JP4666378B2 - Decomposition method for woody waste - Google Patents
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- JP4666378B2 JP4666378B2 JP2006148080A JP2006148080A JP4666378B2 JP 4666378 B2 JP4666378 B2 JP 4666378B2 JP 2006148080 A JP2006148080 A JP 2006148080A JP 2006148080 A JP2006148080 A JP 2006148080A JP 4666378 B2 JP4666378 B2 JP 4666378B2
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- 239000002699 waste material Substances 0.000 title claims description 44
- 238000000354 decomposition reaction Methods 0.000 title claims description 36
- 238000000034 method Methods 0.000 title claims description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 32
- 239000007788 liquid Substances 0.000 claims description 23
- 239000002023 wood Substances 0.000 claims description 17
- 239000003125 aqueous solvent Substances 0.000 claims description 11
- 239000000843 powder Substances 0.000 claims description 11
- 239000003799 water insoluble solvent Substances 0.000 claims description 11
- 238000004821 distillation Methods 0.000 claims description 6
- 239000002916 wood waste Substances 0.000 claims description 5
- 150000001875 compounds Chemical class 0.000 claims description 4
- 239000000463 material Substances 0.000 claims description 3
- 239000002245 particle Substances 0.000 claims description 3
- 125000004432 carbon atom Chemical group C* 0.000 claims description 2
- 239000002351 wastewater Substances 0.000 claims description 2
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 description 24
- 238000011282 treatment Methods 0.000 description 24
- 239000000047 product Substances 0.000 description 19
- VLKZOEOYAKHREP-UHFFFAOYSA-N n-Hexane Chemical compound CCCCCC VLKZOEOYAKHREP-UHFFFAOYSA-N 0.000 description 9
- -1 nitrogen-containing polysaccharides Chemical class 0.000 description 8
- JMFRWRFFLBVWSI-NSCUHMNNSA-N coniferol Chemical compound COC1=CC(\C=C\CO)=CC=C1O JMFRWRFFLBVWSI-NSCUHMNNSA-N 0.000 description 6
- 229920005610 lignin Polymers 0.000 description 6
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 5
- 239000008346 aqueous phase Substances 0.000 description 5
- 239000007857 degradation product Substances 0.000 description 5
- 239000012071 phase Substances 0.000 description 5
- OFBQJSOFQDEBGM-UHFFFAOYSA-N Pentane Chemical compound CCCCC OFBQJSOFQDEBGM-UHFFFAOYSA-N 0.000 description 4
- 229920002678 cellulose Polymers 0.000 description 4
- 239000001913 cellulose Substances 0.000 description 4
- 238000000926 separation method Methods 0.000 description 4
- 239000002904 solvent Substances 0.000 description 4
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 3
- 229920002488 Hemicellulose Polymers 0.000 description 3
- 229940119526 coniferyl alcohol Drugs 0.000 description 3
- 238000011161 development Methods 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 229930015763 p-coumaryl alcohol Natural products 0.000 description 3
- 238000010298 pulverizing process Methods 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- PTNLHDGQWUGONS-UHFFFAOYSA-N trans-p-coumaric alcohol Natural products OCC=CC1=CC=C(O)C=C1 PTNLHDGQWUGONS-UHFFFAOYSA-N 0.000 description 3
- PTNLHDGQWUGONS-OWOJBTEDSA-N trans-p-coumaryl alcohol Chemical compound OC\C=C\C1=CC=C(O)C=C1 PTNLHDGQWUGONS-OWOJBTEDSA-N 0.000 description 3
- 239000003021 water soluble solvent Substances 0.000 description 3
- 235000013162 Cocos nucifera Nutrition 0.000 description 2
- 244000060011 Cocos nucifera Species 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 150000001298 alcohols Chemical class 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 125000000217 alkyl group Chemical group 0.000 description 2
- 238000002144 chemical decomposition reaction Methods 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 239000012530 fluid Substances 0.000 description 2
