JP2011045882A - Method for producing adsorbent and method for producing alcohol or organic acid - Google Patents

Method for producing adsorbent and method for producing alcohol or organic acid Download PDF

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JP2011045882A
JP2011045882A JP2010233967A JP2010233967A JP2011045882A JP 2011045882 A JP2011045882 A JP 2011045882A JP 2010233967 A JP2010233967 A JP 2010233967A JP 2010233967 A JP2010233967 A JP 2010233967A JP 2011045882 A JP2011045882 A JP 2011045882A
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biomass
adsorbent
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residue
alcohol
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JP5203438B2 (en
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Tomomoto Hayakawa
智基 早川
Naoyuki Okuda
直之 奥田
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Tsukishima Kikai Co Ltd
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    • YGENERAL 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
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Abstract

<P>PROBLEM TO BE SOLVED: To provide an adsorbent produced using a biomass residue, a method for producing the adsorbent, and a method for producing an alcohol or organic acid using the adsorbent. <P>SOLUTION: The method for producing an adsorbent comprises drying or carbonizing a biomass residue generated in a process for producing the alcohol or organic acid from a raw-material biomass. The adsorbent provided herein is obtained by the production method. The method for producing the alcohol or organic acid comprises using the adsorbent in the method for producing the alcohol or organic acid from the raw-material biomass. <P>COPYRIGHT: (C)2011,JPO&INPIT

Description

本発明は、原料バイオマスからアルコールや有機酸を製造する際に発生するバイオマス残渣を有効利用した吸着剤、その製造方法、並びに該吸着剤を用いたアルコール又は有機酸の製造方法に関する。   The present invention relates to an adsorbent that effectively uses biomass residues generated when alcohol or organic acid is produced from raw biomass, a method for producing the adsorbent, and a method for producing alcohol or organic acid using the adsorbent.

近年、地球温暖化対策や廃棄物の有効利用の観点から、植物資源を原料とするバイオマスの利用が注目されており、バイオマスをエタノール等のアルコールや有機酸に変換して、エネルギーや化学原料として利用する研究が進められている。特に、次世代自動車燃料として注目されるエタノールをバイオマスから製造する技術に注目が集まっている。   In recent years, from the viewpoint of global warming countermeasures and the effective use of waste, the use of biomass from plant resources has attracted attention. By converting biomass into alcohol such as ethanol and organic acids, it can be used as energy and chemical raw materials. Research to use is underway. In particular, attention has been focused on technology for producing ethanol, which is attracting attention as a next-generation automobile fuel, from biomass.

一般に、エタノール等を製造するための原料バイオマスとしては、サトウキビ等の糖質、トウモロコシ等のデンプン質が多く用いられている。その他にも、バガスや稲わらのような草木系バイオマス、木材チップ等の木質系バイオマス等のセルロース系資源が挙げられる。   Generally, sugars such as sugar cane and starches such as corn are often used as raw material biomass for producing ethanol and the like. Other examples include cellulosic resources such as plant biomass such as bagasse and rice straw, and woody biomass such as wood chips.

収集されたセルロース資源からエタノールを製造する場合、まず、粉砕、蒸煮、爆砕などの物理的手法、あるいは酸、アルカリによる化学的手法による糖化前処理を施した後、酸加水分解法や酵素分解法によってヘキソースやペントースなどの糖類にまで分解する(糖化工程)。   When ethanol is produced from the collected cellulose resources, first, saccharification pretreatment is performed by physical methods such as grinding, steaming, and explosion, or chemical methods using acids and alkalis, followed by acid hydrolysis and enzymatic decomposition. To decompose into saccharides such as hexose and pentose (saccharification process).

次いで、糖化工程で得られた糖類を微生物により発酵させてエタノールに変換させるが(発酵工程)、糖化前処理や糖化工程において酸やアルカリを使用した場合は、発酵工程の前に、それらを中和しておくことが好ましい(中和工程)。そして、エタノールを含む発酵物を蒸留により分離・精製して、エタノールを得ることができる(蒸留工程)。   Next, the saccharides obtained in the saccharification step are fermented by microorganisms and converted to ethanol (fermentation step). However, when acid or alkali is used in the saccharification pretreatment or saccharification step, they are added before It is preferable to neutralize (neutralization step). And the fermented material containing ethanol can be separated and purified by distillation to obtain ethanol (distillation step).

