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熱分解および水熱分解によるバイオマスおよび褐炭の転換に関する研究

劉, 天龍 LIU, TIANLONG リュウ, テンリュウ 九州大学

2020.09.25

概要

Biomass is the only renewable source on energy and organic carbon that has the potential to reduce our overreliance of fossil fuels and mitigate environmental issues. Effective utilization of biomass in the current energy system, which is essential to the establishment of a circular, bio-based economy, necessitates the development of new technologies to overcome the limitations of the structural recalcitrance, low bulk density and high moisture content of biomass. With this perspective, this thesis has been devoted to the combined pyrolytic and hydrothermal conversion of biomass, the implementation of which is expected to achieve a simple and selective production of light oil, clean biochar or/and fuel gas, with sufficiently high recoveries and relatively moderate reaction conditions.

First, the robust structure of biomass, composed of different chemical components (cellulose, hemicellulose and lignin), impedes an effective valorization of that and therefore, fractionation of the biomass into individual components is frequently applied in modern biorefinery such as the pulp and emerged 2nd ethanol industries. To data, various pretreatment technologies have been developed including alkaline-based methods (e.g., Kraft pulping, sulfate pulping) and acid-catalyzed Saccharization (e.g., organosolv pulping, concentrated acid hydrolysis, subcritical water hydrolysis), in which the lignin fraction is isolated as a typical by-product. Lignin though embodies the largest source of bio-aromatics, and the utilization of this feedstock for the production of chemicals has come into the spotlight. However, the recalcitrant condensed structure of the isolated lignin renders a difficult value-added use but mostly as a cheap energy source. We recognize that amongst the existing thermochemical technologies, pyrolysis is the simplest way to convert the lignin into biochar and monomers. Therefore, the conversion of a Klason lignin by a proposed pyrolysis process was investigated, the results of which are discussed in Chapter 2. Second, biomass-derived aqueous stream in modern biorefinery is another by-product with very limited applications, which otherwise must then be treated before discharging to the environment. The aqueous phase of bio-oil from pyrolysis is a representative waste stream, the composition of which is more or less similar to that of effluent water from hydrothermal treatment of biomass. This type of by-products mainly contains water and lots of organic compounds such as phenolic compounds, alcohols and carboxylic acids, etc. Treatment of the pyrolytic aqueous phase by hydrothermal gasification could not only reduce its total organic content but also enable energy recovery in the form of CH4/H2 fuel gases, which are the main driving force for Chapter 3. Regardless of the hazardous properties, the pyrolytic aqueous phase is highly acidic and thus shows great promise as an alternative of mineral acids for leaching alkali and alkaline earth metals (AAEMs) from biochar, which could mitigate ash-related issues during char-related applications. The leaching of char with the aqueous phase was in-detail investigated in Chapter 4. Third, as a promising method to process highly wet feedstocks, hydrothermal gasification was further applied to lignite-to-syngas conversion (Chapter 5).

Six chapters including the detailed works and a general summary are involved in this thesis. Chapter 1 gives a general overview of the core topic of the present work. The importance of biomass as an energy source is presented, along with the technologies for its energetic exploitation. The focus is then moved to hydrothermal processes and, in particular, to hydrothermal gasification. After presenting the most relevant physical and chemical properties of hot-compressed water, the state of the art for HTG is drawn. Finally, the objectives of the present work are stated.

Chapter 2 describes a particular type of pyrolysis that recycles the heavier portion of bio-oil (HO) entirely to pyrolysis, employing the parent feedstock for their capturing or/and recycling. Continuous pyrolysis of a cedar lignin with HO recycling was simulated by repeating fix-bed pyrolysis of HO-loaded lignin up to nine times, and demonstrated the steady state of yields of gas, water, char and light oil (LO) that consisted solely of monomers and furans and lower acids, with neither discharge of HO from the system nor accumulation therein. Theoretical yields of the products were compared with the experimental values, which confirmed the HO–lignin interactions. The recycled HO underwent not only self-pyrolysis/carbonization but also co-pyrolysis or/and carbonization with the lignin, resulting in the char formation and degradation into LO, in particular, phenolic monomers such as catechol, guaiacol and their derivates.

