WO2021153585A1 - Production method for sugar solution - Google Patents

Production method for sugar solution Download PDF

Info

Publication number
WO2021153585A1
WO2021153585A1 PCT/JP2021/002757 JP2021002757W WO2021153585A1 WO 2021153585 A1 WO2021153585 A1 WO 2021153585A1 JP 2021002757 W JP2021002757 W JP 2021002757W WO 2021153585 A1 WO2021153585 A1 WO 2021153585A1
Authority
WO
WIPO (PCT)
Prior art keywords
biomass
cellulose
sugar solution
less
crushed
Prior art date
Application number
PCT/JP2021/002757
Other languages
French (fr)
Japanese (ja)
Inventor
舩田茂行
日笠雅史
山田勝成
Original Assignee
東レ株式会社
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 東レ株式会社 filed Critical 東レ株式会社
Priority to CN202180011274.9A priority Critical patent/CN115023507A/en
Priority to JP2021509936A priority patent/JPWO2021153585A1/ja
Publication of WO2021153585A1 publication Critical patent/WO2021153585A1/en

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12PFERMENTATION OR ENZYME-USING PROCESSES TO SYNTHESISE A DESIRED CHEMICAL COMPOUND OR COMPOSITION OR TO SEPARATE OPTICAL ISOMERS FROM A RACEMIC MIXTURE
    • C12P19/00Preparation of compounds containing saccharide radicals
    • C12P19/14Preparation of compounds containing saccharide radicals produced by the action of a carbohydrase (EC 3.2.x), e.g. by alpha-amylase, e.g. by cellulase, hemicellulase
    • CCHEMISTRY; METALLURGY
    • C13SUGAR INDUSTRY
    • C13KSACCHARIDES OBTAINED FROM NATURAL SOURCES OR BY HYDROLYSIS OF NATURALLY OCCURRING DISACCHARIDES, OLIGOSACCHARIDES OR POLYSACCHARIDES
    • C13K1/00Glucose; Glucose-containing syrups
    • C13K1/02Glucose; Glucose-containing syrups obtained by saccharification of cellulosic materials
    • 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel

