JP2006124496A - Device and method for thermally co-decomposing coal with biomass - Google Patents

Device and method for thermally co-decomposing coal with biomass Download PDF

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JP2006124496A
JP2006124496A JP2004313716A JP2004313716A JP2006124496A JP 2006124496 A JP2006124496 A JP 2006124496A JP 2004313716 A JP2004313716 A JP 2004313716A JP 2004313716 A JP2004313716 A JP 2004313716A JP 2006124496 A JP2006124496 A JP 2006124496A
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biomass
coal
gas
pyrolysis
gasification
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Hiroyuki Kotsuru
広行 小水流
Takafumi Kawamura
隆文 河村
Yasushi Takagi
泰 高木
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Nippon Steel Corp
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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
    • 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

Abstract

<P>PROBLEM TO BE SOLVED: To prevent the formation of soot in a thermal decomposition device, becoming the cause of operational troubles on thermally co-decomposing coal with biomass, and improving the yield of gas, tar and char. <P>SOLUTION: This device and method for thermally co-decomposing the coal with biomass is characterized by using a reaction oven of the thermal decomposition device having a structure with two chambers and two stages, wherein the lower stage is a gasifying oven 2 and the upper stage is a thermal decomposition oven 1, blowing carbonaceous raw materials 13 together with oxygen 14, or with oxygen 14 and steam 15 through a gasifying burner 5 into the gasifying oven to cause a partial oxidation reaction for generating a high temperature gas, then introducing the high temperature gas into the thermal decomposition oven 1 and performing the thermally decomposing gasification is characterized by installing a biomass-blowing in nozzle 4 at the lower direction of the coal-blowing nozzle 3, mixing the biomass with the gasified gas and then putting the coal into the oven. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、石炭およびバイオマスを同時に気流層中で急速に熱分解・ガス化させて、ガス、タール、およびチャーを製造する装置および方法に関するものである。   The present invention relates to an apparatus and method for producing gas, tar, and char by rapidly pyrolyzing and gasifying coal and biomass simultaneously in an air flow layer.

現在までに、石炭を高温で熱分解し、直接メタンを始めとする炭化水素ガスおよびベンゼン−トルエン−キシレン(BTX)を始めとするオイルを製造する石炭熱分解プロセスがいくつか提案されている。   To date, several coal pyrolysis processes have been proposed that pyrolyze coal at high temperatures to produce hydrocarbon gases such as methane directly and oils such as benzene-toluene-xylene (BTX).

特許文献1において、石炭および炭素質原料の酸素によるガス化で生じる高温ガス中に、石炭を吹き込み、石炭の急速加熱・熱分解反応を気流層で行わせ、特にBTXを高収率で得ることが可能であり、かつ、設備のイニシャルコストを低減し、熱補給の必要がない高い熱効率の石炭熱分解方法が示されている。特許文献1では、熱分解される原料は「石炭および炭素質原料」とされているが、石炭と炭素質原料のひとつであるバイオマスとを同時に熱分解する方法については述べられていない。バイオマスを熱分解すると石炭を熱分解した場合と同様に、水素、一酸化炭素、メタン等の炭化水素系ガス、タール、炭化物などが生成される。   In Patent Document 1, coal is blown into a high-temperature gas generated by gasification of coal and carbonaceous raw material with oxygen, and rapid heating / pyrolysis reaction of coal is performed in an air flow layer, and in particular, BTX is obtained in a high yield. It is possible to reduce the initial cost of the equipment, and there is shown a high thermal efficiency coal pyrolysis method that does not require heat supply. In Patent Document 1, although the raw material to be pyrolyzed is “coal and carbonaceous raw material”, it does not describe a method of simultaneously pyrolyzing coal and biomass which is one of carbonaceous raw materials. When biomass is pyrolyzed, hydrocarbon gases such as hydrogen, carbon monoxide, and methane, tar, and carbide are generated as in the case of coal pyrolysis.

近年、発電等にバイオマスが燃料として使用されつつある。しかし、熱分解して得られたガスを工場の燃料や発電に使用する場合には、大量のバイオマスが必要となる。しかし大量のバイオマスを使用することについては収集やハンドリングで問題があり、バイオマスのみで熱分解温度を維持できない場合には石炭を同時に吹き込むことでバイオマス収集量の問題は回避できる。共熱分解とはこのような収集に問題のあるバイオマスを石炭と同時に熱分解することで、効率よく熱分解生成物を製造することを目的とした方法である。   In recent years, biomass is being used as a fuel for power generation and the like. However, when the gas obtained by pyrolysis is used for factory fuel or power generation, a large amount of biomass is required. However, there is a problem in collection and handling when using a large amount of biomass, and when the pyrolysis temperature cannot be maintained with only biomass, the problem of biomass collection can be avoided by blowing coal at the same time. Co-pyrolysis is a method aimed at efficiently producing pyrolysis products by thermally decomposing biomass that has a problem in collection at the same time as coal.

