JP2015209452A - Biomass fuel pretreatment method, its system, and biomass heat generation system using the same - Google Patents

Biomass fuel pretreatment method, its system, and biomass heat generation system using the same Download PDF

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JP2015209452A
JP2015209452A JP2014090104A JP2014090104A JP2015209452A JP 2015209452 A JP2015209452 A JP 2015209452A JP 2014090104 A JP2014090104 A JP 2014090104A JP 2014090104 A JP2014090104 A JP 2014090104A JP 2015209452 A JP2015209452 A JP 2015209452A
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biomass
biomass fuel
drying
power generation
water
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青山 光太郎
Kotaro Aoyama
光太郎 青山
増田 洋人
Hiroto Masuda
洋人 増田
早津 昌樹
Masaki Hayatsu
昌樹 早津
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Hitachi Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/12Heat utilisation in combustion or incineration of waste
    • 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
    • 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
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

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Abstract

PROBLEM TO BE SOLVED: To provide a biomass fuel pretreatment method capable of efficiently producing biomass fuel having high combustion efficiency and having a prescribed water content, its system, and a biomass heat generation system using the same.SOLUTION: Provided is a biomass fuel pretreatment method including: a water-absorbing-drying step 20 of water-absorbing a pulverized woody material with a water-absorbing material so as to be dried; a fermentation-drying step 40 of mixing the woody material with livestock feces so as to be fermented; and a heat exhaust-drying step 50 of feeding a purification gas after gas exhaust treatment to the woody material by biomass heat generation so as to dry to a prescribed water content.

Description

本発明は、再生可能エネルギーとなるバイオマス発電に好適なバイオマス燃料の前処理方法及びそのシステム、これを用いたバイオマス発電システムに関する。   The present invention relates to a pretreatment method and system for biomass fuel suitable for biomass power generation as renewable energy, and a biomass power generation system using the same.

近年、化石燃料は高騰化の傾向にあり、燃焼により発生する二酸化炭素の排出量も多いことから、代替エネルギーとなる再生可能エネルギーの関心が高まっている。再生可能エネルギーとしては、風力、水力、太陽光、地熱などが知られているが、中でも気象条件に左右されず安定した原料確保の観点から、木質、ヤシガラ、畜糞、農業廃棄物などの生物資源由来物質を燃料とするバイオマス発電が重要な発電として注目されている。   In recent years, fossil fuels have been on the rise, and the amount of carbon dioxide generated by combustion is large. Therefore, interest in renewable energy, which is an alternative energy, is increasing. As renewable energy, wind power, hydropower, solar power, geothermal heat, etc. are known, but biological resources such as wood, coconut husk, animal manure, agricultural waste, etc. from the viewpoint of securing stable raw materials, regardless of weather conditions. Biomass power generation using derived materials as fuel has attracted attention as an important power generation.

バイオマス発電で最も多く使用されている原料は、解体材や間伐材などの木質材料である。しかし木質材料は、単位面積当たりのエネルギー密度が低く、含水率など品質のばらつきがあり、また、木質材料の生産量は大きく変動するなどボイラーの運転計画や、燃焼効率に影響を及ぼすことが課題となっている。
従来、ボイラーの燃焼効率を上げるために木質材料をペレットやブリケットなどに加工した固形燃料が利用されている(例えば特許文献1など)。
The most frequently used raw materials for biomass power generation are wood materials such as demolition materials and thinned wood. However, wood materials have low energy density per unit area, variations in quality such as moisture content, and the production volume of wood materials fluctuates greatly, affecting the boiler operation plan and combustion efficiency. It has become.
Conventionally, in order to increase the combustion efficiency of a boiler, a solid fuel obtained by processing a wood material into pellets or briquettes has been used (for example, Patent Document 1).

しかし、このような固形燃料は、品質の安定性がある一方で、製造工程に原料の微粉化が必要であり、製造の工程数が多くなり製造コストが増加してしまうという問題があった。このため、安定した品質、かつ安価な木質材料の製造が望まれている。   However, such a solid fuel has a problem that the quality of the solid fuel is stable, but the raw material is required to be pulverized in the manufacturing process, which increases the number of manufacturing processes and increases the manufacturing cost. For this reason, it is desired to produce a wooden material that is stable and inexpensive.

そこで、特許文献2のバイオマス燃料前処理ユニットでは、ボイラーから供給される蒸気及び、バイオマス発電の燃焼により発生した排ガスの一部をバイオマス燃料の加熱に用いている。
また、特許文献3のバイオマスの製造方法では、湿潤バイオマスを副資材と混合した状態で好気性発酵させる工程が開示されている。
Therefore, in the biomass fuel pretreatment unit of Patent Document 2, steam supplied from a boiler and a part of exhaust gas generated by combustion of biomass power generation are used for heating the biomass fuel.
In addition, in the method for producing biomass of Patent Document 3, a process of aerobic fermentation in a state where wet biomass is mixed with auxiliary materials is disclosed.

特開2012−255108号公報JP 2012-255108 A 特開2013−88033号公報JP 2013-88033 A 特開2011−189268号公報JP 2011-189268 A

しかしながら特許文献2では、発電に用いる蒸気の一部をバイオマス燃料の加熱に用いているため、エネルギーの変換効率が悪いという問題があった。また、特許文献3では、発酵期間が長期間に及ぶと共に、当初原料の含水率が高い場合に発酵では十分に乾燥できない、換言するとある一定の含水率の木質材料でなければ乾燥できないという問題があった。また、活性汚泥や家畜糞尿中に含まれる塩素などの物質が燃焼装置の壁や配管を腐食させてしまうという問題があった。   However, Patent Document 2 has a problem in that energy conversion efficiency is poor because part of the steam used for power generation is used for heating the biomass fuel. Further, in Patent Document 3, there is a problem that the fermentation period extends for a long time, and when the moisture content of the initial raw material is high, it cannot be sufficiently dried by fermentation, in other words, it cannot be dried unless it is a wooden material with a certain moisture content. there were. In addition, there is a problem that substances such as activated sludge and chlorine contained in livestock manure corrode the walls and piping of the combustion apparatus.

