JP2005061817A - Waste dry distillation gasification incineration treatment method - Google Patents

Waste dry distillation gasification incineration treatment method Download PDF

Info

Publication number
JP2005061817A
JP2005061817A JP2004185822A JP2004185822A JP2005061817A JP 2005061817 A JP2005061817 A JP 2005061817A JP 2004185822 A JP2004185822 A JP 2004185822A JP 2004185822 A JP2004185822 A JP 2004185822A JP 2005061817 A JP2005061817 A JP 2005061817A
Authority
JP
Japan
Prior art keywords
combustion
waste
furnace
gasification furnace
combustible gas
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP2004185822A
Other languages
Japanese (ja)
Other versions
JP4139360B2 (en
Inventor
Masamoto Kaneko
正元 金子
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kinsei Sangyo Co Ltd
Original Assignee
Kinsei Sangyo Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kinsei Sangyo Co Ltd filed Critical Kinsei Sangyo Co Ltd
Priority to JP2004185822A priority Critical patent/JP4139360B2/en
Publication of JP2005061817A publication Critical patent/JP2005061817A/en
Application granted granted Critical
Publication of JP4139360B2 publication Critical patent/JP4139360B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Classifications

    • 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
    • Y02W30/62Plastics recycling; Rubber recycling

Landscapes

  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a waste dry distillation gasification incineration treatment method capable of preventing discharge of carbon monoxide in the final stage of dry distillation of waste. <P>SOLUTION: The waste A stored in a gasification furnace 1 is distilled by oxygen supplied from an oxygen supply source 16, and generating combustible gas is introduced to and burnt in a combustion furnace 2. In the dry distillation, oxygen of a quantity for generating the combustible gas required for maintaining the combustion temperature of the combustible gas in the combustion furnace 2 substantially constant at the preset prescribed combustion temperature, is supplied to a gasification furnace 2 from the oxygen supply source 16. When the dry distillation reaches the final stage, combustion of the combustible gas is assisted by an auxiliary combustion means 14 equipped in the combustion furnace 2. In the final stage of the carbonization, when a detecting value of the carbon monoxide concentration in exhaust gas of the combustion furnace 2 is higher than a prescribed value, an oxygen quantity supplied in the gasification furnace 2 from the oxygen supply source 16 is reduced, and a quantity of combustible gas generated in the gasification furnace 2, is controlled so that the carbon monoxide becomes a combustible quantity by the auxiliary combustion means 14. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、廃タイヤ等の廃棄物を乾留して焼却処理する方法に関するものである。   The present invention relates to a method for incinerating a waste such as a waste tire by dry distillation.

廃タイヤ等の廃棄物を焼却処理する方法として、例えば、ガス化炉内に収納した廃棄物の一部を燃焼させつつ、その燃焼熱により該廃棄物の残部を乾留(熱分解)し、該乾留により生成する可燃性ガスを該ガス化炉から燃焼炉に導入して燃焼させる方法が知られている。前記方法では、従来、前記燃焼炉における前記可燃性ガスの燃焼温度を検知し、該可燃性ガスが予め設定された燃焼温度で燃焼されるように、前記ガス化炉に対する酸素供給量を調整して該ガス化炉内の乾留ガス化をフィードバック制御することが知られている(例えば特許文献1参照)。   As a method for incinerating waste such as waste tires, for example, while burning a part of the waste stored in the gasification furnace, the remainder of the waste is dry-distilled (pyrolysis) by the combustion heat, A method is known in which combustible gas generated by dry distillation is introduced from a gasification furnace into a combustion furnace and burned. In the method, conventionally, the combustion temperature of the combustible gas in the combustion furnace is detected, and the oxygen supply amount to the gasification furnace is adjusted so that the combustible gas is combusted at a preset combustion temperature. It is known that feedback control of dry distillation gasification in the gasification furnace is performed (see, for example, Patent Document 1).

前記のようにして廃棄物の乾留ガス化焼却処理を行うときには、まず、酸素供給源から前記ガス化炉内に酸素を供給して、該ガス化炉内に収容した該廃棄物の一部を燃焼させ、その燃焼熱により該廃棄物の残部を乾留することにより、可燃性ガスを生成させる。そして、前記ガス化炉内に生成した可燃性ガスを、前記燃焼炉に導入して完全燃焼させる。   When performing dry distillation gasification incineration treatment of waste as described above, first, oxygen is supplied from the oxygen supply source into the gasification furnace, and a part of the waste contained in the gasification furnace is removed. Combustible gas is generated by burning and carbonizing the remainder of the waste by the combustion heat. And the combustible gas produced | generated in the said gasification furnace is introduce | transduced into the said combustion furnace, and is burned completely.

このとき、前記ガス化炉には、前記燃焼炉における可燃性ガスの燃焼温度を予め設定された所定の燃焼温度に略一定に維持するために必要な可燃性ガスを生成させる量の酸素が、前記酸素供給源から供給される。前記酸素供給源から前記ガス化炉への酸素の供給は、前記燃焼炉における可燃性ガスの燃焼温度が上昇傾向にあれば酸素の供給量を低減し、該燃焼温度が下降傾向にあれば酸素の供給量を増大させるようにして行われる。   At this time, the gasification furnace has an amount of oxygen that generates a combustible gas necessary for maintaining the combustion temperature of the combustible gas in the combustion furnace at a predetermined combustion temperature that is set in advance. Supplied from the oxygen source. The supply of oxygen from the oxygen supply source to the gasification furnace is to reduce the supply amount of oxygen if the combustion temperature of the combustible gas in the combustion furnace tends to increase, and to reduce oxygen if the combustion temperature tends to decrease This is done in such a way as to increase the supply amount.

このようにして、前記ガス化炉内の前記廃棄物の乾留が進行すると、やがて乾留される廃棄物が低減し、該廃棄物の乾留の終了段階に至る。前記乾留の終了段階では、前記酸素供給源から前記ガス化炉への酸素の供給量を最大限に近くしても、前記燃焼炉における可燃性ガスの燃焼温度を所定の燃焼温度に維持するだけの可燃性ガスを生成させることができなくなる。そこで、前記廃棄物の乾留の終了段階では、前記燃焼炉に設けられたバーナにより前記可燃性ガスの燃焼を補助することが行われている。   In this way, as the carbonization of the waste in the gasification furnace proceeds, the waste that is carbonized eventually decreases, and the final stage of the carbonization of the waste is reached. At the end of the dry distillation, even if the amount of oxygen supplied from the oxygen supply source to the gasification furnace is made close to the maximum, the combustion temperature of the combustible gas in the combustion furnace is only maintained at a predetermined combustion temperature. It becomes impossible to produce the combustible gas. Therefore, at the end stage of the carbonization of the waste, combustion of the combustible gas is assisted by a burner provided in the combustion furnace.

ところで、前記廃棄物の材質によっては、前記乾留の終了段階で、一酸化炭素を生成するものがある。前記一酸化炭素の発生量が多い場合、前記燃焼炉で前記バーナにより燃焼を補助しても、該一酸化炭素が十分に燃焼されるに至らず、前記燃焼炉の燃焼排気と共に大気中に排出されることがある。   By the way, depending on the material of the waste, there is one that generates carbon monoxide at the end of the dry distillation. When the amount of carbon monoxide generated is large, even if combustion is assisted by the burner in the combustion furnace, the carbon monoxide is not sufficiently combusted and discharged into the atmosphere together with the combustion exhaust from the combustion furnace. May be.