また、特許文献2において、上段に排熱回収ボイラーを有する噴流床ガス化炉の下部に、石炭粒子を導入して高温の石炭生成ガスを生成させ、その上部にバイオマス燃料を導入して高温の石炭生成ガスと接触させることで、ガス化炉で生成した高温の石炭生成ガスは、低温化されて排熱回収ボイラーにおける灰の堆積・融着に伴う障害の発生を軽減できる石炭の加圧噴流床ガス化方法が開示されている。   Further, in Patent Document 2, coal particles are introduced into a lower part of a spouted bed gasification furnace having an exhaust heat recovery boiler in the upper stage to generate high-temperature coal-forming gas, and biomass fuel is introduced into the upper part to introduce high-temperature coal gas. Pressurized coal jet that can reduce the occurrence of obstacles caused by ash accumulation and fusion in exhaust heat recovery boilers by reducing the temperature of the high-temperature coal-produced gas generated in the gasifier by bringing it into contact with the coal-produced gas A bed gasification method is disclosed.

バイオマスとは生物量の総称であり、FAO(国連食糧農業機関)によれば、農業系(麦わら、サトウキビ、米糠、草木等)、林業系(製紙廃棄物、製材廃材、除間伐材、薪炭林等)、畜産系(家畜廃棄物)、水産系(水産加工残滓)、廃棄物系(生ゴミ、RDF(ゴミ固形化燃料;Refuse Derived Fuel)、庭木、建設廃材、下水汚泥)等に分類される。本明細書において、バイオマスについての定義は上記FAOの定義に準ずる。例えば、木質バイオマスでは、FAO定義における林業系バイオマスと、廃棄物系バイオマスの一部を指し、製紙廃棄物、製材廃材、除間伐材、薪炭林、庭木、木材などの建設廃材、などが該当する。木質バイオマスは含有水分が少なく(50質量%以下)湿分基準の発熱量も高いため、熱分解の際にガス、固体エネルギーを効率よく回収できる。木質バイオマス以外のバイオマスに関しても、基本的に保有湿分基準発熱量が、水分の気化熱+バイオマス自身の顕熱上昇+分解熱以上であれば、有効なエネルギー源になりうる。また、バイオマスは、燃焼時に地球環境に影響を与える二酸化炭素を殆ど生成しないカーボンニュートラルな材料である。
特開平5−295371号公報 特開2002−194363号公報
Biomass is a collective term for biomass, and according to FAO (United Nations Food and Agriculture Organization), agriculture (wheat straw, sugar cane, rice bran, vegetation, etc.), forestry (paper waste, sawn timber, thinned wood, wood-burning forest) Etc.), livestock (livestock waste), fisheries (fishery processing residue), waste (raw garbage, RDF (refined solid fuel), garden trees, construction waste, sewage sludge), etc. The In this specification, the definition about biomass is based on the said FAO definition. For example, woody biomass refers to forestry biomass in the FAO definition and part of waste biomass, and includes papermaking waste, sawn timber, thinned wood, firewood forest, garden wood, construction waste such as wood, etc. . Woody biomass has a low water content (50 mass% or less) and a high heat generation amount based on moisture, so that gas and solid energy can be efficiently recovered during pyrolysis. Regarding biomass other than woody biomass, basically, if the retained moisture reference calorific value is equal to or higher than the heat of vaporization of moisture + the sensible heat rise of the biomass itself + the heat of decomposition, it can be an effective energy source. Biomass is a carbon neutral material that hardly generates carbon dioxide that affects the global environment during combustion.
JP-A-5-295371 JP 2002-194363 A