更に、前記したように解体材や間伐材などから生産される木質材料は、一定した生産量とすることは難しく、一定量を保管しながら、バイオマス発電計画に応じた供給量に調整する必要(課題)がある。   Furthermore, as mentioned above, wood materials produced from demolition materials, thinned wood, etc. are difficult to make a constant production amount, and it is necessary to adjust the supply amount according to the biomass power generation plan while keeping a constant amount ( Problem).

そこで本発明が解決しようとする課題は、燃焼効率が高く、所定含水率のバイオマス燃料を効率よく生産可能なバイオマス燃料前処理方法及びそのシステム、これを用いたバイオマス発電システムを提供することを目的としている。   Therefore, the problem to be solved by the present invention is to provide a biomass fuel pretreatment method and system capable of efficiently producing biomass fuel having a high combustion efficiency and a predetermined moisture content, and a biomass power generation system using the biomass fuel pretreatment method. It is said.

また本発明は、バイオマス発電の発電効率を高めることができるバイオマス燃料前処理方法及びそのシステム、これを用いたバイオマス発電システムを提供することを目的としている。   Another object of the present invention is to provide a biomass fuel pretreatment method and system capable of increasing the power generation efficiency of biomass power generation, and a biomass power generation system using the same.

本発明は、上記の課題を解決するための第1の手段として、粉砕した木質材料を吸水材で吸水して乾燥させる吸水乾燥工程と、前記木質材料に畜糞を混入して発酵させる発酵乾燥工程と、バイオマス発電で排ガス処理後の浄化ガスを前記木質材料に供給して所定含水率に乾燥させる排熱乾燥工程と、を有することを特徴とするバイオマス燃料前処理方法を提供することにある。   The present invention provides, as a first means for solving the above-mentioned problems, a water-absorbing and drying step of absorbing and drying the pulverized wooden material with a water-absorbing material, and a fermentation and drying step of mixing animal feces into the wooden material and fermenting it. And a waste heat drying step of supplying a purified gas after exhaust gas treatment by biomass power generation to the woody material and drying it to a predetermined moisture content, to provide a biomass fuel pretreatment method.

本発明は、上記の課題を解決するための第2の手段として、前記第1の手段において、前記吸水乾燥工程は、前記吸水材と前記木質材料を交互、かつ多段に積層させて前記木質材料を前記吸水材で覆うようにして一定の水分量まで乾燥させることを特徴とするバイオマス燃料前処理方法を提供することにある。   The present invention provides a second means for solving the above-mentioned problems. In the first means, the water-absorbing and drying step includes alternately stacking the water-absorbing material and the wooden material in a multistage manner. It is to provide a biomass fuel pretreatment method characterized in that the water-absorbing material is covered with the water-absorbing material and dried to a certain water content.

本発明は、上記の課題を解決するための第3の手段として、前記第1又は第2の手段において、前記木質材料と前記畜糞は、総灰分量が総燃料重量の0.2以下、好ましくは0.15以下となるように混合することを特徴とするバイオマス燃料前処理方法を提供することにある。   According to the present invention, as a third means for solving the above problems, in the first or second means, the wood material and the animal manure have a total ash content of 0.2 or less of the total fuel weight, preferably Is to provide a biomass fuel pretreatment method characterized by mixing so as to be 0.15 or less.

本発明は、上記の課題を解決するための第4の手段として、前記木質材料と前記畜糞は、総燃料含有塩素濃度が500ppm以下、好ましくは100ppm以下となるように混合することを特徴とするバイオマス燃料前処理方法を提供することにある。   As a fourth means for solving the above-mentioned problems, the present invention is characterized in that the wood material and the animal waste are mixed so that the total fuel-containing chlorine concentration is 500 ppm or less, preferably 100 ppm or less. It is to provide a biomass fuel pretreatment method.

本発明は、上記の課題を解決するための第5の手段として、粉砕した木質材料を吸水材で吸水して乾燥させる吸水乾燥手段と、前記木質材料に畜糞を混入して発酵させる発酵乾燥手段と、バイオマス発電で排ガス処理後の浄化ガスを前記木質材料に供給して所定含水率に乾燥させる排熱乾燥手段と、を有することを特徴とするバイオマス燃料前処理システムを提供することを目的としている。   The present invention provides, as a fifth means for solving the above-mentioned problems, a water-absorbing and drying means for absorbing and drying the pulverized wooden material with a water-absorbing material, and a fermenting and drying means for fermenting livestock dung in the wooden material. And a waste heat drying means for supplying the purified gas after exhaust gas treatment by biomass power generation to the wood material and drying it to a predetermined moisture content, for the purpose of providing a biomass fuel pre-treatment system Yes.

本発明は、上記の課題を解決するための第6の手段として、前記バイオマス燃料前処理システムと、前記バイオマス燃料前処理システムで生産したバイオマス燃料を燃焼する燃焼手段と、前記燃焼手段の熱エネルギーを電気に変換する発電手段と、を有することを特徴とするバイオマス発電システムを提供することにある。   The present invention provides, as sixth means for solving the above problems, the biomass fuel pretreatment system, combustion means for burning biomass fuel produced by the biomass fuel pretreatment system, and thermal energy of the combustion means And a power generation means for converting the electricity into electricity.

上記のような構成によれば、吸水乾燥工程で長期保管と、生産量の平準化を行える。すなわち、発電システムへのバイオマス燃料の供給時期に合わせて、乾燥時間を調整しながらバイオマス燃料を生産することができる。また、バイオマス燃料の乾燥時間を任意に調整できるとともに、生産後、保管している間にバイオマス燃料を次工程である発酵乾燥工程に適した含水率に保つことができる。   According to the above configuration, long-term storage and production leveling can be performed in the water absorption drying process. That is, the biomass fuel can be produced while adjusting the drying time in accordance with the supply timing of the biomass fuel to the power generation system. Moreover, while drying time of biomass fuel can be adjusted arbitrarily, biomass fuel can be kept at the moisture content suitable for the fermentation drying process which is a next process, while storing after production.