そこで、前記一酸化炭素を燃焼をさせるために、前記バーナの火力を増大させることが考えられる。しかし、前記バーナを燃焼させるには燃料が必要であることから、該バーナの火力を増大させると、コストの増加が避けられない。   Therefore, in order to burn the carbon monoxide, it is conceivable to increase the heating power of the burner. However, since fuel is required to burn the burner, an increase in cost is inevitable if the heating power of the burner is increased.

また、一酸化炭素は、通常、その発生源に十分な酸素を供給することにより、発生を防止することができる。しかしながら、前記乾留の終了段階では、前記一酸化炭素の発生源である前記ガス化炉に対して前記酸素供給源から供給される酸素量は最大限に近くなっており、該ガス化炉に対する酸素の供給量をさらに増加させることは難しいとの不都合がある。
特開平2−135280号公報
Carbon monoxide can be prevented from being generated by supplying sufficient oxygen to the generation source. However, at the end stage of the carbonization, the amount of oxygen supplied from the oxygen supply source to the gasifier that is the source of carbon monoxide is close to the maximum, and oxygen to the gasifier is There is an inconvenience that it is difficult to further increase the supply amount.
JP-A-2-135280

本発明は、かかる不都合を解消して、廃棄物を乾留して、該乾留により生成する可燃性ガスを焼却処理するときに、該乾留の終了段階において、安価に一酸化炭素の排出を防止することができる廃棄物の乾留ガス化焼却処理方法を提供することを目的とする。   The present invention eliminates such inconvenience, and prevents carbon monoxide from being discharged at a low cost at the end of the dry distillation when the waste is dry distilled and the combustible gas generated by the dry distillation is incinerated. An object of the present invention is to provide a carbonization incineration treatment method for waste.

かかる目的を達成するために、本発明の廃棄物の乾留ガス化焼却処理方法は、ガス化炉内に収容した廃棄物を、酸素供給源から供給される酸素を用いて乾留して可燃性ガスを生成せしめる工程と、前記ガス化炉内に生成した可燃性ガスを燃焼炉に導入して燃焼せしめる工程と、前記ガス化炉内の廃棄物の乾留時に、前記燃焼炉における前記可燃性ガスの燃焼温度を予め設定された所定の燃焼温度に略一定に維持するために必要な該可燃性ガスを生成させる量の酸素を、前記酸素供給源から前記ガス化炉内に供給する工程と、前記ガス化炉内の廃棄物の乾留が終了段階に至ったときに、前記燃焼炉に備えられた補助燃焼手段により前記可燃性ガスの燃焼を補助する工程とを備える廃棄物の乾留ガス化焼却処理方法において、前記ガス化炉内の廃棄物の乾留の終了段階で、前記燃焼炉の排ガス中の一酸化炭素濃度を検出して、該一酸化炭素濃度の検出値が所定の値よりも高いときには、前記酸素供給源から前記ガス化炉内に供給する酸素量を低減して、前記ガス化炉内で生成する可燃性ガスの量を該可燃性ガス中に含まれる一酸化炭素が前記燃焼炉に備えられた補助燃焼手段により燃焼可能な量となるように制御することを特徴とする。   In order to achieve such an object, the method of dry distillation gasification incineration according to the present invention is a method for combustible gas obtained by dry distillation of waste contained in a gasification furnace using oxygen supplied from an oxygen supply source. Generating a combustible gas in the gasification furnace, introducing the combustible gas generated in the gasification furnace into the combustion furnace and burning the combustible gas, and during the dry distillation of the waste in the gasification furnace, Supplying oxygen from the oxygen supply source into the gasification furnace in an amount that generates the combustible gas necessary for maintaining the combustion temperature at a predetermined predetermined combustion temperature substantially constant; A carbonization incineration treatment of waste comprising a step of assisting combustion of the combustible gas by auxiliary combustion means provided in the combustion furnace when the carbonization of the waste in the gasification furnace reaches an end stage In the method, the waste in the gasifier When the carbon monoxide concentration in the exhaust gas of the combustion furnace is detected at the end of the carbonization of the product, and the detected value of the carbon monoxide concentration is higher than a predetermined value, the gasification furnace is supplied from the oxygen supply source. The amount of combustible gas generated in the gasification furnace is reduced by the amount of oxygen supplied into the gasification furnace, and the carbon monoxide contained in the combustible gas can be combusted by auxiliary combustion means provided in the combustion furnace. It is characterized by controlling so that it may become a quantity.

本発明の方法では、まず、前記ガス化炉内に収容した廃棄物を、前記酸素供給源から該ガス化炉に供給される酸素を用いて乾留し、該乾留により可燃性ガスを生成せしめる。前記廃棄物の乾留は、該廃棄物の一部を燃焼させつつ、その燃焼熱により該廃棄物の残部を乾留することにより行う。   In the method of the present invention, first, the waste housed in the gasification furnace is dry-distilled using oxygen supplied from the oxygen supply source to the gasification furnace, and combustible gas is generated by the dry distillation. The carbonization of the waste is performed by carbonizing the remainder of the waste with the heat of combustion while burning a part of the waste.

前記ガス化炉内に生成した可燃性ガスは、燃焼炉に導入され、前記酸素供給源から該燃焼炉に供給される酸素により燃焼せしめられる。前記可燃性ガスは、前記燃焼炉内で着火されることにより燃焼を開始するが、前記ガス化炉内で生成する可燃性ガスが増加するに従って、それ自体の熱量により自発的に燃焼するようになる。   The combustible gas produced | generated in the said gasification furnace is introduce | transduced into a combustion furnace, and is burned with the oxygen supplied to this combustion furnace from the said oxygen supply source. The combustible gas starts to combust when ignited in the combustion furnace, but as the combustible gas generated in the gasification furnace increases, the combustible gas spontaneously combusts by its own heat quantity. Become.

前記可燃性ガスが自発的に燃焼するようになったならば、前記ガス化炉内の前記廃棄物の乾留は、前記燃焼炉における可燃性ガスの燃焼温度が予め設定された所定の燃焼温度に略一定に維持するために必要な可燃性ガスを生成させるように行われる。このとき、前記可燃性ガスの生成は、前記酸素供給源から前記ガス化炉に供給される酸素量により制御され、前記燃焼炉における可燃性ガスの燃焼温度が上昇傾向にあれば酸素の供給量を低減し、該燃焼温度が下降傾向にあれば酸素の供給量を増大させるようにして行われる。   When the combustible gas spontaneously burns, the carbonization of the waste in the gasification furnace is performed at a predetermined combustion temperature in which the combustion temperature of the combustible gas in the combustion furnace is set in advance. It is carried out so as to generate a combustible gas necessary for maintaining it substantially constant. At this time, the generation of the combustible gas is controlled by the amount of oxygen supplied from the oxygen supply source to the gasifier, and the amount of oxygen supplied if the combustion temperature of the combustible gas in the combustion furnace tends to increase. If the combustion temperature tends to decrease, the oxygen supply amount is increased.