特許文献1において提案されているプロセスは、BTXを始めとするオイルを高い収率で製造することが可能であり、かつ、設備のイニシャルコストを低減し、熱補給のない高い熱効率の石炭熱分解方法である。この方法においては、ガス化炉から発生する高温のガス化ガスと熱分解炉に投入された石炭とが混合される際に、部分的に石炭から発生した揮発分の温度が上がり過ぎることがある。その結果、揮発分の分解が進み過ぎて、有用なオイルや炭化水素ガスとならずに、すすが発生する場合があった。すすが発生すると、有用なオイルや炭化水素ガスが減少するだけでなく、すすの熱分解炉内や配管内での付着や生成するタールへの混入などのトラブル原因となる。   The process proposed in Patent Document 1 is capable of producing BTX and other oils with a high yield, reducing the initial cost of the equipment, and high thermal efficiency coal pyrolysis without heat supply Is the method. In this method, when the high-temperature gasification gas generated from the gasification furnace and the coal put into the pyrolysis furnace are mixed, the temperature of the volatile matter partially generated from the coal may rise too much. . As a result, decomposition of volatile matter has progressed too much, and soot may be generated without becoming a useful oil or hydrocarbon gas. When soot is generated, not only the useful oil and hydrocarbon gas are reduced, but also causes troubles such as adhesion of soot in the pyrolysis furnace and piping and mixing into the generated tar.

また、特許文献2に記載の方法は、バイオマスのみを石炭生成ガスに吹き込み、排熱回収ボイラーに導入されるガス温度を低下させるもので、目的とする生成物もガスだけである。すなわち、ガスだけでなく、タール、およびチャー等の多種類の生成物を回収することは、特許文献2に記載の方法ではできない。   Moreover, the method described in Patent Document 2 blows only biomass into the coal product gas and lowers the gas temperature introduced into the exhaust heat recovery boiler, and the target product is only gas. That is, the method described in Patent Document 2 cannot recover not only gas but also various types of products such as tar and char.

本発明の目的は、石炭とバイオマスとを一緒に熱分解する際に、熱分解炉内において生成する揮発分の過度の分解を防ぎ、ガス、タールおよびチャー等の多種類の生成物の収率を向上させ、すすの発生による操業トラブルを防ぐことにある。   The object of the present invention is to prevent excessive decomposition of volatile matter generated in a pyrolysis furnace when coal and biomass are pyrolyzed together, and yield of various kinds of products such as gas, tar and char. It is to prevent operational troubles caused by soot.

かかる問題を解決するため、本発明の要旨とするところは、以下の通りである。   In order to solve this problem, the gist of the present invention is as follows.

(1)下段がガス化炉で上段が熱分解炉である二段構造の石炭およびバイオマスの共熱分解装置において、前記熱分解炉の側壁に上方から順に、石炭吹き込みノズル、およびバイオマス吹き込みノズルを設けることを特徴とする石炭およびバイオマスの共熱分解装置。   (1) In a two-stage coal and biomass co-pyrolysis apparatus in which the lower stage is a gasification furnace and the upper stage is a pyrolysis furnace, a coal blowing nozzle and a biomass blowing nozzle are sequentially arranged on the side wall of the pyrolysis furnace from above. An apparatus for co-pyrolysis of coal and biomass, characterized by being provided.

(2)(1)に記載の石炭およびバイオマスの共熱分解装置を用い、前記ガス化炉において炭素質原料を酸素または酸素および水蒸気と共に吹き込んで、ガス化ガスを発生させ、前記ガス化ガスを前記熱分解炉に導入し、前記バイオマス吹き込みノズルからバイオマスを投入して前記バイオマスの熱分解を行ない、生成した混合ガス中に前記石炭吹き込みノズルから石炭を投入して、ガス、タールおよびチャーを生成することを特徴とする石炭およびバイオマスの共熱分解方法。   (2) Using the coal and biomass co-pyrolysis apparatus according to (1), a carbonaceous raw material is blown together with oxygen or oxygen and water vapor in the gasification furnace to generate gasification gas, and the gasification gas is Introduced into the pyrolysis furnace, the biomass is injected from the biomass blowing nozzle to thermally decompose the biomass, and the coal is injected into the generated mixed gas from the coal blowing nozzle to generate gas, tar and char A method for co-pyrolysis of coal and biomass.

尚、本発明における「炭素質原料」とは、炭素、および水素で主に構成される物質を指す。炭素質原料として例えば、石炭を熱分解した際に発生する固体のチャーや液体のタール、石油、石油残渣、石油コークス、石炭、石炭コークス、バイオマス、プラスチック類も含まれる。   The “carbonaceous raw material” in the present invention refers to a substance mainly composed of carbon and hydrogen. Examples of the carbonaceous raw material include solid char and liquid tar generated when pyrolyzing coal, petroleum, petroleum residue, petroleum coke, coal, coal coke, biomass, and plastics.

