levoglucosan, a polymeric oxygenate species, was completely decomposed without being detected. While the amount of heavy phenols was reduced by catalytic upgrading, the amount of light phenols was increased because of the catalytic cracking of heavy phenols into light phenols and aromatics. The amount of aromatics increased remarkably as a result of catalytic upgrading, which is attributed to the strong Brönsted acid sites and the shape selectivity of the Meso-MFI catalyst. The addition of Pt made the Meso-MFI catalyst even more active in deoxygenation and in the production of aromatics.


Py-GC/MS rice husk Meso-MFI Pt-Meso-MFI


Due to the increasing cost of crude oil and the environmental problems stemming from the overuse of fossil fuels, it has become increasingly important to develop alternative forms of renewable energy. Among these, biomass is regarded as a promising renewable energy source, and research on its application is being conducted extensively all over the world. In principle, compared to conventional fossil fuels, biomass does not cause a net carbon dioxide increase in the atmosphere, and it contains lower amounts of sulfur and nitrogen. Therefore, the use of biomass has benefits in terms of mitigating climate change as well as addressing the problem of air pollution [13].

Fast pyrolysis, in which biomass is decomposed thermochemically, is attracting a large amount of attention as a practical way to produce alternative liquid fuel that can replace fossil fuels. The liquid product of fast pyrolysis, known as bio-oil, can be used not only as fuel, but also as a raw material in the production of high-value-added chemicals. However, bio-oil has several problems that hinder its direct application to conventional combustion engines. These drawbacks include poor miscibility with petroleum oils, high oxygenate content, corrosivity against metals, and thermochemical instability [4, 5]. Various methods to upgrade bio-oil have been investigated. Catalytic cracking converts oxygenates such as aldehydes and ketones into low-molecular-mass species with low oxygen content through a catalytic reaction. During the process, the oxygen atoms contained in the bio-oil are converted into H2O, CO, and CO2 and removed to improve the bio-oil's quality [6]. Microporous zeolites such as ZSM-5, Y, and Beta have been widely applied for the catalytic upgrading of bio-oil. However, the pore size of these zeolites is so small (< 1 nm) that the pores can be blocked easily and it is difficult for large-sized bio-oil molecules to diffuse into the pores. Meso-MFI zeolite [Meso-MFI] is known to be a powerful catalyst that has strong acid sites like microporous zeolites as well as a large pore size [7].

Recently, various agricultural byproducts and wastes, including straw, olive seed, and nut shell, have been applied to the research of fast pyrolysis [8]. Rice husk is an abundant biomass resource that is produced in the agricultural society of Korea. Previously, waste rice husk was usually composted or incinerated. These conventional treatment methods, however, are not adequate for treating organic waste because they can cause nitrogen deficiency in the composting and smoke emissions. Fast pyrolysis of rice husk can be an alternative way to treat this material because it not only treats organic waste more efficiently, but it also produces bioenergy [9].

In this study, Meso-MFI, which has adequate characteristics for catalytic upgrading of bio-oil, was used for the first time for the catalytic pyrolysis of rice husk. Pyrolysis-gas chromatography/mass spectrometry [Py-GC/MS] was used to analyze the pyrolysis products directly and to examine the effect of the catalyst.

Experimental details

Rice husk

Rice husk was supplied from a rice mill located in Jeonnam, Korea. It was dried in an oven for 24 h at 110°C to minimize the effect of moisture. The sample particles were 8 to 10 mm long, 2.0 to 2.5 mm wide, and 0.1 to 0.15 mm thick. For each experiment, 1 mg of the sample was used.

Ultimate analysis was performed using a TruSpec elemental analyzer (LECO Co., St. Joseph, MI, USA) and an SC-432DR sulfur analyzer (LECO Co., St. Joseph, MI, USA) to quantify C, H, O, N, and S. Proximate analysis was carried out using a thermogravimetric analyzer (Pyris 1 TGA, PerkinElmer, Waltham, MA, USA).

Catalyst synthesis

Meso-MFI with a Si-to-Al ratio of 20 was synthesized by following the procedure described in the literature [7]. A 0.5-wt.% platinum [Pt] was ion-exchanged into Meso-MFI using Pt(NH3)4(NO3)2. Calcination for 3 h at 500°C under O2 atmosphere and H2 reduction was applied to the Pt-Meso-MFI before use [10].

Characterization of catalysts

To examine the specific surface area, pore volume, and pore size distribution of the catalysts used in this study, nitrogen adsorption-desorption was measured at 77 K (BELSORP-MINI, BEL Japan, Inc., Osaka, Japan) for the catalysts pretreated at 200°C under vacuum condition. From the obtained adsorption-desorption isotherms, the specific surface area was determined using the Brunauer-Emmett-Teller [BET] method.

