JP2004217834A - Method for recovering gas in treatment of biomass in cdq - Google Patents

Method for recovering gas in treatment of biomass in cdq Download PDF

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Publication number
JP2004217834A
JP2004217834A JP2003008741A JP2003008741A JP2004217834A JP 2004217834 A JP2004217834 A JP 2004217834A JP 2003008741 A JP2003008741 A JP 2003008741A JP 2003008741 A JP2003008741 A JP 2003008741A JP 2004217834 A JP2004217834 A JP 2004217834A
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gas
biomass
chamber
cdq
cooling
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JP4074521B2 (en
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Atsushi Fujikawa
淳 藤川
Yasutaka Shibahara
康孝 柴原
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Nippon Steel Corp
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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
    • Y02E50/30Fuel 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
    • Y02W30/20Waste processing or separation
    • 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

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for recovering a combustible gas which is useable for other application as a fuel replacing petroleum or LNG and a chemical raw material without utilization by combustion of a combustible gas which can carry out only low-efficiency heat recovery when thermally decomposing biomass such as wood or sewage sludge cake and effectively utilizing the combustible gas produced by the thermal decomposition in CDQ (a coke dry quencher). <P>SOLUTION: The method for recovering the gas in treatment of biomass in CDQ comprises introducing air for partial combustion for burning a part of the combustible gas produced by thermal decomposition of biomass into a pre-chamber 4 in order to keep the temperature of the pre-chamber to a temperature suitable for thermal decomposition of biomass, when charging biomass such as wood or sewage sludge cake into the pre-chamber 4 in the upper part of a cooling chamber 5 in CDQ and carrying out thermal decomposition of the biomass by utilizing sensible heat of red heat coke 1 and using the combustible gas produced by thermal decomposition as a cooling gas and recovering excess combustible gas as a fuel gas. <P>COPYRIGHT: (C)2004,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は、コークス乾式消火設備(Coke Dry Quencher 本明細書ではCDQという)における木材、下水汚泥ケーキ等のバイオマス処理時の可燃ガス回収方法に関するものである。