また、バイオマスと石炭との共熱分解とは、バイオマスと石炭とを共に同じ反応器で熱分解することである。バイオマスを単独で熱分解する場合、共熱分解に比べて大量のバイオマスが必要となる。大量にバイオマスを使用する場合には収集やハンドリングで問題となるおそれがある。しかし、共熱分解を行うことにより、不足するバイオマスを石炭で補うことで効率よく熱分解生成物を製造することが可能となる。   The co-pyrolysis of biomass and coal is to pyrolyze both biomass and coal in the same reactor. When biomass is pyrolyzed alone, a large amount of biomass is required compared to co-pyrolysis. When using a large amount of biomass, there is a risk of problems in collection and handling. However, by performing co-pyrolysis, it becomes possible to efficiently produce a pyrolysis product by supplementing the shortage of biomass with coal.

本発明により、熱分解炉内において生成する揮発分の過度の分解を防ぎ、生成ガスの発熱量の上昇、ガス、タールおよびチャーの収率の上昇が可能となる。さらに、すすの発生を低減させることで、すすの熱分解炉や配管内での付着を防ぐことが可能となる。   According to the present invention, it is possible to prevent excessive decomposition of volatile components generated in the pyrolysis furnace, increase the calorific value of the generated gas, and increase the yield of gas, tar and char. Furthermore, by reducing the generation of soot, it becomes possible to prevent the soot from adhering in a pyrolysis furnace or piping.

以下に、本発明を詳細に説明する。図1に本発明に係る石炭およびバイオマスの共熱分解装置の概略図を例示するが、装置の形状は図1に限定されない。本装置は、熱分解炉1、およびガス化炉2で主に構成される。   The present invention is described in detail below. FIG. 1 illustrates a schematic diagram of a coal and biomass co-pyrolysis apparatus according to the present invention, but the shape of the apparatus is not limited to FIG. 1. This apparatus mainly includes a pyrolysis furnace 1 and a gasification furnace 2.

ガス化される炭素質原料13に含まれる灰分は1500℃程度の高温により溶融状態のスラグ16となるため、ガス化炉2の下部には、スラグ16を排出できるように、スラグタップ7およびスラグ16を捕集する水槽17を設けることが好ましい。   Since the ash contained in the carbonaceous raw material 13 to be gasified becomes a molten slag 16 at a high temperature of about 1500 ° C., the slag tap 7 and the slag are disposed below the gasification furnace 2 so that the slag 16 can be discharged. It is preferable to provide a water tank 17 for collecting 16.

ガス化炉2には、微粉砕された炭素質原料13を酸素14、または、酸素14および水蒸気15と共に供給するための、1本または複数本のガス化バーナー5が設置されている。ガス化炉2においては、投入される炭素質原料13に含まれる炭素、水素をできるだけCO、Hに転換するため炭素質原料13と酸素14、水蒸気15を素早く混合し炭素質原料13から発生する揮発分をすす化する前に酸素14や水蒸気15と反応させる必要がある。そのために、ガス化炉2への炭素質原料13と酸素14、水蒸気15はガス化バーナー5で吹き込まれる。ガス化バーナー5の形状の例としては、二重管の内側を炭素質原料13、外側を酸素14および水蒸気15が流れる構造などがある。 The gasification furnace 2 is provided with one or a plurality of gasification burners 5 for supplying the finely pulverized carbonaceous raw material 13 together with the oxygen 14 or the oxygen 14 and the water vapor 15. In the gasifier 2, carbon and hydrogen contained in the carbonaceous raw material 13 to be input are converted into CO and H 2 as much as possible. It is necessary to react with oxygen 14 and water vapor 15 before sooting the volatile matter. For this purpose, the carbonaceous raw material 13, the oxygen 14, and the water vapor 15 into the gasification furnace 2 are blown by the gasification burner 5. Examples of the shape of the gasification burner 5 include a structure in which a carbonaceous raw material 13 flows inside the double tube and oxygen 14 and water vapor 15 flow outside.

バイオマス12を投入するバイオマス吹き込みノズル4の位置は、熱分解炉1において、石炭吹き込みノズル3の設置位置より下方にする。すなわち、石炭吹き込みノズル3とガス化炉2との間に設置すれば良いが、ガス化ガス8に含まれる微小な灰分が熱分解炉1の炉壁に付着することを防ぐために、スロート6を除く熱分解炉1の下端部周辺に設置することが好ましい。   The position of the biomass blowing nozzle 4 into which the biomass 12 is introduced is set lower than the installation position of the coal blowing nozzle 3 in the pyrolysis furnace 1. That is, the throat 6 may be installed between the coal blowing nozzle 3 and the gasification furnace 2, but in order to prevent minute ash contained in the gasification gas 8 from adhering to the furnace wall of the pyrolysis furnace 1. It is preferable to install it around the lower end of the pyrolysis furnace 1 to be removed.