Definitions

  • the present invention relates to a method for producing a sugar solution that can be used as a fermentation raw material from cellulose-containing biomass.
  • the fermentation production process for chemicals made from sugar is used for the production of various industrial raw materials.
  • sugars derived from edible raw materials such as sugar beet, starch, and sugar beet are industrially used as sugars as raw materials for fermentation.
  • renewable non-edible resources that is, the process of more efficiently producing sugar solution from cellulose-containing biomass, or the obtained sugar solution is efficiently converted into industrial raw material as a fermentation raw material. The construction of the process to do so is an issue for the future.
  • the sugar in the cellulose-containing biomass raw material is embedded in the cell wall that has a complicated structure. Therefore, in order for the enzyme to act efficiently, it is preferable to apply an alkali treatment to the biomass raw material prior to the enzymatic hydrolysis.
  • an alkaline treatment is performed in which a cellulose-containing substance and an alkaline aqueous solution are brought into contact with each other, and a specific pretreatment that repeatedly uses an alkaline filtrate is applied to the cellulose-containing biomass to obtain a sugar solution.
  • a specific pretreatment that repeatedly uses an alkaline filtrate is applied to the cellulose-containing biomass to obtain a sugar solution.
  • the cellulose-containing plant biomass raw material is treated with a treatment agent containing ammonia and immersed in water at 40 to 100 ° C. to elute the polysaccharide in water to obtain a raw material for enzymatic saccharification to be used in the enzymatic saccharification step.
  • a treatment agent containing ammonia containing ammonia and immersed in water at 40 to 100 ° C. to elute the polysaccharide in water to obtain a raw material for enzymatic saccharification to be used in the enzymatic saccharification step.
  • An object of the present invention is to provide a method for reducing fermentation inhibitors such as organic acids and aromatic compounds generated by alkaline treatment of cellulose-containing biomass when producing a sugar solution from cellulose-containing biomass.
  • the present inventor has now crushed cellulose-containing biomass to a specific degree of crushing, brought it into contact with an alkaline aqueous medium to add water, solid-liquid separated the pretreated biomass to which water was added, and hydrolyzed the pretreated biomass. Then, it was found that the sugar solution in which the fermentation inhibitor was reduced could be efficiently obtained.
  • Step (1) A method for producing a sugar solution using cellulose-containing biomass as a raw material.
  • Step (2) A step of contacting the crushed biomass obtained in the step (1) with an alkaline aqueous medium to obtain a pretreated biomass.
  • Step (3) Water is added to the pretreated biomass obtained in step (2) and solid-liquid separation is performed to obtain a cellulose-containing solid content, and step (4): cellulose obtained in step (3).
  • the process of hydrolyzing the contained solids to obtain a sugar solution Including methods.
  • [2] The method for producing a sugar solution according to [1], wherein the step (2) is a step of passing an alkaline medium through the crushed biomass obtained in the step (1) to obtain a pretreated biomass.
  • the step (2) is a step of supplying the crushed biomass and the alkaline medium obtained in the step (1) to a filter and passing the crushed biomass and the alkaline medium through the filter.
  • [4] The method for producing a sugar solution according to any one of [1] to [3], wherein the alkaline aqueous medium of the step (2) is an aqueous medium containing sodium hydroxide and / or potassium hydroxide.
  • Step (5) The sugar solution obtained in step (4) is filtered through a nanofiltration membrane or a reverse osmosis membrane, the sugar solution is recovered as a non-permeate solution, and the permeate solution is used in step (3).
  • the process of reusing water to be added to pretreated biomass The method for producing a sugar solution according to any one of [1] to [6], further comprising.
  • the present invention is a method for producing a sugar solution using cellulose-containing biomass as a raw material.
  • Step (1) The cellulose-containing biomass is crushed so that the ratio of non-passing through a sieve having an opening of 1 mm is 50% or less by dry weight.
  • An example of the process flow diagram of the present invention is shown in FIG. 1, but the flow of the present invention is not limited thereto.
  • Cellulose-containing biomass refers to biological resources containing at least cellulose.
  • cellulose-containing biomass are herbaceous biomass such as bagasse, switchgrass, napiergrass, erianthus, corn stove, straw (rice straw, straw), chaff, or trees, wood chips, waste building materials.
  • Woody biomass such as, aquatic environment-derived biomass such as algae and seaweed, corn husk, wheat husk, soy husk, rice husk, grain husk biomass such as residue after starch extraction from cassabaimo (cassaba lees), etc. Can be mentioned.
  • Herbaceous biomass such as bagasse, rice straw, and oil palm empty fruit bunch is preferable.
  • the water content of the cellulose-containing biomass is not particularly limited, but the preferable range is, for example, about 3% or more, about 3% or more and about 60% or less, about 5% or more, about 5% or more and about 60% or less, about 5% or more. It is about 55% or less, about 5% or more and about 50% or less.
  • the water content of the cellulose-containing biomass is measured by the method detailed in the examples.
  • the cellulose-containing biomass is crushed to a specific degree of crushing to obtain crushed biomass.
  • the pulverization means is not particularly limited, and the pulverization can be performed by using a machine commonly used for coarse pulverization of various materials such as a ball mill, a vibration mill, a cutter mill, a hammer mill, a willley mill, and a jet mill.
  • This mechanical pulverization may be either dry or wet, but is preferably dry pulverization.
  • the degree of crushing of the crushed biomass obtained in the step (1) is such that the weight ratio (dry weight%) that does not pass through a sieve having a mesh size of 1 mm is crushed until the dry weight becomes about 50% or less, preferably about 40% or more.
  • the solid-liquid separation is unexpectedly compared with the case where such pulverization is not performed.
  • the subsequent water content is reduced, which can reduce the fermentation inhibitors derived from the pretreated biomass brought in during the subsequent hydrolysis.
  • the degree of crushing is evaluated by drying the crushed biomass to a water content of 20% or less, and then sieving the crushed biomass with an opening of 1 mm. In the present specification, if the weight ratio (dry weight%) of the crushed biomass that does not pass through the sieve having an opening of 1 mm is low, it may be expressed that the degree of crushing is high.
  • the sieving method and conditions follow ISO 2591-1.
  • step (2) the crushed biomass obtained in step (1) is brought into contact with an alkaline aqueous medium to obtain pretreated biomass.
  • the pretreated biomass referred to here refers to those containing the solid content of the cellulose-containing biomass that has been subjected to alkali treatment so that the cellulose-containing biomass is efficiently hydrolyzed in the subsequent step (4).
  • the method for bringing the crushed biomass obtained in the step (1) into contact with the alkaline aqueous medium is not particularly limited as long as it is an alkaline treatment method for cellulose-containing biomass well known to those skilled in the art, but WO2017 / 170552 is preferable.
  • the alkaline treatment method described is adopted. This method is a method of passing an alkaline aqueous medium through a cellulose-containing biomass to obtain a pretreated biomass and an alkaline treated solution rich in coumaric acid or ferulic acid.
  • the alkaline aqueous medium is passed through the pulverized biomass. You just have to make it liquid.
  • the crushed biomass and the alkaline aqueous medium are supplied to a filter according to the method described in WO2017 / 170552, and the crushed biomass and the alkaline medium are supplied using the filter.
  • a method of passing a liquid can be mentioned.
  • the crushed biomass and the alkaline aqueous medium may be mixed in advance and supplied to the filter, or both may be supplied to the filter separately, but the alkaline aqueous medium is placed on the crushed biomass previously supplied into the filter. It is preferable to add it.
  • the pH of the alkaline filtrate may be in the same range as that of the alkaline aqueous medium, and the preferable pH range is, for example, 7 or more and 12 or less, 8 or more and 12 or less, and the more preferable pH range is 9 or more and 12 or less. A more preferable pH range is 10 or more and 12 or less.
  • the pH of the alkaline filtrate tends to decrease as the reaction progresses. This is because the soluble lignin component acts as a neutralizing agent as the alkaline reaction progresses, and the progress of the reaction can be measured by the degree of this decrease.
  • the pH range of the pulverized biomass after contacting the pulverized biomass with an alkaline aqueous medium can be appropriately adjusted depending on the initial alkali concentration and the like, but is preferably 7 or more and 12.5 or less. , 8 or more and 12.5 or less, a more preferable pH range of 8 or more and 12 or less, and a more preferable pH range of 8 or more and 11 or less. Measuring whether the pH of the alkaline filtrate is in the above range is an effective means for assessing whether the reaction has proceeded to a level sufficient to carry out the subsequent hydrolysis step.
  • the alkaline aqueous medium in contact with the crushed biomass substantially maintains the temperature.
  • the filter is provided with a filter section that allows the ground biomass to pass an alkaline aqueous medium, it is preferable that the alkaline filtrate filtered from the filter section also substantially retains the temperature. Maintaining the temperature of the alkaline aqueous medium and the alkaline filtrate can be carried out by installing a known heat insulating device or heating device in the filter.
  • the filtrate that comes out of the filtration section after being brought into contact with the alkaline aqueous medium may be circulated and brought into contact with the pulverized biomass again, and the number of repetitions is not particularly limited, but the suitable number of times is, for example, at least two times or more. 2 times or more and 20000 or less, 2 times or more and 10000 or less, 2 times or more and 1000 or less, 3 times or more and 10000 or less, 3 times or more and 1000 or less, or 3 times or more and 100 or less.
  • alkaline aqueous medium examples include an alkaline aqueous solution such as an aqueous medium containing ammonia, aqueous ammonia, and a hydroxide, preferably an aqueous medium containing sodium hydroxide and / or potassium hydroxide, and more preferably sodium hydroxide. It is an aqueous medium containing, and more preferably an aqueous solution of sodium hydroxide and / or potassium hydroxide.
  • the alkali concentration of the alkaline aqueous medium can be calculated from the content of alkaline substances (alkaline solids such as hydroxides) in the alkali-containing medium.
  • the upper limit of the alkali concentration of the alkaline aqueous medium is not particularly limited, but is preferably 3, 2, 1.5, 1, 0.7, 0.6, 0.5, 0.4, 0.3 or 0. It is about 2% by weight, and the lower limit is preferably about 0.05, 0.1, 0.2, 0.3, 0.4 or 0.5% by weight.
  • the preferred range of alkali concentration is, for example, about 0.05% by weight or more and about 0.3% by weight or less, about 0.1% by weight or more and about 3% by weight or less, and about 0.1% by weight or more and about 2% by weight.
  • the more preferable range is about 0.1% by weight or more and about 2% by weight, about 0.25% by weight or more and about 1.5% by weight or less, about 0.25% by weight or more and about 1.5% by weight or less, further preferable.
  • the range is about 0.25% by weight or more and about 1.0% by weight or less.
  • the lower limit of the pH of the alkaline aqueous medium is not particularly limited as long as it is alkaline, but is 7 or more, preferably pH 8 or more, more preferably pH 9 or more, and further preferably pH 10 or more.
  • the upper limit of pH is not particularly limited as long as it is less than pH 14, but can be set to pH 13.5 or less from the viewpoint of reducing the amount of alkali used.
  • the preferred pH range is, for example, 7 or more and 13.5 or less, 8 or more and 13.5 or less, the more preferable pH range is 9 or more and 13.5 or less, and the more preferable pH range is 10 or more and 13.5 or less. The range.
  • the upper limit of the temperature of the alkaline aqueous medium is not particularly limited, but is preferably about 110, 100, 95, 90, 80, 75, 70 ° C., and the lower limit is preferably 35, 40, 50, 60, 65. It is about ° C.
  • the temperature range of the alkaline aqueous medium is, for example, about 35 ° C. or higher and 100 ° C. or lower, 40 ° C. or higher and 100 ° C. or lower, 50 ° C. or higher and 100 ° C. or lower, 60 ° C. or higher and 100 ° C. or lower. 65 ° C. or higher and 100 ° C. or lower, 80 ° C. or higher and 100 ° C.
  • temperature ranges are 60 ° C. or higher and 100 ° C. or lower, 65 ° C. or higher and 100 ° C. or lower, 80 ° C. or higher and 100 ° C.
  • the temperature range is 65 ° C. or higher and 100 ° C. or lower, or 80 ° C. or higher and 100 ° C. or lower.
  • the weight ratio between the alkaline aqueous medium and the ground biomass is not particularly limited, but the preferred ranges are, for example, 100: 1 to 2: 1, 90: 1 to 3: 1, 50: 1 to 5 :. 1, 30: 1 to 5: 1, 25: 1 to 7: 1, 25: 1 to 5: 1, 20: 1 to 5: 1.
  • the ratio of the alkali-containing aqueous medium to the crushed biomass can also be set using the amount of alkali used (also referred to as the amount of alkali reaction) calculated by the method for calculating the amount of alkali reaction described in Examples as an index. ..
  • the preferred range of alkali usage is, for example, about 20 mg / g or more and about 300 mg / g or less, about 30 mg / g or more and about 200 mg / g or less, about 40 mg / g or more and about 200 mg / g or less, and about 45 mg / g or more and 180 mg / g.
  • the time for contacting the pulverized biomass with the alkaline aqueous medium is not particularly limited, but the contact time is, for example, about 20 minutes or more and about 72 hours or less, about 20 minutes or more and about 48 hours or less, about 20 minutes or more and about 24 hours or less. About 30 minutes or more and about 48 hours or less, about 30 minutes or more and about 24 hours or less, about 30 minutes or more and about 12 hours or less, about 30 minutes or more and about 6 hours or less, or about 30 minutes or more and about 3 hours or less.
  • the pretreated biomass obtained by contacting the crushed biomass with an alkaline aqueous medium it is preferable that the pretreated biomass is separated and recovered by a method well known to those skilled in the art and supplied to the subsequent step (3).
  • a filter is used to bring the crushed biomass into contact with an alkaline aqueous medium, the solid content remaining in the filter can be recovered as pretreated biomass.
  • the water content of the pretreated biomass supplied to the step (3) is not particularly limited, but the preferred ranges are, for example, about 50% by weight or more and about 99% by weight or less, about 60% by weight or more and about 99% by weight or less, and 70% by weight. About 99% by weight or less, about 80% by weight or more and about 99% by weight or less, or about 80% by weight or more and about 95% by weight or less, more preferably about 80% by weight or more and about 99% by weight or less, still more preferable. Is about 80% by weight or more and about 95% by weight or less.
  • the water content of the pretreated biomass is measured by the method detailed in the Examples.
  • step (3) the obtained pretreated biomass is solid-liquid separated by adding water for the purpose of separating fermentation inhibitors from the pretreated biomass.
  • the fermentation inhibitor which is considered to be derived from lignin in the cellulose-containing biomass, which is generated by the alkaline treatment of the cellulose-containing biomass contained in the pretreated biomass.
  • Specific examples of fermentation inhibitors include organic acids such as formic acid, acetic acid, citric acid, and lactic acid, and aromatic compounds such as ferulic acid, kumalic acid, vanillin, vanillic acid, acetovanillin, 4-hydroxybenzoic acid, silingaic acid, and gallic acid. , HMF, furfural and other furan compounds.
  • the amount of water added to the pretreated biomass is not particularly limited by the weight ratio of the pretreated biomass (dry weight) and the water to be added, but the preferable range is, for example, 1: 1 to 1: 100, 1: 1. ⁇ 1: 50, 1: 1 to 1:30, 1: 1 to 1:20, 1: 1 to 1: 10, 1: 1 to 1: 5, 1: 1 to 1: 3.
  • the pH of the water added to the pretreated biomass is not particularly limited, but the preferred range is, for example, 3 to 9, 3 to 8, 3 to 7, 4 to 9, 4 to 8, 4 to 7, 5 to 9. 5 to 8, 5 to 7.
  • the temperature of the water added to the pretreated biomass is not particularly limited, but the preferred range is, for example, 10 to 60 ° C., 10 to 50 ° C., 10 to 40 ° C., 20 to 60 ° C., 20 to 50 ° C., 20 to 20 to. 40 ° C., 30-60 ° C., 30-50 ° C., 30-40 ° C.
  • the pretreated biomass and the water to be added may be mixed in the reaction tank, or the reaction tank may have a stirrer.
  • the shape of the reaction vessel does not matter as long as the pretreated biomass and the water to be added can come into contact with each other.
  • the pretreated biomass can be transported to the reaction tank by a conveyor or free fall. Further, if the pretreated biomass and water can come into contact with each other, water can be added during transportation such as a conveyor even if it is not in a reaction tank.
  • the device used for solid-liquid separation centrifugation, squeezing, etc. can be applied, and squeezing is preferable.
  • the pressing include a screw press, a belt press, a filter press and the like, but a screw press is preferable.
  • the water content of the cellulose-containing solid content after solid-liquid separation is preferably about 50% by weight or more and about 85% by weight or less, more preferably 50% by weight, from the viewpoint of reducing fermentation inhibitors derived from the pretreated biomass. It is more than about 70% by weight and less than about 70% by weight.
  • the water content of the cellulose-containing solid content is measured by the method for measuring the water content described in Examples.
  • the content of the alkaline aqueous medium in the cellulose-containing solid content is preferably about 5 mg / g-biomass or more and 40 mg / g-biomass or less, and more preferably about 7 mg / g-biomass or more and 35 mg / g-biomass or less. It is more preferably about 10 mg / g-biomass or more and about 30 mg / g-biomass or less.
  • step (4) the cellulose-containing solid content is hydrolyzed to obtain a sugar solution.
  • known hydrolysis methods such as acid hydrolysis, alkaline hydrolysis, and enzyme hydrolysis can be applied, but it is preferable to hydrolyze the cell roll-containing solid content in an aqueous medium with an enzyme.
  • the sugar solution obtained by such an enzymatic hydrolysis step can be obtained as an aqueous solution containing oligosaccharides and / or monosaccharides such as glucose, xylose, arabinose, galactose, xylobiose and cellobiose.
  • the enzyme used is not particularly limited as long as it is cellulose or hemicellulose hydrolase, but for example, a relatively inexpensive commercially available one may be used, and the cellulase enzyme agent is "acremonium cellulase", which is an enzyme derived from the genus Acremonium. (Meiji Seika Pharma Co., Ltd.), "Axel Race Duet” (Danisco Japan Co., Ltd.), an enzyme derived from the genus Trichoderma, "Cellulose” 1.5L (Novozyme Co., Ltd.) and the like can be used.
  • As the hemicellulase enzyme agent "Optimash BG" (Genencore Co., Ltd.) or the like can be used.
  • the origin of the enzyme is not particularly limited, but more preferably the enzyme is derived from filamentous fungi.
  • Enzymes derived from filamentous fungi are rich in polysaccharide-degrading enzymes derived from cellulose-containing biomass such as cellulase, hemicellulase, and ⁇ -glucosidase, and are advantageous for hydrolyzing biomass after alkali treatment. Is.
  • the enzyme used can be used alone or in combination in consideration of the properties of the enzyme preparation, the composition of the desired product, and the like.
  • the amount of suitable enzyme is also not particularly limited and can be appropriately determined.
  • the amount of such an enzyme can be, for example, 0.01 g or more and 1 g or less per 1 g of the raw material substrate, preferably 0.001 g or more and 0.1 g or less.
  • the temperature, pH and time of enzyme hydrolysis can be appropriately set depending on the properties and combinations of enzymes. As a preferable range, for example, the temperature is 30 or more and 60 ° C. or less, more preferably 35 ° C. or more and 50 ° C. or less.
  • the pH is, for example, pH 3 or more and 8 or less, preferably pH 4 or more and 7 or less.
  • the reaction time is, for example, 1 hour or more and 48 hours or less, preferably 6 hours or more and 24 hours or less.
  • the concentration of glucose, xylose or xylobiose in the sugar solution obtained in step (4) is not particularly limited and can be appropriately set by adjusting the reaction conditions of each step.
  • Suitable glucose concentrations include, for example, about 5 g / L or more and 1000 g / L or less, 5 g / L or more and 700 g / L or less, 5 g / L or more and 550 g / L or less, or 10 g / L or more and 550 g / L. It is below the degree.
  • the suitable xylose concentration is, for example, about 1 g / L or more and 100 g / L, 1 g / L or more and 50 g / L or less, or 1 g / L or more and about 10 g / L or less.
  • a suitable xylobiose concentration for example, about 1 g / L or more and 100 g / L, 1 g / L or more and 50 g / L or less, 1 g / L or more and 20 g / L or less, or 1 g / L or more and 15 g / L or more. It is below the degree.
  • the sugar solution produced in step (4) can be used as it is for various industrial applications, but may be post-treated if desired, and specifically, it is subjected to treatments such as membrane treatment, centrifugation, concentration, and drying. You may.
  • Preferable membrane treatment of the sugar solution produced in step (4) includes nanofiltration membrane treatment or reverse osmosis membrane treatment.
  • the nanofiltration membrane is also called a nanofilter (nanofiltration membrane, NF membrane), and is a membrane generally defined as "a membrane that allows monovalent ions to permeate and blocks divalent ions”. .. It is a membrane that is considered to have microvoids of several nanometers, and is mainly used to block fine particles, molecules, ions, salts, etc. in water.
  • a reverse osmosis membrane is also called an RO membrane, and is a membrane generally defined as "a membrane having a desalination function including monovalent ions", and is an ultra-small membrane of several angstroms to several nanometers.
  • the nanofiltration membrane or reverse osmosis membrane treatment refers to the sugar solution produced in step (4) being filtered through the nanofiltration membrane or reverse osmosis membrane treatment, and dissolved sugars, particularly monosaccharides such as glucose and xylose. , Xylobiose, cellobiose, and other oligosaccharides are blocked or filtered to the non-permeable side of the membrane, and the fermentation inhibitor remaining in the sugar solution is permeated as a permeate, and is carried out by the method described in WO2010 / 067785. can.
  • the sugar solution recovered from the non-permeable side of the nanofiltration membrane or reverse osmosis membrane has a further reduction in fermentation inhibitors compared to before the membrane treatment, and the fermentation performance should be improved compared to before the main membrane treatment.
  • the permeated water recovered from the permeation side of the nanofiltration membrane or the reverse osmosis membrane can be used as water to be added to the pretreated biomass in the step (3) (step (5)). By this step, the amount of water used in all the steps can be reduced, and the unexpected effect that the aromatic compound which is a fermentation inhibitor can be further removed by the solid-liquid separation in the step (3) can be obtained.
  • JIS Japanese Industrial Standards
  • Table 1 shows the water content of various cellulose-containing biomass measured by this method. Bagasse, rice straw, and oil palm empty fruit bunches are classified as herbaceous biomass.
  • Alkaline reaction amount y ⁇ b ⁇ 1000 / ⁇ (100-x) ⁇ a ⁇ ... (Equation 1).
  • Comparative Reference Example 1 Relationship between the degree of bagasse crushing during hydrothermal treatment and the moisture content of cellulose-containing solids
  • step (1) use a cutter mill (Varionics BRX-400, manufactured by Nara Kikai Seisakusho Co., Ltd.) for bagasse with a moisture content of 50%. Used and crushed bagasse.
  • the screen hole diameter of the cutter mill was set to 30 mm, and crushing was performed while supplying at a rotation speed of 600 rpm and a supply speed of 1000 kg / hr.
  • the crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with a 1 mm opening under the conditions of ISO 2591-1, and the weight ratio that did not pass was measured and found to be 45%.
  • step (2) bagasse after crushing (moisture content 50%) was hydrothermally treated at 180 ° C. at high pressure for 10 minutes at a solid content of 5%.
  • the obtained pretreated bagasse was filtered through a stainless steel colander (opening ratio: 30%) having an opening of 3 mm, and the solid content (pretreated biomass) remaining on the upper surface of the colander was manually pressed against the colander surface and squeezed.
  • the water content of the obtained pretreated biomass was 90%.
  • step (3) water is added to the pretreated biomass in an amount 1.6 times the solid content (dry weight), and the pretreated biomass to which water is added is applied to a small screw press for a laboratory (HX100 manufactured by Toguni Kogyo Co., Ltd., frequency 10 Hz). ) was separated into solid and liquid. When the water content of the cellulose-containing solid content after solid-liquid separation was measured, the water content was 75%. The results are shown in Table 2.
  • Comparative Reference Example 2 Relationship between the degree of bagasse pulverization during hydrothermal treatment and the moisture content of cellulose-containing solids The pulverization was carried out under the same conditions as in Comparative Example 1 except that the screen hole diameter of the cutter mill was 40 mm. Further, the crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with a mesh opening of 1 mm under the condition of ISO 2591-1, and the weight ratio of not passing was measured and found to be 50%. The water content of the cellulose-containing solid content after solid-liquid separation was 73%. The results are shown in Table 2.
  • Comparative Reference Example 3 Relationship between the degree of bagasse pulverization during hydrothermal treatment and the moisture content of cellulose-containing solids
  • the pulverization conditions were the same as those of Comparative Example 1 except that the screen hole diameter of the cutter mill was 50 mm. Further, the crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with an opening of 1 mm under the condition of ISO 2591-1, and the weight ratio of not passing was measured and found to be 55%. The water content of the cellulose-containing solid content after solid-liquid separation was 70%. The results are shown in Table 2.
  • Comparative Reference Example 4 Relationship between the degree of bagasse pulverization during alkaline treatment and the moisture content of cellulose-containing solids
  • step (1) pulverization was performed under the same pulverization conditions as in Comparative Example 3 except that the screen pore diameter of the cutter mill was 50 mm. Was done. The crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with a 1 mm opening under the conditions of ISO 2591-1, and the weight ratio that did not pass was measured and found to be 55%.
  • step (2) 5.0 kg of the obtained crushed bagus (water content 50%) was put into a multifunctional extractor (manufactured by Izumi Food Machinery Co., Ltd.), and a predetermined concentration was obtained from a spray ball at the top of the tank of the multifunctional extractor.
  • Add 45 kg of the sodium hydroxide aqueous solution (initial temperature: 90 ° C., pH is about 13), and refill the liquid (alkaline filtrate) obtained by self-weight filtration from the filtration net provided in the tank from the spray ball. was repeated.
  • the reaction was carried out for a predetermined time while monitoring the temperature by providing a mechanism for heating between the filtration net and the upper spray ball.
  • the alkaline filtrate was adjusted so as not to drop from 90 ° C. Further, the stirring blade attached to the multifunctional extractor was not used, the bagasse and the cellulose-containing solids were placed on the filtration net, and the shape was adjusted by the stirring blade or the like, or the operation of making a slurry was not performed.
  • the alkaline filtrate was continuously circulated for a predetermined reaction time.
  • the obtained sample was further filtered through a stainless steel colander with a mesh opening of 3 mm (opening ratio: 30%), and the solid content (pretreated biomass) remaining on the upper surface of the colander was manually pressed against the colander surface and squeezed.
  • the water content of the obtained pretreated biomass was 90%.
  • step (3) water was added to the pretreated biomass in an amount 1.6 times the solid content (dry weight), and the pretreated biomass was solid-liquid separated by a small laboratory screw press. When the water content of the cellulose-containing solid content after solid-liquid separation was measured, the water content was 75%. The results are shown in Table 2.
  • Reference Example 1 Relationship between the degree of bagasse pulverization during alkaline treatment and the water content of cellulose-containing solids
  • the pulverization conditions were the same as those of Comparative Reference Example 4 except that the screen hole diameter of the cutter mill was 40 mm. Further, the crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with a mesh opening of 1 mm under the condition of ISO 2591-1, and the weight ratio of not passing was measured and found to be 50%. The water content of the cellulose-containing solid content after solid-liquid separation was 64%. The results are shown in Table 2.
  • Reference Example 2 Relationship between the degree of bagasse pulverization during alkaline treatment and the water content of cellulose-containing solids
  • the pulverization conditions were the same as those of Comparative Reference Example 4 except that the screen hole diameter of the cutter mill was 30 mm. Further, the crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with an opening of 1 mm under the condition of ISO 2591-1, and the weight ratio was measured and found to be 45%. The water content of the cellulose-containing solid content after solid-liquid separation was 60%. The results are shown in Table 2.
  • the pretreatment is an alkaline treatment
  • the proportion of the crushed biomass that does not pass through the sieve with a mesh size of 1 mm decreases (the degree of crushing increases)
  • the moisture content (%) of the cellulose-containing solid content after liquid separation is reduced, and the degree of crushing of the crushed biomass is increased to reduce the fermentation inhibitor derived from the pretreatment that is mixed in when the sugar solution is produced by the subsequent hydrolysis. The possibility of being able to do it was found.
  • Comparative Example 1 Production example of sugar solution from bagasse (steps (1) and (3) not performed) The same pulverization conditions and pretreatment conditions as in Comparative Reference Example 4 were carried out to obtain pretreated biomass. The obtained pretreated biomass was not subjected to the addition of water and solid-liquid separation in step (3), and was pure so that the solid content concentration of the dry base was 5% and the pH was 5.0 in step (4). Water and 35% hydrochloric acid were added to prepare a slurry liquid containing a cellulose-containing solid content.
  • Comparative Example 2 Production Example of Sugar Solution from Bagasse (Step (1) Not Implemented) The same pulverization conditions, pretreatment conditions, and water addition / solid-liquid separation conditions as in Comparative Reference Example 4 were carried out. Using the cellulose-containing solid content after solid-liquid separation, the same hydrolysis operation as in Comparative Example 1 was carried out as step (4). Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the obtained reaction solution and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
  • Comparative Example 3 Production Example of Sugar Solution from Bagasse (Step (3) Not Implemented) The crushing conditions were such that the screen hole diameter of the cutter mill was 40 mm, and the same operation as in Comparative Reference Example 4 was carried out except that solid-liquid separation was performed without adding water to the pretreated biomass. Using the obtained cellulose-containing solid content after solid-liquid separation, the same hydrolysis operation as in Comparative Example 1 was carried out as step (4). Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the obtained reaction solution and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
  • Example 1 Production example of sugar solution from bagasse (implementation of steps (1) to (4)) Using the cellulose-containing solid content after solid-liquid separation obtained in Reference Example 1, the same hydrolysis operation as in Comparative Example 1 was carried out as step (4).
  • Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the obtained reaction solution and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
  • Example 2 Production example of sugar solution from bagasse (implementation of steps (1) to (4)) Using the cellulose-containing solid content after solid-liquid separation obtained in Reference Example 2, the same hydrolysis operation as in Comparative Example 1 was carried out as step (4).
  • Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the obtained reaction solution and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
  • Example 3 Production example of sugar solution from bagasse (implementation of steps (1) to (5))
  • the sugar solution after hydrolysis in the step (4) obtained in Example 1 is solid-liquid separated by centrifugation (manufactured by Saito Centrifuge Industry Co., Ltd., 2,000 rpm), and then microfiltered membrane (manufactured by Millipore). After filtration using a pore diameter of 0.05 ⁇ m PVDF membrane), the sugar solution is recovered as a concentrated solution through a reverse osmosis membrane (cross-linked total aromatic polyamide reverse osmosis membrane UTC80 manufactured by Toray Co., Ltd.), and raw water is collected. Water was recovered as a permeate so that it was concentrated to a quarter.
  • a reverse osmosis membrane cross-linked total aromatic polyamide reverse osmosis membrane UTC80 manufactured by Toray Co., Ltd.
  • Steps (1) to (4) were carried out again under the same conditions as in Example 1, and water recovered in step (3) was added as the permeate of the reverse osmosis membrane (step (step (step)). 5)).
  • Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the sugar solution obtained in step (4) and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.