このようにして、前記ガス化炉内の前記廃棄物の乾留が進行すると、やがて乾留される廃棄物が低減し、該乾留の終了段階に至る。前記乾留の終了段階では、前記酸素供給源から該ガス化炉への酸素の供給量を最大限近くまで増大させても、前記燃焼炉における可燃性ガスの燃焼温度を所定の燃焼温度に維持するだけの可燃性ガスを生成させることができなくなる。そこで、前記燃焼炉では、前記補助燃焼手段により、前記可燃性ガスの燃焼を補助する。   In this manner, when the carbonization of the waste in the gasifier proceeds, the waste to be carbonized eventually decreases, and the final stage of the carbonization is reached. At the end of the dry distillation, the combustion temperature of the combustible gas in the combustion furnace is maintained at a predetermined combustion temperature even when the amount of oxygen supplied from the oxygen supply source to the gasifier is increased to a maximum. It becomes impossible to produce only combustible gas. Therefore, in the combustion furnace, combustion of the combustible gas is assisted by the auxiliary combustion means.

前記乾留の終了段階で、前記廃棄物の材質によっては、前記ガス化炉中に大量の一酸化炭素が生成することがある。このとき、前記一酸化炭素が、前記補助燃焼手段により十分に燃焼されないと、高濃度の一酸化炭素が大気中に排出されることになる。   Depending on the waste material, a large amount of carbon monoxide may be generated in the gasifier at the end of the carbonization. At this time, if the carbon monoxide is not sufficiently burned by the auxiliary combustion means, a high concentration of carbon monoxide is discharged into the atmosphere.

前記高濃度の一酸化炭素が大気中に排出されることを防止するには、前記補助燃焼手段の火力を増大させることが考えられるが、このようにするときにはコストの増加が避けられない。また、前記一酸化炭素の発生源であるガス化炉に十分な酸素を供給して、一酸化炭素の発生自体を防止することも考えられるが、前記乾留の終了段階では、前記酸素供給源から前記ガス化炉への酸素の供給量は最大限に近くなっており、それ以上酸素の供給量を増大することは難しい。   In order to prevent the high-concentration carbon monoxide from being discharged into the atmosphere, it is conceivable to increase the heating power of the auxiliary combustion means, but when doing so, an increase in cost is inevitable. In addition, it is conceivable to supply sufficient oxygen to the gasification furnace, which is the source of carbon monoxide, to prevent the generation of carbon monoxide itself, but at the end of the dry distillation, from the oxygen source The supply amount of oxygen to the gasifier is close to the maximum, and it is difficult to increase the supply amount of oxygen further.

そこで、本発明の方法では、前記乾留の終了段階で、前記燃焼炉の排ガス中の一酸化炭素濃度を検出し、該一酸化炭素濃度の検出値が所定の値よりも高いときには、前記酸素供給源から前記ガス化炉内に供給する酸素量を低減する。このようにすると、前記ガス化炉内での可燃性ガスの生成自体が抑制されるので、これに伴って、該可燃性ガス中に含まれる一酸化炭素の量も低減する。この結果、前記一酸化炭素の量が、前記燃焼炉に備えられた補助燃焼手段により燃焼可能な量となるように制御される。   Therefore, in the method of the present invention, the carbon monoxide concentration in the exhaust gas of the combustion furnace is detected at the end of the dry distillation, and when the detected value of the carbon monoxide concentration is higher than a predetermined value, the oxygen supply The amount of oxygen supplied from the source into the gasifier is reduced. If it does in this way, since the production | generation itself of the combustible gas in the said gasification furnace is suppressed, the amount of carbon monoxide contained in this combustible gas is also reduced in connection with this. As a result, the amount of carbon monoxide is controlled so as to be combustible by auxiliary combustion means provided in the combustion furnace.

従って、前記ガス化炉内で一酸化炭素が生成したとしても、該一酸化炭素を前記燃焼炉内で確実に燃焼させることができ、大気中に排出されることを安価に防止することができる。   Therefore, even if carbon monoxide is generated in the gasification furnace, the carbon monoxide can be reliably burned in the combustion furnace, and can be prevented from being discharged into the atmosphere at a low cost. .

前記乾留が終了すると、前記ガス化炉内の廃棄物は灰化されて、炉外に排出され、次いで新しい廃棄物が炉内に収容されて次の焼却処理が行われる。ところで、前述のように、前記乾留の終了段階で前記可燃性ガスの生成が抑制されると、該乾留の終了後、前記廃棄物が灰化されるまでに長時間を要することになり、処理効率が低下する。   When the dry distillation is completed, the waste in the gasification furnace is incinerated and discharged outside the furnace, and then new waste is accommodated in the furnace and the next incineration process is performed. By the way, as described above, when the generation of the combustible gas is suppressed at the end of the dry distillation, it takes a long time until the waste is incinerated after the dry distillation. Efficiency is reduced.

そこで、本発明の方法では、前記ガス化炉内の廃棄物の乾留の終了段階で、所定時間毎に前記燃焼炉の排ガス中の一酸化炭素濃度を検出し、該一酸化炭素濃度の検出値が前回の検出値より高いときには、前記酸素供給源から前記ガス化炉内に供給する酸素量をそれまでよりも低減し、該一酸化炭素濃度の検出値が前回の検出値より低いときには、前記酸素供給源から前記ガス化炉内に供給する酸素量をそれまでよりも増加することを特徴とする。   Therefore, in the method of the present invention, the carbon monoxide concentration in the exhaust gas of the combustion furnace is detected every predetermined time at the end of the dry distillation of the waste in the gasifier, and the detected value of the carbon monoxide concentration is detected. Is higher than the previous detection value, the amount of oxygen supplied from the oxygen supply source into the gasifier is reduced more than before, and when the detected value of the carbon monoxide concentration is lower than the previous detection value, The amount of oxygen supplied from the oxygen supply source into the gasification furnace is increased more than before.

また、本発明の方法は、前記ガス化炉内の廃棄物の乾留の終了段階で、前記酸素供給源から前記ガス化炉内に供給する酸素量を低減した後、前記燃焼炉の排ガス中の一酸化炭素濃度の検出値が所定の値よりも低くなったきには、前記酸素供給源から前記ガス化炉内に供給する酸素量を増加して、前記乾留が終了した廃棄物を灰化させることを特徴とする。   In the method of the present invention, the amount of oxygen supplied from the oxygen supply source to the gasification furnace is reduced at the end of dry distillation of the waste in the gasification furnace, and then the exhaust gas in the combustion furnace is exhausted. When the detected value of the carbon monoxide concentration becomes lower than a predetermined value, the amount of oxygen supplied from the oxygen supply source into the gasifier is increased, and the waste after the dry distillation is ashed. It is characterized by that.

このようにするときには、前記ガス化炉内で生成する一酸化炭素の量に応じて、前記酸素供給源から該ガス化炉内に供給する酸素量を調整することができ、前記廃棄物の灰化に要する時間を短縮することができる。   When doing so, the amount of oxygen supplied from the oxygen supply source into the gasifier can be adjusted according to the amount of carbon monoxide produced in the gasifier, and the waste ash The time required for conversion can be shortened.

次に、添付の図面を参照しながら本発明の実施の形態についてさらに詳しく説明する。図1は本実施形態に用いる乾留ガス化焼却処理装置のシステム構成図であり、図2は燃焼炉における可燃性ガスの燃焼温度と、一酸化炭素濃度と、ガス化炉に対する酸素供給量との関係を示すグラフである。   Next, embodiments of the present invention will be described in more detail with reference to the accompanying drawings. FIG. 1 is a system configuration diagram of a dry distillation gasification incineration processing apparatus used in the present embodiment. FIG. 2 is a graph showing combustion temperature of a combustible gas in a combustion furnace, carbon monoxide concentration, and oxygen supply amount to the gasification furnace. It is a graph which shows a relationship.