ガス化炉2に微粉砕された炭素質原料13を酸素14、または、酸素14および水蒸気15と共にガス化バーナー5を介して吹き込み、発生した水素、一酸化炭素、二酸化炭素、および水蒸気を主成分とするガス化ガス8は、スロート6を介してガス化炉2と直結している熱分解炉1へ導入される。本発明においては、スロート6は熱分解炉1に含まれるものとする。また、ガス化ガス8の残りのガス成分は、N及び微量の副生成物である。 The finely pulverized carbonaceous raw material 13 is blown into the gasification furnace 2 through the gasification burner 5 together with oxygen 14 or oxygen 14 and water vapor 15, and the generated hydrogen, carbon monoxide, carbon dioxide, and water vapor are the main components. The gasified gas 8 is introduced into the pyrolysis furnace 1 directly connected to the gasification furnace 2 through the throat 6. In the present invention, the throat 6 is assumed to be included in the pyrolysis furnace 1. Further, the remaining gas components of the gasification gas 8 are N 2 and a small amount of by-products.

導入されたガス化ガス8は、バイオマス吹き込みノズル4から導入されるバイオマス12によって冷却され、その一方でバイオマス12は熱分解される。その熱分解により生成した混合ガス9中に、微粉砕された石炭11が石炭吹き込みノズル3より投入される。投入された石炭11は、混合ガス9により加熱・熱分解され、ガス、タールおよびチャーを生成し、生成ガス、タール、およびチャー10となり排出される。   The introduced gasified gas 8 is cooled by the biomass 12 introduced from the biomass blowing nozzle 4, while the biomass 12 is pyrolyzed. Finely pulverized coal 11 is introduced from the coal blowing nozzle 3 into the mixed gas 9 generated by the thermal decomposition. The charged coal 11 is heated and pyrolyzed by the mixed gas 9 to generate gas, tar and char, and is discharged as product gas, tar and char 10.

ここで、ガス化炉2の温度は一般的に石炭に含まれる灰分の融点以上で操業され、好ましくは1200〜1700℃、石炭の反応性、放散熱量、灰の溶融排出性能から考えると、より好ましくは1400〜1600℃である。また、スロート6から石炭吹き込みノズル3までを除く熱分解炉1の温度は、生成するタールの量や性状、生成ガスの量や組成を考慮して決定されるが600℃〜1100℃が好ましく、どのような生成物を望むのかにより適正範囲は異なるが、タール成分を多く望む場合は600〜900℃、ガス成分を多く望む場合は1000〜1100℃がより好ましい。   Here, the temperature of the gasification furnace 2 is generally operated at the melting point or higher of the ash contained in the coal, preferably 1200 to 1700 ° C., considering the reactivity of the coal, the amount of heat dissipated, and the ash melting and discharging performance, Preferably it is 1400-1600 degreeC. Further, the temperature of the pyrolysis furnace 1 excluding the throat 6 to the coal blowing nozzle 3 is determined in consideration of the amount and properties of tar to be generated, the amount and composition of the generated gas, and is preferably 600 ° C to 1100 ° C. The appropriate range varies depending on what kind of product is desired, but 600 to 900 ° C. is more preferable when many tar components are desired, and 1000 to 1100 ° C. is more desirable when many gas components are desired.

ガス化炉2からのガス化ガス8は、バイオマス吹き込みノズル4から投入されるガス化ガス8よりも低い温度のバイオマス12と混合されることにより、生じた混合ガス9の温度をガス化ガス8の温度よりも下げることが可能となる。これにより、高温のガス化ガス8が直接石炭11と接触することは避けられ、石炭11から発生する揮発分と水素との反応は抑制され、過度に熱分解が進んですすが発生することを防止できる。バイオマス12は、石炭11に比べて多量の酸素原子を含有しており、高温のガス化ガス8に触れてもすすの発生量は少なく、BTXなどのオイルを多く含む、軽質のタールを得ることができる。BTXは化学合成などで多用される有用なオイルである。   The gasification gas 8 from the gasification furnace 2 is mixed with the biomass 12 having a temperature lower than that of the gasification gas 8 introduced from the biomass blowing nozzle 4, so that the temperature of the resulting mixed gas 9 is changed to the gasification gas 8. It is possible to lower the temperature below. As a result, it is avoided that the high-temperature gasification gas 8 is in direct contact with the coal 11, the reaction between the volatile matter generated from the coal 11 and hydrogen is suppressed, and excessive pyrolysis proceeds. Can be prevented. The biomass 12 contains a larger amount of oxygen atoms than the coal 11, so that the amount of soot generated is small even when it touches the high-temperature gasification gas 8, and a light tar containing a large amount of oil such as BTX is obtained. Can do. BTX is a useful oil frequently used in chemical synthesis.