Abstract

This production method for a sugar solution comprises steps (1)-(4), and enables production of a sugar solution in which fermentation-inhibiting substances such as organic acids and aromatic compounds are reduced. Step (1): a step for pulverizing cellulose-containing biomass such that the proportion of particles that do not pass through a sieve having a mesh opening size of 1 mm is at most 50% in terms of dry weight. Step (2): a step for obtaining pretreated biomass by bringing the pulverized biomass obtained in step (1) into contact with an alkaline aqueous medium. Step (3): a step for adding water to the pretreated biomass obtained in step (2) for solid-liquid separation, to obtain cellulose-containing solid. Step (4): a step for hydrolyzing the cellulose solid obtained in step (3) to obtain a sugar solution.

Description

糖液の製造方法Manufacturing method of sugar solution
 本発明はセルロース含有バイオマスから発酵原料等で使用可能な糖液を製造する方法に関する。 The present invention relates to a method for producing a sugar solution that can be used as a fermentation raw material from cellulose-containing biomass.
 糖質を原料とした化学品の発酵生産プロセスは、種々の工業原料生産に利用されている。この発酵原料となる糖質として、現在、さとうきび、澱粉、テンサイなどの食用原料に由来するものが工業的に使用されているが、今後の世界人口の増加による食用原料価格の高騰、あるいは食用と競合するという倫理的な側面から、再生可能な非食用資源、すなわちセルロース含有バイオマスをより効率的に糖液を製造するプロセス、あるいは得られた糖液を発酵原料として、効率的に工業原料に変換するプロセスの構築が今後の課題となっている。 The fermentation production process for chemicals made from sugar is used for the production of various industrial raw materials. Currently, sugars derived from edible raw materials such as sugar beet, starch, and sugar beet are industrially used as sugars as raw materials for fermentation. From the ethical aspect of competition, renewable non-edible resources, that is, the process of more efficiently producing sugar solution from cellulose-containing biomass, or the obtained sugar solution is efficiently converted into industrial raw material as a fermentation raw material. The construction of the process to do so is an issue for the future.
 セルロース含有バイオマス原料中の糖質は、複雑な構造をとる細胞壁中に埋め込まれている。したがって、酵素が効率的に作用するようにするために、酵素加水分解に先立って、バイオマス原料にアルカリ処理を施すことが好ましい。 The sugar in the cellulose-containing biomass raw material is embedded in the cell wall that has a complicated structure. Therefore, in order for the enzyme to act efficiently, it is preferable to apply an alkali treatment to the biomass raw material prior to the enzymatic hydrolysis.
 例えば、セルロールの酵素加水分解速度を向上させるために、セルロース含有物とアルカリ水溶液とを接触させるアルカリ処理を行い、アルカリ性濾液を繰り返し利用する特定の前処理をセルロース含有バイオマスに適用することで糖液が高純度で糖を含有することが開示されている(特許文献1)。 For example, in order to improve the enzymatic hydrolysis rate of cellulol, an alkaline treatment is performed in which a cellulose-containing substance and an alkaline aqueous solution are brought into contact with each other, and a specific pretreatment that repeatedly uses an alkaline filtrate is applied to the cellulose-containing biomass to obtain a sugar solution. Is disclosed to contain sugar with high purity (Patent Document 1).
 また、セルロースを含有する植物バイオマス原料を、アンモニアを含む処理剤で処理して40~100℃の水に浸漬し、多糖を水中に溶出せしめ、酵素糖化工程に供するための酵素糖化用原料を得ることが開示されている。本発明によれば、酵素糖化を効率的に行うことができ、そのため、糖の生産効率を向上させた糖の製造方法に用いられる(特許文献2)。 Further, the cellulose-containing plant biomass raw material is treated with a treatment agent containing ammonia and immersed in water at 40 to 100 ° C. to elute the polysaccharide in water to obtain a raw material for enzymatic saccharification to be used in the enzymatic saccharification step. Is disclosed. According to the present invention, enzymatic saccharification can be efficiently performed, and therefore, it is used in a method for producing sugar with improved sugar production efficiency (Patent Document 2).
 しかしながら、アルカリ処理を行う際に生じる有機酸、芳香族化合物といった発酵阻害物質が糖液に混入するという品質課題があり、発酵阻害物質が低減したセルロース糖液の製造方法が依然として求められている。 However, there is a quality problem that fermentation-inhibiting substances such as organic acids and aromatic compounds generated during alkaline treatment are mixed in the sugar solution, and a method for producing a cellulose sugar solution in which fermentation-inhibiting substances are reduced is still required.
WO2017/170552号WO2017 / 170552 WO2012/096236号WO2012 / 096236
 本発明は、セルロース含有バイオマスから糖液を製造する際に、セルロース含有バイオマスのアルカリ処理によって生じる有機酸、芳香族化合物といった発酵阻害物質を低減させる方法を提供することを目的としている。 An object of the present invention is to provide a method for reducing fermentation inhibitors such as organic acids and aromatic compounds generated by alkaline treatment of cellulose-containing biomass when producing a sugar solution from cellulose-containing biomass.
 本発明者は、今般、セルロース含有バイオマスを特定の粉砕度合いまで粉砕し、アルカリ性水性媒体に接触させて水を添加し、水を添加した前処理バイオマスを固液分離し、前処理バイオマスを加水分解すると、発酵阻害物質が低減した糖液を効率的に取得しうることを見出した。 The present inventor has now crushed cellulose-containing biomass to a specific degree of crushing, brought it into contact with an alkaline aqueous medium to add water, solid-liquid separated the pretreated biomass to which water was added, and hydrolyzed the pretreated biomass. Then, it was found that the sugar solution in which the fermentation inhibitor was reduced could be efficiently obtained.
 本発明は、かかる知見に基づくものであり、以下の[1]~[10]で構成される。
[1]セルロース含有バイオマスを原料とする糖液の製造方法であって、工程(1):目開き1mmのふるいで通過しない重量割合が乾燥重量で50%以下になるようにセルロース含有バイオマスを粉砕する工程、
工程(2):工程(1)で得られた粉砕バイオマスをアルカリ性水性媒体に接触させて前処理バイオマスを得る工程、
工程(3):工程(2)で得られた前処理バイオマスに水を添加して固液分離し、セルロース含有固形分を得る工程、および
工程(4):工程(3)で得られたセルロース含有固形分を加水分解して糖液を得る工程、
を含む、方法。
[2]前記工程(2)が、前記工程(1)で得られた粉砕バイオマスにアルカリ性媒体を通液させて前処理バイオマスを得る工程である、[1]に記載の糖液の製造方法。
[3]前記工程(2)が、前記工程(1)で得られた粉砕バイオマスとアルカリ性媒体を濾過器に供給し、該濾過器を用いて粉砕バイオマスとアルカリ性媒体を通液させる工程である、[1]または[2]に記載の糖液の製造方法。
[4]前記工程(2)のアルカリ性水性媒体が水酸化ナトリウムおよび/または水酸化カリウムを含む水性媒体である、[1]~[3]のいずれかに記載の糖液の製造方法。
[5]前記工程(3)の固液分離が圧搾である、[1]~[4]のいずれかに記載の糖液の製造方法。
[6]前記セルロース含有バイオマスがバガスである、[1]~[5]のいずれかに記載の糖液の製造方法。
[7]工程(5):工程(4)で得られた糖液をナノ濾過膜または逆浸透膜に通じて濾過し、非透過液として糖液を回収し、透過液を工程(3)で前処理バイオマスに添加する水に再利用する工程、
をさらに含む、[1]~[6]のいずれかに記載の糖液の製造方法。
[8]目開き1mmのふるいで通過しない重量割合が乾燥重量で50%以下の粉砕セルロース含有バイオマスおよびアルカリ性水性媒体を含有し、含水率が50重量%以上70重量%未満である、セルロース含有固形分。
[9]前記セルロース含有バイオマスがバガスである、[8]に記載のセルロース含有固形分。
[10]目開き1mmのふるいで通過しない重量割合が乾燥重量で40~50%である、粉砕セルロース含有バイオマス。
The present invention is based on such findings, and is composed of the following [1] to [10].
[1] A method for producing a sugar solution using cellulose-containing biomass as a raw material. Step (1): The cellulose-containing biomass is crushed so that the weight ratio that does not pass through a sieve having an opening of 1 mm is 50% or less in terms of dry weight. Process,
Step (2): A step of contacting the crushed biomass obtained in the step (1) with an alkaline aqueous medium to obtain a pretreated biomass.
Step (3): Water is added to the pretreated biomass obtained in step (2) and solid-liquid separation is performed to obtain a cellulose-containing solid content, and step (4): cellulose obtained in step (3). The process of hydrolyzing the contained solids to obtain a sugar solution,
Including methods.
[2] The method for producing a sugar solution according to [1], wherein the step (2) is a step of passing an alkaline medium through the crushed biomass obtained in the step (1) to obtain a pretreated biomass.
[3] The step (2) is a step of supplying the crushed biomass and the alkaline medium obtained in the step (1) to a filter and passing the crushed biomass and the alkaline medium through the filter. The method for producing a sugar solution according to [1] or [2].
[4] The method for producing a sugar solution according to any one of [1] to [3], wherein the alkaline aqueous medium of the step (2) is an aqueous medium containing sodium hydroxide and / or potassium hydroxide.
[5] The method for producing a sugar solution according to any one of [1] to [4], wherein the solid-liquid separation in the step (3) is pressing.
[6] The method for producing a sugar solution according to any one of [1] to [5], wherein the cellulose-containing biomass is bagasse.
[7] Step (5): The sugar solution obtained in step (4) is filtered through a nanofiltration membrane or a reverse osmosis membrane, the sugar solution is recovered as a non-permeate solution, and the permeate solution is used in step (3). The process of reusing water to be added to pretreated biomass,
The method for producing a sugar solution according to any one of [1] to [6], further comprising.
[8] Cellulose-containing solid containing pulverized cellulose-containing biomass and an alkaline aqueous medium having a dry weight of 50% or less and having a water content of 50% by weight or more and less than 70% by weight. Minutes.
[9] The cellulose-containing solid content according to [8], wherein the cellulose-containing biomass is bagasse.
[10] Biomass containing crushed cellulose having a dry weight of 40 to 50% that does not pass through a sieve having an opening of 1 mm.
 本発明によれば、セルロース含有バイオマスのアルカリ処理に由来する発酵阻害物質が低減した高純度の糖液を取得することができる。 According to the present invention, it is possible to obtain a high-purity sugar solution in which fermentation inhibitors derived from alkaline treatment of cellulose-containing biomass are reduced.
本発明の糖液の製造方法の一例を示す工程フロー図である。It is a process flow diagram which shows an example of the manufacturing method of the sugar solution of this invention.
 本発明はセルロース含有バイオマスを原料とする糖液の製造方法であって、工程(1):目開き1mmのふるいで通過しない割合が乾燥重量で50%以下になるようにセルロース含有バイオマスを粉砕する工程、工程(2):粉砕バイオマスをアルカリ性水性媒体に接触させて前処理バイオマスを得る工程、工程(3):前処理バイオマスに水を添加して固液分離し、セルロース含有固形分を分離する工程、および工程(4):セルロース含有固形分を加水分解する工程を含むことを特徴としている。本発明の工程フロー図の一例を図1に示すが、本発明のフローはこれに限定されるものではない。 The present invention is a method for producing a sugar solution using cellulose-containing biomass as a raw material. Step (1): The cellulose-containing biomass is crushed so that the ratio of non-passing through a sieve having an opening of 1 mm is 50% or less by dry weight. Step, Step (2): Step of contacting the crushed biomass with an alkaline aqueous medium to obtain pretreated biomass, Step (3): Add water to the pretreated biomass for solid-liquid separation to separate the cellulose-containing solids. Step and step (4): It is characterized by including a step of hydrolyzing a cellulose-containing solid content. An example of the process flow diagram of the present invention is shown in FIG. 1, but the flow of the present invention is not limited thereto.
 粉体がスラリー化した排水の処理では、粉体の粉砕度が高い程、脱水しにくいことが知られている(J.Soc.Powder Technol.,Japan,38,177-183(2001)の表2参照。)。しかしながら本発明では、一定の粉砕度まで粉砕したセルロース含有バイオマスをアルカリ処理して得られた前処理バイオマスを加水、固液分離すると、そのような粉砕をしない場合と比較して意外にも固液分離後の含水率が低減し、それにより後段の加水分解時に持ち込まれる前処理バイオマス由来の発酵阻害物質を低減することによって、高純度の糖液を得ることができる。 It is known that the higher the degree of pulverization of powder, the more difficult it is to dehydrate in the treatment of wastewater in which powder is slurried (Table of J. Soc Power Technology, Japan, 38, 177-183 (2001)). See 2.). However, in the present invention, when the pretreated biomass obtained by alkali-treating the cellulose-containing biomass crushed to a certain degree of crushing is hydrolyzed and solid-liquid separated, it is surprisingly solid-liquid as compared with the case where such pulverization is not performed. A high-purity sugar solution can be obtained by reducing the water content after separation and thereby reducing the fermentation inhibitor derived from the pretreated biomass brought in during the subsequent hydrolysis.
 以下、本発明について工程を追って説明する。 Hereinafter, the present invention will be described step by step.
 セルロース含有バイオマスとは、すくなくともセルロースを含む生物資源のことを指す。セルロース含有バイオマスの好適な例としては、バガス、スイッチグラス、ネピアグラス、エリアンサス、コーンストーバー、わら(稲わら、麦わら)、油椰子空果房などの草本系バイオマス、あるいは樹木、木屑、廃建材などの木質系バイオマス、さらに藻類、海草など水生環境由来のバイオマス、コーン外皮、小麦外皮、大豆外皮、籾殻、キャッサバイモからデンプンを抽出した後の残渣(キャッサバ粕)などの穀物皮類バイオマスなどが挙げられる。好ましくはバガス、稲わら、油椰子空果房などの草本系バイオマスである。 Cellulose-containing biomass refers to biological resources containing at least cellulose. Preferable examples of cellulose-containing biomass are herbaceous biomass such as bagasse, switchgrass, napiergrass, erianthus, corn stove, straw (rice straw, straw), chaff, or trees, wood chips, waste building materials. Woody biomass such as, aquatic environment-derived biomass such as algae and seaweed, corn husk, wheat husk, soy husk, rice husk, grain husk biomass such as residue after starch extraction from cassabaimo (cassaba lees), etc. Can be mentioned. Herbaceous biomass such as bagasse, rice straw, and oil palm empty fruit bunch is preferable.
 セルロース含有バイオマスの含水率は特に限定されないが、好ましい範囲は、例えば、3%程度以上、3%程度以上60%程度以下、5%程度以上、5%程度以上60%程度以下、5%程度以上55%程度以下、5%程度以上50%程度以下である。セルロース含有バイオマスの含水率は実施例にて詳述される方法によって測定される。 The water content of the cellulose-containing biomass is not particularly limited, but the preferable range is, for example, about 3% or more, about 3% or more and about 60% or less, about 5% or more, about 5% or more and about 60% or less, about 5% or more. It is about 55% or less, about 5% or more and about 50% or less. The water content of the cellulose-containing biomass is measured by the method detailed in the examples.
 工程(1)にて、セルロース含有バイオマスを特定の粉砕度になるまで粉砕して粉砕バイオマスを得る。粉砕手段は特に限定されず、ボールミル、振動ミル、カッターミル、ハンマーミル、ウィレーミル、ジェットミルなど各種材料の粗粉砕に慣用されている機械を用いて行うことができる。この機械的な粉砕は乾式および湿式のいずれでもよいが、好ましくは乾式粉砕である。 In step (1), the cellulose-containing biomass is crushed to a specific degree of crushing to obtain crushed biomass. The pulverization means is not particularly limited, and the pulverization can be performed by using a machine commonly used for coarse pulverization of various materials such as a ball mill, a vibration mill, a cutter mill, a hammer mill, a willley mill, and a jet mill. This mechanical pulverization may be either dry or wet, but is preferably dry pulverization.
 工程(1)で得られる粉砕バイオマスの粉砕度合いとしては、目開き1mmのふるいで通過しない重量割合(乾燥重量%)が乾燥重量で50%程度以下になるまで粉砕し、好ましくは40%程度以上50%程度以下、より好ましくは40程度%以上45程度%以下または45%程度以上50%程度以下になるまで粉砕することで、このような粉砕をしない場合と比較して意外にも固液分離後の含水率が低減し、それにより後段の加水分解時に持ち込まれる前処理バイオマス由来の発酵阻害物質を低減することができる。粉砕度合いは、粉砕バイオマスを乾燥し、含水率20%以下とした後に粉砕バイオマスを目開き1mmのふるいにかけて評価する。なお、本明細書では、目開き1mmのふるいで通過しない粉砕バイオマスの重量割合(乾燥重量%)が低ければ、粉砕度が高いと表現することがある。ふるいの方法・条件はISO 2591-1に従う。 The degree of crushing of the crushed biomass obtained in the step (1) is such that the weight ratio (dry weight%) that does not pass through a sieve having a mesh size of 1 mm is crushed until the dry weight becomes about 50% or less, preferably about 40% or more. By pulverizing until about 50% or less, more preferably about 40% or more and about 45% or less, or about 45% or more and about 50% or less, the solid-liquid separation is unexpectedly compared with the case where such pulverization is not performed. The subsequent water content is reduced, which can reduce the fermentation inhibitors derived from the pretreated biomass brought in during the subsequent hydrolysis. The degree of crushing is evaluated by drying the crushed biomass to a water content of 20% or less, and then sieving the crushed biomass with an opening of 1 mm. In the present specification, if the weight ratio (dry weight%) of the crushed biomass that does not pass through the sieve having an opening of 1 mm is low, it may be expressed that the degree of crushing is high. The sieving method and conditions follow ISO 2591-1.
 工程(2)にて、工程(1)で得られた粉砕バイオマスをアルカリ水性媒体に接触させて前処理バイオマスを得る。ここでいう前処理バイオマスとは、後段の工程(4)にてセルロース含有バイオマスが効率的に加水分解されるようにアルカリ処理を施されたセルロース含有バイオマスの固形分を含むものを指す。 In step (2), the crushed biomass obtained in step (1) is brought into contact with an alkaline aqueous medium to obtain pretreated biomass. The pretreated biomass referred to here refers to those containing the solid content of the cellulose-containing biomass that has been subjected to alkali treatment so that the cellulose-containing biomass is efficiently hydrolyzed in the subsequent step (4).