図1に示す乾留ガス化焼却処理装置は、廃タイヤ等の廃棄物Aを収納し、その乾留・ガス化並びに燃焼・灰化を行わしめるガス化炉1、ガス化炉1で廃棄物Aの乾留により生じる可燃性ガスを燃焼させる燃焼炉2、燃焼炉2における可燃性ガスの燃焼温度Tを検知する温度センサ3、ガス化炉1に酸素(空気)を供給する酸素供給手段4、燃焼炉2に酸素(空気)を供給する酸素供給手段5、燃焼炉2の燃焼排気を排出する排出手段6を備えている。   The dry distillation gasification incineration apparatus shown in FIG. 1 stores waste A such as waste tires, the gasification furnace 1 in which the dry distillation / gasification and combustion / ashing are performed, and the waste gas A in the gasification furnace 1 Combustion furnace 2 that combusts combustible gas generated by dry distillation, temperature sensor 3 that detects the combustion temperature T of the combustible gas in the combustion furnace 2, oxygen supply means 4 that supplies oxygen (air) to the gasification furnace 1, and combustion furnace 2 is provided with oxygen supply means 5 for supplying oxygen (air) to 2 and discharge means 6 for discharging the combustion exhaust of the combustion furnace 2.

ガス化炉1の上面部には、開閉自在な投入扉7を有する投入口8が形成され、該投入口8から廃棄物Aがガス化炉1内に投入できるようになっている。そして、ガス化炉1は、投入扉7を閉じた状態では、その内部が実質的に外気と遮断されるようになっている。ガス化炉1の下部は空室となっており、該空室に酸素供給手段4が接続されている。そして、酸素供給手段4から前記空室に供給される酸素を複数の給気ノズル9を介してガス化炉1の内部に供給するようになっている。   A gas inlet 8 having a door 7 that can be freely opened and closed is formed on the upper surface of the gasifier 1 so that the waste A can be charged into the gasifier 1 from the inlet 8. The gasification furnace 1 is substantially cut off from the outside air when the charging door 7 is closed. A lower portion of the gasification furnace 1 is a vacant chamber, and an oxygen supply means 4 is connected to the vacant chamber. Then, oxygen supplied from the oxygen supply means 4 to the vacant chamber is supplied into the gasification furnace 1 through a plurality of supply nozzles 9.

ガス化炉1の下部の側部には、点火バーナ等により構成される着火装置10が取付けられている。着火装置10は、図示しない燃料供給装置から供給される助燃油等の燃料を燃焼させることにより、ガス化炉1の内部に向かって燃焼炎を生ぜしめ、この燃焼炎によりガス化炉1内の廃棄物Aに着火するようになっている。また、ガス化炉1の外周部には、その冷却構造として該ガス化炉1の内部と隔離されたウォータジャケット11が形成され、ウォータジャケット11はガス化炉1の外部に設けられた図示しない給水装置から給水されるようになっている。   An ignition device 10 composed of an ignition burner or the like is attached to the lower side portion of the gasification furnace 1. The ignition device 10 burns fuel such as auxiliary combustion oil supplied from a fuel supply device (not shown) to generate a combustion flame toward the inside of the gasification furnace 1, and this combustion flame causes the inside of the gasification furnace 1. Waste A is ignited. Further, a water jacket 11 isolated from the inside of the gasification furnace 1 is formed on the outer periphery of the gasification furnace 1 as a cooling structure thereof, and the water jacket 11 is provided outside the gasification furnace 1 and is not shown. Water is supplied from the water supply device.

前記燃焼炉2は、その基部(バーナ部)にガス化炉1の上部に設けられた接続部12から導出されたガス通路13が接続され、ガス化炉1で廃棄物Aの乾留により生じる可燃性ガスが導入されるようになっている。燃焼炉2の後端部には着火装置14が取付けられ、前記ガス通路13から導入される可燃性ガスに着火するようになっている。着火装置14は、前記着火装置10と同様に点火バーナ等により構成され、図示しない燃料供給装置から供給される助燃油等の燃料を燃焼させることにより、燃焼炉2の内部に向かって燃焼炎を生ぜしめるようになっている。   In the combustion furnace 2, a gas passage 13 led out from a connection part 12 provided at the upper part of the gasification furnace 1 is connected to a base part (burner part), and combustible generated by dry distillation of waste A in the gasification furnace 1. Sex gas is introduced. An ignition device 14 is attached to the rear end portion of the combustion furnace 2 so as to ignite the combustible gas introduced from the gas passage 13. The ignition device 14 is composed of an ignition burner and the like, similar to the ignition device 10, and burns fuel such as auxiliary combustion oil supplied from a fuel supply device (not shown) to burn a combustion flame toward the inside of the combustion furnace 2. It is supposed to give birth.

燃焼炉2の外周部は空室となっており、該空室に酸素供給手段5が接続されている。そして、酸素供給手段5から前記空室に供給される酸素を燃焼炉2の外周壁に設けられた複数のノズル孔15を介して燃焼炉2の内部に供給するようになっている。   An outer peripheral portion of the combustion furnace 2 is a vacant chamber, and an oxygen supply means 5 is connected to the vacant chamber. Then, oxygen supplied from the oxygen supply means 5 to the vacant chamber is supplied into the combustion furnace 2 through a plurality of nozzle holes 15 provided in the outer peripheral wall of the combustion furnace 2.

ガス化炉1に酸素を供給する前記酸素供給手段4は、ガス化炉1の外部に設けられた押込ファン等の酸素供給源16と、該酸素供給源16から導出された主酸素供給管17と、該主酸素供給管17から分岐されてガス化炉1の下部に接続された副酸素供給管18とからなる。副酸素供給管18には温度センサ3から入力される検知信号に従って開度が調整される調整弁19が設けられている。   The oxygen supply means 4 for supplying oxygen to the gasification furnace 1 includes an oxygen supply source 16 such as a pushing fan provided outside the gasification furnace 1, and a main oxygen supply pipe 17 led out from the oxygen supply source 16. And a sub-oxygen supply pipe 18 branched from the main oxygen supply pipe 17 and connected to the lower part of the gasification furnace 1. The auxiliary oxygen supply pipe 18 is provided with an adjustment valve 19 whose opening degree is adjusted in accordance with a detection signal input from the temperature sensor 3.

また、燃焼炉2に酸素を供給する前記酸素供給手段5は、前記酸素供給源16と、該酸素供給源16から導出された主酸素供給管17と、該主酸素供給管17から分岐されて燃焼炉2の外周部に接続された副酸素供給管20とからなる。副酸素供給管20には温度センサ3から入力される検知信号に従って開度が調整される調整弁21が設けられている。   The oxygen supply means 5 for supplying oxygen to the combustion furnace 2 is branched from the oxygen supply source 16, a main oxygen supply pipe 17 led out from the oxygen supply source 16, and the main oxygen supply pipe 17. The auxiliary oxygen supply pipe 20 is connected to the outer peripheral portion of the combustion furnace 2. The sub oxygen supply pipe 20 is provided with an adjustment valve 21 whose opening degree is adjusted in accordance with a detection signal input from the temperature sensor 3.

