JP2024519526A - Bioenzymatic pretreatment to control the physical and chemical properties of wheat grass waste granular fuel - Google Patents
Bioenzymatic pretreatment to control the physical and chemical properties of wheat grass waste granular fuel Download PDFInfo
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- 239000002699 waste material Substances 0.000 title claims abstract description 122
- 241001668545 Pascopyrum Species 0.000 title claims abstract description 94
- 239000000446 fuel Substances 0.000 title claims abstract description 53
- 239000000126 substance Substances 0.000 title claims abstract description 10
- 108090000790 Enzymes Proteins 0.000 claims abstract description 37
- 102000004190 Enzymes Human genes 0.000 claims abstract description 37
- 238000000034 method Methods 0.000 claims abstract description 27
- 238000004519 manufacturing process Methods 0.000 claims abstract description 25
- 239000000203 mixture Substances 0.000 claims abstract description 22
- 239000002910 solid waste Substances 0.000 claims abstract description 13
- 238000001035 drying Methods 0.000 claims abstract description 5
- 238000002156 mixing Methods 0.000 claims abstract description 5
- 238000010438 heat treatment Methods 0.000 claims abstract description 4
- 229940088598 enzyme Drugs 0.000 claims description 33
- 239000007788 liquid Substances 0.000 claims description 19
- 108010059892 Cellulase Proteins 0.000 claims description 14
- 101710121765 Endo-1,4-beta-xylanase Proteins 0.000 claims description 14
- 229940106157 cellulase Drugs 0.000 claims description 14
- 102000004882 Lipase Human genes 0.000 claims description 11
- 108090001060 Lipase Proteins 0.000 claims description 11
- 239000004367 Lipase Substances 0.000 claims description 11
- 235000019421 lipase Nutrition 0.000 claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 11
- 239000002245 particle Substances 0.000 claims description 10
- 239000007853 buffer solution Substances 0.000 claims description 9
- 239000007787 solid Substances 0.000 claims description 9
- 238000007873 sieving Methods 0.000 claims description 6
- 238000003756 stirring Methods 0.000 claims description 6
- 239000008187 granular material Substances 0.000 claims description 4
- 244000025254 Cannabis sativa Species 0.000 claims description 3
- 235000013339 cereals Nutrition 0.000 claims 1
- 238000001125 extrusion Methods 0.000 claims 1
- 239000000463 material Substances 0.000 abstract description 7
- 239000002351 wastewater Substances 0.000 abstract description 3
- 238000002360 preparation method Methods 0.000 description 14
- 230000006835 compression Effects 0.000 description 9
- 238000007906 compression Methods 0.000 description 9
- 238000005259 measurement Methods 0.000 description 9
- 238000000465 moulding Methods 0.000 description 9
- 238000012360 testing method Methods 0.000 description 8
- 238000004537 pulping Methods 0.000 description 6
- 230000000052 comparative effect Effects 0.000 description 5
- 239000002028 Biomass Substances 0.000 description 4
- 239000000835 fiber Substances 0.000 description 3
- 229920005610 lignin Polymers 0.000 description 3
- 230000008569 process Effects 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 230000008901 benefit Effects 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 239000008367 deionised water Substances 0.000 description 2
- 229910021641 deionized water Inorganic materials 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 229920002488 Hemicellulose Polymers 0.000 description 1
- 238000002835 absorbance Methods 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
- 239000002154 agricultural waste Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 230000001413 cellular effect Effects 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 230000001143 conditioned effect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 239000005446 dissolved organic matter Substances 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 150000004676 glycans Chemical class 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 238000000691 measurement method Methods 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 229920001282 polysaccharide Polymers 0.000 description 1
- 239000005017 polysaccharide Substances 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000009967 tasteless effect Effects 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
Classifications
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/40—Solid fuels essentially based on materials of non-mineral origin
- C10L5/44—Solid fuels essentially based on materials of non-mineral origin on vegetable substances
- C10L5/445—Agricultural waste, e.g. corn crops, grass clippings, nut shells or oil pressing residues
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
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- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Agronomy & Crop Science (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
- Processing Of Solid Wastes (AREA)
- Preparation Of Compounds By Using Micro-Organisms (AREA)
- Paper (AREA)
Abstract
本発明は、バイオベース材料の製造の分野に属する麦草廃棄物顆粒燃料の物理的および化学的性能の生物酵素による前処理調節方法に関する。前記製造方法は、麦草廃棄物に対して生物酵素前処理を実行し、乾燥させ、酵素前処理後の麦草廃棄物を得て、前記酵素前処理後の麦草廃棄物とパルプ製造廃液を均一に混合し、加熱して押し出して成型し、得ることを含む。本発明の製造方法は簡単で、操作に便利で、実用性が強く、環境に優しく、麦草廃棄物系顆粒燃料の物理的および化学的性能を改善し、現在のパルプ製造中における固形廃棄物と廃液の高価値に利用しにくいという問題を解決できる。【選択図】図1The present invention relates to a method for adjusting the physical and chemical properties of wheat grass waste granular fuel by biological enzyme pretreatment, which belongs to the field of bio-based material production. The method includes carrying out biological enzyme pretreatment on wheat grass waste, drying, obtaining enzyme pretreated wheat grass waste, uniformly mixing the enzyme pretreated wheat grass waste with pulp production wastewater, and heating and extruding the mixture to obtain. The method of the present invention is simple, convenient to operate, highly practical, and environmentally friendly, and can improve the physical and chemical properties of wheat grass waste granular fuel, and solve the problem of the current difficulty in utilizing solid waste and wastewater in high value during pulp production. [Selected Figure] Figure 1
Description
関連出願の相互参照
本出願は2022年4月11日に中国特許庁に提出され、出願番号CN202210373029.9、発明の名称「麦草廃棄物顆粒燃料の物理的および化学的性能の生物酵素による前処理調節方法」の中国特許出願の優先権を主張し、そのすべての内容は参照により本明細書に組み込まれる。
本発明は、バイオベース材料の製造の分野に属し、具体的には麦草廃棄物顆粒燃料の物理的および化学的性能の生物酵素による前処理調節方法に関する。
CROSS-REFERENCE TO RELATED APPLICATIONS This application claims priority to a Chinese patent application filed with the China Patent Office on April 11, 2022, with application number CN202210373029.9, entitled "Method for Pretreatment Adjustment of the Physical and Chemical Performance of Wheat Grass Waste Granule Fuel by Biological Enzymes", the entire contents of which are incorporated herein by reference.