 工程(1)で得られた粉砕バイオマスとアルカリ性水性媒体とを接触させる方法は、当業者にとって周知のセルロース含有バイオマスのアルカリ処理方法であれば特に制限はないが、好ましくは、WO2017/170552号に記載のアルカリ処理方法が採用される。本方法は、セルロース含有バイオマスにアルカリ性水性媒体を通液させて、前処理バイオマスと、クマル酸やフェルラ酸に富むアルカリ処理液を得る方法であり、本発明においては粉砕バイオマスにアルカリ性水性媒体を通液させればよい。 The method for bringing the crushed biomass obtained in the step (1) into contact with the alkaline aqueous medium is not particularly limited as long as it is an alkaline treatment method for cellulose-containing biomass well known to those skilled in the art, but WO2017 / 170552 is preferable. The alkaline treatment method described is adopted. This method is a method of passing an alkaline aqueous medium through a cellulose-containing biomass to obtain a pretreated biomass and an alkaline treated solution rich in coumaric acid or ferulic acid. In the present invention, the alkaline aqueous medium is passed through the pulverized biomass. You just have to make it liquid.
 粉砕バイオマスにアルカリ性水性媒体を通液させる方法としては、WO2017/170552号に記載の方法に準じて、粉砕バイオマスとアルカリ性水性媒体を濾過器に供給し、該濾過器を用いて粉砕バイオマスとアルカリ性媒体を通液させる方法が挙げられる。粉砕バイオマスおよびアルカリ性水性媒体は予め混合して濾過器に供給してもよく、両者を別々に濾過器に供給してもよいが、濾過器中に予め供給された粉砕バイオマス上にアルカリ性水性媒体を添加することが好ましい。 As a method for passing an alkaline aqueous medium through the crushed biomass, the crushed biomass and the alkaline aqueous medium are supplied to a filter according to the method described in WO2017 / 170552, and the crushed biomass and the alkaline medium are supplied using the filter. A method of passing a liquid can be mentioned. The crushed biomass and the alkaline aqueous medium may be mixed in advance and supplied to the filter, or both may be supplied to the filter separately, but the alkaline aqueous medium is placed on the crushed biomass previously supplied into the filter. It is preferable to add it.
 また、アルカリ性濾液のpHは、アルカリ性水性媒体と同様の範囲内であってよく、好ましいpHの範囲は、例えば、7以上12以下、8以上12以下、より好ましいpHの範囲は9以上12以下、さらに好ましいpHの範囲は10以上12以下の範囲である。アルカリ性濾液のpHは反応が進行するとともに低下していく傾向がある。これはアルカリ反応が進行すると可溶性リグニンの成分が中和剤の役割を果たすためであり、この低下度合いによって反応の進行状態を測ることが可能である。特に粉砕バイオマスをアルカリ性水性媒体に接触させた後(反応後)の粉砕バイオマスのpHの範囲は、初期のアルカリ濃度等により適宜調整することができるが、好ましくは、例えば、7以上12.5以下、8以上12.5以下、より好ましいpHの範囲は8以上12以下、さらに好ましいpHの範囲は8以上11以下の範囲である。アルカリ性濾液のpHが上記範囲にあるか測定することは、後続する加水分解工程を行うのに十分なレベルまで反応が進行しているかを評価する上で有効的な手段である。 The pH of the alkaline filtrate may be in the same range as that of the alkaline aqueous medium, and the preferable pH range is, for example, 7 or more and 12 or less, 8 or more and 12 or less, and the more preferable pH range is 9 or more and 12 or less. A more preferable pH range is 10 or more and 12 or less. The pH of the alkaline filtrate tends to decrease as the reaction progresses. This is because the soluble lignin component acts as a neutralizing agent as the alkaline reaction progresses, and the progress of the reaction can be measured by the degree of this decrease. In particular, the pH range of the pulverized biomass after contacting the pulverized biomass with an alkaline aqueous medium (after the reaction) can be appropriately adjusted depending on the initial alkali concentration and the like, but is preferably 7 or more and 12.5 or less. , 8 or more and 12.5 or less, a more preferable pH range of 8 or more and 12 or less, and a more preferable pH range of 8 or more and 11 or less. Measuring whether the pH of the alkaline filtrate is in the above range is an effective means for assessing whether the reaction has proceeded to a level sufficient to carry out the subsequent hydrolysis step.
 また、粉砕バイオマスと接触中のアルカリ性水性媒体は、温度を実質的に保持することが好ましい。濾過器が粉砕バイオマスにアルカリ水性媒体を通液させる濾過部を備えている場合は、濾過部から濾過されるアルカリ性濾液も温度を実質的に保持することが好ましい。アルカリ性水性媒体、アルカリ性濾液の温度を保持することは、濾過器に公知の保温機器または加熱機器を設置することにより実施することができる。 Further, it is preferable that the alkaline aqueous medium in contact with the crushed biomass substantially maintains the temperature. If the filter is provided with a filter section that allows the ground biomass to pass an alkaline aqueous medium, it is preferable that the alkaline filtrate filtered from the filter section also substantially retains the temperature. Maintaining the temperature of the alkaline aqueous medium and the alkaline filtrate can be carried out by installing a known heat insulating device or heating device in the filter.
 アルカリ性水性媒体を接触させた後に濾過部から出てくる濾液は循環して再度粉砕バイオマスに接触させても良く、繰り返す回数は、特に限定されないが、好適な回数は、例えば、少なくとも2回以上、2回以上20000以下、2回以上10000以下、2回以上1000以下、3回以上10000以下、3回以上1000以下または3回以上100以下である。 The filtrate that comes out of the filtration section after being brought into contact with the alkaline aqueous medium may be circulated and brought into contact with the pulverized biomass again, and the number of repetitions is not particularly limited, but the suitable number of times is, for example, at least two times or more. 2 times or more and 20000 or less, 2 times or more and 10000 or less, 2 times or more and 1000 or less, 3 times or more and 10000 or less, 3 times or more and 1000 or less, or 3 times or more and 100 or less.
 アルカリ性水性媒体は、アンモニア、アンモニア水、水酸化物を含む水性媒体などのアルカリ性水溶液が挙げられるが、好ましくは水酸化ナトリウムおよび/または水酸化カリウムを含む水性媒体であり、より好ましくは水酸化ナトリウムを含む水性媒体であり、さらに好ましくは水酸化ナトリウムおよび/または水酸化カリウム水溶液である。 Examples of the alkaline aqueous medium include an alkaline aqueous solution such as an aqueous medium containing ammonia, aqueous ammonia, and a hydroxide, preferably an aqueous medium containing sodium hydroxide and / or potassium hydroxide, and more preferably sodium hydroxide. It is an aqueous medium containing, and more preferably an aqueous solution of sodium hydroxide and / or potassium hydroxide.
 アルカリ性水性媒体のアルカリ濃度は、アルカリ含有性媒体中のアルカリ性物質(水酸化物等のアルカリ固形分)の含有量により算出することができる。アルカリ性水性媒体のアルカリ濃度の上限値は、特に限定されないが、好ましくは3、2、1.5、1、0.7、0.6、0.5、0.4、0.3または0.2重量%程度であり、下限値は、好ましくは0.05、0.1、0.2、0.3、0.4または0.5重量%程度である。また、好ましいアルカリ濃度の範囲は、例えば、0.05重量%程度以上0.3重量%程度以下、0.1重量%程度以上3重量%程度以下、0.1重量%程度以上2重量%程度以下、より好ましい範囲は0.1重量%程度以上2重量%程度、0.25重量%程度以上1.5重量%程度以下、0.25重量%程度以上1.5重量%程度以下、さらに好ましい範囲は0.25重量%程度以上1.0重量%程度以下である。 The alkali concentration of the alkaline aqueous medium can be calculated from the content of alkaline substances (alkaline solids such as hydroxides) in the alkali-containing medium. The upper limit of the alkali concentration of the alkaline aqueous medium is not particularly limited, but is preferably 3, 2, 1.5, 1, 0.7, 0.6, 0.5, 0.4, 0.3 or 0. It is about 2% by weight, and the lower limit is preferably about 0.05, 0.1, 0.2, 0.3, 0.4 or 0.5% by weight. The preferred range of alkali concentration is, for example, about 0.05% by weight or more and about 0.3% by weight or less, about 0.1% by weight or more and about 3% by weight or less, and about 0.1% by weight or more and about 2% by weight. Hereinafter, the more preferable range is about 0.1% by weight or more and about 2% by weight, about 0.25% by weight or more and about 1.5% by weight or less, about 0.25% by weight or more and about 1.5% by weight or less, further preferable. The range is about 0.25% by weight or more and about 1.0% by weight or less.
 また、アルカリ性水性媒体のpHの下限値は、アルカリ性である限り特に限定されないが、7以上、好ましくはpH8以上、より好ましくはpH9以上、さらに好ましくはpH10以上である。pHの上限値は、pH14未満であれば、特に限定はされないが、アルカリの使用量を少なくする観点で、pH13.5以下で設定することができる。また、好ましいpHの範囲は、例えば、7以上13.5以下、8以上13.5以下、より好ましいpHの範囲は9以上13.5以下、さらに好ましいpHの範囲は10以上13.5以下の範囲である。 The lower limit of the pH of the alkaline aqueous medium is not particularly limited as long as it is alkaline, but is 7 or more, preferably pH 8 or more, more preferably pH 9 or more, and further preferably pH 10 or more. The upper limit of pH is not particularly limited as long as it is less than pH 14, but can be set to pH 13.5 or less from the viewpoint of reducing the amount of alkali used. The preferred pH range is, for example, 7 or more and 13.5 or less, 8 or more and 13.5 or less, the more preferable pH range is 9 or more and 13.5 or less, and the more preferable pH range is 10 or more and 13.5 or less. The range.
 アルカリ性水性媒体の温度の上限値は、特に限定されないが、好ましくは110、100、95、90、80、75、70℃程度であり、下限値は、好ましくは35,40、50、60、65℃程度である。また、好ましいアルカリ性水性媒体の温度の範囲は、例えば、35℃程度以上100℃程度以下、40℃程度以上100℃程度以下、50℃程度以上100℃程度以下、60℃程度以上100℃程度以下、65℃程度以上100℃程度以下、80℃程度以上100℃程度以下であり、より好ましい温度の範囲は60℃程度以上100℃程度以下、65℃程度以上100℃程度以下、80℃程度以上100℃程度以下であり、さらに好ましい温度の範囲は65℃程度以上100℃程度以下または80℃程度以上100℃程度以下である。 The upper limit of the temperature of the alkaline aqueous medium is not particularly limited, but is preferably about 110, 100, 95, 90, 80, 75, 70 ° C., and the lower limit is preferably 35, 40, 50, 60, 65. It is about ° C. The temperature range of the alkaline aqueous medium is, for example, about 35 ° C. or higher and 100 ° C. or lower, 40 ° C. or higher and 100 ° C. or lower, 50 ° C. or higher and 100 ° C. or lower, 60 ° C. or higher and 100 ° C. or lower. 65 ° C. or higher and 100 ° C. or lower, 80 ° C. or higher and 100 ° C. or lower, and more preferable temperature ranges are 60 ° C. or higher and 100 ° C. or lower, 65 ° C. or higher and 100 ° C. or lower, 80 ° C. or higher and 100 ° C. The temperature range is 65 ° C. or higher and 100 ° C. or lower, or 80 ° C. or higher and 100 ° C. or lower.
 アルカリ性水性媒体と、粉砕バイオマス(乾燥重量)との重量割合は、特に限定されないが、好ましい範囲は、例えば、100:1~2:1、90:1~3:1、50:1~5:1、30:1~5:1、25:1~7:1、25:1~5:1、20:1~5:1である。 The weight ratio between the alkaline aqueous medium and the ground biomass (dry weight) is not particularly limited, but the preferred ranges are, for example, 100: 1 to 2: 1, 90: 1 to 3: 1, 50: 1 to 5 :. 1, 30: 1 to 5: 1, 25: 1 to 7: 1, 25: 1 to 5: 1, 20: 1 to 5: 1.
 アルカリ含有水性媒体と、粉砕バイオマス(乾燥重量)との割合は、実施例に記載のアルカリ反応量の計算方法で算出されるアルカリ使用量(アルカリ反応量ともいう)を指標として設定することもできる。好ましいアルカリ使用量の範囲は、例えば、20mg/g程度以上300mg/g程度以下、30mg/g程度以上200mg/g程度以下、40mg/g程度以上200mg/g程度以下、45mg/g程度以上180mg/g程度以下、45mg/g程度以上150mg/g程度以下、50mg/g程度以上120mg/g程度以下、60mg/g程度以上120mg/g程度以下であり、より好ましいアルカリ使用量の範囲は45mg/g程度以上150mg/g程度以下、50mg/g程度以上120mg/g程度以下、60mg/g程度以上120mg/g程度以下である。 The ratio of the alkali-containing aqueous medium to the crushed biomass (dry weight) can also be set using the amount of alkali used (also referred to as the amount of alkali reaction) calculated by the method for calculating the amount of alkali reaction described in Examples as an index. .. The preferred range of alkali usage is, for example, about 20 mg / g or more and about 300 mg / g or less, about 30 mg / g or more and about 200 mg / g or less, about 40 mg / g or more and about 200 mg / g or less, and about 45 mg / g or more and 180 mg / g. It is about g or less, about 45 mg / g or more and about 150 mg / g or less, about 50 mg / g or more and about 120 mg / g or less, about 60 mg / g or more and about 120 mg / g or less, and the more preferable range of alkali usage is 45 mg / g. About 150 mg / g or less, about 50 mg / g or more and about 120 mg / g or less, about 60 mg / g or more and about 120 mg / g or less.
 粉砕バイオマスをアルカリ性水性媒体と接触させる時間は、特に限定されないが、接触時間は、例えば、20分程度以上72時間程度以下、20分程度以上48時間程度以下、20分程度以上24時間程度以下、30分程度以上48時間程度以下、30分程度以上24時間程度以下、30分程度以上12時間程度以下、30分程度以上6時間程度以下または30分程度以上3時間程度以下ある。 The time for contacting the pulverized biomass with the alkaline aqueous medium is not particularly limited, but the contact time is, for example, about 20 minutes or more and about 72 hours or less, about 20 minutes or more and about 48 hours or less, about 20 minutes or more and about 24 hours or less. About 30 minutes or more and about 48 hours or less, about 30 minutes or more and about 24 hours or less, about 30 minutes or more and about 12 hours or less, about 30 minutes or more and about 6 hours or less, or about 30 minutes or more and about 3 hours or less.
 粉砕バイオマスをアルカリ水性媒体に接触させて得られた前処理バイオマスは、当業者に周知の方法によって前処理バイオマスを分離・回収し、後段の工程(3)に供給することが好ましい。粉砕バイオマスをアルカリ水性媒体に接触させる際に濾過器を用いる場合は、濾過器に残存する固形分を前処理バイオマスとして回収することができる。 For the pretreated biomass obtained by contacting the crushed biomass with an alkaline aqueous medium, it is preferable that the pretreated biomass is separated and recovered by a method well known to those skilled in the art and supplied to the subsequent step (3). When a filter is used to bring the crushed biomass into contact with an alkaline aqueous medium, the solid content remaining in the filter can be recovered as pretreated biomass.
 工程(3)に供給する前処理バイオマスの含水率は特に限定されないが、好ましい範囲は、例えば、50重量%程度以上99重量%程度以下、60重量%程度以上99重量%程度以下、70重量%程度以上99重量%程度以下、80重量%程度以上99重量%程度以下または80重量%程度以上95重量%程度以下であり、より好ましくは80重量%程度以上99重量%程度以下であり、さらに好ましくは80重量%程度以上95重量%程度以下である。前処理バイオマスの含水率は実施例にて詳述される方法によって測定される。 The water content of the pretreated biomass supplied to the step (3) is not particularly limited, but the preferred ranges are, for example, about 50% by weight or more and about 99% by weight or less, about 60% by weight or more and about 99% by weight or less, and 70% by weight. About 99% by weight or less, about 80% by weight or more and about 99% by weight or less, or about 80% by weight or more and about 95% by weight or less, more preferably about 80% by weight or more and about 99% by weight or less, still more preferable. Is about 80% by weight or more and about 95% by weight or less. The water content of the pretreated biomass is measured by the method detailed in the Examples.
 工程(3)では、得られた前処理バイオマスは、前処理バイオマスから発酵阻害物質を分離する目的で水を添加し、固液分離する。本工程により、前処理バイオマスに含まれるセルロース含有バイオマスのアルカリ処理によって生じる、セルロース含有バイオマス中のリグニン由来とみられる発酵阻害物質を低減することができる。発酵阻害物質の具体例としては、ギ酸、酢酸、クエン酸、乳酸といった有機酸、フェルラ酸、クマル酸、バニリン、バニリン酸、アセトバニリン、4-ヒドロキシ安息香酸、シリンガ酸、没食子酸といった芳香族化合物、HMF、フルフラールといったフラン系化合物が挙げられる。 In step (3), the obtained pretreated biomass is solid-liquid separated by adding water for the purpose of separating fermentation inhibitors from the pretreated biomass. By this step, it is possible to reduce the fermentation inhibitor which is considered to be derived from lignin in the cellulose-containing biomass, which is generated by the alkaline treatment of the cellulose-containing biomass contained in the pretreated biomass. Specific examples of fermentation inhibitors include organic acids such as formic acid, acetic acid, citric acid, and lactic acid, and aromatic compounds such as ferulic acid, kumalic acid, vanillin, vanillic acid, acetovanillin, 4-hydroxybenzoic acid, silingaic acid, and gallic acid. , HMF, furfural and other furan compounds.
 前処理バイオマスに添加する水の量としては、前処理バイオマス(乾燥重量)と添加する水の重量割合で、特に限定されないが、好ましい範囲は、例えば、1:1~1:100、1:1~1:50、1:1~1:30、1:1~1:20、1:1~1:10、1:1~1:5、1:1~1:3である。 The amount of water added to the pretreated biomass is not particularly limited by the weight ratio of the pretreated biomass (dry weight) and the water to be added, but the preferable range is, for example, 1: 1 to 1: 100, 1: 1. ~ 1: 50, 1: 1 to 1:30, 1: 1 to 1:20, 1: 1 to 1: 10, 1: 1 to 1: 5, 1: 1 to 1: 3.
 前処理バイオマスに添加する水のpHとしては、特に限定されないが、好ましい範囲は、例えば、3~9、3~8、3~7、4~9、4~8、4~7、5~9、5~8、5~7である。 The pH of the water added to the pretreated biomass is not particularly limited, but the preferred range is, for example, 3 to 9, 3 to 8, 3 to 7, 4 to 9, 4 to 8, 4 to 7, 5 to 9. 5 to 8, 5 to 7.
 前処理バイオマスに添加する水の温度としては、特に限定されないが、好ましい範囲は、例えば、10~60℃、10~50℃、10~40℃、20~60℃、20~50℃、20~40℃、30~60℃、30~50℃、30~40℃である。 The temperature of the water added to the pretreated biomass is not particularly limited, but the preferred range is, for example, 10 to 60 ° C., 10 to 50 ° C., 10 to 40 ° C., 20 to 60 ° C., 20 to 50 ° C., 20 to 20 to. 40 ° C., 30-60 ° C., 30-50 ° C., 30-40 ° C.
 前処理バイオマスへの水の添加方法としては、反応槽で前処理バイオマスと添加する水とを混合しても良いし、反応槽には攪拌機が有っても良い。また反応槽は前処理バイオマスと添加する水とが接触できれば形状を問わない。また、前処理バイオマスはコンベアや自然落下などにより反応槽まで搬送することができる。また、前処理バイオマスと水とが接触できれば、反応槽で無くともコンベアなどの搬送中に水を添加することもできる。 As a method of adding water to the pretreated biomass, the pretreated biomass and the water to be added may be mixed in the reaction tank, or the reaction tank may have a stirrer. The shape of the reaction vessel does not matter as long as the pretreated biomass and the water to be added can come into contact with each other. In addition, the pretreated biomass can be transported to the reaction tank by a conveyor or free fall. Further, if the pretreated biomass and water can come into contact with each other, water can be added during transportation such as a conveyor even if it is not in a reaction tank.
 固液分離で用いられる装置としては、遠心分離、圧搾などを適用することができ、圧搾が好ましい。圧搾としては、スクリュープレス、ベルトプレス、フィルタープレスなどがあるが、スクリュープレスが好ましい。 As the device used for solid-liquid separation, centrifugation, squeezing, etc. can be applied, and squeezing is preferable. Examples of the pressing include a screw press, a belt press, a filter press and the like, but a screw press is preferable.