このとき、各工程からバイオマス残渣が発生する。すなわち、糖化工程から糖化残渣、中和工程から中和残渣や汚泥、発酵工程から発酵残渣、蒸留工程から蒸留残渣が発生する。これらのバイオマス残渣は多量の未利用有機物を含んでいるため、これらを処分することはエネルギー回収のロスとなるが、現状では、埋立て、焼却、メタン発酵などの方法により廃棄物として処理されている。   At this time, biomass residue is generated from each step. That is, a saccharification residue is generated from the saccharification step, a neutralization residue and sludge from the neutralization step, a fermentation residue from the fermentation step, and a distillation residue from the distillation step. Since these biomass residues contain a large amount of unused organic matter, disposing of them will result in a loss of energy recovery, but currently they are treated as waste by methods such as landfill, incineration, and methane fermentation. Yes.

一方で、セルロースを含む木質材を、所定の温度条件および酸素条件下で熱処理して得られる炭化物が、吸着剤、触媒、イオン交換体として用いられることが知られている(例えば、特許文献1参照。)。しかし、上記炭化物は、セルロース、でんぷん、あるいはこれらを含有する木質系廃棄物や農産廃棄物等の未利用植物資源を原料としており、バイオマス残渣を有効利用して製造されたものではない。   On the other hand, it is known that a carbide obtained by heat-treating a wood material containing cellulose under a predetermined temperature condition and oxygen condition is used as an adsorbent, a catalyst, and an ion exchanger (for example, Patent Document 1). reference.). However, the above-mentioned carbides are not produced by using biomass residue effectively, using cellulose, starch, or unused plant resources such as woody waste and agricultural waste containing these as raw materials.

特許第3138749号公報Japanese Patent No. 3138749

バイオマス残渣を埋立て処理する場合、広大な処分場が必要となる。また、焼却やメタン発酵などにより、バイオマス残渣の減容化、並びに熱回収が可能となるが、この場合は設備が過大になることや、得られる熱やバイオガスのハンドリングを考慮する必要があり、必ずしも有効な手段とはいえない。
そこで本発明は、原料バイオマスからアルコールまたは有機酸を製造する過程で発生するバイオマス残渣を利用した吸着剤、その製造方法、並びに該吸着剤を用いたアルコール又は有機酸の製造方法を提供することを目的とする。
When landfilling biomass residue, a vast disposal site is required. Incineration and methane fermentation can reduce the volume of biomass residue and recover heat, but in this case, it is necessary to consider excessive facilities and handling of the resulting heat and biogas. However, it is not necessarily an effective means.
Therefore, the present invention provides an adsorbent using biomass residue generated in the process of producing alcohol or organic acid from raw biomass, a method for producing the adsorbent, and a method for producing alcohol or organic acid using the adsorbent. Objective.

本発明は、未利用有機物を多量に含んでいるにもかかわらず、廃棄物として処分されてしまうバイオマス残渣に注目し、これを有効に利用する方法を鋭意検討した結果、バイオマス残渣を乾燥又は炭化することによって、優れた吸着剤が得られることを見出し、本発明を完成した。   The present invention pays attention to a biomass residue that is disposed of as waste even though it contains a large amount of unused organic matter, and as a result of earnestly examining a method for effectively using this, the biomass residue is dried or carbonized. As a result, it was found that an excellent adsorbent was obtained, and the present invention was completed.

即ち、本発明の吸着剤の製造方法は、原料バイオマスからアルコール又は有機酸を製造する過程において発生するバイオマス残渣を130〜230℃で3〜30分間酸加水分解し、得られた糖化残渣を乾燥又は炭化することを特徴とする。
本発明のアルコール又は有機酸の製造方法は、原料バイオマスからアルコール又は有機酸を製造する過程において発生するバイオマス残渣を130〜230℃で3〜30分間酸加水分解し、得られた糖化残渣を乾燥又は炭化することにより得られる吸着剤を利用することを特徴とする。
That is, in the method for producing an adsorbent of the present invention, a biomass residue generated in the process of producing an alcohol or an organic acid from raw material biomass is subjected to acid hydrolysis at 130 to 230 ° C. for 3 to 30 minutes, and the obtained saccharification residue is dried. Or, it is carbonized.
The method for producing alcohol or organic acid according to the present invention comprises subjecting biomass residue generated in the process of producing alcohol or organic acid from raw biomass to acid hydrolysis at 130 to 230 ° C. for 3 to 30 minutes, and drying the obtained saccharification residue Alternatively, an adsorbent obtained by carbonization is used.