The present invention is in the field of bio-based material production, specifically, a method for bioenzymatic pretreatment modulation of the physical and chemical properties of wheat grass waste granule fuel.
グローバルなエネルギー変換の重要な瞬間に、持続可能なグリーンクリーンエネルギーとしての農業廃棄物繊維原料は、持続可能な再生可能クリーンエネルギとして、研究者の注目の焦点になっている。麦草の備蓄量は膨大であるが、利用率は低く、開発と利用の大きな可能性がある。麦草は、パルプ化および製紙産業の繊維原料の1つであるが、麦草のパルプ製造は、材料準備からパルプになるプロセス全体中に、主に材料準備段階に生成された麦草廃棄物、前処理および磨砕プロセスに生成された廃液を含む一部の廃棄物及び廃液を生成する。固形廃棄物が収集された後、大量のスペースが占有され、前処理とパルプ製造中によって生成される廃液には、大量の溶存有機物が含まれ、これらはすべて、パルプ化および製紙企業の汚染物負荷になり、該部分の材料を最大限に活用して、バイオマス顆粒燃料に加工して製造すると、紙工場の固形廃棄物の蓄積と廃液の処理をしにくいという問題を効果的に改善することができる。したがって、これらの廃棄物及び廃液をどのように効果的に使用して、それを高付加価値のあるバイオマスエネルギー製品に変換することは、現在の草類のバイオマス繊維原料が製紙のために解決する必要がある技術的なボトルネックの1つである。 At the key moment of global energy transformation, agricultural waste fiber raw materials as a sustainable green clean energy have become the focus of researchers' attention as a sustainable renewable clean energy. Wheat grass reserves are huge, but the utilization rate is low, and there is great potential for development and utilization. Wheat grass is one of the fiber raw materials for the pulping and papermaking industry, but the pulp production of wheat grass generates some waste and waste liquid during the whole process from material preparation to pulp, mainly including wheat grass waste generated in the material preparation stage and waste liquid generated in the pretreatment and grinding process. After the solid waste is collected, a large amount of space is occupied, and the waste liquid generated during pretreatment and pulp production contains a large amount of dissolved organic matter, all of which become the pollutant load of pulping and papermaking enterprises. By making full use of the material of this part and processing it into biomass granular fuel for production, it can effectively improve the problem of the accumulation of solid waste and the difficulty of treating waste liquid in paper factories. Therefore, how to effectively use these waste materials and wastewater and convert them into high-value-added bioenergy products is one of the technical bottlenecks that the current grass biomass fiber feedstock needs to resolve for papermaking.
上記の問題を解決するために、本発明は、生物酵素調節により前処理された、麦草の生化学機械パルプ製造中に生成した固体残留物とパルプ製造中に生成した廃液を利用して顆粒燃料を製造する方法を提供する。麦草廃棄物を最初に生物酵素で前処理調節し、次に麦草のパルプ製造中に各段階に生成された廃液と、一定の質量比で混合し、加熱することにより、より良好に結合して成型させ、顆粒燃料を得る。 To solve the above problems, the present invention provides a method for producing granular fuel using solid residues generated during the biochemical-mechanical pulping of wheat grass, which have been pretreated by biological enzyme regulation, and waste liquid generated during the pulp production. Wheat grass waste is first pretreated and conditioned with biological enzymes, and then mixed with waste liquids generated at each stage during the pulp production of wheat grass in a certain mass ratio and heated to better bind and mold the mixture into granular fuel.
上記の技術的目的を達成するために、本発明は以下の技術的解決手段を採用する。 To achieve the above technical objectives, the present invention employs the following technical solutions:
本発明の第1の態様は、
麦草廃棄物に対して生物酵素前処理を実行し、乾燥させ、酵素前処理後の麦草廃棄物を得て、
前記酵素前処理後の麦草廃棄物とパルプ製造廃液を均一に混合し、加熱して押し出して成型し、麦草廃棄物顆粒燃料を得ることを含む麦草廃棄物顆粒燃料の物理的および化学的性能の生物酵素による前処理調節方法を提供する。
The first aspect of the present invention is a method for producing a cellular membrane comprising the steps of:
The wheat grass waste is subjected to biological enzyme pretreatment and dried to obtain enzyme pretreated wheat grass waste.