また、排熱乾燥工程で供給する排ガス量を制御して急速乾燥を行うことができるため、バイオマス発電に供給する燃料の量を調整することができる。   Moreover, since rapid drying can be performed by controlling the amount of exhaust gas supplied in the exhaust heat drying step, the amount of fuel supplied to biomass power generation can be adjusted.

また、従来のように木質材料を乾燥するために新たな加熱設備や、その燃料費や、ペレット化する工程を必要とすることなく低コストで所定含水率のバイオマス燃料を製造することができる。   Further, a biomass fuel having a predetermined moisture content can be produced at low cost without requiring a new heating facility, a fuel cost thereof, and a pelletizing step for drying the wood material as in the prior art.

上記のような構成によれば、当初原料の含水率(初期原料の含水率)に係わらず、例えば、含水率を40%以下、好ましくは20%以下の所定含水率のバイオマス燃料を生産することができる。   According to the above configuration, regardless of the moisture content of the initial raw material (the moisture content of the initial raw material), for example, producing a biomass fuel having a predetermined moisture content of 40% or less, preferably 20% or less, for example. Can do.

上記のような構成によれば、前記木質材料と前記畜糞は、総灰分量が総燃料重量の0.2以下、好ましくは0.15以下となるように混合しているので、排ガス中のダストの発生量を低減でき、排ガス処理設備の負荷を低減して安定した発電運転を実現できる。   According to the above configuration, the wood material and the animal manure are mixed so that the total ash content is 0.2 or less, preferably 0.15 or less of the total fuel weight. The amount of generated gas can be reduced, and the load of the exhaust gas treatment facility can be reduced to realize a stable power generation operation.

上記のような構成によれば、前記木質材料と前記畜糞は、総燃料含有塩素濃度が500ppm以下、好ましくは100ppm以下となるように混合しているので、鉄材等への腐食性を有する塩素を低減して、バイオマス燃料を用いたバイオマス発電システムの壁や配管の腐食を防止できる。   According to the above configuration, the wood material and the animal waste are mixed so that the total fuel-containing chlorine concentration is 500 ppm or less, preferably 100 ppm or less. It can reduce and can prevent the corrosion of the wall and piping of the biomass power generation system using biomass fuel.

本発明のバイオマス燃料前処理方法の説明図である。It is explanatory drawing of the biomass fuel pre-processing method of this invention. 木質材料のサイズと乾燥時間の関係を示すグラフである。It is a graph which shows the relationship between the size of woody material, and drying time. 吸水乾燥工程の説明図である。It is explanatory drawing of a water absorption drying process. バイオマス燃料前処理方法の各工程の含水率を示すグラフである。It is a graph which shows the moisture content of each process of a biomass fuel pre-processing method. 本発明のバイオマス燃料前処理システム及びバイオマス発電システムの説明図である。It is explanatory drawing of the biomass fuel pre-processing system and biomass power generation system of this invention.

本発明のバイオマス燃料前処理方法及びそのシステム、これを用いたバイオマス発電システムの実施形態を添付の図面を参照しながら、以下詳細に説明する。   Embodiments of a biomass fuel pretreatment method and system and a biomass power generation system using the biomass fuel pretreatment method of the present invention will be described in detail below with reference to the accompanying drawings.

本発明でバイオマス燃料とは、木質、ヤシガラ、畜糞、農業廃棄物などの動植物性資源をいう。
本発明で木質材料とは、解体材、間伐材、剪定材など植物バイオマスをいう。
本発明で畜糞とは、鶏糞、牛糞、豚糞のうちいずれか、又は2種以上の混合物をいう。
In the present invention, the biomass fuel refers to animal and plant resources such as wood, coconut husk, animal manure, and agricultural waste.
In the present invention, the woody material refers to plant biomass such as demolition material, thinning material, and pruning material.
In the present invention, livestock droppings refers to any of chicken droppings, cow droppings, pig droppings, or a mixture of two or more.

[バイオマス燃料前処理方法]
図1は、本発明のバイオマス燃料前処理方法の説明図である。図示のように、本発明のバイオマス燃料前処理方法は、木質粉砕工程10と、吸水乾燥工程20と、畜糞/木質混合工程30と、発酵乾燥工程40と、排熱乾燥工程50を主な基本構成としている。
[Biomass fuel pretreatment method]
FIG. 1 is an explanatory diagram of the biomass fuel pretreatment method of the present invention. As shown in the figure, the biomass fuel pretreatment method of the present invention mainly includes a wood crushing step 10, a water absorption drying step 20, a livestock dung / wood mixing step 30, a fermentation drying step 40, and an exhaust heat drying step 50. It is configured.

[木質粉砕工程10]
木質粉砕工程10は、解体材、間伐材、剪定材などの植物バイオマスである木質材料を粉砕機により所定サイズに粉砕する工程である。
図2は温度条件100℃における木質材料のサイズと乾燥時間の関係を示すグラフである。同グラフの縦軸は、含水率(%)を示し、横軸は時間(min)を示している。温度条件100℃において、同グラフに示すように150mmサイズの木質材料を含水率が45%から20%へ乾燥する場合、約110分を必要とする。また、30mmサイズの木質材料を含水率が45%から20%へ乾燥する場合、約45分を必要とする。さらに、10mm以下サイズの木質材料を含水率が45%から20%へ乾燥する場合、約15分を必要とする。このようにサイズが細かくなるに従って木質材料の単位重量当りの表面積が増加するため乾燥時間を短縮できる。本実施形態の木質粉砕工程10では、乾燥時間、後述する燃焼手段160に供給可能なサイズを考慮して、木質材料を最長辺1mm〜100mm、好ましくは5mm〜50mmの大きさに粉砕している。
[Wood crushing step 10]
The wood crushing step 10 is a step of crushing a wood material, which is plant biomass such as a demolition material, a thinning material, and a pruning material, to a predetermined size by a crusher.
FIG. 2 is a graph showing the relationship between the size of the wood material at a temperature condition of 100 ° C. and the drying time. The vertical axis of the graph represents the moisture content (%), and the horizontal axis represents time (min). When the moisture content is dried from 45% to 20% at a temperature condition of 100 ° C., as shown in the graph, it takes about 110 minutes. In addition, when drying a 30 mm size woody material from 45% to 20%, it takes about 45 minutes. Furthermore, when drying a wood material having a size of 10 mm or less from a moisture content of 45% to 20%, about 15 minutes are required. Since the surface area per unit weight of the wood material increases as the size becomes smaller in this way, the drying time can be shortened. In the wood crushing step 10 of the present embodiment, considering the drying time and the size that can be supplied to the combustion means 160 described later, the wood material is pulverized to a length of 1 mm to 100 mm, preferably 5 mm to 50 mm on the longest side. .