本発明によれば、多量の未利用有機物を含んでいるにもかかわらず、従来は廃棄処分されていたバイオマス残渣を有効に利用することができるため、エネルギー回収効率が向上し、産業上非常に有用であるといえる。   According to the present invention, the biomass residue that has been disposed of in the past can be effectively used despite the fact that it contains a large amount of unused organic matter. It can be said that it is useful.

本発明の吸着剤は、原料バイオマスからアルコール又は有機酸を製造する過程において発生するバイオマス残渣を乾燥して製造されることを特徴とする。ここで、原料バイオマスとは、太陽エネルギーの第一次産物である植物体を意味し、サトウキビなどの糖質系バイオマス、トウモロコシなどのデンプン系バイオマス、バガスや稲わらなどの草木系バイオマス、木材チップ等の木質系バイオマス等を含むが、糖質系バイオマスやデンプン系バイオマスは、本来、食用資源である。従って、草木系バイオマス、木質系バイオマスなどのセルロースを含む原料バイオマスを用いることが好ましい。特に、余剰農産物、農産廃棄物、間伐材、及び木質建材等が好ましく用いられる。農産廃棄物としては、バガスや稲わら等が挙げられる。木質建材としては、製材工程残材、製品製造工程残材、新築、解体現場から発生する建築廃材、家具等一般ゴミ木質廃棄物等が挙げられる。   The adsorbent of the present invention is produced by drying a biomass residue generated in the process of producing an alcohol or an organic acid from raw material biomass. Here, raw material biomass means a plant that is the primary product of solar energy, sugar-based biomass such as sugar cane, starch-based biomass such as corn, plant-based biomass such as bagasse and rice straw, and wood chips. Although woody biomass and the like are included, carbohydrate biomass and starch biomass are inherently edible resources. Therefore, it is preferable to use raw material biomass containing cellulose, such as vegetation biomass and woody biomass. In particular, surplus agricultural products, agricultural waste, thinned wood, and wooden building materials are preferably used. Examples of agricultural waste include bagasse and rice straw. Examples of the woody building materials include lumber process residue, product production process residue, new construction, building waste generated from the demolition site, and general waste woody waste such as furniture.

本発明で用いられるバイオマス残渣は、糖化残渣、中和残渣、発酵残渣、蒸留残渣のうち少なくとも1つ以上を含む。これらの中でも、糖化残渣はセルロース、ヘミセルロースが除去されており、その部分が炭化時に細孔構造を形成しやすいため、糖化残渣を用いることが好ましい。
ここで、バイオマス残渣とは、原料バイオマスからアルコール又は有機酸を製造
する過程において発生するものであって、主にリグニンを含有している。
また、「糖化残渣」とは、後述する糖化工程で得られる糖類を含む溶液と分離された残渣を意味する。
「中和残渣」とは、中和の際に用いるアルカリ塩が沈殿する際、有機酸等を巻き込み、無機物、有機物が混在して発生する含水固形分を意味する。
「発酵残渣」とは、後述する発酵工程で得られるアルコールや有機酸などの有機化合物と分離された残渣を意味する。
「蒸留残渣」とは、後述する蒸留工程で、目的の有機化合物を分離・精製した後の排水を意味する。
The biomass residue used in the present invention includes at least one of saccharification residue, neutralization residue, fermentation residue, and distillation residue. Among these, saccharification residue is preferably used because cellulose and hemicellulose are removed from the saccharification residue and the portion easily forms a pore structure during carbonization.
Here, the biomass residue is generated in the process of producing alcohol or organic acid from raw material biomass, and mainly contains lignin.
The “saccharification residue” means a residue separated from a solution containing a saccharide obtained in a saccharification step described later.
The “neutralization residue” means a water-containing solid content generated by mixing an organic acid and the like when an alkali salt used for neutralization is precipitated, and including an inorganic substance and an organic substance.
“Fermentation residue” means a residue separated from an organic compound such as an alcohol or an organic acid obtained in a fermentation process described later.
The “distillation residue” means waste water after separation and purification of the target organic compound in the distillation step described later.