The enzyme-pretreated wheat grass waste and pulp manufacturing waste liquid are uniformly mixed, heated, extruded and molded to obtain wheat grass waste granular fuel. A method for pretreating and adjusting the physical and chemical properties of wheat grass waste granular fuel using a biological enzyme is also provided.
本発明は、生物酵素を使用して、麦草の化学機械的パルプ製造中に生成した固形廃棄物及び廃液の性能を前処理調節し、低コストで環境に優しい顆粒燃料を製造する。 The present invention uses biological enzymes to pre-treat and adjust the performance of solid waste and effluent generated during the chemical-mechanical pulping of wheat grass to produce low-cost, environmentally friendly granular fuel.
本発明の第2の態様は、いずれか一項の上記方法によって製造された麦草廃棄物顆粒燃料を提供する。 A second aspect of the present invention provides wheat grass waste granular fuel produced by any one of the above methods.
本発明の第3の態様は、クリーンエネルギの分野における上記麦草廃棄物顆粒燃料の使用を提供する。 A third aspect of the present invention provides a use of the wheat grass waste granular fuel in the field of clean energy.
本発明の有益な効果は以下のとおりである。
(1)本発明で使用されている麦草の生化学的機械パルプ製造中に生成される固形廃棄物麦草廃棄物及び廃液は、廃棄物の高付加価値の利用の利点を有する。
(2)本発明の顆粒燃料には、主にC、H、およびOの3つの要素が含まれ、燃焼によって生成されるガスは主にCO2であり、クリーン製品である。
(3)本発明の前処理に使用される生物酵素は、無毒無味で環境にやさしい。
(4)本発明の製造方法は簡単で実用的であり、経済的および環境的な利点が良好である。
The beneficial effects of the present invention are as follows:
(1) The solid waste wheat grass waste and waste liquid generated during the biochemical-mechanical pulping of wheat grass used in the present invention have the advantage of high added value utilization of waste.
(2) The granular fuel of the present invention mainly contains three elements: C, H, and O, and the gas produced by combustion is mainly CO2 , which is a clean product.
(3) The biological enzymes used in the pretreatment of the present invention are non-toxic, tasteless, and environmentally friendly.
(4) The manufacturing method of the present invention is simple and practical, and has good economic and environmental advantages.
本発明の一部を形成する添付の図面は、本発明のさらなる理解を提供するために使用され、本発明の例示的な実施例およびそれらの説明は、本発明を説明するために使用され、本発明の不適切な制限を構成するものではない。
以下の詳細な説明はすべて例示的なものであり、本発明のさらなる説明を提供することを意図していることに留意されたい。特に明記しない限り、本発明で使用されるすべての技術用語および科学用語は、当業者によって一般に理解されるのと同じ意味を有する。 Please note that the following detailed description is all exemplary and intended to provide further explanation of the present invention. Unless otherwise specified, all technical and scientific terms used in the present invention have the same meaning as commonly understood by those skilled in the art.
本発明の1番目の目的は、麦草の生化学的機械パルプ製造中の固形廃棄物と廃液のリサイクルの問題を解決することである。 The first object of the present invention is to solve the problem of recycling solid waste and waste liquid during the biochemical-mechanical pulping of wheat grass.
本発明の2番目の目的は、麦草廃棄物顆粒燃料性能の生物酵素による前処理調節方法を提供することである。 A second object of the present invention is to provide a method for adjusting wheat grass waste granule fuel performance by pretreatment with biological enzymes.
本発明3番目の目的は、麦草パルプ製造中の廃棄物及び廃液を利用して顆粒燃料を製造する方法を提供することである。 The third object of the present invention is to provide a method for producing granular fuel using waste and waste liquor from wheat grass pulp production.
この目的のために、本発明は、生物酵素調節の麦草廃棄物/パルプ製造廃液系顆粒燃料の製造方法を提供し、具体的には、
工場麦草材料準備中によって生成された麦草廃棄物を生物酵素前処理し、次に、特定の割合で、パルプ廃液と混合し均一に撹拌して、加熱して押出成型して顆粒燃料を得るステップを含む。
To this end, the present invention provides a method for the production of a bioenzyme-regulated wheat grass waste/pulp mill effluent-based granular fuel, specifically comprising:
The process involves bioenzyme pretreatment of wheat grass waste generated during the preparation of wheat grass material in factories, and then mixing it with pulp waste liquor in a specific ratio, stirring uniformly, and heating and extruding it to obtain granular fuel.
いくつかの実施例において、前記麦草廃棄物は、60メッシュの標準ふるいにかけた後、60メッシュ(0.22mm)より大きい麦草廃棄物であり、
いくつかの実施例において、前記酵素は、リパーゼ、キシラナーゼ及びセルラーゼを含む。
In some embodiments, the wheat grass waste is larger than 60 mesh (0.22 mm) after passing through a 60 mesh standard sieve;
In some embodiments, the enzymes include lipase, xylanase, and cellulase.