[吸水乾燥工程20]
吸水乾燥工程20は、ストックヤード、サイロなどの集積個所(容器内)に吸水材を敷き、その上に所定サイズに粉砕した木質材料を載せてそれを多層に構成して吸水乾燥する工程である。具体的には吸水材に木質材料に含まれる水分が吸い込まれて、吸水材がゲル状となり、木質材料を一定の水分量まで乾燥できる。本実施形態の吸水材は、一例として、ポリアクリル酸ナトリウム、ポリアクリル酸塩系、ポリスルホン酸塩系、無水マレイン酸塩系、ポリアクリルアミド系、ポリビニルアルコール系、ポリエチレンオキシド系、ポリアスパラギン酸塩系、ポリグルタミン酸塩系、ポリアルギン酸塩系のいずれか、又は複数の組み合わせを主原料とする高吸水性高分子、吸水性ポリマー、高吸水性樹脂、高分子吸収体などを土嚢袋等に収納、又はシート状に形成したものである。このような吸水材は、吸水後に乾燥させて再利用することができる。本発明の吸水乾燥工程20では、大気環境中(例えば、10℃から40℃の範囲)で、所定サイズに粉砕した木質材料を吸水材上に保管し乾燥している。本発明の吸水乾燥工程は、通常、大気環境中で行うことができるが、後段の排熱が十分に存在する場合には、吸水乾燥と同時に後述する排ガス処理手段170の浄化ガスを供給し温風乾燥するようにしてもよい。また、乾燥時間は特に限定しないが、投入した木質材料を乾燥しながら留めておく(乾燥時間を任意に調整する)ことができるため、発電システムへのバイオマス燃料の供給時期に合わせて、木質材料の投入から前述の供給時期までの間は吸水乾燥工程で保持しておくことが望ましい。
[Water absorption drying step 20]
The water absorption drying process 20 is a process in which a water absorption material is laid on an accumulation point (inside a container) such as a stockyard or a silo, and a wooden material crushed to a predetermined size is placed on the water absorption material to form a multilayer structure for water absorption drying. . Specifically, moisture contained in the wood material is sucked into the water absorbing material, the water absorbing material becomes a gel, and the wood material can be dried to a certain amount of moisture. The water-absorbing material of the present embodiment includes, for example, sodium polyacrylate, polyacrylate, polysulfonate, anhydrous maleate, polyacrylamide, polyvinyl alcohol, polyethylene oxide, polyaspartate , Containing a superabsorbent polymer, a superabsorbent polymer, a superabsorbent polymer, a polymer absorbent, etc., mainly composed of any one of polyglutamate, polyalginate, or a combination thereof in a sandbag, Or it formed in the sheet form. Such a water-absorbing material can be reused by drying after water absorption. In the water absorption drying step 20 of the present invention, the wood material pulverized to a predetermined size is stored on the water absorption material and dried in an atmospheric environment (for example, in the range of 10 ° C. to 40 ° C.). The water absorption drying process of the present invention can usually be carried out in an atmospheric environment. However, when there is sufficient exhaust heat in the subsequent stage, the purified gas of the exhaust gas treatment means 170 described later is supplied at the same time as the water absorption drying and the temperature is increased. You may make it wind dry. Although the drying time is not particularly limited, the input wood material can be kept dry while being dried (the drying time can be arbitrarily adjusted), so that the wood material can be adjusted according to the timing of supplying the biomass fuel to the power generation system. It is desirable to hold in the water absorption and drying process from the time of the charging until the aforementioned supply time.

図3は吸水乾燥工程の説明図である。(1)に示すように、吸水材22の上に、所定サイズに粉砕した木質材料24を敷く。その上に吸水材22を配置し、同様に所定サイズに粉砕した木質材料24を敷き、吸水材22と木質材料24を交互かつ多段に積層させている。   FIG. 3 is an explanatory diagram of the water absorption drying process. As shown in (1), a wooden material 24 crushed to a predetermined size is laid on the water absorbing material 22. The water absorbing material 22 is disposed thereon, and similarly, a wooden material 24 pulverized to a predetermined size is laid, and the water absorbing material 22 and the wooden material 24 are alternately laminated in multiple stages.

一例として高吸水性高分子を吸水材22として用いた場合、木質材料24は概ね100mm以下の厚さにほぼ均等に敷き詰める。(2)に示すように、多段に積層する手段としては、各層がスライド可能とし、傾斜させた際に乾燥した木質材料24が落下して下方の搬送コンベア上に載せることができる多段式のラック26を用いることができる。   As an example, when a highly water-absorbing polymer is used as the water-absorbing material 22, the wood material 24 is spread almost uniformly on a thickness of approximately 100 mm or less. As shown in (2), as a means for stacking in multiple stages, each layer is slidable, and when tilted, a dry wooden material 24 can be dropped and placed on a lower conveyor. 26 can be used.