Chapter 3 proposes a sequential conversion of biomass into syngas and clean biochar, without use of external chemicals. Aqueous pyrolytic phase of bio-oil was used as a useful agent to leach alkali and alkaline earth metallic species from the char, and then was subjected to HTG in a continuous flow reactor at 350°C for 280 min, employing a 4.6 wt% ruthenium/activated-charcoal catalyst. The leaching transforms 92% of K form the char to the solution and the resultant carbon conversion by the subsequent HTG was 99% while a CH4-rich fuel gas and clean water abundance in K were produced.

Chapter 4 in-detail investigated repeated leaching of char with pyrolytic aqueous phase at ambient temperature in a batch mode. The leaching of AAEMs is initially rapid and followed by a slower rate towards equilibrium, which can be broadly described by a pseudo-second order model. In terms of the leaching kinetics of K, Mg and Ca, the leaching almost reaches equilibrium within 1 h, with near-steady removal rates of 65, 55 and 74%, respectively. Repeated leaching of biochar with the aqueous phase up to 18 times enables the internal recycling of the pyrolytic products.

Chapter 5 demonstrated a sequence of degradation, dissolution and catalytic hydrothermal gasification of lignite in alkaline water. A Victorian lignite was subjected to hydrothermal treatment (HT) in an aqueous solution of NaOH at 250°C, and then oxidation with pressurized O2 at 100°C. The sequential HT and oxidation near-completely solubilized the lignite. The resulting solution was successfully converted by CHTG in a flow reactor at 350°C for 10 h, employing a 16 wt% ruthenium/activated-charcoal catalyst. The initial carbon conversion to gas was as high as 98% while CH4, CO2 and H2 were produced. The catalyst deactivation was in detail discussed and caused mainly by the coke deposition that is related to the heavier portion (molecular mass >1,000) of the solubilized lignite.

Chapter 6 summarizes the general conclusions, perspectives and recommendations based on the finding in the preceding chapters.

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参考文献

[1] Dudley B. BP statistical review of world energy. BP Statistical Review of World Energy, London, accessed June 2019.

[2] Kruse A. Supercritical water gasification. Biofuels, Bioproducts and Biorefining 2008, 2, 415–437.

[3] Kruse A., Dinjus E. Hot compressed water as reaction medium and reactant: Properties and synthesis reactions. The Journal of Supercritical Fluids 2007, 39, 362–380.

[4] Kashimura N., Hayashi J-i., Chiba T. Degradation of a Victorian brown coal in sub- critical water. Fuel 2004, 83, 353–358.

[5] Zheng Q., Morimoto M., Sato H., Takanohashi T. Molecular composition of extracts obtained by hydrothermal extraction of brown coal. Fuel 2015, 159, 751–758.

[6] Modell M., Reid R. C., Amin S. I. Gasification process. U.S. Patent 4,113,446, 1978.

[7] Yamaguchi D., Sanderson P. J., Lim S., Aye L. Supercritical water gasification of Victorian brown coal: Experimental characterisation. International Journal of Hydrogen Energy 2009, 34, 3342–3350.

[8] Ge Z., Guo S., Guo L., Cao C., Su X., Jin H. Hydrogen production by non-catalytic partial oxidation of coal in supercritical water: Explore the way to complete gasification of lignite and bituminous coal. International Journal of Hydrogen Energy 2013, 38, 12786–12794.

[9] Kumabe K., Nishimura Y., Kambara S., Moritomi H. Kinetic study of subcritical steam gasification of coal using calcium-based carbon dioxide sorbent. Industrial & Engineering Chemistry Research 2014, 53, 2183–2188.

[10] Ge Z., Jin H., Guo L. Hydrogen production by catalytic gasification of coal in supercritical water with alkaline catalysts: Explore the way to complete gasification of coal. International Journal of Hydrogen Energy 2014, 39, 19583–19592.

[11] Lan R., Jin H., Guo L., Ge Z., Guo S., Zhang X. Hydrogen production by catalytic gasification of coal in supercritical water. Energy & Fuels 2014, 28, 6911–6917.