いくつかの実施例において、前記パルプ製造中の廃液は、パルプ黒液である。 In some embodiments, the waste liquor from the pulp manufacturing process is black liquor.
いくつかの実施例において、酵素前処理は、麦草廃棄物を60メッシュのふるいにかけて粒径0.22mmより大きい麦草廃棄物を得て、使用のために105℃条件下で4h乾燥させて準備し、pH5.0の緩衝溶液を調合し、前処理温度を50℃に制御し、0.05g(固形廃棄物含有量の0.50wt%)リパーゼ/キシラナーゼ/セルラーゼを加えて処理し、10min撹拌し、次に、10g麦草廃棄物を加えて混合し、6h撹拌し、リパーゼ/キシラナーゼ/セルラーゼで処理された麦草廃棄物を60℃のオーブンに入れて乾燥させて使用に備えることである。 In some embodiments, the enzyme pretreatment is to sieve the wheat grass waste through a 60 mesh sieve to obtain wheat grass waste with a particle size larger than 0.22 mm, prepare it for use by drying it under 105°C conditions for 4 h, prepare a buffer solution with a pH of 5.0, control the pretreatment temperature at 50°C, add 0.05 g (0.50 wt% of the solid waste content) of lipase/xylanase/cellulase to treat, stir for 10 min, then add 10 g of wheat grass waste and mix, stir for 6 h, and put the lipase/xylanase/cellulase treated wheat grass waste into a 60°C oven to dry it for use.
いくつかの実施例において、前記顆粒燃料の具体的な製造ステップは、上記酵素前処理後の麦草廃棄物に一定量の廃液を加えて均一に混合して乾燥処理し、麦草廃棄物の質量割合は74.0%であり、廃液における固形物の質量割合は24.0%であり、混合物における水の質量割合は2.0%であり、該混合物1.0gを成形金型スリーブ内に添加し、圧力6MPa、温度100℃の条件下で油圧プレスにおいて圧縮成形し、その密度、熱価及び機械性能を測定することである。ここでパルプ廃液に含まれる多糖類とリグニンの両方が、バインダーとして使用することができる特定の接着性能を有し、燃焼の性能を向上させることもできる。 In some embodiments, the specific steps of producing the granular fuel are to add a certain amount of waste liquid to the wheat grass waste after the enzyme pretreatment, mix uniformly, and dry so that the mass ratio of the wheat grass waste is 74.0%, the mass ratio of solids in the waste liquid is 24.0%, and the mass ratio of water in the mixture is 2.0%. 1.0 g of the mixture is added into a molding die sleeve, and compression molded in a hydraulic press under conditions of a pressure of 6 MPa and a temperature of 100°C, and its density, heat value, and mechanical properties are measured. Here, both the polysaccharides and lignin contained in the pulp waste liquid have specific adhesive properties that can be used as binders, and can also improve combustion performance.
いくつかの実施例において、顆粒燃料は、油圧プレスを介して圧縮され成形した。 In some embodiments, the granular fuel is compressed and molded via a hydraulic press.
以下、具体的な実施例を参照して本発明をさらに詳細に説明し、前記具体的な実施例は、本発明を限定するものではなく、説明であることに留意されたい。 The present invention will now be described in more detail with reference to specific examples. Please note that the specific examples are for illustrative purposes only and do not limit the present invention.
次の実施例及び比較例の黒液はすべて、ある製紙工場から取ったパルプ黒液である。 All of the black liquor in the following examples and comparative examples is pulp black liquor taken from a paper mill.
比較例1
顆粒燃料の製造及び性能の測定:60メッシュのスクリーンでふるいにかけた粒径0.22mm以下の麦草廃棄物を105℃の条件下で4h乾燥させ、次に10.0wt%の脱イオン水を加えて混合して均一に撹拌し、次に1.0gの十分に均一に混合した麦草廃棄物を成形金型スリーブ内に入れ、液圧プレスの圧力6MP、常温条件下で圧縮成形した。その密度を測定し、また、バイオマス顆粒燃料の熱価を熱量計により測定し、万能試験機を介してその水平圧縮強度を測定した。
Comparative Example 1
Granular fuel preparation and performance measurement: Wheat grass waste with a particle size of 0.22 mm or less was sieved through a 60-mesh screen and dried at 105°C for 4 hours, then 10.0 wt% deionized water was added and mixed and stirred uniformly, and 1.0 g of the thoroughly and uniformly mixed wheat grass waste was placed in a molding die sleeve and compressed under a hydraulic press pressure of 6 MPa at room temperature. The density was measured, and the heat value of the biomass granular fuel was measured by a calorimeter, and its horizontal compression strength was measured by a universal testing machine.