以下、原料バイオマスからアルコール又は有機酸などの有機化合物を製造する方法を説明する。
原料バイオマスからアルコール又は有機酸を製造する方法としては、公知の如何なる方法をも用いることができるが、例えば、糖化工程、中和工程、発酵工程、及び蒸留工程を含む製造方法が例示できる。以下、各工程について順次説明するが、使用する原料バイオマスの種類等に応じて、適宜、変更可能である。
Hereinafter, a method for producing an organic compound such as alcohol or organic acid from raw material biomass will be described.
As a method for producing alcohol or organic acid from raw material biomass, any known method can be used, and examples thereof include a production method including a saccharification step, a neutralization step, a fermentation step, and a distillation step. Hereinafter, although each process is demonstrated one by one, it can change suitably according to the kind etc. of raw material biomass to be used.

糖化工程は、セルロースやヘミセルロースなどの多糖類から、単糖〜2糖程度までの糖類に加水分解を行う工程をいう。加水分解法としては、従来公知の方法を用いることができるが、特に酸加水分解法が好ましく用いられる。酸加水分解法に用いる酸としては硫酸が好ましく、特に硫酸濃度0.5〜5質量%のものが好ましい。また、加水分解(糖化)の条件としては、130〜230℃で3〜30分反応させることが好ましく、より好ましくは、150〜210℃で3〜10 分である。
加水分解反応は、反応物を反応器から抽出し、温度を下げることにより停止される。反応停止後、単糖〜2糖程度までの糖類を含む反応溶液を水平ベルトフィルター、トレイフィルター等の濾過機で濾過洗浄することにより、糖類を含む溶液と糖化残渣とを分離する。
A saccharification process says the process of hydrolyzing from polysaccharides, such as a cellulose and a hemicellulose, to the saccharide | sugar to monosaccharide-about 2 saccharides. As a hydrolysis method, a conventionally known method can be used, but an acid hydrolysis method is particularly preferably used. As the acid used in the acid hydrolysis method, sulfuric acid is preferable, and one having a sulfuric acid concentration of 0.5 to 5% by mass is particularly preferable. Moreover, as conditions of hydrolysis (saccharification), it is preferable to make it react for 3 to 30 minutes at 130-230 degreeC, More preferably, it is 3 to 10 minutes at 150-210 degreeC.
The hydrolysis reaction is stopped by extracting the reactants from the reactor and lowering the temperature. After the reaction is stopped, the solution containing saccharides from monosaccharide to about 2 saccharides is filtered and washed with a filter such as a horizontal belt filter or tray filter to separate the saccharide-containing solution from the saccharification residue.

糖化工程の前処理として、糖化前処理を行うことが好ましい。糖化前処理は、糖化工程における加水分解反応を促進させるために実施されるものであって、物理的手法と化学的手法の2つに大別される。物理的手法としては、収集した原料バイオマスを粉砕、蒸煮、爆砕する方法が挙げられ、化学的手法としては、収集した原料バイオマスを酸、アルカリ処理する方法が挙げられる。このような糖化前処理を施すことによって、糖化工程における加水分解反応を促進することができ、加水分解に使用する試薬の量に対する加水分解率が向上し、糖類の収率が上昇する。また、同程度の加水分解率を得るために使用する試薬の量を削減することができる。   As pretreatment for the saccharification step, saccharification pretreatment is preferably performed. The saccharification pretreatment is performed in order to promote the hydrolysis reaction in the saccharification step, and is roughly divided into two methods, a physical method and a chemical method. Examples of the physical method include a method of pulverizing, steaming, and exploding the collected raw material biomass. Examples of the chemical method include a method of treating the collected raw material biomass with an acid and an alkali. By performing such saccharification pretreatment, the hydrolysis reaction in the saccharification step can be promoted, the hydrolysis rate with respect to the amount of the reagent used for hydrolysis is improved, and the yield of saccharides is increased. In addition, the amount of reagent used to obtain the same degree of hydrolysis can be reduced.