燃焼炉2の燃焼排気を排出する前記排出手段6は、該燃焼排気を冷却する冷却炉22、消石灰、活性炭等により該燃焼排気の脱硫と脱臭を行う脱硫・脱臭装置23、バグフィルタ24、該燃焼排気を煙突25に押し込む押込ファン26とを備えている。煙突25には、前記燃焼排気中の一酸化炭素を検出するCOセンサ27が備えられており、検知信号がガス化炉1の調整弁19に送られるようになっている。   The discharge means 6 for discharging the combustion exhaust of the combustion furnace 2 includes a cooling furnace 22 for cooling the combustion exhaust, a desulfurization / deodorization device 23 for desulfurization and deodorization of the combustion exhaust by slaked lime, activated carbon, etc., a bag filter 24, A pushing fan 26 for pushing the combustion exhaust into the chimney 25 is provided. The chimney 25 is provided with a CO sensor 27 that detects carbon monoxide in the combustion exhaust gas, and a detection signal is sent to the regulating valve 19 of the gasifier 1.

次に、図1に示す装置による本実施形態の乾留ガス化焼却処理方法について、説明する。   Next, the dry distillation gasification incineration processing method of this embodiment by the apparatus shown in FIG. 1 will be described.

本実施形態の乾留ガス化焼却処理方法では、まず、ガス化炉1の投入扉7が開かれて、廃棄物Aが投入口8から該ガス化炉1内に投入される。次いで、投入扉7を閉じた後に、着火装置10が所定時間作動されることにより、ガス化炉1内の廃棄物Aに着火され、該廃棄物Aの部分的燃焼が開始される。   In the dry distillation gasification incineration processing method of the present embodiment, first, the charging door 7 of the gasification furnace 1 is opened, and the waste A is charged into the gasification furnace 1 from the charging port 8. Next, after closing the closing door 7, the ignition device 10 is operated for a predetermined time, whereby the waste A in the gasification furnace 1 is ignited and partial combustion of the waste A is started.

前記廃棄物Aの部分的燃焼の開始に際して、ガス化炉1に接続された副酸素供給管18の調整弁19は、わずかな開度で開かれており、酸素供給源16からガス化炉1内に比較的少量の酸素(空気)が供給される。このため、廃棄物Aの部分的燃焼は、ガス化炉1内に存在していた酸素と、酸素供給源16から供給される比較的少量の酸素とを用いて開始される。   At the start of the partial combustion of the waste A, the regulating valve 19 of the auxiliary oxygen supply pipe 18 connected to the gasification furnace 1 is opened with a slight opening, and the gasification furnace 1 is supplied from the oxygen supply source 16. A relatively small amount of oxygen (air) is supplied inside. For this reason, the partial combustion of the waste A is started using oxygen existing in the gasification furnace 1 and a relatively small amount of oxygen supplied from the oxygen supply source 16.

このようにガス化炉1内の廃棄物Aの下層部における部分的燃焼が開始されると、その燃焼熱により廃棄物Aの上層部の乾留が開始され、該乾留により可燃性ガスの生成が始まる。そして、ガス化炉1内で生成した可燃性ガスは、ガス通路13を介して燃焼炉2の基端部(バーナ部)に導入され、燃焼炉2の着火装置14により着火されて燃焼を開始する。   Thus, when the partial combustion in the lower layer part of the waste A in the gasification furnace 1 is started, dry distillation of the upper layer part of the waste A is started by the combustion heat, and combustible gas is generated by the dry distillation. Begins. The combustible gas generated in the gasification furnace 1 is introduced into the base end portion (burner portion) of the combustion furnace 2 through the gas passage 13 and is ignited by the ignition device 14 of the combustion furnace 2 to start combustion. To do.

このとき、ガス化炉1では、副酸素供給管18の調整弁19の開度を、ガス化炉1への酸素供給量が廃棄物Aの下層部における継続的な部分的燃焼に必要な程度になるように制限しつつ、段階的に徐々に増大させる。このようにすると、ガス化炉1における廃棄物Aの部分的燃焼は、酸素供給源16から供給される少量の酸素を消費しつつ徐々に安定化する一方、その燃焼範囲が酸素供給源16から供給される酸素量に応じて、廃棄物Aの下層部において徐々に拡大していく。そして、廃棄物Aの下層部における燃焼の安定化に伴って、その燃焼熱による廃棄物Aの上層部の乾留も徐々に活発化して安定に進行するようになり、該乾留により生成する可燃性ガスの量も徐々に増大していく。   At this time, in the gasification furnace 1, the opening degree of the regulating valve 19 of the sub-oxygen supply pipe 18 is set so that the oxygen supply amount to the gasification furnace 1 is necessary for continuous partial combustion in the lower layer portion of the waste A. While gradually limiting, it is gradually increased. In this way, the partial combustion of the waste A in the gasification furnace 1 is gradually stabilized while consuming a small amount of oxygen supplied from the oxygen supply source 16, while the combustion range is from the oxygen supply source 16. It gradually expands in the lower layer part of the waste A according to the amount of oxygen supplied. And with the stabilization of combustion in the lower layer part of the waste A, the dry distillation of the upper layer part of the waste A due to the combustion heat gradually becomes active and proceeds stably, and the combustibility generated by the dry distillation. The amount of gas will also increase gradually.

この結果、図2の上段に示すように、温度センサ3により検知される燃焼炉2における可燃性ガスの燃焼温度Tも上昇していく。尚、ガス化炉1の着火装置10は、廃棄物Aの下層部における燃焼が安定化したことが確認された時点で停止される。   As a result, as shown in the upper part of FIG. 2, the combustion temperature T of the combustible gas in the combustion furnace 2 detected by the temperature sensor 3 also increases. The ignition device 10 of the gasification furnace 1 is stopped when it is confirmed that the combustion in the lower layer portion of the waste A is stabilized.

次いで、温度センサ3により検知される可燃性ガスの燃焼温度Tがさらに上昇し、該可燃性ガスが自然燃焼し得る温度として予め設定された燃焼温度T1よりも僅かに低い温度に達すると、調整弁19は燃焼温度Tが燃焼温度T1に略一定に維持されるように自動的にフィードバック制御される。 Next, when the combustion temperature T of the combustible gas detected by the temperature sensor 3 further increases and reaches a temperature slightly lower than the combustion temperature T 1 set in advance as a temperature at which the combustible gas can spontaneously burn, The regulating valve 19 is automatically feedback controlled so that the combustion temperature T is maintained substantially constant at the combustion temperature T 1 .