比較例2
顆粒燃料の製造及び性能の測定:60メッシュのふるいにかけて残した粒径0.22mm以上の麦草廃棄物を105℃条件下で4h乾燥させ、次に10.0wt%の脱イオン水を加えて混合して均一に撹拌し、次に1.0gの十分に均一に混合した麦草廃棄物を成形金型スリーブ内に入れ、油圧プレス圧力6MPa、常温条件下で圧縮成形した。その密度を測定し、また、顆粒燃料の熱価を熱量計ーにより測定し、万能試験機を介してその水平圧縮強度を測定した。
Comparative Example 2
Granular fuel production and performance measurement: Wheat grass waste with a particle size of 0.22 mm or more left after sieving through a 60-mesh sieve was dried at 105°C for 4 hours, then 10.0 wt% deionized water was added and mixed and stirred uniformly, and 1.0 g of the thoroughly and uniformly mixed wheat grass waste was placed in a molding die sleeve and compressed at room temperature under a hydraulic press pressure of 6 MPa. The density was measured, and the heat value of the granular fuel was measured by a calorimeter, and the horizontal compression strength was measured by a universal testing machine.
比較例3
顆粒燃料の製造及び性能の測定:60メッシュのふるいにかけて残した粒径0.22mm以上の麦草廃棄物を105℃の条件下で4h乾燥させ、次に一定量の黒液を加えて均一に混合し且つ乾燥処理して麦草廃棄物の質量割合を74.0%、廃液における固形物の質量割合を24.0%、混合物における水の質量割合を2.0%にし、1.0gの乾燥後の麦草廃棄物/廃液混合物を成形金型スリーブ内に入れ、油圧プレス圧力6MPa、常温条件下で圧縮成形した。その密度を測定し、また、顆粒燃料の熱価を熱量計ーにより測定し、万能試験機を介してその水平圧縮強度を測定した。
Comparative Example 3
Granular fuel production and performance measurement: Wheat grass waste with a particle size of 0.22 mm or more left after sieving through a 60-mesh sieve was dried under the condition of 105°C for 4 hours, then a certain amount of black liquor was added and mixed uniformly, and dried to make the mass ratio of the wheat grass waste 74.0%, the mass ratio of solid matter in the waste liquor 24.0%, and the mass ratio of water in the mixture 2.0%, and 1.0 g of the dried wheat grass waste/waste liquor mixture was placed in a molding die sleeve and compressed under a hydraulic press pressure of 6 MPa at room temperature. The density was measured, and the heat value of the granular fuel was measured by a calorimeter, and its horizontal compressive strength was measured by a universal testing machine.
実施例1
(1)顆粒燃料の生物酵素処理:60メッシュのふるいにかけて残した粒径0.22mm以上の麦草廃棄物を105℃の条件下で4h乾燥させ使用に備え、pH5.0の緩衝溶液を調製し、前処理温度を50℃に制御し、0.05g(固形廃棄物含有量の0.50%を占め)キシラナーゼを加えて処理し、10min撹拌し、次に、10g麦草廃棄物を加えて混合し、6h撹拌し、キシラナーゼで前処理された麦草廃棄物を60℃のオーブンに入れて乾燥させて使用に備えた。
(2)顆粒燃料の製造及び性能の測定:上記キシラナーゼで処理した麦草廃棄物に一定量の黒液を加えて均一に混合し且つ乾燥処理し、ここで麦草廃棄物の質量割合は74.0%、廃液における固形物の質量割合は24.0%であり、混合物における水の質量割合は2.0%であり、1.0gの乾燥後の麦草廃棄物/廃液混合物を成形金型スリーブ内に入れ、油圧プレス圧力6MPa、温度100℃の条件下で圧縮成形した。顆粒燃料の密度を測定し、顆粒燃料の熱価を熱量計ーにより測定し、万能試験機を介してその水平圧縮強度を測定した。
Example 1
(1) Bioenzyme treatment of granular fuel: Wheat grass waste with a particle size of 0.22 mm or more was left through a 60-mesh sieve and dried at 105°C for 4 hours in preparation for use. A buffer solution of pH 5.0 was prepared, the pretreatment temperature was controlled at 50°C, 0.05 g (accounting for 0.50% of the solid waste content) of xylanase was added for treatment, and stirred for 10 min. Then, 10 g of wheat grass waste was added and mixed, and stirred for 6 hours. The wheat grass waste pretreated with xylanase was placed in an oven at 60°C and dried in preparation for use.
(2) Production of granular fuel and measurement of its performance: A certain amount of black liquor was added to the above-mentioned xylanase-treated wheat grass waste, mixed uniformly, and dried, in which the mass ratio of the wheat grass waste was 74.0%, the mass ratio of solid matter in the waste liquor was 24.0%, and the mass ratio of water in the mixture was 2.0%. 1.0 g of the dried wheat grass waste/waste liquor mixture was placed in a molding die sleeve and compression molded under the conditions of a hydraulic press pressure of 6 MPa and a temperature of 100° C. The density of the granular fuel was measured, the heat value of the granular fuel was measured by a calorimeter, and its horizontal compressive strength was measured by a universal testing machine.