使用される石炭11および炭素質原料13の粒径は、熱分解速度を速くして熱分解生成物収率を増加させ、ガス化反応率を向上させるために、できるだけ小さいことが望ましい。石炭11は、微粉炭燃焼で一般に用いられる数十μm以下の粒径であると、ガス化反応性および熱分解生成物収率は確保できるため好ましい。その他の炭素質原料13は、プラスチック類の場合は反応性が高いため粒径が数mm以下でもガス化が進行し、下水汚泥の場合は1mm程度以下、石炭チャーの場合は数十μm以下が好ましい。   The particle sizes of the coal 11 and the carbonaceous raw material 13 used are desirably as small as possible in order to increase the pyrolysis rate by increasing the thermal decomposition rate and to improve the gasification reaction rate. It is preferable that the coal 11 has a particle size of several tens of μm or less that is generally used in pulverized coal combustion because gasification reactivity and yield of thermal decomposition products can be secured. The other carbonaceous raw material 13 is highly reactive in the case of plastics, and thus gasification proceeds even if the particle size is several mm or less. preferable.

また、バイオマス12の粒径についても小さい方が好ましいが、バイオマスは反応性が高く数mm程度の粒径でも問題無く本発明効果を発揮することが可能である。特に限定されないが、バイオマス12としては、製紙廃棄物(パルプ黒液、チップダスト)、製材廃材(樹皮、のこ屑、鉋屑)、林地残材(枝、葉、梢、端尺材、低質材)、除間伐材(スギ、ヒノキ、マツ類)特用林産からのもの(食用菌類の廃ホダ木)、薪炭林(シイ、コナラ、マツ)、短伐期林業(ヤナギ、ポプラ、ユーカリ、マツ)および剪定枝条(街路樹、庭木)などの木質バイオマスであることが好ましい。   Moreover, although it is preferable that the particle size of the biomass 12 is small, the biomass is highly reactive and even if the particle size is about several mm, the effect of the present invention can be exhibited without any problem. Although not particularly limited, the biomass 12 includes papermaking waste (pulp black liquor, chip dust), sawn wood waste (bark, sawdust, sawdust), forest land residue (branches, leaves, treetops, edge material, low quality material) ), Thinned wood (cedar, cypress, pine) from special forest (waste wood of edible fungi), firewood forest (shii, oak, pine), short-term forestry (willow, poplar, eucalyptus, pine) ) And pruned branches (street trees, garden trees).

高温のガス化ガス8とバイオマス12との混合後の温度は、石炭11と混合すると1400℃を超える場合にはすすが発生し始めるおそれがあること、600℃以下の低温では石炭の熱分解反応が進行しないおそれがあることから600℃〜1400℃とすることが好ましい。高温のガス化ガス8とバイオマス12との混合後のガス温度の調整は、バイオマス12の投入量の増減で行なう。   If the temperature after mixing the high-temperature gasification gas 8 and the biomass 12 exceeds 1400 ° C. when mixed with the coal 11, soot may start to be generated, and if the temperature is below 600 ° C., the pyrolysis reaction of coal Is preferably set to 600 ° C. to 1400 ° C. Adjustment of the gas temperature after mixing the high-temperature gasification gas 8 and the biomass 12 is performed by increasing or decreasing the input amount of the biomass 12.

バイオマス12と熱分解炉1に投入される石炭11との投入割合は、熱分解炉1の出口温度の設定により異なるが、石炭11とバイオマス12との総量におけるバイオマス12の比率を、20質量%〜60質量%とすることが好ましい。前記質量の範囲内であると、混合ガス9の温度を石炭11からのすす発生を抑える温度にできる点で好ましい。   The charging ratio of the biomass 12 and the coal 11 input to the pyrolysis furnace 1 varies depending on the setting of the outlet temperature of the pyrolysis furnace 1, but the ratio of the biomass 12 in the total amount of the coal 11 and biomass 12 is 20% by mass. It is preferable to set it as -60 mass%. It is preferable in the range of the said mass at the point which can make the temperature of the mixed gas 9 into the temperature which suppresses the generation of soot from the coal 11.