これにより、吸水乾燥工程20を省スペースで行うことができる。また、上下の吸水材の間に木質材料を配置することにより、吸水材22と木質材料24との接触面積が増加し乾燥時間を短縮することができ、さらに外部雰囲気の湿度の影響を受けにくくなるため、木質材料24の水分量を一定に保つことができる。
図4はバイオマス燃料前処理方法の各工程の含水率を示すグラフである。同グラフの縦軸は、含水率(%)を示し、横軸は各工程を示している。同グラフに示すように、当初原料の含水率が70%の場合、木質粉砕工程10では含水率に変化はなく、吸水乾燥工程20において60%まで乾燥させている。本発明の吸水乾燥工程20は、加熱乾燥と比べ安価で再利用可能な吸水材を用いて、投入した木質材料を一時保管しながら乾燥させることを主目的とし、後段の発酵乾燥に適した含水率約60%前後に設定している。
Thereby, the water absorption drying process 20 can be performed in a space-saving manner. In addition, by arranging the wood material between the upper and lower water-absorbing materials, the contact area between the water-absorbing material 22 and the wood material 24 can be increased, the drying time can be shortened, and it is less susceptible to the humidity of the external atmosphere. Therefore, the moisture content of the wooden material 24 can be kept constant.
FIG. 4 is a graph showing the water content in each step of the biomass fuel pretreatment method. The vertical axis of the graph represents the moisture content (%), and the horizontal axis represents each step. As shown in the graph, when the moisture content of the initial raw material is 70%, the moisture content is not changed in the wood crushing step 10 and is dried to 60% in the water absorption drying step 20. The water-absorbing and drying step 20 of the present invention is mainly intended to dry the stored wood material while temporarily storing it using a water-absorbing material that is cheaper and reusable than heat drying, and is suitable for subsequent fermentation and drying. The rate is set around 60%.

[畜糞/木質混合工程30]
畜糞/木質混合工程30は、吸水乾燥工程20を行った木質材料に、畜糞を混合させている。畜糞は、鶏糞、牛糞、豚糞のうちいずれか、又は2種以上の混合物であり、木質材料との混合比(畜糞/木質材料)を0.01〜1、好ましくは0.1〜0.8としている。本発明の畜糞/木質混合工程30は、畜糞と木質材料が均一に混合できればよく、混合方法は特に限定していない。
[Livestock droppings / woody mixing step 30]
In the livestock droppings / woody mixing step 30, the livestock droppings are mixed with the woody material subjected to the water absorption drying step 20. Livestock droppings are any of chicken droppings, cow droppings, pig droppings, or a mixture of two or more kinds, and the mixing ratio with the woody material (livestock droppings / woody material) is 0.01 to 1, preferably 0.1 to 0. Eight. The livestock droppings / wood mixing step 30 of the present invention is not particularly limited as long as the livestock droppings and the woody material can be mixed uniformly.

また、畜糞/木質混合工程30は、総灰分量が総燃料重量の0.2以下、好ましくは0.15以下となるように混合することが望ましい。これにより、後段の燃焼手段160で発生する排ガス中のダストの排出量を低減して、排ガス処理手段170の負荷(処理する排ガス量)を低減することができる。   Moreover, it is desirable to mix the livestock manure / woody mixing step 30 so that the total ash content is 0.2 or less, preferably 0.15 or less of the total fuel weight. Thereby, it is possible to reduce the discharge amount of dust in the exhaust gas generated by the combustion unit 160 at the subsequent stage, and to reduce the load (the amount of exhaust gas to be processed) of the exhaust gas processing unit 170.

また、畜糞/木質混合工程30は、総燃料含有塩素濃度が500ppm以下、好ましくは100ppm以下となるように混合することが望ましい。これにより、鉄材等への腐食性を有する塩素を低減して、バイオマス発電システム200の壁、配管の腐食を低減することができる。   Further, it is desirable that the livestock excrement / woody mixing step 30 is mixed so that the total fuel-containing chlorine concentration is 500 ppm or less, preferably 100 ppm or less. Thereby, the corrosive chlorine to an iron material etc. can be reduced and the wall of the biomass power generation system 200 and corrosion of piping can be reduced.

[発酵乾燥工程40]
発酵乾燥工程40は、畜糞と木質材料が混合した状態で発酵させる工程である。畜糞と木質材料の混合物は、発酵により発熱するが、発酵温度が80℃以下となるように保持するのが望ましい。これは発酵温度が80℃を超えると木質材料が自然発火するおそれがあるためである。また本発明の発酵乾燥工程40は、発酵時間を1週間ほどに設定し、図4に示すように含水率が45%まで乾燥させている。本発明の発酵乾燥工程40は、あらかじめ吸水乾燥工程20を経て含水率が60%前後に調整されているため、発酵時間を約1週間、含水率40%〜50%となるように設定することができる。
[Fermentation drying step 40]
Fermentation drying process 40 is a process of making it ferment in the state where livestock dung and woody material were mixed. The mixture of livestock droppings and woody material generates heat by fermentation, but it is desirable to keep the fermentation temperature at 80 ° C. or lower. This is because if the fermentation temperature exceeds 80 ° C., the wood material may spontaneously ignite. In the fermentation drying process 40 of the present invention, the fermentation time is set to about one week, and the moisture content is dried to 45% as shown in FIG. In the fermentation drying process 40 of the present invention, the water content is adjusted to about 60% through the water absorption drying process 20 in advance, so that the fermentation time is set to about 40% to 50% for about 1 week. Can do.

[排熱乾燥工程50]
排熱乾燥工程50は、バイオマス発電システム200で排ガス処理された浄化ガスを用いて温風乾燥する工程である。本発明の排熱乾燥工程50は、後述する排ガス処理手段170で排ガス処理された浄化ガスを用いている。このような浄化ガスは、排ガス中に含まれる有害物質が浄化されており、バイオマス燃料の乾燥に用いても排ガスに含まれる有害物質の影響が及ばない。
[Exhaust heat drying step 50]
The exhaust heat drying process 50 is a process of drying with warm air using the purified gas that has been treated with the exhaust gas in the biomass power generation system 200. The exhaust heat drying process 50 of the present invention uses purified gas that has been subjected to exhaust gas treatment by an exhaust gas treatment means 170 described later. In such a purified gas, harmful substances contained in the exhaust gas are purified, and even when used for drying biomass fuel, the harmful substances contained in the exhaust gas are not affected.