実施例2
(1)顆粒燃料の酵素処理:60メッシュのふるいにかけて残した粒径0.22mm以上の麦草廃棄物を105℃の条件下で4h乾燥させ使用に備え、pH5.0の緩衝溶液を調製し、前処理温度を50℃に制御し、0.05g(固形廃棄物含有量の0.50%を占め)リパーゼを加えて処理し、10min撹拌し、次に、10g麦草廃棄物を加えて混合し、6h撹拌し、リパーゼで処理された麦草廃棄物を60℃のオーブンに入れて乾燥させて使用に備えた。
(2)顆粒燃料の製造及び性能の測定:上記リパーゼで処理した麦草廃棄物に一定量の黒液を加えて均一に混合し且つ乾燥処理し、ここで麦草廃棄物の質量割合は74.0%であり、廃液における固形物の質量割合は24.0%であり、混合物における水の質量割合は2.0%であり、1.0gの乾燥後の麦草廃棄物/廃液混合物を成形金型スリーブ内に入れ、油圧プレス圧力6MPa、温度100℃の条件下で圧縮成形した。顆粒燃料の密度を測定し、顆粒燃料の熱価を熱量計ーにより測定し、万能試験機を介してその水平圧縮強度を測定した。
Example 2
(1) Enzyme treatment of granular fuel: wheat grass waste with a particle size of 0.22 mm or more was left through a 60-mesh sieve and dried at 105°C for 4 hours in preparation for use. A buffer solution of pH 5.0 was prepared, the pretreatment temperature was controlled at 50°C, 0.05 g (accounting for 0.50% of the solid waste content) of lipase was added for treatment, and stirred for 10 min. Then, 10 g of wheat grass waste was added and mixed, and stirred for 6 hours. The lipase-treated wheat grass waste was then placed in a 60°C oven and dried in preparation for use.
(2) Production of granular fuel and measurement of its performance: A certain amount of black liquor was added to the above-mentioned lipase-treated wheat grass waste, mixed uniformly, and dried, in which the mass ratio of the wheat grass waste was 74.0%, the mass ratio of solid matter in the waste liquor was 24.0%, and the mass ratio of water in the mixture was 2.0%. 1.0 g of the dried wheat grass waste/waste liquor mixture was placed in a molding die sleeve and compression molded under the conditions of a hydraulic press pressure of 6 MPa and a temperature of 100° C. The density of the granular fuel was measured, the heat value of the granular fuel was measured by a calorimeter, and its horizontal compression strength was measured by a universal testing machine.
実施例3
(1)顆粒燃料の酵素処理:60メッシュのふるいにかけて残した粒径0.22mm以上の麦草廃棄物を、105℃条件下で4h乾燥させて使用に備え、pH5.0の緩衝溶液を調製し、ウォーターバスの温度を50℃に制御し、0.05g(固形廃棄物含有量の0.50%を占め)セルラーゼを加えて処理し、10min撹拌し、次に、10g麦草廃棄物を加えて混合し、6h撹拌し、セルラーゼで処理された麦草廃棄物を60℃のオーブンに入れて乾燥させて使用に備えた。
(2)顆粒燃料の製造及び性能の測定:上記セルラーゼで処理した麦草廃棄物に一定量の黒液を加えて均一に混合し且つ乾燥処理し、麦草廃棄物の質量を74.0%、廃液における固形物の質量を24.0%、混合物における水の質量を2.0%にし、1.0gの乾燥後の麦草廃棄物/廃液混合物を成形金型スリーブ内に入れ、油圧プレス圧力6MPa、温度100℃の条件下で圧縮成形した。顆粒燃料の密度を測定し、顆粒燃料の熱価を熱量計ーにより測定し、万能試験機を介してその水平圧縮強度を測定した。
Example 3
(1) Enzyme treatment of granular fuel: Wheat grass waste with a particle size of 0.22 mm or more was left after sieving through a 60-mesh sieve and dried at 105°C for 4 hours in preparation for use. A buffer solution of pH 5.0 was prepared, the temperature of the water bath was controlled at 50°C, 0.05 g (accounting for 0.50% of the solid waste content) of cellulase was added for treatment, and stirred for 10 min. Then, 10 g of wheat grass waste was added and mixed, and stirred for 6 hours. The wheat grass waste treated with cellulase was then placed in an oven at 60°C and dried in preparation for use.
(2) Production of granular fuel and measurement of its performance: A certain amount of black liquor was added to the above-mentioned cellulase-treated wheat grass waste, mixed uniformly, and dried to make the mass of the wheat grass waste 74.0%, the mass of solids in the waste liquid 24.0%, and the mass of water in the mixture 2.0%, and 1.0 g of the dried wheat grass waste/waste liquid mixture was placed in a molding die sleeve and compression molded under conditions of a hydraulic press pressure of 6 MPa and a temperature of 100° C. The density of the granular fuel was measured, the heat value of the granular fuel was measured by a calorimeter, and its horizontal compressive strength was measured by a universal testing machine.