次に実施例を挙げて本発明を具体的に説明するが、これらの実施例は何ら本発明を制限するものではない。   EXAMPLES Next, although an Example is given and this invention is demonstrated concretely, these Examples do not restrict | limit this invention at all.

(実施例)図1に記載の装置を用い、石炭処理量750kg/h、バイオマス処理量250kg/hの処理条件における本発明の実施例を以下に示す。本実施例ではバイオマスとして木質バイオマスである木材チップ(水分15質量%)を、ガス化炉でガス化される炭素質原料として石炭を使用した。   (Embodiment) An embodiment of the present invention under the processing conditions of a coal throughput of 750 kg / h and a biomass throughput of 250 kg / h using the apparatus shown in FIG. In this embodiment, wood chips (water content 15% by mass), which are woody biomass, are used as biomass, and coal is used as a carbonaceous raw material that is gasified in a gasifier.

ガス化炉には石炭500kg/h、酸素376Nm/h、水蒸気30kg/hを投入する。ガス化炉内は、温度1550℃、圧力0.3MPaで操業され、石炭は部分酸化されて、水素16%、CO一酸化炭素47%、CO二酸化炭素13.5%、水蒸気20%、および窒素3.5%のガス化ガス970Nm/hが発生した。熱分解炉の直径は45cm、高さは7m、石炭吹き込みノズルは熱分解炉の直胴部の下端(図1における、スロート及びその上の傾斜部は含まず)より上方0.5mの場所に対向して2カ所、バイオマス吹き込みノズルは熱分解炉直胴部の下端に対向して2カ所設置されている。ガス化炉、熱分解炉で使用する石炭は粒径40μm程度に微粉砕したものを、熱分解炉で使用するバイオマス(木材チップ)は5mm以下に破砕したものを窒素ガスによる気流搬送で投入した。 The gasifier is charged with 500 kg / h coal, 376 Nm 3 / h oxygen, and 30 kg / h steam. The gasifier is operated at a temperature of 1550 ° C. and a pressure of 0.3 MPa, and the coal is partially oxidized to produce hydrogen 16%, CO carbon monoxide 47%, CO 2 carbon dioxide 13.5%, steam 20%, and A gasified gas of 970 Nm 3 / h containing 3.5% nitrogen was generated. The pyrolysis furnace has a diameter of 45 cm, a height of 7 m, and the coal blowing nozzle is located 0.5 m above the lower end of the straight body of the pyrolysis furnace (not including the throat and the inclined part above it in FIG. 1). The two biomass blowing nozzles are opposed to each other so as to face the lower end of the direct pyrolysis furnace body. The coal used in the gasification furnace and pyrolysis furnace is finely pulverized to a particle size of about 40 μm, and the biomass (wood chips) used in the pyrolysis furnace is crushed to 5 mm or less by nitrogen gas flow transportation. .

熱分解炉には、バイオマス吹き込みノズルよりバイオマス250kg/hと、石炭吹込みノズルより石炭250kg/hとを投入した。   The pyrolysis furnace was charged with 250 kg / h of biomass from the biomass blowing nozzle and 250 kg / h of coal from the coal blowing nozzle.

その結果、スロートで1500℃を超えていたガス化ガスはバイオマスと混合されて、混合ガスとなることにより約1150℃程度に低下した。その後、混合ガスは石炭と混合され、混合後の熱分解温度は900℃となり、熱分解炉出口で1400Nm/hのガス、235kg/hのチャー、73kg/hのタールが生成した。生成ガス中のC1−C3成分(軽質炭化水素ガス収率)は合計で53Nm/hであった。 As a result, the gasified gas, which exceeded 1500 ° C. at the throat, was mixed with the biomass and became a mixed gas, which was reduced to about 1150 ° C. Thereafter, the mixed gas was mixed with coal, the pyrolysis temperature after mixing was 900 ° C., and 1400 Nm 3 / h gas, 235 kg / h char, and 73 kg / h tar were produced at the pyrolysis furnace outlet. The C1-C3 component (light hydrocarbon gas yield) in the product gas was 53 Nm 3 / h in total.

また、連続200時間の操業においてトラブルの原因となるすすの発生による熱分解炉内での付着物は見られなかった。   In addition, no deposits were observed in the pyrolysis furnace due to the generation of soot causing trouble in continuous 200-hour operation.