 固液分離後のセルロース含有固形分の含水率は、前処理バイオマス由来の発酵阻害物質を低減させるという観点から、好ましくは50重量%程度以上85重量%程度以下であり、より好ましくは50重量%程度以上70重量%程度未満である。セルロース含有固形分の含水率は実施例に記載の含水率の測定方法によって測定される。 The water content of the cellulose-containing solid content after solid-liquid separation is preferably about 50% by weight or more and about 85% by weight or less, more preferably 50% by weight, from the viewpoint of reducing fermentation inhibitors derived from the pretreated biomass. It is more than about 70% by weight and less than about 70% by weight. The water content of the cellulose-containing solid content is measured by the method for measuring the water content described in Examples.
 セルロース含有固形分中のアルカリ性水性媒体の含有量は、好ましくは5mg/g-バイオマス程度以上40mg/g-バイオマス程度以下であり、より好ましくは7mg/g-バイオマス程度以上35mg/g-バイオマス程度以下であり、さらに好ましくは10mg/g-バイオマス程度以上30mg/g-バイオマス程度以下である。セルロース含有固形分中のアルカリ性水性媒体の含有量を上記範囲に低減することで、後段の加水分解時に持ち込まれる前処理バイオマス由来の発酵阻害物質を低減することができる。 The content of the alkaline aqueous medium in the cellulose-containing solid content is preferably about 5 mg / g-biomass or more and 40 mg / g-biomass or less, and more preferably about 7 mg / g-biomass or more and 35 mg / g-biomass or less. It is more preferably about 10 mg / g-biomass or more and about 30 mg / g-biomass or less. By reducing the content of the alkaline aqueous medium in the cellulose-containing solid content to the above range, it is possible to reduce the fermentation inhibitor derived from the pretreated biomass brought in during the subsequent hydrolysis.
 工程(4)では、セルロール含有固形分を加水分解して糖液を得る。加水分解工程では、酸加水分解、アルカリ加水分解、酵素加水分解等の公知の加水分解法を適用することができるが、セルロール含有固形分を水媒体中、酵素で加水分解処理することが好ましい。かかる酵素加水分解工程によって得られる糖液は、例えば、グルコース、キシロース、アラビノース、ガラクトース、キシロビオース、セロビオースをはじめとする、オリゴ糖および/または単糖を含有する水溶液として取得することができる。 In step (4), the cellulose-containing solid content is hydrolyzed to obtain a sugar solution. In the hydrolysis step, known hydrolysis methods such as acid hydrolysis, alkaline hydrolysis, and enzyme hydrolysis can be applied, but it is preferable to hydrolyze the cell roll-containing solid content in an aqueous medium with an enzyme. The sugar solution obtained by such an enzymatic hydrolysis step can be obtained as an aqueous solution containing oligosaccharides and / or monosaccharides such as glucose, xylose, arabinose, galactose, xylobiose and cellobiose.
 使用される酵素はセルロースまたはヘミセルロース加水分解酵素である限り特に限定されないが、例えば、比較的安価な市販のものでよく、セルラーゼ酵素剤としては、アクレモニウム属由来の酵素である“アクレモニウムセルラーゼ”(Meiji Seika ファルマ株式会社)やトリコデルマ属由来の酵素である“アクセルレース・デュエット”(ダニスコ・ジャパン社)、“Celluclast” 1.5L(ノボザイム社)などを用いることができる。ヘミセルラーゼ酵素剤としては、“Optimash BG”(ジェネンコア社)などを用いることができる。酵素の由来は特に限定されないが、より好ましくは糸状菌由来の酵素である。糸状菌由来の酵素は、セルラーゼ、ヘミセルラーゼ、β-グルコシダーゼなどのセルロース含有バイオマス由来の多糖の分解酵素を豊富に含んでおり、アルカリ処理した後のバイオマスに対して加水分解反応を行う上で有利である。 The enzyme used is not particularly limited as long as it is cellulose or hemicellulose hydrolase, but for example, a relatively inexpensive commercially available one may be used, and the cellulase enzyme agent is "acremonium cellulase", which is an enzyme derived from the genus Acremonium. (Meiji Seika Pharma Co., Ltd.), "Axel Race Duet" (Danisco Japan Co., Ltd.), an enzyme derived from the genus Trichoderma, "Cellulose" 1.5L (Novozyme Co., Ltd.) and the like can be used. As the hemicellulase enzyme agent, "Optimash BG" (Genencore Co., Ltd.) or the like can be used. The origin of the enzyme is not particularly limited, but more preferably the enzyme is derived from filamentous fungi. Enzymes derived from filamentous fungi are rich in polysaccharide-degrading enzymes derived from cellulose-containing biomass such as cellulase, hemicellulase, and β-glucosidase, and are advantageous for hydrolyzing biomass after alkali treatment. Is.
 使用される酵素は、酵素剤の性質、所望の製品の組成等を勘案して、単独もしくは組み合わせて用いることができる。好適な酵素の量もまた、特に限定されず適宜決定することができる。かかる酵素の量は、例えば、原料基質1gあたり0.01g以上1g以下とすることができ、好ましくは0.001g以上0.1g以下である。酵素加水分解の温度、pHおよび時間は、酵素の性質や組み合わせ等によって適宜設定することができる。好適な範囲としては、例えば、温度は30以上60℃以下、より好ましくは35℃以上50℃以下である。また、pHは、例えばpH3以上8以下、好ましくはpH4以上7以下である。また、反応時間は、例えば、1時間以上48時間以下、好ましくは6時間以上24時間以下である。 The enzyme used can be used alone or in combination in consideration of the properties of the enzyme preparation, the composition of the desired product, and the like. The amount of suitable enzyme is also not particularly limited and can be appropriately determined. The amount of such an enzyme can be, for example, 0.01 g or more and 1 g or less per 1 g of the raw material substrate, preferably 0.001 g or more and 0.1 g or less. The temperature, pH and time of enzyme hydrolysis can be appropriately set depending on the properties and combinations of enzymes. As a preferable range, for example, the temperature is 30 or more and 60 ° C. or less, more preferably 35 ° C. or more and 50 ° C. or less. The pH is, for example, pH 3 or more and 8 or less, preferably pH 4 or more and 7 or less. The reaction time is, for example, 1 hour or more and 48 hours or less, preferably 6 hours or more and 24 hours or less.
 工程(4)で得られる糖液におけるグルコース、キシロースまたはキシロビオースの濃度は、特に限定されず、各工程の反応条件等を調節することにより適宜設定することができる。好適なグルコース濃度としては、例えば、5g/L程度以上1000g/L程度以下、5g/L程度以上700g/L程度以下、5g/L程度以上550g/L程度以下または10g/L程度以上550g/L程度以下である。また、好適なキシロース濃度としては、例えば、1g/L程度以上100g/L、1g/L程度以上50g/L程度以下または1g/L程度以上10g/L程度以下である。また、好適なキシロビオース濃度としては、例えば、1g/L程度以上100g/L、1g/L程度以上50g/L程度以下、1g/L程度以上20g/L程度以下または1g/L程度以上15g/L程度以下である。 The concentration of glucose, xylose or xylobiose in the sugar solution obtained in step (4) is not particularly limited and can be appropriately set by adjusting the reaction conditions of each step. Suitable glucose concentrations include, for example, about 5 g / L or more and 1000 g / L or less, 5 g / L or more and 700 g / L or less, 5 g / L or more and 550 g / L or less, or 10 g / L or more and 550 g / L. It is below the degree. The suitable xylose concentration is, for example, about 1 g / L or more and 100 g / L, 1 g / L or more and 50 g / L or less, or 1 g / L or more and about 10 g / L or less. As a suitable xylobiose concentration, for example, about 1 g / L or more and 100 g / L, 1 g / L or more and 50 g / L or less, 1 g / L or more and 20 g / L or less, or 1 g / L or more and 15 g / L or more. It is below the degree.
 工程(4)で製造される糖液はそのまま各種産業用途に使用されうるが、所望により後処理をしてもよく、具体的には、膜処理、遠心分離、濃縮、乾燥等の処理を施してもよい。 The sugar solution produced in step (4) can be used as it is for various industrial applications, but may be post-treated if desired, and specifically, it is subjected to treatments such as membrane treatment, centrifugation, concentration, and drying. You may.
 工程(4)で製造される糖液の好ましい膜処理としては、ナノ濾過膜または逆浸透膜処理が挙げられる。 Preferable membrane treatment of the sugar solution produced in step (4) includes nanofiltration membrane treatment or reverse osmosis membrane treatment.
 ナノ濾過膜とは、ナノフィルター(ナノフィルトレーション膜、NF膜)とも呼ばれるものであり、「一価のイオンは透過し、二価のイオンを阻止する膜」と一般に定義される膜である。数ナノメートル程度の微小空隙を有していると考えられる膜で、主として、水中の微小粒子や分子、イオン、塩類等を阻止するために用いられる。 The nanofiltration membrane is also called a nanofilter (nanofiltration membrane, NF membrane), and is a membrane generally defined as "a membrane that allows monovalent ions to permeate and blocks divalent ions". .. It is a membrane that is considered to have microvoids of several nanometers, and is mainly used to block fine particles, molecules, ions, salts, etc. in water.
 逆浸透膜とはRO膜とも呼ばれるものであり、「1価のイオンを含めて脱塩機能を有する膜」と一般的に定義される膜であり、数オングストロームから数ナノメートル程度の超微小空隙を有していると考えられる膜で、主として海水淡水化や超純水製造などイオン成分除去に用いられる。 A reverse osmosis membrane is also called an RO membrane, and is a membrane generally defined as "a membrane having a desalination function including monovalent ions", and is an ultra-small membrane of several angstroms to several nanometers. A membrane that is thought to have voids and is mainly used for removing ionic components such as desalination of seawater and production of ultrapure water.
 ナノ濾過膜または逆浸透膜処理とは、工程(4)で製造された糖液をナノ濾過膜または逆浸透膜処理に通じて濾過し、溶解している糖、特にグルコースやキシロースといった単糖や、キシロビオースやセロビオースといったオリゴ糖を膜の非透過側に阻止または濾別し、糖液に残存する発酵阻害物質を透過液として透過させる処理であり、WO2010/067785号に記載の方法によって実施することできる。 The nanofiltration membrane or reverse osmosis membrane treatment refers to the sugar solution produced in step (4) being filtered through the nanofiltration membrane or reverse osmosis membrane treatment, and dissolved sugars, particularly monosaccharides such as glucose and xylose. , Xylobiose, cellobiose, and other oligosaccharides are blocked or filtered to the non-permeable side of the membrane, and the fermentation inhibitor remaining in the sugar solution is permeated as a permeate, and is carried out by the method described in WO2010 / 067785. can.
 ナノ濾過膜または逆浸透膜の非透過側から回収される糖液は、膜処理前と比較してさらに発酵阻害物質が低減しており、本膜処理前と比較して発酵性能を向上させることができ、さらに、ナノ濾過膜または逆浸透膜の透過側から回収される透過水は前記工程(3)での前処理バイオマスに添加する水として使用することができる(工程(5))。本工程により、全工程における水の使用量を削減できると共に、工程(3)の固液分離によって発酵阻害物質である芳香族化合物を更に除去できるという予想外の効果を得ることができる。 The sugar solution recovered from the non-permeable side of the nanofiltration membrane or reverse osmosis membrane has a further reduction in fermentation inhibitors compared to before the membrane treatment, and the fermentation performance should be improved compared to before the main membrane treatment. Further, the permeated water recovered from the permeation side of the nanofiltration membrane or the reverse osmosis membrane can be used as water to be added to the pretreated biomass in the step (3) (step (5)). By this step, the amount of water used in all the steps can be reduced, and the unexpected effect that the aromatic compound which is a fermentation inhibitor can be further removed by the solid-liquid separation in the step (3) can be obtained.
 以下、本発明を実施例により具体的に説明するが、本発明はこれら実施例に限定されない。また、特に指摘されない限り、本明細書に記載の単位および測定方法は日本工業規格(JIS)による。 Hereinafter, the present invention will be specifically described with reference to Examples, but the present invention is not limited to these Examples. Unless otherwise specified, the units and measurement methods described in this specification are in accordance with the Japanese Industrial Standards (JIS).
 本実施例での各種分析方法は以下の通り。 The various analysis methods in this example are as follows.
 [糖濃度の測定方法]
 各実施例、比較例において得られた糖化液に含まれる糖濃度は、下記に示す高速液体クロマトグラフィー(HPLC)条件で、標品との比較により定量した。
カラム:Luna NH(Phenomenex社製)
移動相:超純水;アセトニトリル=25:75
流速:0.6mL/min
反応液:なし
検出方法:RI(示差屈折率)
温度:30℃。
[Measurement method of sugar concentration]
The sugar concentration contained in the saccharified solution obtained in each Example and Comparative Example was quantified by comparison with the standard under the conditions of high performance liquid chromatography (HPLC) shown below.
Column: Luna NH 2 (manufactured by Phenomenex)
Mobile phase: Ultrapure water; Acetonitrile = 25: 75
Flow velocity: 0.6 mL / min
Reaction solution: None Detection method: RI (differential refractive index)
Temperature: 30 ° C.
 [フラン系・芳香族系化合物の濃度の測定方法]
 糖液に含まれるフラン系化合物(HMF、フルフラール)およびフェノール系化合物(バニリンなど)の濃度は、以下に示す条件でHPLCにより分析し、標品との比較により定量した。
カラム:Synergi HidroRP 4.6mm×250mm(Phenomenex製)
移動相:アセトニトリル-0.1%HPO(流速1.0mL/min)検出方法:UV(283nm)
温度:40℃。
[Method for measuring the concentration of furan / aromatic compounds]
The concentrations of furan compounds (HMF, furfural) and phenol compounds (vanillin, etc.) contained in the sugar solution were analyzed by HPLC under the conditions shown below and quantified by comparison with the standard.
Column: Synergy HydroRP 4.6 mm x 250 mm (manufactured by Phenomenex)
Mobile phase: Acetonitrile-0.1% H 3 PO 4 (flow velocity 1.0 mL / min) Detection method: UV (283 nm)
Temperature: 40 ° C.
 [有機酸の濃度の測定方法]
 糖液に含まれる有機酸(酢酸、ギ酸)は、以下に示す条件でHPLCにより分析し、標品との比較により定量した。
カラム:Shim-Pack SPR-HとShim-Pack SCR101H(株式会社島津製作所製)の直列
移動相:5mM p-トルエンスルホン酸(流速0.8mL/min)
反応液:5mM p-トルエンスルホン酸、20mM ビストリス、0.1mM EDTA・2Na(流速0.8mL/min)
検出方法:電気伝導度
温度:45℃。
[Measurement method of organic acid concentration]
The organic acids (acetic acid, formic acid) contained in the sugar solution were analyzed by HPLC under the conditions shown below and quantified by comparison with the standard.
Column: Series mobile phase of Sim-Pack SPR-H and Sim-Pack SCR101H (manufactured by Shimadzu Corporation): 5 mM p-toluenesulfonic acid (flow velocity 0.8 mL / min)
Reaction solution: 5 mM p-toluenesulfonic acid, 20 mM bis tris, 0.1 mM EDTA · 2Na (flow rate 0.8 mL / min)
Detection method: Electrical conductivity Temperature: 45 ° C.
 [含水率の測定方法]
 以下の実験で用いるセルロース含有バイオマス、前処理バイオマス、セルロース含有固形分の含水率を測定した。含水率(重量%;以下、単に%にて示す)は、赤外線水分計(“FD-720”、ケット科学研究所製)を使用して、試料を120℃の温度に保持し、蒸発後の安定値と初期値との差分から得られる値である含水率を測定した。
[Measurement method of water content]
The water content of cellulose-containing biomass, pretreated biomass, and cellulose-containing solids used in the following experiments was measured. The water content (% by weight; hereinafter simply indicated by%) is determined by holding the sample at a temperature of 120 ° C. using an infrared moisture meter (“FD-720”, manufactured by Kett Scientific Research Institute) and after evaporation. The water content, which is a value obtained from the difference between the stable value and the initial value, was measured.
 参考までに本方法で測定した各種セルロース含有バイオマスの含水率を表1に示す。バガス、稲わら、油椰子空果房は草本系バイオマスに分類される。 For reference, Table 1 shows the water content of various cellulose-containing biomass measured by this method. Bagasse, rice straw, and oil palm empty fruit bunches are classified as herbaceous biomass.
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000001
 [アルカリ反応量の計算方法]
 アルカリ反応量の計算方法については、例えば含水率x(%)のセルロース含有バイオマス原料a(g)に対して、y(%)の水酸化ナトリウム水溶液b(g)を添加して反応する場合、アルカリの反応量(単位:mg/g-dryバイオマス)を以下の式1で計算した。
[Calculation method of alkali reaction amount]
Regarding the calculation method of the alkali reaction amount, for example, when a reaction is carried out by adding y (%) sodium hydroxide aqueous solution b (g) to cellulose-containing biomass raw material a (g) having a water content of x (%). The reaction amount of alkali (unit: mg / g-dry biomass) was calculated by the following formula 1.
 アルカリ反応量=y×b×1000/{(100-x)×a}・・・(式1)。 Alkaline reaction amount = y × b × 1000 / {(100-x) × a} ... (Equation 1).
 比較参考例1:水熱処理時のバガス粉砕度とセルロース含有固形分含水率の関係
 工程(1)として、含水率50%のバガスをカッターミル(奈良機械製作所株式会社製、バリオニクスBRX-400)を使用しバガスを粉砕した。粉砕条件は、カッターミルのスクリーン孔径を30mmと設定し、回転速度600rpm、供給速度1000kg/hrで供給しながら粉砕を行った。粉砕バイオマスを乾燥重量割合測定のため含水率20%に乾燥させ、ISO 2591-1の条件で目開き1mmのふるいにかけ、通過しない重量割合を測定したところ45%であった。
Comparative Reference Example 1: Relationship between the degree of bagasse crushing during hydrothermal treatment and the moisture content of cellulose-containing solids As step (1), use a cutter mill (Varionics BRX-400, manufactured by Nara Kikai Seisakusho Co., Ltd.) for bagasse with a moisture content of 50%. Used and crushed bagasse. As the crushing conditions, the screen hole diameter of the cutter mill was set to 30 mm, and crushing was performed while supplying at a rotation speed of 600 rpm and a supply speed of 1000 kg / hr. The crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with a 1 mm opening under the conditions of ISO 2591-1, and the weight ratio that did not pass was measured and found to be 45%.
 工程(2)として、粉砕後(含水率50%)のバガスを高圧で180℃、固形分5%で10分水熱処理を行った。得られた前処理バガスを目開き3mmのステンレス製ザル(開口率:30%)で濾過し、ザルの上面に残った固形分(前処理バイオマス)をザル面に対し手で押え付け絞った。得られた前処理バイオマスの含水率は90%であった。 As step (2), bagasse after crushing (moisture content 50%) was hydrothermally treated at 180 ° C. at high pressure for 10 minutes at a solid content of 5%. The obtained pretreated bagasse was filtered through a stainless steel colander (opening ratio: 30%) having an opening of 3 mm, and the solid content (pretreated biomass) remaining on the upper surface of the colander was manually pressed against the colander surface and squeezed. The water content of the obtained pretreated biomass was 90%.