実施例4
(1)顆粒燃料の酵素処理:60メッシュのふるいにかけて残した粒径0.22mm以上の麦草廃棄物を105℃の条件下で4h乾燥させ使用に備え、pH5.0の緩衝溶液を調製し、前処理温度を50℃に制御し、0.05g(固形廃棄物含有量の0.50%を占め)キシラナーゼ/セルラーゼを加えて処理し、10min撹拌し、次に、10g麦草廃棄物を加えて混合し、6h撹拌し、キシラナーゼ/セルラーゼで処理された麦草廃棄物を60℃のオーブンに入れて乾燥させて使用に備えた。
(2)顆粒燃料の製造及び性能の測定:上記キシラナーゼ/セルラーゼで処理した麦草廃棄物に一定量の黒液を加えて均一に混合し且つ乾燥処理し、麦草廃棄物の質量割合を74.0%、廃液における固形物の質量割合を24.0%、混合物における水の質量割合を2.0%にし、乾燥後の麦草廃棄物/廃液混合物1.0gを成形金型スリーブ内に入れ、油圧プレス圧力6MPa、温度100℃の条件下で圧縮成形した。顆粒燃料の密度を測定し、顆粒燃料の熱価を熱量計ーにより測定し、万能試験機を介してその水平圧縮強度を測定した。
Example 4
(1) Enzyme treatment of granular fuel: The wheat grass waste with a particle size of 0.22 mm or more that was left after sieving through a 60-mesh sieve was dried under conditions of 105°C for 4 hours in preparation for use, a buffer solution of pH 5.0 was prepared, the pretreatment temperature was controlled at 50°C, 0.05 g (accounting for 0.50% of the solid waste content) of xylanase/cellulase was added for treatment, and stirred for 10 min, then 10 g of wheat grass waste was added and mixed, and stirred for 6 hours, and the wheat grass waste treated with xylanase/cellulase was placed in an oven at 60°C and dried in preparation for use.
(2) Production of granular fuel and measurement of its performance: A certain amount of black liquor was added to the wheat grass waste treated with the xylanase/cellulase, mixed uniformly, and dried to make the mass ratio of the wheat grass waste 74.0%, the mass ratio of solids in the waste liquid 24.0%, and the mass ratio of water in the mixture 2.0%, and 1.0 g of the dried wheat grass waste/waste liquid mixture was placed in a molding die sleeve and compression molded under hydraulic press pressure of 6 MPa and temperature of 100° C. The density of the granular fuel was measured, the heat value of the granular fuel was measured by a calorimeter, and its horizontal compressive strength was measured by a universal testing machine.
実施例5
(1)顆粒燃料の酵素処理:60メッシュのふるいにかけて残した粒径0.22mm以上の麦草廃棄物を105℃の条件下で4h乾燥させ使用に備え、pH5.0の緩衝溶液を調製し、前処理温度を50℃に制御し、0.05g(固形廃棄物含有量の0.50%を占め)リパーゼ/キシラナーゼ/セルラーゼを加えて処理し、10min撹拌し、次に、10g麦草廃棄物を加えて混合し、6h撹拌し、リパーゼ/キシラナーゼ/セルラーゼで処理された麦草廃棄物を60℃のオーブンに入れて乾燥させて使用に備えた。
(2)顆粒燃料の製造及び性能の測定:上記リパーゼ/キシラナーゼ/セルラーゼで処理した麦草廃棄物に一定量の黒液を加えて均一に混合し且つ乾燥処理し、麦草廃棄物の質量割合を74.0%、廃液における固形物の質量割合を24.0%、混合物における水の質量割合を2.0%にし、1.0gの乾燥後の麦草廃棄物/廃液混合物を成形金型スリーブ内に入れ、油圧プレス圧力6MPa、温度100℃の条件下で圧縮成形した。顆粒燃料の密度を測定し、顆粒燃料の熱価を熱量計ーにより測定し、万能試験機を介してその水平圧縮強度を測定した。
Example 5
(1) Enzyme treatment of granular fuel: The wheat grass waste with a particle size of 0.22 mm or more that was left after sieving through a 60-mesh sieve was dried under the condition of 105°C for 4 hours in preparation for use, a buffer solution of pH 5.0 was prepared, the pretreatment temperature was controlled at 50°C, 0.05 g (accounting for 0.50% of the solid waste content) of lipase/xylanase/cellulase was added for treatment, and stirred for 10 min, then 10 g of wheat grass waste was added and mixed, and stirred for 6 hours, and the wheat grass waste treated with lipase/xylanase/cellulase was placed in a 60°C oven and dried in preparation for use.
(2) Production of granular fuel and measurement of its performance: A certain amount of black liquor was added to the wheat grass waste treated with the lipase/xylanase/cellulase, mixed uniformly, and dried to make the mass ratio of the wheat grass waste 74.0%, the mass ratio of solids in the waste liquid 24.0%, and the mass ratio of water in the mixture 2.0%, and 1.0 g of the dried wheat grass waste/waste liquid mixture was placed in a molding die sleeve and compression molded under conditions of a hydraulic press pressure of 6 MPa and a temperature of 100° C. The density of the granular fuel was measured, the heat value of the granular fuel was measured by a calorimeter, and its horizontal compressive strength was measured by a universal testing machine.
原料の分析:
測定方法は、麦草廃棄物におけるセルロース、ヘミセルロース、酸不溶性リグニン含有量をNREL法に応じて測定し、元素組成分析を、自動要素分析器によって測定し、パルプ廃液におけるリグニン含有量を、紫外分光光度計によって吸光度を測定して計算し、糖成分の含有量を、ICS5000+イオンクロマトグラフによって測定することであり、測定結果を表1及び表2に示す。
Raw material analysis:
The measurement method was to measure the cellulose, hemicellulose, and acid-insoluble lignin contents in the wheat grass waste according to the NREL method, measure the elemental composition analysis by an automatic element analyzer, calculate the lignin content in the pulp waste liquor by measuring the absorbance by an ultraviolet spectrophotometer, and measure the sugar component content by an ICS5000+ ion chromatograph. The measurement results are shown in Tables 1 and 2.