具体的には、温度センサ3により検知される可燃性ガスの燃焼温度Tが燃焼温度T1より小さくなると、調整弁19の開度を大きくしてガス化炉1への酸素供給量を増加させ、可燃性ガスの生成を助長する。逆に、温度センサ3により検知される可燃性ガスの燃焼温度Tが燃焼温度T1より大きくなると、調整弁19の開度を小さくしてガス化炉1への酸素供給量を低減させ、可燃性ガスの生成を抑制する。このように、調整弁19の開度をフィードバック制御することにより、図2の上段に示すように、燃焼炉2における可燃性ガスの燃焼温度Tが略一定の燃焼温度T1に維持され、ガス化炉1内の廃棄物Aの下層部の燃焼と、上層部の乾留とが安定に進行する。 Specifically, when the combustion temperature T of the combustible gas detected by the temperature sensor 3 becomes smaller than the combustion temperature T 1 , the opening of the regulating valve 19 is increased to increase the amount of oxygen supplied to the gasifier 1. , To help generate flammable gas. Conversely, when the combustion temperature T of the combustible gas detected by the temperature sensor 3 becomes higher than the combustion temperature T 1 , the opening of the regulating valve 19 is reduced to reduce the amount of oxygen supplied to the gasifier 1 and combustible. Suppresses the generation of sex gases. Thus, by feedback controlling the opening of the adjustment valve 19, as shown in the upper part of FIG. 2, the combustion temperature T of the combustible gas is maintained at a substantially constant combustion temperature T 1 of the combustion furnace 2, gas Combustion of the lower layer portion of the waste A in the conversion furnace 1 and dry distillation of the upper layer portion proceed stably.

燃焼炉2における可燃性ガスの燃焼温度Tが略一定の燃焼温度T1に維持されるようになると、燃焼炉2の着火装置14が停止され、該可燃性ガスは継続的に自然燃焼することとなる。尚、燃焼炉2における可燃性ガスの燃焼に際しては、温度センサ3により検知される可燃性ガスの燃焼温度Tに対応して、燃焼炉2に接続された副酸素供給管20の調整弁21の開度が自動的に調節され、該可燃性ガスの完全燃焼に必要とされる量の酸素が燃焼炉2内に供給される。 When the combustion temperature T of the combustible gas in the combustion furnace 2 is maintained at a substantially constant combustion temperature T 1 , the ignition device 14 of the combustion furnace 2 is stopped, and the combustible gas is continuously spontaneously combusted. It becomes. When combusting the combustible gas in the combustion furnace 2, the adjustment valve 21 of the auxiliary oxygen supply pipe 20 connected to the combustion furnace 2 corresponds to the combustion temperature T of the combustible gas detected by the temperature sensor 3. The opening degree is automatically adjusted, and the amount of oxygen required for complete combustion of the combustible gas is supplied into the combustion furnace 2.

燃焼炉2における可燃性ガスの燃焼により生じた燃焼排気(排ガス)は、冷却塔22で冷却され、脱硫・脱臭装置23で消石灰、活性炭により脱硫、脱臭された後、バグフィルター24で微細な塵埃が除去される。そして、最終的には押込ファン26により煙突25に導入され、煙突25から大気中に排出される。   Exhaust gas (exhaust gas) generated by the combustion of combustible gas in the combustion furnace 2 is cooled by the cooling tower 22, desulfurized and deodorized by slaked lime and activated carbon by the desulfurization / deodorization device 23, and then fine dust is produced by the bag filter 24. Is removed. And finally, it is introduce | transduced into the chimney 25 by the pushing fan 26, and is discharged | emitted from the chimney 25 in air | atmosphere.

前記廃棄物Aは、材質によっては、ガス化炉1内で乾留されたときに一酸化炭素を発生し、該一酸化炭素は、ガス化炉1内で生成する可燃性ガスの一部として、燃焼炉2に導入される。前記可燃性ガスは、調整弁19の開度がフィードバック制御されている段階では、それ自体大きな熱量を備えており、前記一酸化炭素は、燃焼炉2で十分に燃焼せしめられる。従って、煙突25に設けられたCOセンサ27で検出される燃焼排気中の一酸化炭素濃度は、大気中に排出されても環境に影響を与えない程度の量となっている。   Depending on the material, the waste A generates carbon monoxide when carbonized in the gasification furnace 1, and the carbon monoxide is a part of the combustible gas generated in the gasification furnace 1. It is introduced into the combustion furnace 2. The combustible gas itself has a large amount of heat when the opening degree of the regulating valve 19 is feedback controlled, and the carbon monoxide is sufficiently burned in the combustion furnace 2. Therefore, the carbon monoxide concentration in the combustion exhaust gas detected by the CO sensor 27 provided in the chimney 25 is an amount that does not affect the environment even if it is discharged into the atmosphere.

ところが、ガス化炉1内の乾留が進行して、乾留の終了段階に至ると、前記廃棄物Aのうち可燃性ガスを生成することができる部分が少なくなり、調整弁19の開度が殆ど全開に達しても、ガス化炉1内で生成する可燃性ガスの燃焼温度Tが所定の燃焼温度T1を維持することができなくなる。すると、燃焼炉2で再び着火装置14に点火して可燃性ガスの燃焼を補助しても、前記一酸化炭素が十分に燃焼せしめられず、COセンサ27により検出される一酸化炭素濃度が高くなってくる。そこで、本実施形態の方法では、温度センサ3により検知される可燃性ガスの燃焼温度Tが所定の温度T2まで降下したならば、ガス化炉1内の乾留が終了段階に入ったものと判断し、一酸化炭素濃度の制御を開始する。 However, when dry distillation in the gasification furnace 1 proceeds and reaches the final stage of dry distillation, the portion of the waste A that can generate combustible gas is reduced, and the opening of the regulating valve 19 is almost all. Even when the valve is fully opened, the combustion temperature T of the combustible gas generated in the gasifier 1 cannot maintain the predetermined combustion temperature T 1 . Then, even if the ignition device 14 is ignited again in the combustion furnace 2 to assist the combustion of the combustible gas, the carbon monoxide is not sufficiently burned, and the carbon monoxide concentration detected by the CO sensor 27 is high. It becomes. Therefore, in the method of the present embodiment, if the combustion temperature T of the combustible gas detected by the temperature sensor 3 falls to a predetermined temperature T 2 , the dry distillation in the gasification furnace 1 has entered the end stage. Judgment and control of carbon monoxide concentration are started.

尚、本実施形態の方法では、温度センサ3により検知される可燃性ガスの燃焼温度Tが一旦所定の温度T2まで降下した後、再び上昇することがある。このような場合には、ガス化炉1内の乾留は、まだ終了段階に入ったわけではなく、何らかの原因で前記可燃性ガスの燃焼温度Tが一時的に温度T2まで降下したに過ぎないと考えられる。そこで、前記可燃性ガスの燃焼温度Tが一旦所定の温度T2まで降下した後、再び上昇したときには、前記一酸化炭素濃度の制御を中止し、再び調整弁19,21の開度を自動的に調整する制御を行うするようにする。 In the method of this embodiment, the combustion temperature T of the combustible gas detected by the temperature sensor 3 may once rise to a predetermined temperature T 2 and then rise again. In such a case, the dry distillation in the gasification furnace 1 has not yet entered the end stage, and the combustion temperature T of the combustible gas has only temporarily dropped to the temperature T 2 for some reason. Conceivable. Therefore, when the combustion temperature T of the combustible gas once falls to the predetermined temperature T 2 and then rises again, the control of the carbon monoxide concentration is stopped and the opening degree of the regulating valves 19 and 21 is automatically set again. Control to be adjusted to.