- 239000002803 fossil fuel Substances 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 230000002250 progressing effect Effects 0.000 description 2
- 239000011802 pulverized particle Substances 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 235000018185 Betula X alpestris Nutrition 0.000 description 1
- 235000018212 Betula X uliginosa Nutrition 0.000 description 1
- 239000002028 Biomass Substances 0.000 description 1
- 241000218645 Cedrus Species 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 241000233866 Fungi Species 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000004128 high performance liquid chromatography Methods 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000000178 monomer Substances 0.000 description 1
- 150000002772 monosaccharides Chemical class 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 229920001282 polysaccharide Polymers 0.000 description 1
- 239000005017 polysaccharide Substances 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/50—Improvements relating to the production of bulk chemicals
- Y02P20/54—Improvements relating to the production of bulk chemicals using solvents, e.g. supercritical solvents or ionic liquids
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/78—Recycling of wood or furniture waste
Landscapes
- Processing Of Solid Wastes (AREA)
Description
本発明は木質系廃材の処理に関するもので、さらに詳しくは廃材の粉砕粉末を、超臨界状態または亜臨界状態の水および常温で液状を保つ非水溶系の溶剤の混合液に接触させることを特徴とする木質系廃材の分解処理方法に関するものである。 The present invention relates to the treatment of wood-based waste materials. More specifically, the waste material pulverized powder is brought into contact with a mixture of supercritical or subcritical water and a non-aqueous solvent that remains liquid at room temperature. The present invention relates to a method for decomposing a wood-based waste material.
石油や石炭などの化石燃料をエネルギー資源としてきた従来の発展に対して、地球環境維持、持続可能な社会の実現に向けて、バイオマスエネルギーや太陽エネルギーなど、化石燃料以外のエネルギー開発が急速に行われている。 Energy development other than fossil fuels, such as biomass energy and solar energy, has been rapidly progressing toward the maintenance of the global environment and the realization of a sustainable society in contrast to the conventional development that has used fossil fuels such as oil and coal. It has been broken.
また、地球環境保護の観点からは廃棄物においても、廃棄物処理場の不足や廃棄物の再利用・リサイクルなど多くの課題があり、その対策技術が多く検討されている。 Also, from the viewpoint of protecting the global environment, there are many problems with waste, such as a shortage of waste disposal sites and reuse / recycling of waste.
このような状況の中で、樹皮や間伐材、剪定枝、建築廃材などから発生する木質系廃材の再利用技術の開発も強く求められている。また、木質系廃材は、上記建築廃材などだけでなく、東南アジアなどで多く栽培されているパーム椰子の椰子殻廃材や廃葉・廃幹なども大量に発生するため、その利用方法の開発が望まれている。 Under such circumstances, there is a strong demand for the development of recycling technology for wood-based waste materials generated from bark, thinned wood, pruned branches, building waste, and the like. In addition to the above-mentioned building waste materials, wooden waste materials such as palm coconut shell waste, waste leaves and stems that are cultivated in Southeast Asia are also generated in large quantities. It is rare.
木質系廃材の分解処理方法としては、菌類による生物的分解や、酸・アルカリなどによる化学的分解が多く検討されており、最近では高温高圧水による処理もいろいろ検討が進んでいる。 As a decomposition treatment method of woody waste materials, biological decomposition by fungi and chemical decomposition by acid, alkali, etc. have been studied a lot. Recently, various treatments by high-temperature high-pressure water have been studied.
特に最近では、超臨界流体を用いた分解処理方法が多く提案されている。例えば、特許文献1では超臨界水や亜臨界水による木材の高速糖化、特許文献2では植物由来廃棄物を超臨界水あるいは亜臨界水で分解処理する方法、特許文献3ではリグノセルロースやセルロース、含窒素多糖質類やタンパク質を超臨界アルコールや亜臨界アルコールで処理する方法が提案されている。
エネルギー問題および環境問題の観点からも、多くの木質系廃材の分解処理方法が検討されているが、処理速度や工業規模での効率的な処理手法や処理量に課題がある。 From the viewpoints of energy problems and environmental problems, many woody waste decomposition methods have been studied, but there are problems with processing speed and efficient processing techniques and throughput on an industrial scale.