浄化ガスは、一例としてガス温度が100℃〜160℃となり、排熱乾燥工程50を行う装置に供給している。排熱乾燥工程50は、図4に示すように含水率を20%に調整することができる。本発明の排熱乾燥工程50は、浄化ガスの供給量の増減により、含水率又は乾燥時間を制御することができる。これにより、バイオマス発電へのバイオマス燃料の供給時期に合わせることができる。また排熱乾燥工程50は、木質材料の含水率を、40%以下、好ましくは20%以下となるように設定している。   As an example, the purified gas has a gas temperature of 100 ° C. to 160 ° C. and is supplied to an apparatus that performs the exhaust heat drying step 50. In the exhaust heat drying step 50, the moisture content can be adjusted to 20% as shown in FIG. The exhaust heat drying process 50 of the present invention can control the moisture content or the drying time by increasing or decreasing the supply amount of the purified gas. Thereby, it can match with the supply time of the biomass fuel to biomass power generation. In the exhaust heat drying step 50, the moisture content of the wood material is set to 40% or less, preferably 20% or less.

これにより、本発明のバイオマス燃料前処理方法は、複数の乾燥工程を行うことで、当初原料の含水率に係わらずバイオマス燃料を所定含水率に容易に制御できる。また、バイオマス燃料の集積量と使用量のバランスが偏り、保管量が増えた状態においても、長期間乾燥工程内に留めることができる。   Thereby, the biomass fuel pretreatment method of the present invention can easily control the biomass fuel to a predetermined moisture content regardless of the moisture content of the initial raw material by performing a plurality of drying steps. Moreover, even when the balance between the amount of biomass fuel accumulated and the amount used is biased and the storage amount is increased, the biomass fuel can be kept in the drying process for a long period of time.

[バイオマス燃料前処理システム100]
図5は本発明のバイオマス燃料前処理システム及びバイオマス発電システムの説明図である。本発明のバイオマス燃料前処理システム100は、前述の木質粉砕工程10を行う木質粉砕手段110と、吸水乾燥工程20と行う吸水乾燥手段120と、畜糞/木質混合工程30を行う畜糞/木質乾燥手段130と、発酵乾燥工程40を行う発酵乾燥手段140と、排熱乾燥工程50を行う排熱乾燥手段150を主な基本構成としている。
[Biomass fuel pretreatment system 100]
FIG. 5 is an explanatory diagram of the biomass fuel pretreatment system and the biomass power generation system of the present invention. The biomass fuel pretreatment system 100 of the present invention includes a wood crushing means 110 that performs the above-described wood crushing process 10, a water absorption drying means 120 that performs the water absorption drying process 20, and a livestock dung / wood drying means that performs the animal dung / wood mixing process 30. 130, the fermentation drying means 140 that performs the fermentation drying process 40, and the exhaust heat drying means 150 that performs the exhaust heat drying process 50 are the main basic components.

木質粉砕手段110は、木質材料を最長辺1mm〜100mm、好ましくは5mm〜50mmの大きさに粉砕する粉砕機である。   The wood crushing means 110 is a crusher that crushes a wood material into a size having a longest side of 1 mm to 100 mm, preferably 5 mm to 50 mm.

吸水乾燥手段120は、吸水材を敷き、その上に所定サイズに粉砕した木質材料を載せて吸水乾燥するストックヤード、サイロなどの集積個所(容器内)である。また、吸水乾燥手段120は、集積個所で吸水材と木質材料を交互かつ多段に積層させることもできる。   The water absorption and drying means 120 is an accumulation point (inside a container) such as a stockyard or a silo in which a water absorbing material is laid and a wooden material crushed to a predetermined size is placed thereon to absorb and dry. Moreover, the water absorption drying means 120 can also laminate | stack a water absorption material and a wooden material alternately and in a multistage in an accumulation | aggregation location.

畜糞/木質混合手段130は、畜糞/木質材料の混合比を0.01〜1、好ましくは0.1〜0.8となるように混合するストックヤード、サイロなどの集積個所(容器内)である。また、畜糞/木質混合手段130は、総灰分量が総燃料重量の0.2以下、好ましくは0.15以下となるように混合することが望ましい。また、畜糞/木質混合手段130は、総燃料含有塩素濃度が500ppm以下、好ましくは100ppm以下となるように混合することが望ましい。   The animal manure / wood mixing means 130 is an accumulation site (in a container) such as a stockyard or silo for mixing the animal manure / wood material to a mixing ratio of 0.01 to 1, preferably 0.1 to 0.8. is there. Further, it is desirable that the livestock manure / wood mixing means 130 mix so that the total ash content is 0.2 or less, preferably 0.15 or less of the total fuel weight. Further, it is desirable that the livestock excrement / woody mixing means 130 mix so that the total fuel-containing chlorine concentration is 500 ppm or less, preferably 100 ppm or less.

発酵乾燥手段140は、畜糞と木質材料が混合した状態で発酵させるストックヤード、サイロなどの集積個所(容器内)である。   The fermentation drying means 140 is an accumulation site (inside a container) such as a stockyard or silo that is fermented in a state where livestock dung and woody material are mixed.