糖化前処理や糖化工程で酸やアルカリを使用した場合、糖類を含む溶液のpHを調整する(中和工程)。調整後のpHとしては、pH5〜9が好ましい。また、溶液のpH調整に使用する試薬としては、糖類を含む溶液のpHに応じて適宜選択され、例えば、中和前の溶液がアルカリ性の場合は、塩酸や硫酸などが挙げられ、中和前の溶液が酸性の場合は、水酸化ナトリウム、水酸化カルシウム、アンモニアなどが挙げられる。これらの中でも、水酸化カルシウムなどのカルシウムを含有した試薬を用いることが好ましい。カルシウムを含有した試薬を用いると、中和工程で発生する中和残渣中のカルシウム含有量が高くなり、このようなカルシウム含有中和残渣をバイオマス残渣として吸着剤の製造に使用することにより、例えば、水処理におけるリン吸着能の付与など、カルシウムを含有しないバイオマス残渣に比べ、高機能を発揮する吸着剤を得ることができる。なお、中和工程で発生する中和残渣は沈降分離等によって分離される。   When acid or alkali is used in the saccharification pretreatment or saccharification step, the pH of the solution containing the saccharide is adjusted (neutralization step). As pH after adjustment, pH 5-9 is preferable. The reagent used for adjusting the pH of the solution is appropriately selected according to the pH of the solution containing saccharides. For example, when the solution before neutralization is alkaline, hydrochloric acid or sulfuric acid may be used. When the solution is acidic, sodium hydroxide, calcium hydroxide, ammonia and the like can be mentioned. Among these, it is preferable to use a reagent containing calcium such as calcium hydroxide. When a reagent containing calcium is used, the calcium content in the neutralization residue generated in the neutralization process is increased, and by using such a calcium-containing neutralization residue as a biomass residue for the production of an adsorbent, for example, Compared with biomass residues not containing calcium, such as imparting phosphorus adsorption capacity in water treatment, an adsorbent exhibiting high functionality can be obtained. The neutralization residue generated in the neutralization step is separated by sedimentation separation or the like.

発酵工程は、単糖類から微生物による発酵によってエタノールや有機酸に変換する工程をいう。発酵に用いられる微生物としては、酵母や細菌が例として挙げられるが、遺伝子組み替え微生物も好ましく用いられる。遺伝子組み替え微生物とは、エタノール等への変換に必要な酵素遺伝子を有していない微生物に、遺伝子工学技術によりこれら遺伝子を導入し、エタノール等への発酵を可能にしたものである。この遺伝子組み替え微生物としては、例えばアルコール発酵性を有する遺伝子組み替え大腸菌等が挙げられる。   The fermentation process refers to a process of converting monosaccharides to ethanol or organic acids by fermentation with microorganisms. Examples of microorganisms used for fermentation include yeast and bacteria, but genetically modified microorganisms are also preferably used. Genetically modified microorganisms are those in which these genes are introduced into a microorganism that does not have an enzyme gene necessary for conversion to ethanol or the like by genetic engineering technology, and fermentation to ethanol or the like is made possible. Examples of the genetically modified microorganism include genetically modified Escherichia coli having alcohol fermentability.

発酵工程における発酵の条件としては、使用した微生物に応じて、適宜、決定される。
また、発酵工程で発生する発酵残渣は、遠心分離機等で分離される。
The conditions for fermentation in the fermentation process are appropriately determined according to the microorganism used.
Moreover, the fermentation residue generated in the fermentation process is separated by a centrifuge or the like.

発酵工程で得られる有機化合物は、炭素数2〜4のアルコール又は有機酸である。炭素数2〜4のアルコールとしては、エタノール、i−プロパノール、n−ブタノール等が挙げられ、エタノールが最も好ましい。有機酸としては、乳酸、ギ酸、酢酸、プロピオン酸、酪酸、クエン酸、リンゴ酸、フマール酸、コハク酸等が挙げられ、乳酸が最も好ましい。   The organic compound obtained in the fermentation process is an alcohol or organic acid having 2 to 4 carbon atoms. Examples of the alcohol having 2 to 4 carbon atoms include ethanol, i-propanol, and n-butanol, and ethanol is most preferable. Examples of the organic acid include lactic acid, formic acid, acetic acid, propionic acid, butyric acid, citric acid, malic acid, fumaric acid, succinic acid and the like, and lactic acid is most preferable.

蒸留工程は、発酵工程で得られる有機化合物を含む溶液中から、目的のアルコール又は有機酸を蒸留により分離する工程をいう。   A distillation process says the process of isolate | separating the target alcohol or organic acid by distillation from the solution containing the organic compound obtained by a fermentation process.