前記一酸化炭素濃度の制御は、まず、温度センサ3により検知される可燃性ガスの燃焼温度Tが所定の温度T2まで降下したときに、COセンサ27により検出される一酸化炭素濃度を所定の基準値(例えば50ppm)と比較する。次に、前記可燃性ガスの燃焼温度Tが所定の温度T2まで降下したときに、COセンサ27により検出される一酸化炭素濃度aが、図2の中段に示すように所定の基準値より高かった場合には、図2の下段に示すように、調整弁19の開度を小さくする。 The control of the concentration of carbon monoxide, first, when the combustion temperature T of the combustible gas detected by the temperature sensor 3 drops to a predetermined temperature T 2, a predetermined carbon monoxide concentration detected by the CO sensor 27 To a reference value (for example, 50 ppm). Next, when the combustion temperature T of the combustible gas falls to a predetermined temperature T 2 , the carbon monoxide concentration a detected by the CO sensor 27 is greater than a predetermined reference value as shown in the middle stage of FIG. If it is higher, as shown in the lower part of FIG.

調整弁19の開度を小さくすると、ガス化炉1内では供給される酸素量が低減するので、可燃性ガスの生成量自体が低減し、これに伴って一酸化炭素の生成量も低減するので、燃焼炉2内で該一酸化炭素を着火装置14の燃焼炎により十分に燃焼させることが可能になる。   When the opening degree of the regulating valve 19 is reduced, the amount of oxygen supplied in the gasifier 1 is reduced, so that the amount of combustible gas produced itself is reduced, and the amount of carbon monoxide produced is also reduced accordingly. Therefore, the carbon monoxide can be sufficiently burned by the combustion flame of the ignition device 14 in the combustion furnace 2.

そこで、本実施形態の方法では、前記可燃性ガスの燃焼温度Tが所定の温度T2まで降下した後、所定時間毎にCOセンサ27により一酸化炭素濃度を検出する。ここで、一酸化炭素濃度の検出値b、c、d、eが、前回の検出値a,b,c,dよりも高くなった場合は、前回の調整弁19の開度を小さくする操作によっても、一酸化炭素を燃焼炉2内で燃焼可能とするには不十分であるものと判断し、調整弁19の開度を逐次、所定量ずつ小さくし、ガス化炉1に供給される酸素量をさらに低減させる。 Therefore, in the method of this embodiment, after the combustion temperature T of the combustible gas drops to a predetermined temperature T 2, to detect the concentration of carbon monoxide by the CO sensor 27 every predetermined time. Here, when the detected values b, c, d, e of the carbon monoxide concentration are higher than the previous detected values a, b, c, d, an operation for reducing the opening degree of the previous adjusting valve 19. Therefore, it is determined that the carbon monoxide is not sufficient to be combusted in the combustion furnace 2, and the opening degree of the regulating valve 19 is successively reduced by a predetermined amount and supplied to the gasifier 1. Further reduce the amount of oxygen.

一方、COセンサ27により検出される一酸化炭素濃度が、例えば図2の中段に示す検出値c’のように、前回の検出値bよりも低くなった場合は、前回の調整弁19の開度を小さくする操作により、一酸化炭素が燃焼炉2内で燃焼可能になったものと判断する。そして、この場合には、図2の下段に破線で示すように、調整弁19の開度を前回よりも所定量大きくする。   On the other hand, when the carbon monoxide concentration detected by the CO sensor 27 is lower than the previous detection value b, for example, as the detection value c ′ shown in the middle stage of FIG. 2, the previous adjustment valve 19 is opened. It is determined that the carbon monoxide can be burned in the combustion furnace 2 by the operation of decreasing the degree. In this case, as indicated by a broken line in the lower part of FIG. 2, the opening degree of the adjustment valve 19 is increased by a predetermined amount from the previous time.

そして、前記一酸化炭素濃度の制御の結果、COセンサ27により検出される一酸化炭素濃度が、例えば図2の中段に示す検出値fのように、所定の基準値よりも低くなったならば、調整弁19の開度を所定時間毎に所定量ずつ大きくし、ガス化炉1内の廃棄物Aを灰化させる。尚、この場合にも、前記所定時間毎に、COセンサ27により一酸化炭素濃度を検知し、その検出値が前回の検出よりも高くなった場合には、調整弁19の開度を所定量ずつ小さくする。   As a result of the control of the carbon monoxide concentration, if the carbon monoxide concentration detected by the CO sensor 27 becomes lower than a predetermined reference value, for example, as a detection value f shown in the middle part of FIG. The opening degree of the regulating valve 19 is increased by a predetermined amount every predetermined time, and the waste A in the gasification furnace 1 is ashed. In this case as well, when the carbon monoxide concentration is detected by the CO sensor 27 every predetermined time and the detected value becomes higher than the previous detection, the opening degree of the adjusting valve 19 is set to a predetermined amount. Make it smaller.

前記のようにすることにより、大気中に排出される一酸化炭素が環境に影響を与えない程度の量となるように制御することができる。また、前記一酸化炭素濃度の制御では、COセンサ27により検出される一酸化炭素濃度が、前回の検出値よりも低くなった場合または、所定の基準値よりも低くなった場合に、調整弁19の開度を前回よりも大きくすることにより、ガス化炉1内における廃棄物Aの灰化に要する時間を短縮することができる。   By doing so, it is possible to control the amount of carbon monoxide discharged into the atmosphere so as not to affect the environment. Further, in the control of the carbon monoxide concentration, when the carbon monoxide concentration detected by the CO sensor 27 is lower than the previous detection value or lower than a predetermined reference value, the regulating valve By making the opening degree of 19 larger than the previous time, the time required for ashing the waste A in the gasification furnace 1 can be shortened.

次に、本実施形態の方法では、ガス化炉1内において廃棄物Aの灰化が終了したならば、灰化した廃棄物Aをガス化炉1の炉外に排出し、投入口8から新しい廃棄物Aをガス化炉1内に投入する。そして、前述の手順をくり返すことにより、次の処理が行われる。   Next, in the method of the present embodiment, when the ashing of the waste A is completed in the gasification furnace 1, the ashed waste A is discharged out of the furnace of the gasification furnace 1, and is supplied from the inlet 8. New waste A is introduced into the gasifier 1. And the following process is performed by repeating the above-mentioned procedure.

本発明の方法に用いる乾留ガス化焼却処理装置のシステム構成図。The system block diagram of the dry distillation gasification incineration processing apparatus used for the method of this invention. 燃焼炉における可燃性ガスの燃焼温度と、一酸化炭素濃度と、ガス化炉に対する酸素供給量との関係を示すグラフ。The graph which shows the relationship between the combustion temperature of the combustible gas in a combustion furnace, carbon monoxide density | concentration, and the oxygen supply amount with respect to a gasification furnace.

符号の説明Explanation of symbols

1…ガス化炉、 2…燃焼炉、 14…補助燃焼手段、 16…酸素供給源、 27…COセンサ、 A…廃棄物。   DESCRIPTION OF SYMBOLS 1 ... Gasification furnace, 2 ... Combustion furnace, 14 ... Auxiliary combustion means, 16 ... Oxygen supply source, 27 ... CO sensor, A ... Waste.