To investigate the acidic properties of the catalysts, NH3 temperature-programmed desorption [TPD] analysis was carried out using a TPD/TPR 2900 analyzer (Micromeritics Instrument Co., Norcross, GA, USA). Before each analysis, the sample was pretreated with He gas at 250°C and was then cooled down to 100°C. While heating the sample from 100 to 400°C at a rate of 10°C/min with a N2 flow rate of 50 mL/min, the amount of NH3 desorbed from the catalyst was measured using a thermal conductivity detector.

Pyrolysis-gas chromatography/mass spectrometry

Py-GC/MS experiments were performed using a vertical furnace type pyrolyzer (Py-2020D, Frontier-Lab Ltd., Fukushima, Japan). About 1 mg of the rice husk sample was put on the metal sample cup floor. An intermediate layer made of quartz wool was installed above the sample to prevent contact between the catalyst and the sample. About 1 mg of the catalyst was located above the quartz wool layer. Therefore, catalytic upgrading was supposed to take place when the vapor-phase pyrolysis products passed through the catalyst layer. The metal sample cup containing the catalyst and the sample was inserted into the preheated pyrolyzer through which helium carrier gas flowed.

Vapor species produced from pyrolysis reactions for 3 min at 500°C were analyzed directly using a GC (HP 6890N Gas Chromatography)/MS (HP 5973 inert Mass Spectral Detector, Agilent Technologies Inc., Santa Clara, CA, USA) connected to the pyrolyzer. An HP-5 MS (30 m × 0.25 mm × 0.25 μm) capillary column was used for the analysis. Carrier gas was supplied with a split ratio of 50:1, and the GC/MS interface temperature was controlled at 300°C. The GC oven temperature was programmed to rise from 40 to 300°C at a rate of 5°C/min so that the analysis was conducted for 66 min, including 4 min maintained at 40°C before heating and 10 min maintained at 300°C after heating. Each peak appearing in the obtained mass spectra was interpreted using the NIST05 library.

Results and discussion

Sample analysis

The physicochemical properties of waste rice husk are displayed in Table 1. A rice husk consists mainly of carbon and oxygen, and the oxygen content was relatively high (38.1%), which may be attributed to oxygen-containing functional groups such as hydroxyl and carbonyl groups that are abundant in rice husks. Combustibles accounted for 78.8%. Compared to general wood biomass containing less than 1 wt.% ash, the rice husk was shown to consist of more than 10 wt.% of ash, which can be a drawback in the production of bio-oil. Sulfur was not detected, implying that the produced bio-oil will be a clean fuel.
Table 1

Physicochemical characteristics of rice husk

Elemental analysisa

Proximate analysis


Content (wt.%)


Content (wt.%)



















aOn dry and ash free basis; bcalculated by difference.

Catalyst characterization

Table 2 displays the physical properties of the catalysts used in this study. The specific surface area of Meso-MFI was larger than that of the commercial MFI catalyst (411 m2/g), and the pore size was about 4.1 nm, which is large enough to allow bio-oil molecules to diffuse into the pores. When Pt was added, the specific surface area decreased slightly due to the blocking of the pores by the Pt.
Table 2

Physical properties of the catalysts


SBET (m2/g)

Vtot (cm3/g)

Average pore size (nm)

Si/Al ratio











Figure 1 shows the result of temperature programmed desorption of ammonia [NH3-TPD] analysis performed to examine the acid properties of the catalysts. Meso-MFI exhibited two peaks: a low-temperature peak at about 230°C and a high-temperature peak at about 400°C. The low-temperature peak represents weak acid sites, while the high-temperature peak represents the strong Brönsted acid sites [7]. As with a typical microporous MFI catalyst, Meso-MFI has both weak acid sites and strong acid sites. When Pt was added, the amount of acid sites decreased because Pt replaced some of them, but strong acid sites still existed.
Figure 1

NH 3 -TPD curves of catalysts.

Catalytic upgrading using Py-GC/MS

To analyze the distribution of pyrolysis products easily and accurately, the Py-GC/MS method was used. Fast pyrolysis was carried out at 500°C, which has been suggested to be the optimal temperature for catalytic pyrolysis of biomass [7]. It is well known that the product of fast pyrolysis of biomass includes volatile species and nonvolatile oligomers. Py-GC/MS can be used only for the analysis of volatile species. More than 100 peaks appeared in the chromatograms obtained from the fast pyrolysis of rice husk. The number of peaks increased when catalysts were used compared to non-catalytic pyrolysis.