原料バイオマスのうち、高分子状の糖の部分のみがアルコール又は有機酸への変換に利用されており、そのため、バイオマス残渣は空隙構造になっており表面積が大きい。従って、このバイオマス残渣を乾燥又は炭化することにより、優れた吸着剤を製造することができる。
バイオマス残渣を乾燥する方法としては、吸着剤中の水分を10質量%以下とするような手段であれば特に制限はないが、例えば、キルン式乾燥機、スチームチューブ型乾燥機で乾燥させることにより、速やかに達成することができる。
Of the raw material biomass, only the polymer sugar portion is used for conversion to alcohol or organic acid, and therefore the biomass residue has a void structure and a large surface area. Therefore, an excellent adsorbent can be produced by drying or carbonizing the biomass residue.
The method for drying the biomass residue is not particularly limited as long as the moisture content in the adsorbent is 10% by mass or less. For example, by drying with a kiln type dryer or a steam tube type dryer. Can be achieved quickly.

また、バイオマス残渣を炭化する方法としては、貧酸素下条件で300〜1000℃で加熱する方法が例示できる。ここで貧酸素下とは、酸素濃度10%以下のことをいい、好ましくは5%以下、特に好ましくは3%以下である。また、加熱炉として、セメント製造等に使用されるロータリーキルンを用いることにより、一度に大量のバイオマス残渣を処理することが可能となる。
このようにして得られる炭化物は、多数の細孔を有するため吸着剤としての機能が十分に発揮される。
Moreover, as a method of carbonizing a biomass residue, the method of heating at 300-1000 degreeC on conditions under poor oxygen can be illustrated. Here, “under oxygen” means an oxygen concentration of 10% or less, preferably 5% or less, particularly preferably 3% or less. Moreover, it becomes possible to process a large amount of biomass residue at a time by using the rotary kiln used for cement manufacture etc. as a heating furnace.
Since the carbide thus obtained has a large number of pores, it functions sufficiently as an adsorbent.

バイオマス残渣を乾燥又は炭化した後に、更に賦活化処理を施すことが好ましい。賦活処理を施すことにより、活性炭として利用することもできる。   It is preferable to further activate the biomass residue after drying or carbonizing. By applying the activation treatment, it can be used as activated carbon.

このようにして得られる吸着剤は、例えば、排水からの難分解性物質、着色物質の除去に用いられるに用いられる。   The adsorbent obtained in this way is used, for example, for removing persistent substances and colored substances from waste water.

また、本発明により得られる吸着剤は、上述の原料バイオマスからアルコール又は有機酸などの有機化合物の製造方法、特に、中和工程において好適に用いられる。
以下、実施例を挙げて本発明をより詳しく説明する。
Moreover, the adsorbent obtained by this invention is used suitably in the manufacturing method of organic compounds, such as alcohol or an organic acid, especially a neutralization process from the above-mentioned raw material biomass.
Hereinafter, the present invention will be described in more detail with reference to examples.

吸着剤の製造
スギ木材チップを、2%希硫酸中で160℃で加水分解した。次いで、残存する固形分(スギ木材チップ固形分に対して70質量%)を加水分解機から取り出し、洗浄水中に硫酸の残存が確認できなくなるまで水洗浄を行った。さらに、真空濾過機を用いて洗浄を行いながら脱水を行った。脱水した残渣を、恒温機(エアバス)を用いて、105℃で一昼夜乾燥させた。乾燥後の残渣の含水率は3.5%であった。次いで、該乾燥物を、窒素置換した電気炉(酸素含有率 5.0%)を用い、800℃で2時間加熱処理して炭化物(吸着剤:スギ木材チップ固形分に対して40質量%)を得た。
Production of adsorbent Cedar wood chips were hydrolyzed at 160 ° C. in 2% dilute sulfuric acid. Subsequently, the remaining solid content (70% by mass with respect to the cedar wood chip solid content) was taken out from the hydrolyzer, and washed with water until no sulfuric acid remained in the washing water. Furthermore, dehydration was performed while washing using a vacuum filter. The dehydrated residue was dried at 105 ° C. for a whole day and night using a thermostatic device (air bath). The moisture content of the residue after drying was 3.5%. Next, the dried product was heat-treated at 800 ° C. for 2 hours using an electric furnace (oxygen content 5.0%) purged with nitrogen to obtain a carbide (adsorbent: 40% by mass based on solid content of cedar wood chips). Got.