排熱乾燥手段150は、バイオマス発電システム200で排ガス処理された浄化ガスを用いて温風乾燥するストックヤード、サイロなどの集積個所(容器内)である。なお、各種手段の間にベルトコンベアなどの搬送手段を配置して、木質材料を搬送するように構成している。また、排熱乾燥手段は、バイオマス燃料を燃焼手段に供給するベルトコンベアの搬送面をケーシングで覆い、内部に浄化ガスを供給して搬送面上でバイオマス材料を一定の水分量まで乾燥する構成を採用してもよい。これにより、発酵乾燥工程からバイオマス発電システムへバイオマス燃料を搬送する間を利用して乾燥させることができる。   The exhaust heat drying means 150 is an accumulation location (inside the container) such as a stockyard or a silo that is dried with warm air using the purified gas that has been treated with the exhaust gas in the biomass power generation system 200. In addition, conveying means, such as a belt conveyor, is arranged between the various means so as to convey the wood material. Further, the exhaust heat drying means covers the conveyor surface of the belt conveyor that supplies biomass fuel to the combustion means with a casing, supplies purified gas inside, and dries the biomass material to a certain amount of moisture on the conveyor surface. It may be adopted. Thereby, it can be made to dry using a period during which biomass fuel is conveyed from the fermentation drying process to the biomass power generation system.

このように本発明のバイオマス燃料前処理システムは、複数の乾燥手段を行うことで、当初原料の含水率に係わらずバイオマス燃料を所定含水率に容易に制御できる。また、バイオマス燃料の集積量と使用量のバランスが偏り、保管量が増えた状態においても、長期間乾燥工程内に留めることができる。   Thus, the biomass fuel pretreatment system of the present invention can easily control the biomass fuel to a predetermined moisture content regardless of the moisture content of the initial raw material by performing a plurality of drying means. Moreover, even when the balance between the amount of biomass fuel accumulated and the amount used is biased and the storage amount is increased, the biomass fuel can be kept in the drying process for a long period of time.

[バイオマス発電システム200]
本発明のバイオマス発電システム200は、バイオマス燃料前処理システム100と、燃焼手段160と、排ガス処理手段170と、発電手段180を主な基本構成としている。バイオマス燃料前処理システム100は前述のシステムと同様の構成である。
[Biomass power generation system 200]
The biomass power generation system 200 of the present invention has a biomass fuel pretreatment system 100, a combustion means 160, an exhaust gas treatment means 170, and a power generation means 180 as main basic configurations. The biomass fuel pretreatment system 100 has the same configuration as the above-described system.

[燃焼手段160]
燃焼手段160は、バイオマス燃料前処理システム100で生産されたバイオマス燃料を燃焼可能な流動床、ストーカ炉などである。燃焼手段160は加熱バーナー(不図示)と、排ガスの熱を回収する熱交換機(不図示)を備え、排ガスと水との間で熱交換を行い、発電に利用可能な蒸気を発生させている。燃焼手段に流動床を適用した場合、木質材料の最長辺は5mm〜50mmの大きさに粉砕することが望ましい。
[Combustion means 160]
The combustion means 160 is a fluidized bed, a stoker furnace, or the like that can burn the biomass fuel produced by the biomass fuel pretreatment system 100. The combustion means 160 includes a heating burner (not shown) and a heat exchanger (not shown) that recovers the heat of the exhaust gas, and exchanges heat between the exhaust gas and water to generate steam that can be used for power generation. . When a fluidized bed is applied to the combustion means, the longest side of the wood material is desirably pulverized to a size of 5 mm to 50 mm.

[排ガス処理手段170]
排ガス処理手段170は、排ガス中に含まれる有害成分やダストを除去可能な還元触媒、電気集塵機、脱硫装置を組み合わせた構成である。排ガス処理手段170の還元触媒ではNOx等が除去され、電気集塵機では粒子状物質が除去され、脱硫装置では硫黄酸化物が除去された浄化ガスが大気中に放出される。排ガス処理手段170で排ガス処理された浄化ガスの一部は、前述の排熱処理工程50(排熱処理手段150)又は、吸水乾燥工程20(吸水乾燥手段120)の乾燥に用いている。
[Exhaust gas treatment means 170]
The exhaust gas treatment means 170 has a configuration in which a reduction catalyst capable of removing harmful components and dust contained in the exhaust gas, an electric dust collector, and a desulfurization apparatus are combined. NOx and the like are removed from the reduction catalyst of the exhaust gas treatment means 170, particulate matter is removed from the electrostatic precipitator, and purified gas from which sulfur oxides are removed is released into the atmosphere by the desulfurization apparatus. A part of the purified gas treated with the exhaust gas by the exhaust gas treatment means 170 is used for drying in the above-described exhaust heat treatment process 50 (exhaust heat treatment means 150) or the water absorption drying process 20 (water absorption drying means 120).

[発電手段180]
発電手段180は、熱エネルギーを電気に変換するものであり、タービンを備え、蒸気でタービンを回転させて発電させている。
このような構成のバイオマス発電システム200は、バイオマス燃料前処理システム100で生産された所定含水率のバイオマス燃料を用いているため燃焼効率がよい。また、木質材料と畜糞の総灰分量が総燃料重量の0.2%以下、好ましくは0.15%以下となるように混合されているため、排ガス中のダストの発生量を低減でき、排ガス処理手段の負荷を低減して安定した発電運転を実現できる。さらに、木質材料と畜糞の総燃料含有塩素濃度が500ppm以下、好ましくは100ppm以下となるように混合しているので鉄材等への腐食性を有する塩素を低減して、燃焼手段の壁や配管の腐食を防止できる。
[Power generation means 180]
The power generation means 180 converts thermal energy into electricity, includes a turbine, and generates power by rotating the turbine with steam.
Since the biomass power generation system 200 having such a configuration uses the biomass fuel having a predetermined water content produced by the biomass fuel pretreatment system 100, the combustion efficiency is good. Moreover, since the total ash content of the wood material and livestock excrement is mixed so that the total fuel weight is 0.2% or less, preferably 0.15% or less, the amount of dust generated in the exhaust gas can be reduced, and the exhaust gas A stable power generation operation can be realized by reducing the load on the processing means. Furthermore, since the total fuel-containing chlorine concentration of the wood material and livestock manure is mixed to be 500 ppm or less, preferably 100 ppm or less, chlorine that is corrosive to iron materials and the like is reduced, and the walls of the combustion means and piping Corrosion can be prevented.