【0002】
【従来の技術】
CDQでは、赤熱コークスをCDQ本体のプレチャンバーに装入し冷却室に下降させ、冷却室下部より導入した冷却ガスである不活性ガスを赤熱コークスと熱交換させ、赤熱コークスの熱を回収した高温の不活性ガスを環状ダクト及び煙道を経由してボイラーに導入して熱交換した後、循環ブロワーで再度冷却室へ圧送して循環させるようになっている。ボイラーで熱交換により得られた蒸気は発電機に送られ電気エネルギーとして回収される。
【0003】
このCDQを利用したバイオマスの処理方法として、CDQ本体のプレチャンバーにバイオマス(下水汚泥ケーキ)を装入して熱分解処理する方法が例えば特許文献1に開示されている。
【0004】
特許文献1に開示されている熱分解処理方法は、赤熱コークスの顕熱を利用しプレチャンバー内で下水汚泥ケーキの有機成分を熱分解するとともに、下水汚泥ケーキ中の水分と赤熱コークスとを水性ガス化反応させ、CO、H等の可燃ガスとして煙道に導き、煙道にて燃焼用空気を導入し燃焼させるものである。
【0005】
しかし、木材、下水汚泥ケーキ等のバイオマスに含まれる灰分は、石炭の灰分に比べNa、K等のアルカリ金属成分が多く含まれており、その融点が低く付着性が高い。そのため、木材、下水汚泥ケーキ等のバイオマスから発生したバイオマス灰分を含む可燃ガスを燃焼する場合は、バイオマス灰分の溶融を回避するため、燃焼温度に制約がある(通常900℃)。すなわち、高温にてバイオマス灰分を含む可燃ガスを燃焼させるとバイオマス灰分が溶融し、粘着性を発し炉壁への付着による煉瓦への悪影響やボイラーの伝熱管表面に付着し熱効率を低下させるトラブルを生じる。そのため、900℃程度の燃焼温度にて燃焼せざるを得ず、結果として効率の低い熱回収しかできない。
【0006】
一方、可燃性の揮発分を多く含む木材、下水汚泥ケーキ等のバイオマスをCDQにて熱分解し、熱分解により生成した可燃ガスの利用法としては、熱分解にて生成した大量の可燃ガスを燃料ガスとして回収することが可能であれば、石油・LNGを代替する燃料や化学原料として他用途に使用することが考えられる。さらに、可燃ガスを回収した後、バイオマス灰分を除去すれば、灰の溶融問題が生じることなく高温燃焼が可能となり、高効率な熱回収が可能となる。
【0007】
CDQにおいて可燃ガスを含有する冷却ガスの余剰分を回収する方法は、例えば特許文献2に記載されているが、この特許文献2に記載のCDQは、バイオマスを処理するものではない。バイオマスには上述のように灰分が含まれているため、熱分解温度等の特別な管理が必要である。
【0008】
【特許文献1】
特許第2789988号公報
【0009】
【特許文献2】
特開2001−200257号公報
【0010】
【発明が解決しようとする課題】
本発明が解決しようとする課題は、CDQにおいて木材、下水汚泥ケーキ等のバイオマスを熱分解させ、熱分解によって生成した可燃ガスを有効利用するにあたり、低効率な熱回収しかできない可燃ガスの燃焼による利用ではなく、石油・LNGを代替する燃料や化学原料として他用途に使用可能な可燃ガスの回収方法を提供することにある。
【0011】
【課題を解決するための手段】
上記課題を解決するために、本発明のCDQにおけるバイオマス処理時の可燃ガス回収方法は、赤熱コークスをCDQ本体の冷却室に装入し、冷却室下部より冷却ガスを導入して、この冷却ガスと赤熱コークスを冷却室内で接触させて冷却ガスを昇熱させ、この昇熱したガスを冷却室から環状ダクト及び煙道を経由してボイラーに搬送して昇熱ガスの熱を回収して冷却ガスとし、再度循環させて冷却室下部に導入する冷却ガスとして再利用するCDQにおいて、前記冷却室上部のプレチャンバーに、木材、下水汚泥ケーキ等のバイオマスを装入し、このバイオマスを赤熱コークスの顕熱を利用して熱分解させ、熱分解により生成した可燃ガスを前記冷却ガスとして使用するとともに、余剰の可燃ガスを燃料ガスとして回収するにあたり、前記プレチャンバーをバイオマスの熱分解に適した温度にするために、バイオマスの熱分解により生成した可燃ガスの一部を燃焼させる部分燃焼用空気をプレチャンバーに導入することを特徴とする。
【0012】
プレチャンバーに導入する部分燃焼用空気量は、プレチャンバー温度により制御する。
【0013】
また、プレチャンバーに水及び/又は蒸気を導入しても良い。この水及び/又は蒸気は、プレチャンバー温度の制御用として使用されるとともに、バイオマス固定炭素や赤熱コークスと水性ガス化反応し、可燃ガスの生成量を増加させる作用も有する。
【0014】
さらに、回収する燃料ガスのガスカロリーを調整するための空気を環状ダクト及び/又は煙道に導入しても良い。
【0015】
【発明の実施の形態】
以下、本発明の実施の形態を図面に示す実施例に基づき説明する。
【0016】
実施例1
図1は、本発明に係る可燃ガス回収方法を実施するCDQの構成図である。CDQでは、赤熱コークス1をCDQ本体2上部のコークス装入口3から、蓋3aを開放した後プレチャンバ4に装入して冷却室5に下降させ、冷却室5下部の冷却ガス管14から供給する冷却ガスとしての不活性ガスを赤熱コークス1と熱交換させ、赤熱コークス1の熱を回収した高温の不活性ガスを環状ダクト6から煙道10を経由してボイラー13に導入して熱交換した後、循環ブロワー15で冷却室5下部へ圧送して循環させるようになっている。冷却されたコークスはCDQ本体2最下部のコークス排出口7から排出される。
【0017】