さらに、酸・アルカリによる化学的分解では、分解処理後の液体の分離や液管理、液の二次処理などの工程が必須であり、その工程に大きなエネルギーを要し、更なる環境問題を引き起こす可能性も考えられる。 Furthermore, chemical decomposition with acid / alkali requires steps such as liquid separation and liquid management after the decomposition treatment, and secondary treatment of the liquid, which requires a large amount of energy and causes further environmental problems. There is a possibility.
超臨界流体を用いた分解処理は、短時間で処理することが可能である。しかし、水で処理した場合には、処理後の分解物を水中より分離回収することが必要となり、溶媒との混和などの工程が必要となる。超臨界アルコールなどのアルコール系で処理する場合、超臨界水系に比べると一般的に反応が遅くなるが、アルコールは水に比べて低温、低圧で超臨界状態となるため、より有用と考えられる。一方、アルコール系により超臨界処理を行った場合、油溶成分を非水溶系の溶剤を用いて抽出することは困難である。これは、アルコール系が非水溶系の溶剤と相溶性を持つためである。 The decomposition process using a supercritical fluid can be performed in a short time. However, in the case of treatment with water, it is necessary to separate and recover the treated decomposition product from water, and a step such as mixing with a solvent is required. In the case of treatment with an alcohol system such as a supercritical alcohol, the reaction is generally slower than that of a supercritical water system, but the alcohol is considered to be more useful because it is in a supercritical state at a lower temperature and lower pressure than water. On the other hand, when the supercritical treatment is performed with an alcohol system, it is difficult to extract the oil-soluble component using a non-aqueous solvent. This is because the alcohol system is compatible with the non-water-soluble solvent.
以上述べてきたような従来法の欠点を考え、本発明の目的は、低コストで容易に木質系廃材を分解処理かつ分離する方法を提供することである。 In view of the disadvantages of the conventional methods as described above, an object of the present invention is to provide a method for easily decomposing and separating wooden waste materials at low cost.
本発明は、分解処理する木質系廃材の粉砕粉末と非水溶系の溶剤と水を加熱して、前記非水溶系の溶剤と水の少なくとも一方を亜臨界あるいは超臨界状態にして前記木質系廃材の粉砕粉末を分解し、その後、木質系廃材の第1分解生成物を含んだ非水溶系の溶剤と、木質系廃材の第2分解生成物を含んだ水に分離し、分解生成物と非水溶系の溶剤は非水溶系の溶剤を揮発させることや蒸留操作によって第1分解生成物を分離し、水中に含まれる分解生成物は水を揮発させることや蒸留操作によって第2分解生成物を分離することを特徴とする。また、前記非水溶系の溶剤として2〜20個の範囲で炭素原子を持ち、常温で液状を保つ化合物を用いることを特徴とする。 The present invention heats the pulverized powder of a wood-based waste material to be decomposed, a water-insoluble solvent, and water to bring at least one of the water-insoluble solvent and water into a subcritical or supercritical state. Is then separated into a non-aqueous solvent containing the first decomposition product of the wooden waste material and water containing the second decomposition product of the wooden waste material. The water-soluble solvent separates the first decomposition product by volatilizing the non-water-soluble solvent or distillation operation, and the decomposition product contained in water removes the second decomposition product by volatilizing water or distillation operation. It is characterized by separating. In addition, a compound having 2 to 20 carbon atoms and keeping a liquid state at room temperature is used as the water-insoluble solvent.
なお、粉砕粉末の平均粒径が1mm以下であることが、分解処理効率向上のためには望ましい。 Note that the average particle size of the pulverized powder is preferably 1 mm or less in order to improve the decomposition efficiency.
本発明は、木質系廃材の粉砕粉末を超臨界状態または亜臨界状態にした、非水溶系の溶剤および水の混合物を用いて処理することにより、木質系廃材の主成分であり、一般には難分解物であるセルロースやヘミセルロース、リグニンなどを分解する。上記分解物のうち、難水溶性の分解物を超臨界状態の非水溶系の溶剤中にも溶解させる。非水溶系の溶剤は、水に対して非相溶性かつ比重の差により水と容易に分離することから、分液が容易であり、分液後の溶剤を揮発させ、新たな原料として利用できる分解生成物の回収が容易になる。また、溶剤を再回収し利用することにより、環境への配慮も可能となる。 The present invention is a main component of wood waste by treating with a mixture of water-insoluble solvent and water in which the pulverized powder of wood waste is in a supercritical state or subcritical state. Decomposes degradation products such as cellulose, hemicellulose, and lignin. Of the above decomposed products, a hardly water-soluble decomposed product is dissolved in a supercritical non-aqueous solvent. A water-insoluble solvent is incompatible with water and easily separated from water due to the difference in specific gravity. Therefore, it is easy to separate the liquid, and the solvent after separation can be volatilized and used as a new raw material. Recovery of decomposition products is facilitated. In addition, environmental considerations are possible by re-collecting and using the solvent.