 工程(3)として、前処理バイオマスに水を固形分(乾燥重量)の1.6倍量添加し、水を添加した前処理バイオマスをラボ用小型スクリュープレス(富国工業株式会社製HX100、周波数10Hz)で固液分離した。固液分離後のセルロース含有固形分の含水率を測定したところ、含水率は75%であった。結果を表2に示す。 As step (3), water is added to the pretreated biomass in an amount 1.6 times the solid content (dry weight), and the pretreated biomass to which water is added is applied to a small screw press for a laboratory (HX100 manufactured by Toguni Kogyo Co., Ltd., frequency 10 Hz). ) Was separated into solid and liquid. When the water content of the cellulose-containing solid content after solid-liquid separation was measured, the water content was 75%. The results are shown in Table 2.
 比較参考例2:水熱処理時のバガス粉砕度とセルロース含有固形分含水率の関係
 粉砕条件としてカッターミルのスクリーン孔径を40mmとする以外は、比較例1と同様の条件で実施した。また、粉砕バイオマスを乾燥重量割合測定のため含水率20%に乾燥させ、ISO 2591-1の条件で目開き1mmのふるいにかけ、通過しない重量割合を測定したところ50%であった。また固液分離後のセルロース含有固形分の含水率は73%であった。結果を表2に示す。
Comparative Reference Example 2: Relationship between the degree of bagasse pulverization during hydrothermal treatment and the moisture content of cellulose-containing solids The pulverization was carried out under the same conditions as in Comparative Example 1 except that the screen hole diameter of the cutter mill was 40 mm. Further, the crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with a mesh opening of 1 mm under the condition of ISO 2591-1, and the weight ratio of not passing was measured and found to be 50%. The water content of the cellulose-containing solid content after solid-liquid separation was 73%. The results are shown in Table 2.
 比較参考例3:水熱処理時のバガス粉砕度とセルロース含有固形分含水率の関係
 粉砕条件をカッターミルのスクリーン孔径を50mmとする以外は、比較例1と同様の条件で実施した。また、粉砕バイオマスを乾燥重量割合測定のため含水率20%に乾燥させ、ISO 2591-1の条件で目開き1mmのふるいにかけ、通過しない重量割合を測定したところ55%であった。また固液分離後のセルロース含有固形分の含水率は70%であった。結果を表2に示す。
Comparative Reference Example 3: Relationship between the degree of bagasse pulverization during hydrothermal treatment and the moisture content of cellulose-containing solids The pulverization conditions were the same as those of Comparative Example 1 except that the screen hole diameter of the cutter mill was 50 mm. Further, the crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with an opening of 1 mm under the condition of ISO 2591-1, and the weight ratio of not passing was measured and found to be 55%. The water content of the cellulose-containing solid content after solid-liquid separation was 70%. The results are shown in Table 2.
 比較参考例4:アルカリ処理時のバガス粉砕度とセルロース含有固形分含水率の関係
 工程(1)として、粉砕条件をカッターミルのスクリーン孔径を50mmとする以外は比較例3と同じ粉砕条件で粉砕を行った。粉砕バイオマスを乾燥重量割合測定のため含水率20%に乾燥させ、ISO 2591-1の条件で目開き1mmのふるいにかけ、通過しない重量割合を測定したところ55%であった。
Comparative Reference Example 4: Relationship between the degree of bagasse pulverization during alkaline treatment and the moisture content of cellulose-containing solids As step (1), pulverization was performed under the same pulverization conditions as in Comparative Example 3 except that the screen pore diameter of the cutter mill was 50 mm. Was done. The crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with a 1 mm opening under the conditions of ISO 2591-1, and the weight ratio that did not pass was measured and found to be 55%.
 工程(2)として、得られた粉砕バガス(含水率50%)を多機能抽出機(イズミフードマシナリ社製)に5.0kg投入し、上記多機能抽出機のタンク上部のスプレーボールから所定濃度の水酸化ナトリウム水溶液45kg(初期温度:90℃、pHは約13付近)を添加し、タンク内に付設された濾過網から自重濾過で得られた液(アルカリ性濾液)を再度スプレーボールから入れることを繰り返した。なお、濾過網から上部のスプレーボールの間に加温する機構を設けて温度を監視しながら反応を所定時間行った。反応中は、アルカリ性濾液が90℃から低下しないように調整した。また、上記多機能抽出機に付設されている攪拌羽根は使用せず、バガスおよびセルロース含有固形分は濾過網上に置き、攪拌羽根などで形状を整えたり、スラリー化する動作は行わなかった。アルカリ性濾液を所定の反応時間として循環しつづけた。得られたサンプルを目開き3mmのステンレス製ザル(開口率:30%)でさらに濾過し、ザルの上面に残った固形分(前処理バイオマス)をザル面に対し手で押え付け絞った。得られた前処理バイオマスの含水率は90%であった。 As step (2), 5.0 kg of the obtained crushed bagus (water content 50%) was put into a multifunctional extractor (manufactured by Izumi Food Machinery Co., Ltd.), and a predetermined concentration was obtained from a spray ball at the top of the tank of the multifunctional extractor. Add 45 kg of the sodium hydroxide aqueous solution (initial temperature: 90 ° C., pH is about 13), and refill the liquid (alkaline filtrate) obtained by self-weight filtration from the filtration net provided in the tank from the spray ball. Was repeated. The reaction was carried out for a predetermined time while monitoring the temperature by providing a mechanism for heating between the filtration net and the upper spray ball. During the reaction, the alkaline filtrate was adjusted so as not to drop from 90 ° C. Further, the stirring blade attached to the multifunctional extractor was not used, the bagasse and the cellulose-containing solids were placed on the filtration net, and the shape was adjusted by the stirring blade or the like, or the operation of making a slurry was not performed. The alkaline filtrate was continuously circulated for a predetermined reaction time. The obtained sample was further filtered through a stainless steel colander with a mesh opening of 3 mm (opening ratio: 30%), and the solid content (pretreated biomass) remaining on the upper surface of the colander was manually pressed against the colander surface and squeezed. The water content of the obtained pretreated biomass was 90%.
 工程(3)として、前処理バイオマスに水を固形分(乾燥重量)の1.6倍量添加し、前処理バイオマスをラボ用小型スクリュープレスで固液分離した。固液分離後のセルロース含有固形分の含水率を測定したところ、含水率は75%であった。結果を表2に示す。 As step (3), water was added to the pretreated biomass in an amount 1.6 times the solid content (dry weight), and the pretreated biomass was solid-liquid separated by a small laboratory screw press. When the water content of the cellulose-containing solid content after solid-liquid separation was measured, the water content was 75%. The results are shown in Table 2.
 参考例1:アルカリ処理時のバガス粉砕度とセルロース含有固形分含水率の関係
 粉砕条件をカッターミルのスクリーン孔径を40mmとする以外は、比較参考例4と同様の条件で実施した。また、粉砕バイオマスを乾燥重量割合測定のため含水率20%に乾燥させ、ISO 2591-1の条件で目開き1mmのふるいにかけ、通過しない重量割合を測定したところ50%であった。また、固液分離後のセルロース含有固形分の含水率は64%であった。結果を表2に示す。
Reference Example 1: Relationship between the degree of bagasse pulverization during alkaline treatment and the water content of cellulose-containing solids The pulverization conditions were the same as those of Comparative Reference Example 4 except that the screen hole diameter of the cutter mill was 40 mm. Further, the crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with a mesh opening of 1 mm under the condition of ISO 2591-1, and the weight ratio of not passing was measured and found to be 50%. The water content of the cellulose-containing solid content after solid-liquid separation was 64%. The results are shown in Table 2.
 参考例2:アルカリ処理時のバガス粉砕度とセルロース含有固形分含水率の関係
 粉砕条件をカッターミルのスクリーン孔径を30mmとする以外は、比較参考例4と同様の条件で実施した。また、粉砕バイオマスを乾燥重量割合測定のため含水率20%に乾燥させ、ISO 2591-1の条件で目開き1mmのふるいにかけ、重量割合を測定したところ45%であった。また、固液分離後のセルロース含有固形分の含水率は60%であった。結果を表2に示す。
Reference Example 2: Relationship between the degree of bagasse pulverization during alkaline treatment and the water content of cellulose-containing solids The pulverization conditions were the same as those of Comparative Reference Example 4 except that the screen hole diameter of the cutter mill was 30 mm. Further, the crushed biomass was dried to a moisture content of 20% for measuring the dry weight ratio, sieved with an opening of 1 mm under the condition of ISO 2591-1, and the weight ratio was measured and found to be 45%. The water content of the cellulose-containing solid content after solid-liquid separation was 60%. The results are shown in Table 2.
Figure JPOXMLDOC01-appb-T000002
Figure JPOXMLDOC01-appb-T000002
 表1から分かるとおり、前処理が水熱処理である場合、粉砕バイオマスの目開き1mmのふるいで通過しない割合(乾燥重量%)が低下する(粉砕度が高まる)につれて、固液分離後のセルロース含有固形分含水率(%)が高まり、粉体がスラリー化した排水の処理では粉体の粉砕度が高い程、脱水しにくいという当業者に周知の情報(J.Soc.Powder Technol.,Japan,38,177-183(2001)の表2参照。)と一致する結果であった。一方、前処理がアルカリ処理である場合は、粉砕バイオマスの目開き1mmのふるいで通過しない割合(乾燥重量%)が低下する(粉砕度が高まる)につれて、当業者に周知の情報に反して固液分離後のセルロース含有固形分含水率(%)が低下し、粉砕バイオマスの粉砕度を高めることにより、後段の加水分解で糖液を製造する際に混入する前処理由来の発酵阻害物質を低減できる可能性が見いだされた。 As can be seen from Table 1, when the pretreatment is hydrothermal treatment, the content of cellulose after solid-liquid separation decreases as the proportion of crushed biomass that does not pass through a sieve with a mesh size of 1 mm (dry weight%) decreases (the degree of crushing increases). Information well known to those skilled in the art that the higher the degree of crushing of the powder, the more difficult it is to dehydrate in the treatment of wastewater in which the solid content moisture content (%) is increased and the powder is made into a slurry (J. Soc Power Technology, Japan, Japan, The results were in agreement with Table 2 of 38,177-183 (2001). On the other hand, when the pretreatment is an alkaline treatment, as the proportion of the crushed biomass that does not pass through the sieve with a mesh size of 1 mm (dry weight%) decreases (the degree of crushing increases), it is hardened contrary to the information well known to those skilled in the art. The moisture content (%) of the cellulose-containing solid content after liquid separation is reduced, and the degree of crushing of the crushed biomass is increased to reduce the fermentation inhibitor derived from the pretreatment that is mixed in when the sugar solution is produced by the subsequent hydrolysis. The possibility of being able to do it was found.
 比較例1:バガスからの糖液の製造例(工程(1)および(3)未実施)
 比較参考例4と同じ粉砕条件、前処理条件を実施し、前処理バイオマスを得た。得られた前処理バイオマスは工程(3)である水を添加・固液分離に供さず、工程(4)として乾燥ベースの固形分濃度が5%、pHが5.0になるように純水および35%塩酸を添加して、セルロース含有固形分を含んだスラリー液を作成した。得られたスラリー液500mLに、ダニスコ・ジャパン株式会社製の酵素である“アクセルレース・デュエット”5mLを添加し、スラリー温度を50℃に維持して常時攪拌を行って8時間反応を行った。得られた反応液の糖、酢酸、芳香族化合物濃度を測定し、得られたグルコース100gに対する酢酸、クマル酸重量を求めた結果を表3に示す。
Comparative Example 1: Production example of sugar solution from bagasse (steps (1) and (3) not performed)
The same pulverization conditions and pretreatment conditions as in Comparative Reference Example 4 were carried out to obtain pretreated biomass. The obtained pretreated biomass was not subjected to the addition of water and solid-liquid separation in step (3), and was pure so that the solid content concentration of the dry base was 5% and the pH was 5.0 in step (4). Water and 35% hydrochloric acid were added to prepare a slurry liquid containing a cellulose-containing solid content. To 500 mL of the obtained slurry liquid, 5 mL of "Axel Race Duet", an enzyme manufactured by Danisco Japan Co., Ltd., was added, and the slurry temperature was maintained at 50 ° C., and the mixture was constantly stirred and reacted for 8 hours. Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the obtained reaction solution and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
 比較例2:バガスからの糖液の製造例(工程(1)未実施)
 比較参考例4と同じ粉砕条件、前処理条件、水添加・固液分離条件を実施した。固液分離後のセルロース含有固形分を用いて、工程(4)として比較例1と同様の加水分解操作を実施した。得られた反応液の糖、酢酸、芳香族化合物濃度を測定し、得られたグルコース100gに対する酢酸、クマル酸重量を求めた結果を表3に示す。
Comparative Example 2: Production Example of Sugar Solution from Bagasse (Step (1) Not Implemented)
The same pulverization conditions, pretreatment conditions, and water addition / solid-liquid separation conditions as in Comparative Reference Example 4 were carried out. Using the cellulose-containing solid content after solid-liquid separation, the same hydrolysis operation as in Comparative Example 1 was carried out as step (4). Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the obtained reaction solution and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
 比較例3:バガスからの糖液の製造例(工程(3)未実施)
 粉砕条件をカッターミルのスクリーン孔径を40mmとし、前処理バイオマスに水を添加せずに固液分離した以外は比較参考例4と同様の操作を実施した。得られた固液分離後のセルロース含有固形分を用いて、工程(4)として比較例1と同様の加水分解操作を実施した。得られた反応液の糖、酢酸、芳香族化合物濃度を測定し、得られたグルコース100gに対する酢酸、クマル酸重量を求めた結果を表3に示す。
Comparative Example 3: Production Example of Sugar Solution from Bagasse (Step (3) Not Implemented)
The crushing conditions were such that the screen hole diameter of the cutter mill was 40 mm, and the same operation as in Comparative Reference Example 4 was carried out except that solid-liquid separation was performed without adding water to the pretreated biomass. Using the obtained cellulose-containing solid content after solid-liquid separation, the same hydrolysis operation as in Comparative Example 1 was carried out as step (4). Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the obtained reaction solution and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
 実施例1:バガスからの糖液の製造例(工程(1)~(4)実施)
 参考例1で得られた固液分離後のセルロース含有固形分を用いて、工程(4)として比較例1と同様の加水分解操作を実施した。得られた反応液の糖、酢酸、芳香族化合物濃度を測定し、得られたグルコース100gに対する酢酸、クマル酸重量を求めた結果を表3に示す。
Example 1: Production example of sugar solution from bagasse (implementation of steps (1) to (4))
Using the cellulose-containing solid content after solid-liquid separation obtained in Reference Example 1, the same hydrolysis operation as in Comparative Example 1 was carried out as step (4). Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the obtained reaction solution and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
 実施例2:バガスからの糖液の製造例(工程(1)~(4)実施)
 参考例2で得られた固液分離後のセルロース含有固形分を用いて、工程(4)として比較例1と同様の加水分解操作を実施した。得られた反応液の糖、酢酸、芳香族化合物濃度を測定し、得られたグルコース100gに対する酢酸、クマル酸重量を求めた結果を表3に示す。
Example 2: Production example of sugar solution from bagasse (implementation of steps (1) to (4))
Using the cellulose-containing solid content after solid-liquid separation obtained in Reference Example 2, the same hydrolysis operation as in Comparative Example 1 was carried out as step (4). Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the obtained reaction solution and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
 実施例3:バガスからの糖液の製造例(工程(1)~(5)実施)
 実施例1で得られた工程(4)の加水分解後の糖液を、遠心分離(斎藤遠心機工業株式会社製、2,000rpm)により固液分離後、精密濾過膜(ミリポア社製、細孔径0.05μmPVDF膜)を使用して濾過を行った後、逆浸透膜(東レ株式会社製、架橋全芳香族ポリアミド系逆浸透膜UTC80)に通じて濃縮液として糖液を回収し、原水の4分の1にまで濃縮されるように透過液として水を回収した。
Example 3: Production example of sugar solution from bagasse (implementation of steps (1) to (5))
The sugar solution after hydrolysis in the step (4) obtained in Example 1 is solid-liquid separated by centrifugation (manufactured by Saito Centrifuge Industry Co., Ltd., 2,000 rpm), and then microfiltered membrane (manufactured by Millipore). After filtration using a pore diameter of 0.05 μm PVDF membrane), the sugar solution is recovered as a concentrated solution through a reverse osmosis membrane (cross-linked total aromatic polyamide reverse osmosis membrane UTC80 manufactured by Toray Co., Ltd.), and raw water is collected. Water was recovered as a permeate so that it was concentrated to a quarter.
 再度、実施例1と同様の条件で工程(1)~(4)までを実施し、工程(3)での水の添加は前記逆浸透膜の透過液として回収した水を使用した(工程(5))。工程(4)として得られた糖液の糖、酢酸、芳香族化合物濃度を測定し、得られたグルコース100gに対する酢酸、クマル酸重量を求めた結果を表3に示す。 Steps (1) to (4) were carried out again under the same conditions as in Example 1, and water recovered in step (3) was added as the permeate of the reverse osmosis membrane (step (step (step)). 5)). Table 3 shows the results of measuring the sugar, acetic acid, and aromatic compound concentrations of the sugar solution obtained in step (4) and determining the weights of acetic acid and coumaric acid with respect to 100 g of the obtained glucose.
Figure JPOXMLDOC01-appb-T000003
Figure JPOXMLDOC01-appb-T000003
 表3から分かるとおり、工程(1)~(4)の全てを実施していない比較例1~3に比べて、実施例1~3ではグルコースに対する酢酸、クマル酸重量が相対的に低減された。特に、比較例2ならびに実施例1および2の比較結果から、粉体バイオマスの粉砕度として目開き1mmのふるいで通過しない重量割合(乾燥重量%)が50%を超えると、糖液中の発酵阻害物質の濃度が高まってしまうことが明らかになった。また、実施例1と3の結果より、工程(5)を実施することで糖液中のクマル酸濃度がより低減されることが明らかになった。 As can be seen from Table 3, the weights of acetic acid and coumaric acid relative to glucose were relatively reduced in Examples 1 to 3 as compared with Comparative Examples 1 to 3 in which all of steps (1) to (4) were not performed. .. In particular, from the comparative results of Comparative Example 2 and Examples 1 and 2, when the weight ratio (dry weight%) of the powdery biomass that does not pass through the sieve with an opening of 1 mm exceeds 50%, fermentation in the sugar solution It became clear that the concentration of the inhibitor increased. Further, from the results of Examples 1 and 3, it was clarified that the coumaric acid concentration in the sugar solution was further reduced by carrying out the step (5).