プレチャンバー4には、木材、下水汚泥ケーキ等のバイオマス装入口8と部分燃焼用空気導入口9が設けられている。バイオマスのうち、木材は10〜50mm程度にハンマークラッシャー等(図示せず)により粗粉砕してバイオマス装入口8より連続的に装入される。煙道10には、衝突壁11と、衝突壁11によって分離されたダストを回収するためのダストキャッチャ12が設けられている。また、ボイラー13と循環ブロワー15との間の配管にはダスト分離のためのサイクロン16が設けられている。さらに、循環ブロワー15の出側には余剰の可燃ガス(冷却ガス)を回収するためのガス回収管17が設けられている。
【0018】
以上の構成を有するCDQにおいて、プレチャンバー4に投入されたバイオマスは、赤熱コークス1の顕熱により熱分解され、CO、H等の可燃ガスが発生する。しかしながら、バイオマスに含有される水分の蒸発潜熱、蒸発した水分と赤熱コークス1との水性ガス化反応での吸熱、発生ガスの昇温顕熱などが赤熱コークス1の顕熱から奪われ、結果としてプレチャンバー4の温度が低下する。
【0019】
一方、木材、下水汚泥等のバイオマスの熱分解による発生ガスの組成は、その熱分解温度により決定される。700〜800℃程度の低温にて熱分解すると、タール等の液成分が生成する。このタール等の液成分は、高温では気体であるが、400℃程度まで温度を低下させると液体として結露する。そのため、タール等の液成分が発生するとボイラー13の伝熱管等にて結露して付着し、熱効率を悪化させる要因となる。さらに低温にて熱分解すると、本来、可燃性ガスとして発生する量が減少し、固体のままコークス排出口7からコークスとともに排出されるか、または、ダストキャッチャ12若しくはサイクロン16にてダストとして回収されてしまい、有効に利用することができなくなる。
【0020】
そのため、大量のバイオマスをCDQ本体2のプレチャンバー4に装入し高効率でトラブルを生じないように熱分解させるためには、プレチャンバー4の温度を一定に保つ必要がある。また、プレチャンバー4の温度低下は、ボイラー13にて回収される熱量の低下にもつながり、主蒸気量を低下させる。主蒸気量の低下は、発電効率の低下にもつながる。
【0021】
そこで、本発明では、部分燃焼用空気導入口9よりプレチャンバー4に空気を導入するようにしている。導入された部分燃焼用空気は、バイオマスより発生した可燃ガスの一部と反応・燃焼し、プレチャンバー4の温度低下を防止し、タール等の液成分を発生することなく、バイオマスを高効率に熱分解できる温度(約900℃)に維持する。また、プレチャンバー4の温度を低下させないことにより、ボイラー13にて回収する熱量の低下を回避することが可能となり、発電効率の低下を招かない。
【0022】
また、プレチャンバー4にて発生した可燃ガスは、冷却室5下部より導入され赤熱コークス1と熱交換した高温のコークス冷却ガスと混合され、環状ダクト6から煙道10に導かれボイラー13にて熱交換され冷却される。ボイラー13にて冷却されたコークス冷却ガスと可燃ガスとの混合ガスは、循環ブロワー15にて昇圧され、冷却室5に赤熱コークス1の冷却ガスとして再導入される。この循環使用によりコークス冷却ガスは可燃ガスとなり、赤熱コークス冷却用として必要のない余剰分の可燃ガスは、ガス回収管17から燃料ガスとして回収され、石油・LNGを代替する燃料や化学原料として他用途に有効利用される。
【0023】
実施例2
図2は、本発明に係る他の可燃ガス回収方法を実施するCDQの構成図である。図1に示したCDQと同一の構成には同一の符号を付し、その説明を省略する。
【0024】
本実施例では、プレチャンバー4の温度を一定にするため、プレチャンバー4の温度により、プレチャンバー4に導入する部分燃焼用空気の量を制御するようにしている。具体的には、プレチャンバー4に設けた温度センサ18にて計測されるプレチャンバー4の温度が所定の温度(約900℃)となるように、制御器19により、部分燃焼用空気の導入管に設けた流量調整弁20の開閉度を調整する。
【0025】
実施例3
図3は、本発明に係る他の可燃ガス回収方法を実施するCDQの構成図である。図1及び図2に示したCDQと同一の構成には同一の符号を付し、その説明を省略する。
【0026】
先の実施例2では、プレチャンバー4の温度を一定にするため、プレチャンバー4に導入する部分燃焼用空気の量を制御するようにしたが、本実施例では部分燃焼用空気の量は変化させず、その代わりに、プレチャンバー4に設けた水及び/又は蒸気の導入口21から水及び/又は蒸気を導入しプレチャンバー4の温度を制御するようにしている。具体的には、プレチャンバー4に設けた温度センサ18にて計測されるプレチャンバー4の温度が所定の温度(約900℃)となるように、制御器22により、水及び/又は蒸気の導入管に設けた流量調整弁23の開閉度を調整する。
【0027】
本実施例によれば、プレチャンバー4に導入された水及び/又は蒸気とバイオマス固定炭素や赤熱コークス1との水性ガス化反応により、可燃ガス(H、CO)が発生し、可燃性ガスの増量を行うことができる。
【0028】
実施例4
図4は、本発明に係る他の可燃ガス回収方法を実施するCDQの構成図である。図1〜図3に示したCDQと同一の構成には同一の符号を付し、その説明を省略する。
【0029】
本実施例では、煙道10に空気導入口24を設け、そこからガスカロリー調整用の空気を導入するようにしている。
【0030】