(比較例)熱分解炉におけるバイオマス吹き込みノズルの位置を石炭ノズルと同高さに石炭吹き込みノズルと直交する位置に2カ所設置した以外は実施例と同一の条件でガス化炉の操業を行なった。熱分解炉に、バイオマス250kg/hと石炭250kg/hとを投入した際の熱分解炉内温度は900℃となり、チャーの生成量は240kg/h、生成ガス中のC1−C3成分は43Nm/hとなった。タール発生量は76kg/hであったがタール中の350℃以上留分割合は30wt%となり、実施例の22wt%と比較してBTXなどの有用なオイルの含有量の少ない重質なタールとなった。 (Comparative example) The gasification furnace was operated under the same conditions as in the example except that the biomass injection nozzles in the pyrolysis furnace were installed at two positions at the same height as the coal nozzles and perpendicular to the coal injection nozzles. . When the biomass 250 kg / h and coal 250 kg / h are charged into the pyrolysis furnace, the temperature in the pyrolysis furnace becomes 900 ° C., the amount of char produced is 240 kg / h, and the C1-C3 component in the produced gas is 43 Nm 3. / H. The tar generation amount was 76 kg / h, but the fraction of 350 ° C. or higher in the tar was 30 wt%, and a heavy tar with a low content of useful oil such as BTX compared to 22 wt% in the examples became.

また、連続200時間の操業後に熱分解炉内を調べたところ、すすの付着が確認された。   Further, when the inside of the pyrolysis furnace was examined after continuous operation for 200 hours, adhesion of soot was confirmed.

実施例および比較例を表1に示す。   Examples and comparative examples are shown in Table 1.

Figure 2006124496
Figure 2006124496

本発明に係る、石炭およびバイオマスの共熱分解装置の概略図である。It is the schematic of the co-pyrolysis apparatus of coal and biomass based on this invention.

符号の説明Explanation of symbols

1 熱分解炉、
2 ガス化炉、
3 石炭吹き込みノズル、
4 バイオマス吹き込みノズル、
5 ガス化バーナー、
6 スロート、
7 スラグタップ、
8 ガス化ガス、
9 混合ガス、
10 生成ガス、タール、およびチャー、
11 石炭、
12 バイオマス、
13 炭素質原料、
14 酸素、
15 水蒸気、
16 スラグ、
17 水槽。
1 pyrolysis furnace,
2 gasifier,
3 Coal blowing nozzle,
4 Biomass blowing nozzle,
5 Gasification burner,
6 Throat,
7 Slag tap,
8 Gasification gas,
9 mixed gas,
10 product gas, tar and char,
11 Coal,
12 biomass,
13 Carbonaceous raw material,
14 oxygen,
15 water vapor,
16 slag,
17 Aquarium.

Claims (2)

下段がガス化炉で上段が熱分解炉である二段構造の石炭およびバイオマスの共熱分解装置において、前記熱分解炉の側壁に上方から順に、石炭吹き込みノズルおよびバイオマス吹き込みノズルを設けることを特徴とする石炭およびバイオマスの共熱分解装置。   In the two-stage coal and biomass co-pyrolysis apparatus in which the lower stage is a gasification furnace and the upper stage is a pyrolysis furnace, a coal blowing nozzle and a biomass blowing nozzle are provided in order from the top on the side wall of the pyrolysis furnace. Co-pyrolysis equipment for coal and biomass. 請求項1に記載の石炭およびバイオマスの共熱分解装置を用い、
前記ガス化炉において炭素質原料を酸素または酸素および水蒸気と共に吹き込んで、ガス化ガスを発生させ、
前記ガス化ガスを前記熱分解炉に導入し、前記バイオマス吹き込みノズルからバイオマスを投入して前記バイオマスの熱分解を行ない、生成した混合ガス中に前記石炭吹き込みノズルから石炭を投入して、ガス、タールおよびチャーを生成することを特徴とする石炭およびバイオマスの共熱分解方法。
Using the coal and biomass co-pyrolysis apparatus according to claim 1,
In the gasification furnace, carbonaceous raw material is blown together with oxygen or oxygen and water vapor to generate gasified gas,
The gasification gas is introduced into the pyrolysis furnace, biomass is introduced from the biomass blowing nozzle to perform pyrolysis of the biomass, coal is introduced from the coal blowing nozzle into the generated mixed gas, gas, A method for co-pyrolysis of coal and biomass characterized by producing tar and char.
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