本発明に供される木質系廃材は、どのような木の廃材でも分解可能であり、杉や檜の間伐材や樹皮、剪定枝はもちろん、それらの建築廃材などから発生する木質系廃材も分解できる。さらに、東南アジアなどで多く栽培されているパーム椰子の椰子殻廃材や廃葉・廃幹など、どのような木でもかまわない。 The wood-based waste material used in the present invention can be decomposed by any wood waste material, and wood-based waste materials generated from such thinned wood, bark, and pruned branches of cedar and birch, as well as from such construction waste materials are also decomposed it can. Further, any kind of palm coconut shell waste, waste leaves, and stems, which are often cultivated in Southeast Asia, may be used.
このような木質系廃材の主要な構成成分はセルロース、ヘミセルロース、リグニンであり、本発明では、温度や圧力、処理時間などの分解処理条件を変えることで、どの成分をどの程度まで分解するかを調整することができる。 The main components of such wood-based waste materials are cellulose, hemicellulose, and lignin. In the present invention, by changing the decomposition treatment conditions such as temperature, pressure, treatment time, etc., which components are decomposed to what extent. Can be adjusted.
ただし、本発明に供される木質系廃材は、分解処理前に粉砕する必要がある。粉砕粒度はできるだけ細かい方が望ましく、できれば1mm以下が好ましい。粉砕粒度が大きいと分解に長時間を要し、十分分解できない可能性がある。また、粉砕のためには木質系廃材の含有水分濃度はできるだけ小さい方がよく、50%以下が好ましい。そのため、廃材の種類によっては予め乾燥処理を施した方がよいものもある。 However, the wood-based waste material provided for the present invention needs to be pulverized before the decomposition treatment. The pulverized particle size is desirably as fine as possible, and preferably 1 mm or less. If the pulverized particle size is large, the decomposition takes a long time and may not be sufficiently decomposed. For pulverization, the water content of the wood-based waste material should be as low as possible, preferably 50% or less. Therefore, depending on the type of waste material, it may be better to perform a drying process in advance.
粉砕処理には、一般的な粉砕処理装置である破砕機やカッターミル、ディスクミルなどを組み合わせて使用できる。 For the pulverization process, a general pulverization apparatus such as a crusher, a cutter mill, a disk mill, etc. can be used in combination.
本発明に供されるアルキル化合物群および芳香族を含むアルキル化合物群は、ペンタン、ヘキサン、トルエン等からなる群から選択される少なくとも1つの溶剤であることが好ましい。なお、これらのアルキル化合物および芳香族を含むアルキル化合物は1種類あるいは2種類以上の混合液でもかまわない。 The alkyl compound group and the aromatic alkyl compound group used in the present invention are preferably at least one solvent selected from the group consisting of pentane, hexane, toluene and the like. In addition, these alkyl compounds and alkyl compounds containing aromatics may be one kind or a mixture of two or more kinds.
本発明のアルキル化合物および芳香族を含むアルキル化合物は、処理する木質系廃材の
種類や量によって決められるが、少なすぎると廃材の分解によって生じる分解物を溶解し難くなり、多すぎると分解処理および分液後の液の処理工程や時間が多くなるため、適度な量を選択する必要がある。
The alkyl compound of the present invention and the alkyl compound containing aromatics are determined by the type and amount of the wood-based waste material to be treated, but if the amount is too small, it becomes difficult to dissolve the decomposition products generated by the decomposition of the waste material, and if too much, Since the treatment process and time of the liquid after the liquid separation increase, it is necessary to select an appropriate amount.