Claims (10)

  1.  セルロース含有バイオマスを原料とする糖液の製造方法であって、
    工程(1):目開き1mmのふるいで通過しない重量割合が乾燥重量で50%以下になるようにセルロース含有バイオマスを粉砕する工程、
    工程(2):工程(1)で得られた粉砕バイオマスをアルカリ性水性媒体に接触させて前処理バイオマスを得る工程、
    工程(3):工程(2)で得られた前処理バイオマスに水を添加して固液分離し、セルロース含有固形分を得る工程、および
    工程(4):工程(3)で得られたセルロース含有固形分を加水分解して糖液を得る工程、
    を含む、方法。
    A method for producing a sugar solution using cellulose-containing biomass as a raw material.
    Step (1): A step of crushing cellulose-containing biomass so that the weight ratio that does not pass through a sieve having a mesh size of 1 mm is 50% or less in terms of dry weight.
    Step (2): A step of contacting the crushed biomass obtained in the step (1) with an alkaline aqueous medium to obtain a pretreated biomass.
    Step (3): Water is added to the pretreated biomass obtained in step (2) and solid-liquid separation is performed to obtain a cellulose-containing solid content, and step (4): cellulose obtained in step (3). The process of hydrolyzing the contained solids to obtain a sugar solution,
    Including methods.
  2.  前記工程(2)が、前記工程(1)で得られた粉砕バイオマスにアルカリ性媒体を通液させて前処理バイオマスを得る工程である、請求項1に記載の糖液の製造方法。 The method for producing a sugar solution according to claim 1, wherein the step (2) is a step of passing an alkaline medium through the crushed biomass obtained in the step (1) to obtain pretreated biomass.
  3.  前記工程(2)が、前記工程(1)で得られた粉砕バイオマスとアルカリ性媒体を濾過器に供給し、該濾過器を用いて粉砕バイオマスとアルカリ性媒体を通液させる工程である、請求項1または2に記載の糖液の製造方法。 The step (2) is a step of supplying the crushed biomass and the alkaline medium obtained in the step (1) to a filter and passing the crushed biomass and the alkaline medium through the filter using the filter. Alternatively, the method for producing a sugar solution according to 2.
  4.  前記工程(2)のアルカリ性水性媒体が水酸化ナトリウムおよび/または水酸化カリウムを含む水性媒体である、請求項1~3のいずれかに記載の糖液の製造方法。 The method for producing a sugar solution according to any one of claims 1 to 3, wherein the alkaline aqueous medium of the step (2) is an aqueous medium containing sodium hydroxide and / or potassium hydroxide.
  5.  前記工程(3)の固液分離が圧搾である、請求項1~4のいずれかに記載の糖液の製造方法。 The method for producing a sugar solution according to any one of claims 1 to 4, wherein the solid-liquid separation in the step (3) is pressing.
  6.  前記セルロース含有バイオマスがバガスである、請求項1~5のいずれかに記載の糖液の製造方法。 The method for producing a sugar solution according to any one of claims 1 to 5, wherein the cellulose-containing biomass is bagasse.
  7.  工程(5):工程(4)で得られた糖液をナノ濾過膜または逆浸透膜に通じて濾過し、非透過液として糖液を回収し、透過液を工程(3)で前処理バイオマスに添加する水に再利用する工程、
    をさらに含む、請求項1~6のいずれかに記載の糖液の製造方法。
    Step (5): The sugar solution obtained in step (4) is filtered through a nanofiltration membrane or a reverse osmosis membrane, the sugar solution is recovered as a non-permeable solution, and the permeated solution is pretreated biomass in step (3). The process of reusing water to be added to
    The method for producing a sugar solution according to any one of claims 1 to 6, further comprising.
  8.  目開き1mmのふるいで通過しない重量割合が乾燥重量で50%以下の粉砕セルロース含有バイオマスおよびアルカリ性水性媒体を含有し、含水率が50重量%以上70重量%未満である、セルロース含有固形分。 Cellulose-containing solid content containing crushed cellulose-containing biomass and an alkaline aqueous medium having a dry weight of 50% or less that does not pass through a sieve having an opening of 1 mm and having a water content of 50% by weight or more and less than 70% by weight.
  9.  前記セルロース含有バイオマスがバガスである、請求項8に記載のセルロース含有固形分。 The cellulose-containing solid content according to claim 8, wherein the cellulose-containing biomass is bagasse.
  10.  目開き1mmのふるいで通過しない重量割合が乾燥重量で40~50%である、粉砕セルロース含有バイオマス。 Biomass containing crushed cellulose having a dry weight of 40 to 50% that does not pass through a sieve with a 1 mm opening.
PCT/JP2021/002757 2020-01-28 2021-01-27 Production method for sugar solution WO2021153585A1 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
CN202180011274.9A CN115023507A (en) 2020-01-28 2021-01-27 Method for producing sugar solution
JP2021509936A JPWO2021153585A1 (en) 2020-01-28 2021-01-27