バイオマスをプレチャンバー4にて熱分解し可燃ガスを生成する場合、プレチャンバー4の温度条件や赤熱コークス1の投入等により、熱分解により発生するガス量及び組成が変動する。燃料ガスとして回収するガスは一定なカロリーに制御した方が有効利用しやすいため、変動したカロリー分を煙道10に導入した空気により燃焼させることで、燃料ガスとして回収するガスのカロリーを一定に保つようにしている。空気により燃焼させた変動カロリー分の熱量は、燃焼により熱に変換されボイラー13にて熱回収され有効利用される。
【0031】
空気量の制御は、サイクロン16の出側に設けたガスカロリー計25にて計測されたガスカロリーが所定カロリーとなるように、制御器26にて空気導入管に設けた流量調整弁27の開閉度を調整することによって行う。
【0032】
なお、本実施例では、ガスカロリー調整用の空気を煙道10に導入するようにしたが、環状ダクト6から導入しても良いし、煙道10と環状ダクト6の両方から導入しても良い。
【0033】
【発明の効果】
本発明によれば、プレチャンバーの温度がバイオマスの熱分解に適した温度になるので、バイオマスの熱分解が効率的に行われ、設備トラブルや熱回収効率の低下を生じることなく、可燃ガスの回収を行うことができる。
【図面の簡単な説明】
【図1】本発明に係る可燃ガス回収方法を実施するCDQの構成図である。
【図2】本発明に係る他の可燃ガス回収方法を実施するCDQの構成図である。
【図3】本発明に係る他の可燃ガス回収方法を実施するCDQの構成図である。
【図4】本発明に係る他の可燃ガス回収方法を実施するCDQの構成図である。
【符号の説明】
1 赤熱コークス
2 CDQ本体
3 コークス装入口
3a コークス装入口の蓋
4 プレチャンバー
5 冷却室
6 環状ダクト
7 コークス排出口
8 バイオマス装入口
9 部分燃焼用空気導入口
9 燃焼用空気導入口
10 煙道
11 衝突壁
12 ダストキャッチャ
13 ボイラー
14 冷却ガス管
15 循環ブロワー
16 サイクロン
17 ガス回収管
18 温度センサ
19 制御器
20 流量調整弁
21 水及び/又は蒸気の導入口
22 制御器
23 流量調整弁
24 空気導入口
25 ガスカロリー計
26 制御器
27 流量調整弁
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a method for recovering combustible gas at the time of treating biomass of wood, sewage sludge cake, and the like in a coke dry quencher (hereinafter, referred to as CDQ) in a coke dry quencher.
[0002]
[Prior art]
In the CDQ, red hot coke is charged into the pre-chamber of the CDQ main body, lowered into the cooling chamber, and the inert gas, which is a cooling gas introduced from the lower part of the cooling chamber, exchanges heat with the red hot coke to recover the heat of the red hot coke. After introducing the inert gas into the boiler through the annular duct and the flue to exchange heat, the inert gas is again pumped to the cooling chamber by the circulation blower and circulated. The steam obtained by heat exchange in the boiler is sent to a generator and collected as electric energy.
[0003]
As a method of treating biomass using CDQ, a method of loading biomass (sewage sludge cake) into a pre-chamber of a CDQ main body and performing a thermal decomposition treatment is disclosed in Patent Document 1, for example.
[0004]
The thermal decomposition treatment method disclosed in Patent Document 1 uses the sensible heat of red hot coke to thermally decompose organic components of sewage sludge cake in a pre-chamber, and converts water and red hot coke in sewage sludge cake to aqueous. by gasification reaction, CO, leads to the flue as a combustible gas such as H 2, is intended for introducing combustion air in the flue combustion.