また、処理温度および圧力は、アルキル化合物群および芳香族を含むアルキル化合物群が亜臨界あるいは超臨界になる温度、圧力以上が好ましい。
ペンタンの臨界温度は469.7K、臨界圧力33.7MPa、ヘキサンの臨界温度は507.5K、臨界圧力30.1MPa、トルエンの臨界温度は591.8K、臨界圧力は41.0MPaである。
Further, the treatment temperature and pressure are preferably equal to or higher than the temperature and pressure at which the alkyl compound group and the aromatic alkyl-containing compound group become subcritical or supercritical.
The critical temperature of pentane is 469.7K, the critical pressure is 33.7MPa, the critical temperature of hexane is 507.5K, the critical pressure is 30.1MPa, the critical temperature of toluene is 591.8K, and the critical pressure is 41.0MPa.
本発明の処理方法では、亜臨界あるいは超臨界状態の水に、亜臨界あるいは超臨界状態のアルキル化合物群および芳香族を含むアルキル化合物群を添加させることによって、木質系廃材の分解と分解処理後の生成物の分離、回収を容易に行うことができる。 In the treatment method of the present invention, after the decomposition and decomposition treatment of the wood-based waste material, the subcritical or supercritical water is added with the subcritical or supercritical alkyl compound group and the aromatic alkyl compound group. The product can be easily separated and recovered.
本発明の処理方法は、例えば、まず分解処理する木質系廃材を粉砕機などにより微粉化する。次に、その粉砕粉末と水および非水溶系の溶剤を耐圧容器に入れる。次に、この耐圧容器を加熱して水および非水溶系の溶剤が亜臨界あるいは超臨界状態になるよう調節して、数秒〜数十分の処理を行う。この処理により、木質系廃材粉末のセルロースやヘミセルロース、リグニンは、それらの低分子化合物やモノマー、オリゴマーなどに分解される。その後、耐圧容器を常温常圧に戻して開放することにより、水と非水溶系の溶剤は比重により分離する。さらに、分解生成物と非水溶系の溶剤は非水溶系の溶剤を揮発させることや蒸留操作によって分離される。また、水中に含まれる分解生成物も同様に揮発させることや蒸留操作によって分離される。さらに、水および非水溶系の溶剤にも溶解しない固体成分の場合は、ろ過などで容易に分離できる。 In the treatment method of the present invention, for example, first, the wood waste material to be decomposed is pulverized by a pulverizer or the like. Next, the pulverized powder, water, and a water-insoluble solvent are placed in a pressure vessel. Next, the pressure vessel is heated to adjust the water and the non-aqueous solvent to a subcritical or supercritical state, and a treatment for several seconds to several tens of minutes is performed. Through this treatment, cellulose, hemicellulose, and lignin in the woody waste powder are decomposed into their low molecular compounds, monomers, oligomers, and the like. Thereafter, the pressure vessel is returned to normal temperature and pressure and opened to separate water and the non-aqueous solvent by specific gravity. Furthermore, the decomposition product and the water-insoluble solvent are separated by volatilizing the water-insoluble solvent or by a distillation operation. In addition, decomposition products contained in water are similarly separated by volatilization or distillation. Further, in the case of a solid component that does not dissolve in water or a non-aqueous solvent, it can be easily separated by filtration or the like.
以下具体的実施例を挙げて、本発明をより詳細に説明する。 Hereinafter, the present invention will be described in more detail with reference to specific examples.
本実施例では、木質系廃材として200×300×50mmの板状に切り出したパーム椰子廃幹を用いた。 In this example, a palm palm waste trunk cut into a plate shape of 200 × 300 × 50 mm was used as the wood-based waste material.
このパーム椰子廃幹を、φ10mmのスクリーンを付けた槇野産業製カッターミルVM−22で数mm程度に粗粉砕した。次に、その粗粉砕品を槇野産業製微粉砕機DD−2−3.7により、さらに粉砕を行った。なお、スクリーンはΦ0.35mmを用いた。その結果、平均粒径約0.15mmの微粉末が得られた。 This palm palm trunk was coarsely pulverized to a few millimeters with a cutter mill VM-22 manufactured by Sugano Sangyo Co., Ltd. equipped with a 10 mm screen. Next, the coarsely pulverized product was further pulverized by a fine pulverizer DD-2-3.7 manufactured by Hadano Sangyo. The screen used was Φ0.35 mm. As a result, a fine powder having an average particle size of about 0.15 mm was obtained.