本発明は、特に、木質材料及び畜糞を混合したバイオマス燃料を用いて発電するバイオマス発電システムに広く適用することができる。   In particular, the present invention can be widely applied to a biomass power generation system that generates power using a biomass fuel obtained by mixing a woody material and livestock dung.

10………木質粉砕工程、20………吸水乾燥工程、22………吸水材、24………木質材料、26………ラック、30………畜糞/木質混合工程、40………発酵乾燥工程、50………排熱乾燥工程、100………バイオマス燃料前処理システム、110………木質粉砕手段、120………吸水乾燥手段、130………畜糞/木質混合手段、140………発酵乾燥手段、150………排熱乾燥手段、160………燃焼手段、170………排ガス処理手段、180………発電手段、200………バイオマス発電システム。 10 ......... Wood crushing step, 20 ......... Water-absorbing and drying step, 22 ......... Water-absorbing material, 24 ......... Wooden material, 26 ......... Rack, 30 ...... Animal dung / wood mixing step, 40 ......... Fermentation drying process, 50 .... exhaust heat drying process, 100 .... biomass fuel pretreatment system, 110 .... wood pulverization means, 120 .... water absorption drying means, 130 .... livestock dung / wood mixing means, 140. ... Fermentation drying means, 150 ......... Waste heat drying means, 160 ... ... Combustion means, 170 ... ... Exhaust gas treatment means, 180 ... ... Power generation means, 200 ... ... Biomass power generation system.

Claims (6)

粉砕した木質材料を吸水材で吸水して乾燥させる吸水乾燥工程と、
前記木質材料に畜糞を混入して発酵させる発酵乾燥工程と、
バイオマス発電で排ガス処理後の浄化ガスを前記木質材料に供給して所定含水率に乾燥させる排熱乾燥工程と、
を有することを特徴とするバイオマス燃料前処理方法。
A water absorption drying process in which the pulverized wood material is absorbed with a water absorbing material and dried;
A fermentation drying process in which livestock dung is mixed and fermented with the wooden material;
An exhaust heat drying step of supplying purified gas after exhaust gas treatment with biomass power generation to the wood material and drying it to a predetermined moisture content;
A biomass fuel pretreatment method comprising:
前記吸水乾燥工程は、前記吸水材と前記木質材料を交互、かつ多段に積層させて前記木質材料を前記吸水材で覆うようにして一定の水分量まで乾燥させることを特徴とする請求項1に記載のバイオマス燃料前処理方法。   The water absorption drying step is characterized in that the water absorption material and the wood material are alternately laminated in multiple stages, and the wood material is covered with the water absorption material and dried to a certain amount of water. The biomass fuel pretreatment method as described. 前記木質材料と前記畜糞は、総灰分量が総燃料重量の0.2以下、好ましくは0.15以下となるように混合することを特徴とする請求項1又は2に記載のバイオマス燃料前処理方法。   The biomass fuel pretreatment according to claim 1 or 2, wherein the wood material and the animal manure are mixed so that the total ash content is 0.2 or less, preferably 0.15 or less of the total fuel weight. Method. 前記木質材料と前記畜糞は、総燃料含有塩素濃度が500ppm以下、好ましくは100ppm以下となるように混合することを特徴とする請求項1ないし3のいずれか1項に記載のバイオマス燃料前処理方法。   The biomass fuel pretreatment method according to any one of claims 1 to 3, wherein the wooden material and the animal manure are mixed so that a total fuel-containing chlorine concentration is 500 ppm or less, preferably 100 ppm or less. . 粉砕した木質材料を吸水材で吸水して乾燥させる吸水乾燥手段と、
前記木質材料に畜糞を混入して発酵させる発酵乾燥手段と、
バイオマス発電で排ガス処理後の浄化ガスを前記木質材料に供給して所定含水率に乾燥させる排熱乾燥手段と、
を有することを特徴とするバイオマス燃料前処理システム。
Water absorption drying means for absorbing and drying the pulverized wooden material with a water absorbing material,
Fermentation drying means for mixing and fermenting livestock dung into the wooden material,
Waste heat drying means for supplying purified gas after exhaust gas treatment with biomass power generation to the wood material and drying it to a predetermined moisture content;
A biomass fuel pretreatment system comprising:
請求項5に記載のバイオマス燃料前処理システムと、
前記バイオマス燃料前処理システムで生産したバイオマス燃料を燃焼する燃焼手段と、
前記燃焼手段の熱エネルギーを電気に変換する発電手段と、
を有することを特徴とするバイオマス発電システム。
A biomass fuel pretreatment system according to claim 5;
Combustion means for burning biomass fuel produced by the biomass fuel pretreatment system;
Power generation means for converting thermal energy of the combustion means into electricity;
A biomass power generation system characterized by comprising:
JP2014090104A 2014-04-24 2014-04-24 Biomass fuel pretreatment method, its system, and biomass heat generation system using the same Pending JP2015209452A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2017125151A (en) * 2016-01-15 2017-07-20 東邦瓦斯株式会社 Method for manufacturing biomass solid material
CN107880913A (en) * 2017-12-27 2018-04-06 大连地拓环境科技有限公司 A kind of biogas residue machine-made carbon and preparation method thereof
CN110923032A (en) * 2019-12-05 2020-03-27 西安圣华农业科技股份有限公司 Method for preparing biomass fuel by using chicken manure

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2017125151A (en) * 2016-01-15 2017-07-20 東邦瓦斯株式会社 Method for manufacturing biomass solid material
CN107880913A (en) * 2017-12-27 2018-04-06 大连地拓环境科技有限公司 A kind of biogas residue machine-made carbon and preparation method thereof
CN110923032A (en) * 2019-12-05 2020-03-27 西安圣华农业科技股份有限公司 Method for preparing biomass fuel by using chicken manure

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