バイオマスアルコール排水の脱色処理
木質バイオマスからアルコールを製造する際発生する排水を生物処理(メタン発酵、及び活性汚泥処理)すると、排水中の有機物は除去されるが、着色成分は残存する。この生物処理液を、実施例1で製造した吸着剤を充填した吸着塔に通液すると、着色成分が吸着され、処理液は無色透明になった。実験条件は以下の通りである。
カラム形状 直径30cm×高さ400cm(吸着剤充填高さ250cm)
吸着剤充填密度 200kg/m3
通液速度 0.18m/h
空筒速度 0.72h−1
通液温度 20℃
結果を表1に示す。
Decolorization treatment of biomass alcohol wastewater When wastewater generated when alcohol is produced from woody biomass is biologically treated (methane fermentation and activated sludge treatment), organic matter in the wastewater is removed, but coloring components remain. When this biological treatment liquid was passed through the adsorption tower filled with the adsorbent produced in Example 1, the colored components were adsorbed and the treatment liquid became colorless and transparent. The experimental conditions are as follows.
Column shape Diameter 30cm x Height 400cm (Adsorbent filling height 250cm)
Adsorbent packing density 200kg / m3
Flow rate 0.18m / h
Cylinder speed 0.72h-1
Fluid temperature 20 ℃
The results are shown in Table 1.

Figure 2011045882
Figure 2011045882

発酵効率の検討
木質バイオマスからアルコール又は有機酸を製造するプロセスにおいて、発酵原液を至適pH調整する中和工程がある。この工程では、pH調整とともに発酵阻害物質を沈殿除去する。実施例1で調整した吸着剤を発酵前調整工程において発酵原液と混合することにより、液中に溶解している発酵阻害物質が吸着され、発酵効率が改善された。実験条件は以下の通りである。
吸着
吸着剤添加量 発酵液に対して1重量%
吸着時間 10分間
発酵
発酵温度 30℃
発酵時間 48時間
使用菌体 サッカロマイセス・セレビシエ(Saccharomyces cerevisiae)
種菌添加率 培養液を発酵原液に対して5重量%
栄養塩と添加率 コーンスティープリカーを発酵原液に対して0.5重量%
結果を表2に示す。
Examination of fermentation efficiency In the process of producing alcohol or organic acid from woody biomass, there is a neutralization step for adjusting the pH of the fermentation stock solution to an optimum pH. In this step, the fermentation inhibitor is precipitated and removed together with pH adjustment. By mixing the adsorbent prepared in Example 1 with the fermentation stock solution in the pre-fermentation adjustment step, the fermentation inhibitor dissolved in the solution was adsorbed, and the fermentation efficiency was improved. The experimental conditions are as follows.
Adsorption Adsorbent addition amount 1% by weight of fermentation broth
Adsorption time 10 minutes Fermentation Fermentation temperature 30 ℃
Fermentation time 48 hours Bacteria used Saccharomyces cerevisiae
Inoculum addition rate 5% by weight of culture broth based on fermentation stock solution
Nutrient salt and addition rate 0.5% by weight of corn steep liquor
The results are shown in Table 2.

Figure 2011045882
Figure 2011045882

本発明の方法により、エタノールを高効率で製造できることは明らかである。   It is clear that ethanol can be produced with high efficiency by the method of the present invention.

本発明は、アルコールや有機酸の製造分野で利用が可能である。   The present invention can be used in the field of producing alcohols and organic acids.

Claims (2)

原料バイオマスからアルコール又は有機酸を製造する過程において発生するバイオマス残渣を130〜230℃で3〜30分間酸加水分解し、得られた糖化残渣を乾燥又は炭化することを特徴とする吸着剤の製造方法。   Production of adsorbent characterized by acid hydrolysis of biomass residue generated in the process of producing alcohol or organic acid from raw material biomass at 130-230 ° C. for 3-30 minutes, and drying or carbonizing the obtained saccharification residue Method. 原料バイオマスからアルコール又は有機酸を製造する過程において発生するバイオマス残渣を130〜230℃で3〜30分間酸加水分解し、得られた糖化残渣を乾燥又は炭化することにより得られる吸着剤を利用することを特徴とするアルコール又は有機酸の製造方法。 Utilize an adsorbent obtained by acid hydrolysis of biomass residue generated in the process of producing alcohol or organic acid from raw material biomass at 130-230 ° C. for 3-30 minutes, and drying or carbonizing the obtained saccharification residue A method for producing an alcohol or organic acid, characterized in that:
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