この微粉末0.4gを耐熱・耐圧容器に入れ、トルエン約10mlと水約10mlを添加した。その耐熱・耐圧容器を高温槽に入れて350℃まで加温し、1分処理した。また、同様の条件で30分および1時間処理したサンプルも作成した。 0.4 g of this fine powder was put in a heat-resistant / pressure-resistant container, and about 10 ml of toluene and about 10 ml of water were added. The heat-resistant / pressure-resistant container was placed in a high-temperature bath and heated to 350 ° C. and treated for 1 minute. Moreover, the sample processed for 30 minutes and 1 hour on the same conditions was also created.
その後、耐熱・耐圧容器を水浴槽に移して常温まで冷却してから、耐熱・耐圧容器を開放し、常圧に戻した。 Thereafter, the heat and pressure resistant container was transferred to a water bath and cooled to room temperature, and then the heat and pressure resistant container was opened and returned to normal pressure.
1分処理した場合は、わずかな残渣物と濃茶色の液体が残っていたが、30分以上処理した場合固形物は殆どなくなり、液体のみとなっていた。わずかな残渣は濾紙により濾過して液体と固体を分離した。さらに液体を水相とトルエン相に分液し、各々を高速液体クロマトグラフィーで分析した。 When treated for 1 minute, a slight residue and a dark brown liquid remained, but when treated for 30 minutes or more, almost no solid matter was found and only liquid was obtained. The slight residue was filtered through filter paper to separate the liquid and solid. Further, the liquid was separated into an aqueous phase and a toluene phase, and each was analyzed by high performance liquid chromatography.
水相に比べ、トルエン相中には難水溶性の分解物が多く含まれていた。1分処理した場合に比べ30分以上処理した液体には、上記分解生成物である酢酸等の有機酸を多く含む
ことが判った。
Compared to the aqueous phase, the toluene phase contained a lot of poorly water-soluble decomposition products. It was found that the liquid treated for 30 minutes or more compared with the case of treating for 1 minute contains a large amount of organic acid such as acetic acid as the decomposition product.
この結果より、上記条件で処理することで、水相とトルエン相は異なる分解物成分を溶解した状態になることが判った。特にトルエン相には、難水溶性のリグニン由来の分解物を含むことが確認でき、有用な分解物を効率良く分解処理と共に抽出することが可能となった。 From this result, it was found that by treating under the above conditions, the aqueous phase and the toluene phase are in a state in which different decomposition product components are dissolved. In particular, it was confirmed that the toluene phase contained degradation products derived from poorly water-soluble lignin, and useful degradation products could be efficiently extracted together with the degradation treatment.
また、不溶成分は分液前に濾紙を用いて濾過することにより、液相から分離回収することが可能である。 Further, insoluble components can be separated and recovered from the liquid phase by filtering with a filter paper before liquid separation.
本実施例では、木質系廃材として実施例1と同じ方法で粉砕したパーム椰子廃幹を用いた。 In this example, a palm palm waste trunk pulverized by the same method as in Example 1 was used as the wooden waste material.
非水溶系溶剤としてヘキサンを用い、水を加えた状態にて処理温度を180℃、240℃、280℃に変更した以外は、実施例1と同様の条件で1分間処理した。 The treatment was performed for 1 minute under the same conditions as in Example 1 except that hexane was used as the non-aqueous solvent and the treatment temperature was changed to 180 ° C., 240 ° C., and 280 ° C. with water added.