[12] Yu J., Lu X., Shi Y., Chen Q., Guan Q., Ning P., Tian S., Gu J. Catalytic gasification of lignite in supercritical water with Ru/CeO2–ZrO2. International Journal of Hydrogen Energy 2016, 41, 4579–4591.

[13] Huber G. W., Shabaker J. W., Dumesic J. A. Raney Ni-Sn catalyst for H2 production from biomass-derived hydrocarbons. Science 2003, 300, 2075–2077.

[14] Elliott D. C., Phelps M., Sealock Jr L. J., Baker E. G. Chemical processing in high- pressure aqueous environments. 4. Continuous-flow reactor process development experiments for organics destruction. Industrial & Engineering Chemistry Research 1994, 33, 566–574.

[15] Elliott D. C., Hart T. R., Neuenschwander G. G. Chemical processing in high-pressure aqueous environments. 8. Improved catalysts for hydrothermal gasification. Industrial & Engineering Chemistry Research 2006, 45, 3776–3781.

[16] Nakagawa H., Namba A., Böhlmann M., Miura K. Hydrothermal dewatering of brown coal and catalytic hydrothermal gasification of the organic compounds dissolving in the water using a novel Ni/carbon catalyst. Fuel 2004, 83, 719–725.

[17] Morimoto M., Nakagawa H., Miura K. Hydrothermal extraction and hydrothermal gasification process for brown coal conversion. Fuel 2008, 87, 546–551.

[18] Hayashi J-i., Matsuo Y., Kusakabe K., Morooka S. Depolymerization of lower rank coals by low-temperature O2 oxidation. Energy & Fuels 1997, 11, 227–235.

[19] Wang W., Hou Y., Wu W., Niu M., Liu W. Production of benzene polycarboxylic acids from lignite by alkali-oxygen oxidation. Industrial & Engineering Chemistry Research 2012, 51, 14994–15003.

[20] Li W., Hou Y., Yang F., Wu W. Production of benzene carboxylic acids and small- molecule fatty acids from lignite by two-stage alkali-oxygen oxidation. Industrial & Engineering Chemistry Research 2017, 56, 1971–1978.

[21] Miller J., Evans L., Littlewolf A., Trudell D. Batch microreactor studies of lignin and lignin model compound depolymerization by bases in alcohol solvents. Fuel 1999, 78, 1363–1366.

[22] Muangrat R., Onwudili J. A., Williams P. T. Influence of alkali catalysts on the production of hydrogen-rich gas from the hydrothermal gasification of food processing waste. Applied Catalysis B: Environmental 2010, 100, 440–449.

[23] Elliott D. C., Sealock L. J. J., Baker E. G. Chemical processing in high-pressure aqueous environments. 3. Batch reactor process development experiments for organics destruction. Industrial & Engineering Chemistry Research 1994, 33, 558–565.

[24] Onwudili J. A., Williams P. T. Hydrogen and methane selectivity during alkaline supercritical water gasification of biomass with ruthenium-alumina catalyst. Applied Catalysis B: Environmental 2013, 132–133, 70–79.

[25] Davda R., Shabaker J., Huber G., Cortright R., Dumesic J. A. A review of catalytic issues and process conditions for renewable hydrogen and alkanes by aqueous-phase reforming of oxygenated hydrocarbons over supported metal catalysts. Applied Catalysis B: Environmental 2005, 56, 171–186.

[26] Elliott D. C., Sealock Jr L. J., Baker E. G. Chemical processing in high-pressure aqueous environments. 2. Development of catalysts for gasification. Industrial & Engineering Chemistry Research 1993, 32, 1542–1548.

[27] Ravenelle R. M., Copeland J. R., Kim W. G., Crittenden J. C., Sievers C. Structural changes of γ-Al2O3-supported catalysts in hot liquid water. ACS Catalysis 2011, 1, 552–561.

[28] Muangrat R., Onwudili J. A., Williams P. T. Influence of NaOH, Ni/Al2O3 and Ni/SiO2 catalysts on hydrogen production from the subcritical water gasification of model food waste compounds. Applied Catalysis B: Environmental 2010, 100, 143–156.