[0005]
However, ash contained in biomass such as wood and sewage sludge cake contains more alkali metal components such as Na and K than ash of coal, and has a low melting point and high adhesion. Therefore, when combustible gas containing biomass ash generated from biomass such as wood and sewage sludge cake is burned, the combustion temperature is restricted (usually 900 ° C.) in order to avoid melting of biomass ash. In other words, when combustible gas containing biomass ash is burned at high temperatures, the biomass ash melts, causing stickiness and adverse effects on bricks due to adhesion to the furnace wall and troubles that lower thermal efficiency by adhering to the surface of the heat transfer tube of the boiler. Occurs. Therefore, combustion must be performed at a combustion temperature of about 900 ° C., and as a result, only low-efficiency heat recovery can be performed.
[0006]
On the other hand, biomass such as wood and sewage sludge cake containing a large amount of flammable volatiles is thermally decomposed by CDQ, and as a method of using the flammable gas generated by the pyrolysis, a large amount of flammable gas generated by the pyrolysis is used. If it can be recovered as a fuel gas, it can be considered to be used for other purposes as a fuel or chemical raw material to replace petroleum and LNG. Furthermore, if the biomass ash is removed after recovering the combustible gas, high-temperature combustion can be performed without causing the ash melting problem, and highly efficient heat recovery can be performed.
[0007]
A method of recovering a surplus of cooling gas containing combustible gas in CDQ is described in Patent Document 2, for example, but the CDQ described in Patent Document 2 does not process biomass. Since biomass contains ash as described above, special management such as thermal decomposition temperature is required.
[0008]
[Patent Document 1]
Japanese Patent No. 2789988
[Patent Document 2]
JP 2001-200257 A
[Problems to be solved by the invention]
The problem to be solved by the present invention is to thermally decompose biomass such as wood and sewage sludge cake in CDQ, and to effectively use the combustible gas generated by the pyrolysis. It is an object of the present invention to provide a method for recovering combustible gas that can be used for other purposes as a fuel or chemical raw material that substitutes for petroleum or LNG, instead of using it.
[0011]
[Means for Solving the Problems]
In order to solve the above-mentioned problems, a method for recovering combustible gas during biomass treatment in a CDQ according to the present invention comprises charging a red hot coke into a cooling chamber of a CDQ main body, introducing a cooling gas from a lower part of the cooling chamber, And the red hot coke are brought into contact in the cooling chamber to raise the temperature of the cooling gas, and the heated gas is transported from the cooling chamber to the boiler via the annular duct and the flue to recover the heat of the heated gas and cool it. In the CDQ, which is converted into a gas and circulated again and reused as a cooling gas introduced into the lower part of the cooling chamber, biomass such as wood and sewage sludge cake is charged into a pre-chamber at the upper part of the cooling chamber, and the biomass is converted into red hot coke. Thermal decomposition using sensible heat, while using the combustible gas generated by the pyrolysis as the cooling gas, and recovering excess combustible gas as a fuel gas, Les chamber to a temperature suitable for the pyrolysis of biomass, and introducing a partial combustion air for burning a portion of the combustible gas produced by the pyrolysis of biomass in the pre-chamber.
[0012]
The amount of partial combustion air introduced into the pre-chamber is controlled by the pre-chamber temperature.
[0013]
Further, water and / or steam may be introduced into the pre-chamber. The water and / or steam is used for controlling the pre-chamber temperature, and also has a function of causing a water gasification reaction with biomass-fixed carbon and red-hot coke to increase the amount of combustible gas generated.
[0014]
Further, air for adjusting the gas calories of the recovered fuel gas may be introduced into the annular duct and / or the flue.
[0015]
BEST MODE FOR CARRYING OUT THE INVENTION
Hereinafter, embodiments of the present invention will be described based on examples shown in the drawings.
[0016]
Example 1
FIG. 1 is a configuration diagram of a CDQ that implements the combustible gas recovery method according to the present invention. In the CDQ, the red hot coke 1 is introduced into the prechamber 4 after opening the lid 3a from the coke charging inlet 3 on the upper part of the CDQ main body 2, lowered into the cooling chamber 5, and supplied from the cooling gas pipe 14 below the cooling chamber 5. The inert gas as a cooling gas to be exchanged with the red hot coke 1 is heat-exchanged, and the high-temperature inert gas recovered from the heat of the red hot coke 1 is introduced into the boiler 13 from the annular duct 6 via the flue 10 to perform heat exchange. After that, the circulating blower 15 feeds and circulates the pressure to the lower part of the cooling chamber 5. The cooled coke is discharged from the coke discharge port 7 at the bottom of the CDQ main body 2.