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP2020-011657 2020-01-28
JP2020011657 2020-01-28

Publications (1)

Publication Number Publication Date
WO2021153585A1 true WO2021153585A1 (en) 2021-08-05

Family

ID=77079036

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/JP2021/002757 WO2021153585A1 (en) 2020-01-28 2021-01-27 Production method for sugar solution

Country Status (3)

Country Link
JP (1) JPWO2021153585A1 (en)
CN (1) CN115023507A (en)
WO (1) WO2021153585A1 (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010220512A (en) * 2009-03-23 2010-10-07 Jfe Engineering Corp Pretreatment method for enzymic hydrolysis treatment of herbaceous biomass, and method for producing ethanol by using herbaceous biomass as raw material
JP2012029567A (en) * 2010-07-28 2012-02-16 Taisei Corp Method for saccharifying wood-based biomass
JP2013220067A (en) * 2012-04-17 2013-10-28 National Agriculture & Food Research Organization Enzymatic saccharification method for cellulosic biomass raw material
JP5425348B1 (en) * 2012-03-29 2014-02-26 三菱重工メカトロシステムズ株式会社 Biomass processing system, sugar liquid production method using biomass raw material, alcohol production method
WO2017170552A1 (en) * 2016-03-29 2017-10-05 東レ株式会社 Method for producing sugar liquor

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
BR112016003282B8 (en) * 2013-08-22 2022-04-05 Toray Industries Methods of producing a sugar liquid and a chemical substance
EP3088530B1 (en) * 2013-12-27 2020-04-29 Toray Industries, Inc. Method for producing sugar solution

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010220512A (en) * 2009-03-23 2010-10-07 Jfe Engineering Corp Pretreatment method for enzymic hydrolysis treatment of herbaceous biomass, and method for producing ethanol by using herbaceous biomass as raw material
JP2012029567A (en) * 2010-07-28 2012-02-16 Taisei Corp Method for saccharifying wood-based biomass
JP5425348B1 (en) * 2012-03-29 2014-02-26 三菱重工メカトロシステムズ株式会社 Biomass processing system, sugar liquid production method using biomass raw material, alcohol production method
JP2013220067A (en) * 2012-04-17 2013-10-28 National Agriculture & Food Research Organization Enzymatic saccharification method for cellulosic biomass raw material
WO2017170552A1 (en) * 2016-03-29 2017-10-05 東レ株式会社 Method for producing sugar liquor

Also Published As

Publication number Publication date
JPWO2021153585A1 (en) 2021-08-05
CN115023507A (en) 2022-09-06

Similar Documents

Publication Publication Date Title
JP4928254B2 (en) Method for saccharification of cellulose-containing materials
JP6007791B2 (en) Method for producing sugar solution
JP6167902B2 (en) Method for producing sugar solution
WO2012019305A1 (en) Method for dilute acid pretreatment of l1gnocellulosic feedstocks
EP3242871A1 (en) Methods for extracting and converting hemicellulose sugars
WO2013122051A1 (en) Method for producing sugar solution, sugar solution, and method for producing ethanol
WO2012019306A1 (en) Recycle of leachate during lignocellulosic conversion processes
WO2021153585A1 (en) Production method for sugar solution
EP1879462B1 (en) Process for preparing a soluble non-caloric fiber composition
AU2017244707B2 (en) Method for producing sugar liquor
WO2014012017A2 (en) Two-loop dilute preprocessing and pretreatment of cellulosic feedstocks
EP2828392A2 (en) Process for the production of organic compounds from plant species
JP6036498B2 (en) Method for producing ethanol from lignocellulosic material
US20150337402A1 (en) Plant-biomass hydrolysis method
CA2998282C (en) Self-sufficient process for the production of biomass hydrolysate with reduced salt content
WO2011125992A1 (en) Method for treating plant biomass, method for producing saccharide from plant biomass, and method for producing alcohol and/or organic acid from plant biomass
JP6331490B2 (en) Method for producing ethanol from lignocellulose-containing biomass
JP6123504B2 (en) Ethanol production method
JPWO2021153585A5 (en)
WO2014024989A1 (en) Method for producing coumaramide
JP6375645B2 (en) Ethanol production method from lignocellulose
JP2013247924A (en) Method for preprocessing biomass containing lignocellulose

Legal Events

Date Code Title Description
ENP Entry into the national phase

Ref document number: 2021509936

Country of ref document: JP

Kind code of ref document: A

121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 21748372

Country of ref document: EP

Kind code of ref document: A1

NENP Non-entry into the national phase

Ref country code: DE

122 Ep: pct application non-entry in european phase

Ref document number: 21748372

Country of ref document: EP

Kind code of ref document: A1