表1 麦草材料から準備した廃棄物の化学成分及び元素組成分析(%)
Table 1 Chemical and elemental composition analysis (%) of waste prepared from wheat grass material
表2 黒液成分及び含有量の分析
Table 2 Analysis of black liquor components and contents
表3 バイオマス顆粒燃料の物理的および化学的性能分析
最後に、上記の説明は本発明の好ましい実施例にすぎず、本発明を限定することを意図するものではないことに留意されたい。本発明は前述の実施例を参照して詳細に説明されているが、当業者にとって、それらは、前述の実施例に記載された技術的解決手段を依然として修正することができるか、またはそれらの一部を同等に置き換えることができる。本発明の精神と原則におけるいかなる修正、同等の置換、改善などはすべて、本発明の保護範囲内に含まれるものとする。 Finally, please note that the above description is only a preferred embodiment of the present invention, and is not intended to limit the present invention. Although the present invention has been described in detail with reference to the above embodiments, for those skilled in the art, they can still modify the technical solutions described in the above embodiments, or replace parts of them with equivalents. Any modifications, equivalent replacements, improvements, etc. in the spirit and principle of the present invention shall all be included in the protection scope of the present invention.
Claims (14)
麦草廃棄物に対して生物酵素前処理を実行し、乾燥させ、酵素前処理後の麦草廃棄物を得て、
前記酵素前処理後の麦草廃棄物とパルプ製造廃液を均一に混合し、加熱して押し出して成型し、麦草廃棄物顆粒燃料を得ることを含む麦草廃棄物顆粒燃料の物理的および化学的性能の生物酵素による前処理調節方法。 The method for adjusting the physical and chemical properties of wheat grass waste granule fuel by bioenzymatic pretreatment is as follows:
The wheat grass waste is subjected to biological enzyme pretreatment and dried to obtain enzyme pretreated wheat grass waste.
The method for adjusting the physical and chemical properties of wheat grass waste granular fuel by pretreatment with biological enzymes includes uniformly mixing the wheat grass waste and pulp manufacturing waste liquid after the enzyme pretreatment, and heating and extruding the mixture to obtain wheat grass waste granular fuel.
酵素を緩衝溶液に追加した後、前記乾燥した麦草廃棄物を加えて混合して撹拌し、酵素処理した麦草廃棄物を得るステップと、を含むことを特徴とする請求項1に記載の方法。 drying and preparing the wheat grass waste for use;
2. The method according to claim 1, further comprising the steps of: adding an enzyme to a buffer solution, followed by adding the dried grass waste and mixing and stirring to obtain an enzyme-treated grass waste.
麦草廃棄物を60メッシュのふるいでふるいにかけて粒径0.22mmより大きい麦草廃棄物を得て、使用のために105℃条件下で4h乾燥させて準備するステップと、
pH5.0の緩衝溶液を調合し、前処理温度を50℃に制御し、固形廃棄物含有量の0.50wt%の生物酵素を追加し、10min撹拌し、次に、麦草廃棄物を加えて混合し、6h撹拌するステップと、を含むことを特徴とする請求項2に記載の方法。 The biological enzyme pretreatment is
Sieving the wheat grass waste through a 60 mesh sieve to obtain wheat grass waste with a particle size of more than 0.22 mm, and drying it under 105° C. for 4 h to prepare it for use;
The method according to claim 2, comprising the steps of: preparing a buffer solution of pH 5.0; controlling the pretreatment temperature at 50°C; adding biological enzymes of 0.50 wt% of the solid waste content; stirring for 10 min; and then adding and mixing wheat grass waste, and stirring for 6 h.
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CN100365198C (en) * | 2005-11-18 | 2008-01-30 | 山东轻工业学院 | Process for enzyme treating before pulping by plant fibre raw material |
CN100558519C (en) * | 2007-12-18 | 2009-11-11 | 南京林业大学 | Stalk wood shavings plate-making method after complex enzyme is handled |
CN101768494A (en) * | 2010-03-09 | 2010-07-07 | 中国科学院过程工程研究所 | Straw densification briquetting fuel preparation method for biomass power generation and boiler combustion |
EP2759597A1 (en) * | 2013-01-23 | 2014-07-30 | Sekab E-Technology AB | Image analysis based process control of processes for production of sugar from lignocellulosic biomass |
CN111674045A (en) * | 2020-05-27 | 2020-09-18 | 安徽元琛环保科技股份有限公司 | Preparation method of PLA-based composite material for 3D printing and prepared material |
CN113337323B (en) * | 2021-06-28 | 2023-03-10 | 齐鲁工业大学 | Waste-based granular fuel in wheat straw pulping process and preparation method and application thereof |
CN114686287B (en) * | 2022-04-11 | 2023-02-28 | 齐鲁工业大学 | Method for regulating physical and chemical properties of wheat straw waste residue granular fuel through biological enzyme pretreatment |
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2022
- 2022-04-11 CN CN202210373029.9A patent/CN114686287B/en active Active
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2023
- 2023-06-08 WO PCT/CN2023/099078 patent/WO2023198227A1/en active Application Filing
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WO2023198227A1 (en) | 2023-10-19 |
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