[0017]
The pre-chamber 4 is provided with a biomass loading inlet 8 for wood, sewage sludge cake and the like, and an air inlet 9 for partial combustion. Among the biomass, the wood is roughly pulverized to about 10 to 50 mm by a hammer crusher or the like (not shown) and is continuously charged from the biomass inlet 8. The flue 10 is provided with a collision wall 11 and a dust catcher 12 for collecting dust separated by the collision wall 11. A cyclone 16 for dust separation is provided in a pipe between the boiler 13 and the circulation blower 15. Further, a gas recovery pipe 17 for recovering excess combustible gas (cooling gas) is provided on the outlet side of the circulation blower 15.
[0018]
In CDQ having the above configuration, the biomass charged into the pre-chamber 4 is thermally decomposed by the sensible heat of the red hot coke 1, CO, combustible gases such as H 2 is generated. However, latent heat of evaporation of water contained in biomass, heat absorption in the water gasification reaction of evaporated water with red hot coke 1, sensible heat of generated gas, etc. are deprived from sensible heat of red hot coke 1, resulting in The temperature of the pre-chamber 4 decreases.
[0019]
On the other hand, the composition of the gas generated by pyrolysis of biomass such as wood and sewage sludge is determined by its pyrolysis temperature. When thermally decomposed at a low temperature of about 700 to 800 ° C., liquid components such as tar are generated. The liquid component such as tar is a gas at a high temperature, but condenses as a liquid when the temperature is lowered to about 400 ° C. For this reason, when a liquid component such as tar is generated, it is condensed and adheres to the heat transfer tube of the boiler 13 or the like, which is a factor of deteriorating thermal efficiency. Further, when pyrolysis is performed at a lower temperature, the amount of flammable gas originally generated is reduced, and the solid is discharged together with coke from the coke outlet 7 as a solid, or collected as dust in the dust catcher 12 or the cyclone 16. And cannot be used effectively.
[0020]
Therefore, in order to charge a large amount of biomass into the pre-chamber 4 of the CDQ main body 2 and thermally decompose it at high efficiency without causing any trouble, it is necessary to keep the temperature of the pre-chamber 4 constant. Further, a decrease in the temperature of the pre-chamber 4 also leads to a decrease in the amount of heat recovered in the boiler 13 and reduces the amount of main steam. A decrease in the amount of main steam also leads to a decrease in power generation efficiency.
[0021]
Therefore, in the present invention, air is introduced into the pre-chamber 4 from the air inlet 9 for partial combustion. The introduced partial combustion air reacts with and burns a part of the combustible gas generated from the biomass, prevents the temperature of the pre-chamber 4 from dropping, and efficiently converts the biomass without generating liquid components such as tar. Maintain the temperature at which pyrolysis can be performed (about 900 ° C). In addition, since the temperature of the pre-chamber 4 is not decreased, it is possible to avoid a decrease in the amount of heat recovered by the boiler 13, and does not cause a decrease in power generation efficiency.
[0022]
The combustible gas generated in the pre-chamber 4 is mixed with the high-temperature coke cooling gas that has been introduced from the lower part of the cooling chamber 5 and exchanged heat with the red-hot coke 1, is guided from the annular duct 6 to the flue 10, and is passed through the boiler 13. Heat exchange and cooling. The mixed gas of the coke cooling gas and the combustible gas cooled by the boiler 13 is pressurized by the circulation blower 15 and re-introduced into the cooling chamber 5 as the cooling gas of the red hot coke 1. By this circulation, the coke cooling gas becomes combustible gas, and surplus combustible gas unnecessary for cooling red hot coke is recovered as a fuel gas from the gas recovery pipe 17, and is used as a fuel or chemical raw material for replacing petroleum and LNG. Effectively used for applications.
[0023]
Example 2
FIG. 2 is a configuration diagram of a CDQ that implements another flammable gas recovery method according to the present invention. The same components as those of the CDQ shown in FIG. 1 are denoted by the same reference numerals, and description thereof will be omitted.
[0024]
In this embodiment, in order to keep the temperature of the pre-chamber 4 constant, the amount of the partial combustion air introduced into the pre-chamber 4 is controlled by the temperature of the pre-chamber 4. Specifically, the controller 19 controls the introduction pipe of the partial combustion air so that the temperature of the pre-chamber 4 measured by the temperature sensor 18 provided in the pre-chamber 4 becomes a predetermined temperature (about 900 ° C.). The opening / closing degree of the flow control valve 20 provided in the above is adjusted.