この結果、180℃では、粉砕粉末はほとんど変わらず、約80%程度の残渣と淡黄色の液体が得られた。240℃では約50%程度の残渣と濃黄色の液体が得られ、280℃では約20%程度の残渣と濃茶色の液体が得られ、350℃では実施例1とほぼ同様のわずかな残渣と濃茶色の液体が得られた。これらの残渣は濾紙により分離して、実施例1と同様に液体の分析を行った。 As a result, at 180 ° C., the pulverized powder hardly changed, and about 80% of a residue and a light yellow liquid were obtained. About 240% residue and a dark yellow liquid are obtained at 240 ° C., about 20% residue and a dark brown liquid are obtained at 280 ° C., and a slight residue almost the same as in Example 1 is obtained at 350 ° C. A dark brown liquid was obtained. These residues were separated by filter paper, and the liquid was analyzed in the same manner as in Example 1.
180℃で処理した場合、水相、トルエン相ともにコニフェリルアルコールやp−クマリルアルコール、単糖類、糖の分解物などが含まれているものの、処理温度が低く、分解処理が進んでいないことがわかる。一方、240℃で処理した液体には、水相側に比べ、難水溶性のリグニン等の低分子成分やオリゴマーが多く、コニフェリルアルコールやp−クマリルアルコールのリグニン由来の分解物などが含まれていた。また、280℃で処理した液体には実施例1と同様のコニフェリルアルコールやp−クマリルアルコール、糖の分解物などが多く含まれていた。 When treated at 180 ° C, both aqueous phase and toluene phase contain coniferyl alcohol, p-coumaryl alcohol, monosaccharides, sugar degradation products, etc., but the treatment temperature is low and the decomposition treatment is not progressing. I understand. On the other hand, the liquid treated at 240 ° C. has more low-molecular components and oligomers such as poorly water-soluble lignin than the aqueous phase, and contains lignin-derived degradation products such as coniferyl alcohol and p-coumaryl alcohol. It was. Further, the liquid treated at 280 ° C. contained a lot of coniferyl alcohol, p-coumaryl alcohol, sugar decomposition products and the like as in Example 1.
以上のように本発明は、環境に大きな影響を及ぼしている木質系廃材を容易に分解させることができ、かつ、分解後の生成物の回収を容易に行うことができる。さらに、処理後の廃液などの処理も容易に行えるため、従来の超臨界水や亜臨界水を用いた方法に比べて、大幅に装置を簡略化でき、産業上有効である。
As described above, according to the present invention, it is possible to easily decompose a wood-based waste material that has a great influence on the environment, and to easily recover a product after the decomposition. Furthermore, since the waste liquid after the treatment can be easily treated, the apparatus can be greatly simplified and industrially effective as compared with the conventional method using supercritical water or subcritical water.
Claims (3)
その後、木質系廃材の第1分解生成物を含んだ非水溶系の溶剤と、木質系廃材の第2分解生成物を含んだ水に分離し、
分解生成物と非水溶系の溶剤は非水溶系の溶剤を揮発させることや蒸留操作によって第1分解生成物を分離し、
水中に含まれる分解生成物は水を揮発させることや蒸留操作によって第2分解生成物を分離する
木質系廃材の分解処理方法。 The wood waste material ground powder to be decomposed, the water-insoluble solvent and water are heated, and at least one of the water-insoluble solvent and water is brought into a subcritical or supercritical state. Disassemble,
After that, it is separated into a water-insoluble solvent containing the first decomposition product of the wooden waste material and water containing the second decomposition product of the wooden waste material,
The decomposition product and the non-aqueous solvent are separated from the first decomposition product by volatilizing the non-aqueous solvent or by distillation operation,
A method for decomposing a wooden waste material, wherein a decomposition product contained in water is volatilized and the second decomposition product is separated by distillation operation .
請求項1記載の木質系廃材の分解処理方法。 The method for decomposing a wood-based waste material according to claim 1, wherein an average particle size of the pulverized powder is 1 mm or less.
請求項1または請求項2に記載の木質系廃材の分解処理方法。 The method for decomposing a wooden waste material according to claim 1 or 2 , wherein a compound having 2 to 20 carbon atoms and maintaining a liquid state at room temperature is used as the non-aqueous solvent.
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US8759498B2 (en) | 2011-12-30 | 2014-06-24 | Renmatix, Inc. | Compositions comprising lignin |
KR101461283B1 (en) * | 2012-11-28 | 2014-11-19 | 연세대학교 산학협력단 | Method for decomposition of biomass in sub- and supercritical solnent |
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