The yields and compositions of the pyrolysis products were changed due to catalytic upgrading. Catalysts can affect the production of volatile liquid products via two pathways during the catalytic pyrolysis process. First, the product species can be cracked into gasses or converted into coke or char, which reduces the volatile liquid species. Second, catalysts decompose nonvolatile oligomers into volatile monomers, increasing the amount of volatile liquid species. The change in the liquid product yield due to catalytic upgrading is determined by a sum of these two opposite effects [11].

Total GC/MS peak areas of liquid products were plotted in Figure 2 to examine the effects of the catalysts on the yield of volatile liquid products. Because bio-oil contains various species, it is difficult to obtain a quantitative analytic result from GC/MS. Nevertheless, it is possible to compare the product yield by comparing the peak areas because the peak area is proportional to the product yield [12]. The use of catalysts resulted in a decreased total peak area for the liquid product, which may be attributed to cracking of volatile species into CO, C1-C4 hydrocarbons, and H2O. In particular, when Pt was added, the reduction of the total peak area for the liquid product was larger due to a stronger cracking effect. This result indicates that catalytic upgrading reduces the liquid product yield.
Figure 2

Total GC/MS peak areas for liquid products from catalytic pyrolysis of rice husk.

To investigate the change in the composition of the pyrolysis product due to catalytic upgrading, the pyrolysis products obtained with and without a catalyst were divided into seven groups, i.e., acids, hydrocarbons, oxygenates, phenolics, anhydrosugars, aromatics, and gas. Figure 3 compares the product distributions expressed as area percentage.
Figure 3

Product distribution from catalytic pyrolysis of rice husk.

As shown in Figure 3, catalytic upgrading reduced the amount of oxygenates due to cracking by the catalysts. In particular, anhydrosugars, which are polymers such as levoglucosan, were cracked into low-molecular-mass species, while aldehydes and ketones were converted into H2O by dehydration or into CO and CO2 by decarbonylation and decarboxylation. It was observed that catalytic upgrading resulted in an increased gas yield, levoglucosan was decomposed completely, and the amount of carbonyl-containing species was decreased (data not shown). The reduction of total oxygenates due to Meso-MFI and Pt-Meso-MFI was 38% and 49%, respectively. Oxygenates degrade the quality of bio-oil by reducing its heating value and producing air pollutants upon combustion. Therefore, a reduction of oxygenate production by catalytic upgrading may help to produce higher-quality bio-oil. In particular, Pt-Meso-MFI showed a higher deoxygenation effect, which is believed to be due to enhanced cracking, dehydrogenation, hydrogenolysis, and hydrocracking reactions over Pt [13].

The total amount of phenolics was reduced due to catalytic upgrading, but the amount of light phenols was increased. This result is attributed to cracking of heavy phenols into light phenols and aromatics due to the outstanding cracking ability of the Meso-MFI catalyst. Figure 4 illustrates this trend clearly. By catalytic upgrading, the amount of phenol and monomeric phenols was increased (Figure 4a), while the amount of heavy phenols was decreased (Figure 4b).
Figure 4

Effect of catalysts on the phenolic products (a) the light phenol (b) the heavy phenol.

Aromatics that were not produced by non-catalytic pyrolysis appeared after catalytic upgrading. In particular, the amount of high-value-added mono-aromatics such as toluene and p-xylene increased remarkably (Figure 5). The existence of strong Brönsted acid sites is known to increase the yield of aromatics [7, 12]. It has also been reported that the shape selectivity of the MFI structure of MFI catalysts increases the selectivity for aromatics [12]. Therefore, the high selectivity of Meso-MFI for aromatics observed in this study is attributed to its strong Brönsted acid sites and MFI structure. The further increase in the aromatic yield due to the addition of Pt can be explained by the dehydrogenation reactions promoted by Pt. The alkenes produced by dehydrogenation reactions are converted into aromatics on the strong Brönsted acid sites [7].
Figure 5

Effect of catalysts on the aromatic products.


In this study, catalytic pyrolysis of waste rice husk was carried out using Py/GC-MS. The catalytic activities of Meso-MFI and Pt-Meso-MFI were evaluated by comparing the product compositions with that of non-catalytic pyrolysis.