[0025]
Example 3
FIG. 3 is a configuration diagram of a CDQ that implements another flammable gas recovery method according to the present invention. The same components as those of the CDQ shown in FIGS. 1 and 2 are denoted by the same reference numerals, and description thereof will be omitted.
[0026]
In the previous embodiment 2, the amount of the partial combustion air introduced into the pre-chamber 4 is controlled in order to keep the temperature of the pre-chamber 4 constant. However, in the present embodiment, the amount of the partial combustion air varies. Instead, water and / or steam is introduced from the water and / or steam inlet 21 provided in the pre-chamber 4 to control the temperature of the pre-chamber 4. Specifically, the controller 22 introduces water and / or steam so that the temperature of the pre-chamber 4 measured by the temperature sensor 18 provided in the pre-chamber 4 becomes a predetermined temperature (about 900 ° C.). The degree of opening and closing of the flow control valve 23 provided in the pipe is adjusted.
[0027]
According to the present embodiment, a combustible gas (H 2 , CO) is generated by a water gasification reaction between the water and / or steam introduced into the pre-chamber 4 and the biomass-fixed carbon or the red-hot coke 1, and the combustible gas is generated. Can be increased.
[0028]
Example 4
FIG. 4 is a configuration diagram of a CDQ that implements another flammable gas recovery method according to the present invention. The same components as those of the CDQ shown in FIGS. 1 to 3 are denoted by the same reference numerals, and description thereof will be omitted.
[0029]
In the present embodiment, an air inlet 24 is provided in the flue 10 and air for adjusting gas calories is introduced therefrom.
[0030]
When biomass is thermally decomposed in the pre-chamber 4 to generate a combustible gas, the amount and composition of the gas generated by the pyrolysis fluctuate depending on the temperature conditions of the pre-chamber 4 and the input of the red-hot coke 1. Controlling the gas to be recovered as fuel gas to a constant calorie is easier to use effectively, so by burning the fluctuating calorie with the air introduced into the flue 10, the calorie of the gas to be recovered as fuel gas is kept constant. I try to keep it. The amount of heat of the fluctuating calories burned by the air is converted into heat by the combustion, recovered by the boiler 13, and used effectively.
[0031]
The air amount is controlled by opening and closing a flow control valve 27 provided on an air introduction pipe by a controller 26 so that the gas calorie measured by a gas calorie meter 25 provided on the outlet side of the cyclone 16 becomes a predetermined calorie. This is done by adjusting the degree.
[0032]
In this embodiment, the air for adjusting the gas calorie is introduced into the flue 10, but may be introduced from the annular duct 6, or may be introduced from both the flue 10 and the annular duct 6. good.
[0033]
【The invention's effect】
According to the present invention, the temperature of the pre-chamber becomes a temperature suitable for the thermal decomposition of biomass, so that the thermal decomposition of the biomass is performed efficiently, without causing equipment troubles and a decrease in the heat recovery efficiency, without causing the combustion of the flammable gas. Recovery can be performed.
[Brief description of the drawings]
FIG. 1 is a configuration diagram of a CDQ for implementing a combustible gas recovery method according to the present invention.
FIG. 2 is a configuration diagram of a CDQ that implements another flammable gas recovery method according to the present invention.
FIG. 3 is a configuration diagram of a CDQ that implements another flammable gas recovery method according to the present invention.