[29] Kudo S., Hachiyama Y., Takashima Y., Tahara J., Idesh S., Norinaga K., Hayashi J-i. Catalytic hydrothermal reforming of lignin in aqueous alkaline medium. Energy & Fuels 2014, 28, 76–85.

[30] Liu T. L., Cao J. P., Zhao X. Y., Wang J. X., Ren X. Y., Fan X., Zhao Y. P., Wei X. Y. In situ upgrading of Shengli lignite pyrolysis vapors over metal-loaded HZSM-5 catalyst. Fuel Processing Technology 2017, 160, 19–26.

[31] Penninger J. Selectivity effects in aqueous supercritical fluid extraction of subbituminous coal. Fuel 1989, 68, 983–989.

[32] Hayashi J-i., Aizawa S., Kumagai H., Chiba T. Evaluation of macromolecular structure of a brown coal by means of oxidative degradation in aqueous phase. Energy & Fuels 1999, 13, 69–76.

[33] Liu P., Wang L., Zhou Y., Pan T., Lu X., Zhang D. Effect of hydrothermal treatment on the structure and pyrolysis product distribution of Xiaolongtan lignite. Fuel 2016, 164, 110–118.

[34] Hayashi J-i., Chiba T. Quantitative description of oxidative degradation of brown coal in aqueous phase on the basis of Bethe Lattice statistics. Energy & Fuels 1999, 13, 1230–1238.

[35] Kruse A., Dinjus E. Hydrogen from methane and supercritical water. Angewandte Chemie International Edition 2003, 42, 909–911.

[36] Idesh S., Kudo S., Norinaga K., Hayashi J-i. Catalytic hydrothermal reforming of water-soluble organics from the pyrolysis of biomass using a Ni/carbon catalyst impregnated with Pt. Energy & Fuels 2012, 26, 67–74.

[37] Chakinala A. G., Chinthaginjala J. K., Seshan K., van Swaaij W. P., Kersten S. R., Brilman D. W. Catalyst screening for the hydrothermal gasification of aqueous phase of bio-oil. Catalysis Today 2012, 195, 83–92.

[38] Zhang L., Xu C. C., Champagne P. Activity and stability of a novel Ru modified Ni catalyst for hydrogen generation by supercritical water gasification of glucose. Fuel 2012, 96, 541–545.

[39] Lee I. G., Ihm S. K. Catalytic gasification of glucose over Ni/activated charcoal in supercritical water. Industrial & Engineering Chemistry Research 2009, 48, 1435– 1442.

[40] Kawazoe K. Axial dispersion in packed bed wherein mass transfer between fluid and particle exists. Kagaku Kogaku 1968, 32, 1122–1127.

[41] Davda R., Shabaker J., Huber G., Cortright R., Dumesic J. A. Aqueous-phase reforming of ethylene glycol on silica-supported metal catalysts. Applied Catalysis B: Environmental 2003, 43, 13–26.

[42] Wambach J., Schubert M., Döbeli M., Vogel F. Characterization of a spent Ru/C catalyst after gasification of biomass in supercritical water. CHIMIA 2012, 66, 706– 711.

[43] Forzatti P., Lietti L. Catalyst deactivation. Catalysis Today 1999, 52, 165–181.

[44] de Vlieger D. J. M., Lefferts L., Seshan K. Ru decorated carbon nanotubes – a promising catalyst for reforming bio-based acetic acid in the aqueous phase. Green Chemistry 2014, 16, 864–874.

[45] Hayashi J-i., Kudo S., Kim H. S., Norinaga K., Matsuoka K., Hosokai S. Low- temperature gasification of biomass and lignite: Consideration of key thermochemical phenomena, rearrangement of reactions, and reactor configuration. Energy & Fuels 2014, 28, 4–21.

[46] van der Meijden C. M., Veringa H. J., Rabou L. P. The production of synthetic natural gas (SNG): A comparison of three wood gasification systems for energy balance and overall efficiency. Biomass and Bioenergy 2010, 34, 302–311.

[47] Matsumura Y. Evaluation of supercritical water gasification and biomethanation for wet biomass utilization in Japan. Energy Conversion and Management 2002, 43, 1301–1310.

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