The yield of oxygenates that can degrade the product bio-oil was reduced due to catalytic upgrading, by 38% with Meso-MFI and by 49% with Pt-Meso-MFI, demonstrating the outstanding activity of the Pt-Meso-MFI catalyst in deoxygenation. Catalytic upgrading over Meso-MFI increased the amount of light phenols, which is attributed to cracking of heavy phenols into light phenols and aromatics due to the catalytic effect of mesoporous Meso-MFI. In addition, Meso-MFI exhibited a good selectivity for aromatics, which is ascribed to its strong acid sites and shape selectivity due to the MFI structure. Pt-Meso-MFI was even more effective in the upgrading of bio-oil because of the additional catalytic effect of Pt.



meso-MFI zeolite


temperature programmed desorption of ammonia


pyrolysis gas chromatography/mass spectrometry.


Authors’ Affiliations

Graduate School of Energy and Environmental System Engineering, University of Seoul
Department of Chemical Engineering, Kangwon National University
Department of Chemical Engineering, Kongju National University
Department of Environmental Engineering, Sunchon National University
Department of Chemistry, BK21 School of Chemical Materials Science and Department of Energy Science, Sungkyunkwan University
Department of Mineral Resources and Energy Engineering, Chonbuk National University
School of Environmental Engineering, University of Seoul


  1. McKendry P: Energy production from biomass (part 1): overview of biomass. Bioresour Technol 2002, 83: 37–46. 10.1016/S0960-8524(01)00118-3View ArticleGoogle Scholar
  2. Garcìa-Pèrez M, Chaala A, Roy C: Vacuum pyrolysis of sugarcane bagasse. J Anal Appl Pyrol 2002, 65: 111–136. 10.1016/S0165-2370(01)00184-XView ArticleGoogle Scholar
  3. Demirbas A: Biomass resource facilities and biomass conversion processing for fuels and chemicals. Energy Conv Manag 2001, 42: 1357–1378. 10.1016/S0196-8904(00)00137-0View ArticleGoogle Scholar
  4. Adjaye JD, Bakhshi NN: Upgrading of a wood-derived oil over various catalysts. Biomass Bioenerg 1994, 7: 201–211. 10.1016/0961-9534(94)00060-7View ArticleGoogle Scholar
  5. Vitolo S, Seggiani M, Frediani P, Ambrosini G, Politi L: Catalytic upgrading of pyrolytic oils to fuel over different zeolites. Fuel 1999, 78: 1147–1159. 10.1016/S0016-2361(99)00045-9View ArticleGoogle Scholar
  6. Bridgwater AV: Production of high grade fuels and chemicals from catalytic pyrolysis of biomass. Catal Today 1996, 29: 285–295. 10.1016/0920-5861(95)00294-4View ArticleGoogle Scholar
  7. Park HJ, Heo HS, Jeon JK, Kim J, Ryoo R, Jeong KE, Park YK: Highly valuable chemicals production from catalytic upgrading of radiata pine sawdust-derived pyrolytic vapors over mesoporous MFI zeolites. Appl Catal B Environ 2010, 95: 365–373. 10.1016/j.apcatb.2010.01.015View ArticleGoogle Scholar
  8. Butler E, Devlin G, Meier D, McDonnell K: A review of recent laboratory research and commercial developments in fast pyrolysis and upgrading. Renew Sust Energ Rev 2011, 15: 4171–4186. 10.1016/j.rser.2011.07.035View ArticleGoogle Scholar
  9. Heo HS, Park HJ, Dong JI, Park SH, Kim S, Suh DJ, Suh YW, Kim SS, Park YK: Fast pyrolysis of rice husk under different reaction conditions. J Ind Eng Chem 2010, 16: 27–31. 10.1016/j.jiec.2010.01.026View ArticleGoogle Scholar
  10. Park HJ, Park KH, Jeon JK, Kim J, Ryoo R, Jeong KE, Park SH, Park YK: Production of phenolics and aromatics by pyrolysis of Miscanthus. Fuel In revision In revision
  11. Qiang L, Zhe T, Ying Z, Xi-feng Z: Catalytic upgrading of biomass fast pyrolysis vapors with Pd/SBA-15 catalysts. Ind Eng Chem Res 2010, 49: 2573–2580. 10.1021/ie901198sView ArticleGoogle Scholar
  12. Heo HS, Kim SG, Jeong KE, Jeon JK, Park SH, Kim JM, Kim SS, Park YK: Catalytic upgrading of oil fractions separated from food waste leachate. Bioresour Technol 2011, 102: 3952–3957. 10.1016/j.biortech.2010.11.099View ArticleGoogle Scholar
  13. Meriaudeau P, Naccache C: Dehydrocyclization of alkanes over zeolite-supported metal catalysts: monofunctional or bifunctional route. Catal Rev Sci Eng 1997, 39: 5–48. 10.1080/01614949708006467View ArticleGoogle Scholar


© Jeon et al; licensee Springer. 2012

This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.