FIG. 4 is a configuration diagram of a CDQ that implements another flammable gas recovery method according to the present invention.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Red hot coke 2 CDQ main body 3 Coke inlet 3a Coke inlet lid 4 Pre-chamber 5 Cooling room 6 Annular duct 7 Coke outlet 8 Biomass inlet 9 Partial combustion air inlet 9 Combustion air inlet 10 Flue 11 Collision wall 12 Dust catcher 13 Boiler 14 Cooling gas pipe 15 Circulation blower 16 Cyclone 17 Gas recovery pipe 18 Temperature sensor 19 Controller 20 Flow control valve 21 Water and / or steam inlet 22 Controller 23 Flow control valve 24 Air inlet 25 Gas calorie meter 26 Controller 27 Flow control valve

Claims (4)

赤熱コークスをCDQ本体の冷却室に装入し、冷却室下部より冷却ガスを導入して、この冷却ガスと赤熱コークスを冷却室内で接触させて冷却ガスを昇熱させ、この昇熱したガスを冷却室から環状ダクト及び煙道を経由してボイラーに搬送して昇熱ガスの熱を回収して冷却ガスとし、再度循環させて冷却室下部に導入する冷却ガスとして再利用するCDQにおいて、前記冷却室上部のプレチャンバーに、木材、下水汚泥ケーキ等のバイオマスを装入し、このバイオマスを赤熱コークスの顕熱を利用して熱分解させ、熱分解により生成した可燃ガスを前記冷却ガスとして使用するとともに、余剰の可燃ガスを燃料ガスとして回収するにあたり、
前記プレチャンバーをバイオマスの熱分解に適した温度にするために、バイオマスの熱分解により生成した可燃ガスの一部を燃焼させる部分燃焼用空気をプレチャンバーに導入することを特徴とするCDQにおけるバイオマス処理時の可燃ガス回収方法。
The red hot coke is charged into the cooling chamber of the main body of the CDQ, a cooling gas is introduced from the lower part of the cooling chamber, and the cooling gas is brought into contact with the red hot coke in the cooling chamber to raise the temperature of the cooling gas. In the CDQ which is conveyed from the cooling chamber to the boiler via the annular duct and the flue to recover the heat of the heat-raising gas to form a cooling gas, and is circulated again and reused as the cooling gas introduced into the lower part of the cooling chamber, Wood, biomass such as sewage sludge cake is charged into the pre-chamber above the cooling chamber, and this biomass is thermally decomposed using the sensible heat of red-hot coke, and the combustible gas generated by the pyrolysis is used as the cooling gas. And recovering excess combustible gas as fuel gas,
A biomass in a CDQ, wherein partial combustion air for burning a part of combustible gas generated by biomass pyrolysis is introduced into the prechamber in order to bring the prechamber to a temperature suitable for biomass pyrolysis. Combustible gas recovery method during treatment.
前記プレチャンバーに導入する部分燃焼用空気量を、プレチャンバー温度により制御することを特徴とする請求項1に記載のCDQにおけるバイオマス処理時の可燃ガス回収方法。The method according to claim 1, wherein the amount of the partial combustion air introduced into the pre-chamber is controlled by a pre-chamber temperature. 前記プレチャンバーに水及び/又は蒸気を導入することを特徴とする請求項1又は2記載のCDQにおけるバイオマス処理時の可燃ガス回収方法。3. The method of claim 1, wherein water and / or steam is introduced into the pre-chamber. 回収する燃料ガスのガスカロリーを調整するための空気を前記環状ダクト及び/又は煙道に導入することを特徴とする請求項1〜3のいずれか1項に記載のCDQにおけるバイオマス処理時の可燃ガス回収方法。The flammable fuel for treating biomass in the CDQ according to any one of claims 1 to 3, wherein air for adjusting gas calories of the fuel gas to be recovered is introduced into the annular duct and / or the flue. Gas recovery method.
JP2003008741A 2003-01-16 2003-01-16 Combustible gas recovery method during biomass processing in CDQ Expired - Fee Related JP4074521B2 (en)

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JP2013119587A (en) * 2011-12-07 2013-06-17 Jfe Steel Corp Method of recovering sensible heat from scorching coke
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CN105441091A (en) * 2015-11-27 2016-03-30 天津大学 Closed type vaporizing coke quenching device in coking industry
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JP2013119587A (en) * 2011-12-07 2013-06-17 Jfe Steel Corp Method of recovering sensible heat from scorching coke
KR101558928B1 (en) 2013-08-22 2015-10-12 재단법인 포항산업과학연구원 The Coke Dry Quenching using circulating gas controlled the amount of oxidative materials by absorbent and the method thereof
CN105441091A (en) * 2015-11-27 2016-03-30 天津大学 Closed type vaporizing coke quenching device in coking industry
CN105441091B (en) * 2015-11-27 2018-07-31 天津大学 Closed vaporization coke quenching device in coking industry
CN109777906A (en) * 2019-03-14 2019-05-21 石欣 A kind of device and method using red burnt high temperature heat production metallized pellet
CN109825315A (en) * 2019-03-14 2019-05-31 石欣 A kind of cooling coke and sewage gasification burning processing unit and method
CN109777906B (en) * 2019-03-14 2023-08-15 石欣 Device and method for producing metallized pellets by utilizing red coke high-temperature heat energy

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