Claims (3)

ガス化炉内に収容した廃棄物を、酸素供給源から供給される酸素を用いて乾留して可燃性ガスを生成せしめる工程と、
前記ガス化炉内に生成した可燃性ガスを燃焼炉に導入して燃焼せしめる工程と、
前記ガス化炉内の廃棄物の乾留時に、前記燃焼炉における前記可燃性ガスの燃焼温度を予め設定された所定の燃焼温度に略一定に維持するために必要な該可燃性ガスを生成させる量の酸素を、前記酸素供給源から前記ガス化炉内に供給する工程と、
前記ガス化炉内の廃棄物の乾留が終了段階に至ったときに、前記燃焼炉に備えられた補助燃焼手段により前記可燃性ガスの燃焼を補助する工程とを備える廃棄物の乾留ガス化焼却処理方法において、
前記ガス化炉内の廃棄物の乾留の終了段階で、前記燃焼炉の排ガス中の一酸化炭素濃度を検出して、該一酸化炭素濃度の検出値が所定の値よりも高いときには、前記酸素供給源から前記ガス化炉内に供給する酸素量を低減して、前記ガス化炉内で生成する可燃性ガスの量を該可燃性ガス中に含まれる一酸化炭素が前記燃焼炉に備えられた補助燃焼手段により燃焼可能な量となるように制御することを特徴とする廃棄物の乾留ガス化焼却処理方法。
A step of producing a combustible gas by dry distillation of waste contained in a gasification furnace using oxygen supplied from an oxygen supply source;
Introducing the combustible gas generated in the gasification furnace into the combustion furnace and burning it;
An amount for generating the combustible gas necessary for maintaining the combustion temperature of the combustible gas in the combustion furnace at a predetermined predetermined combustion temperature substantially constant during dry distillation of the waste in the gasification furnace Supplying oxygen from the oxygen supply source into the gasifier,
A process of assisting combustion of the combustible gas by auxiliary combustion means provided in the combustion furnace when dry distillation of the waste in the gasification furnace has reached an end stage; In the processing method,
When the carbon monoxide concentration in the exhaust gas of the combustion furnace is detected at the end of dry distillation of the waste in the gasification furnace, and the detected value of the carbon monoxide concentration is higher than a predetermined value, the oxygen The amount of oxygen supplied from the supply source into the gasification furnace is reduced, and the combustion furnace is provided with carbon monoxide contained in the combustible gas in an amount of the combustible gas generated in the gasification furnace. A waste carbonization incineration method for waste, which is controlled so as to be combustible by auxiliary combustion means.
前記ガス化炉内の廃棄物の乾留の終了段階で、所定時間毎に前記燃焼炉の排ガス中の一酸化炭素濃度を検出し、該一酸化炭素濃度の検出値が前回の検出値より高いときには、前記酸素供給源から前記ガス化炉内に供給する酸素量をそれまでよりも低減し、該一酸化炭素濃度の検出値が前回の検出値より低いときには、前記酸素供給源から前記ガス化炉内に供給する酸素量をそれまでよりも増加することを特徴とする請求項1記載の廃棄物の乾留ガス化焼却処理方法。   When the carbon monoxide concentration in the exhaust gas of the combustion furnace is detected every predetermined time at the end of the carbonization of the waste in the gasification furnace, and the detected value of the carbon monoxide concentration is higher than the previous detection value The amount of oxygen supplied from the oxygen supply source into the gasification furnace is reduced more than before, and when the detection value of the carbon monoxide concentration is lower than the previous detection value, the oxygenation source supplies the gasification furnace. The method of claim 1, wherein the amount of oxygen supplied to the inside is increased more than before. 前記ガス化炉内の廃棄物の乾留の終了段階で、前記酸素供給源から前記ガス化炉内に供給する酸素量を低減した後、前記燃焼炉の排ガス中の一酸化炭素濃度の検出値が所定の値よりも低くなったきには、前記酸素供給源から前記ガス化炉内に供給する酸素量を増加して、前記乾留が終了した廃棄物を灰化させることを特徴とする請求項1または請求項2記載の廃棄物の乾留ガス化焼却処理方法。   After reducing the amount of oxygen supplied from the oxygen supply source to the gasification furnace at the end of dry distillation of the waste in the gasification furnace, the detected value of the carbon monoxide concentration in the exhaust gas of the combustion furnace is 2. The waste after the dry distillation is incinerated by increasing the amount of oxygen supplied from the oxygen supply source into the gasification furnace when lower than a predetermined value. Or the carbonization incineration processing method of the waste of Claim 2 characterized by the above-mentioned.
JP2004185822A 2003-07-30 2004-06-24 Waste gasification incineration treatment method of waste Expired - Fee Related JP4139360B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2004185822A JP4139360B2 (en) 2003-07-30 2004-06-24 Waste gasification incineration treatment method of waste

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP2003282666 2003-07-30
JP2004185822A JP4139360B2 (en) 2003-07-30 2004-06-24 Waste gasification incineration treatment method of waste

Publications (2)

Publication Number Publication Date
JP2005061817A true JP2005061817A (en) 2005-03-10
JP4139360B2 JP4139360B2 (en) 2008-08-27

Family

ID=34380196

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2004185822A Expired - Fee Related JP4139360B2 (en) 2003-07-30 2004-06-24 Waste gasification incineration treatment method of waste

Country Status (1)

Country Link
JP (1) JP4139360B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009192091A (en) * 2008-02-12 2009-08-27 Kinsei Sangyo:Kk Carbonizing gasification incineration device and incineration disposal method
CN102359729A (en) * 2011-09-23 2012-02-22 北京航天动力研究所 Method and system for jointly and circularly generating electricity by gasifying municipal garbage at high temperature

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009192091A (en) * 2008-02-12 2009-08-27 Kinsei Sangyo:Kk Carbonizing gasification incineration device and incineration disposal method
CN102359729A (en) * 2011-09-23 2012-02-22 北京航天动力研究所 Method and system for jointly and circularly generating electricity by gasifying municipal garbage at high temperature

Also Published As

Publication number Publication date
JP4139360B2 (en) 2008-08-27

Similar Documents

Publication Publication Date Title
JP5762713B2 (en) Dry distillation gasification incineration processing equipment
JP3869210B2 (en) Waste incineration method
US5619938A (en) Method of incinerating waste material by way of dry distillation and gasification
JP3033015B2 (en) Semi-dry distillation gasification incineration method and apparatus
JP4139360B2 (en) Waste gasification incineration treatment method of waste
JP4050189B2 (en) Waste gasification incineration treatment method of waste
JP5798728B2 (en) Dry distillation gasification incineration processing equipment
JP5890050B2 (en) Dry distillation gasification incineration processing equipment
JP5256553B2 (en) Dry distillation gasification incineration processing apparatus and incineration processing method
JP2856693B2 (en) Waste incineration method
JP4231820B2 (en) Dry distillation gasification incineration equipment
KR0138509B1 (en) Apparatus for incinerating waste material
JP3017661B2 (en) Dry distillation gasification and incineration of waste
JP3152586B2 (en) Dry distillation gasification and incineration of waste
JP3824627B1 (en) Method for melting waste asbestos
JP5762714B2 (en) Dry distillation gasification incineration processing equipment
JP5256558B2 (en) Dry distillation gasifier
JP3549805B2 (en) Waste incineration method
JP4139355B2 (en) Dry distillation gasification incineration equipment
KR0138508B1 (en) Apparatus for incinerating waste material
JP3117793U (en) Combustible gasification burner device
JP3583043B2 (en) Waste incineration method
JP3728416B2 (en) Incineration equipment
JPH10185137A (en) Semi-dry distillation gasification incineration method and device thereof
JPH0849829A (en) Batch type incinerator

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20070625

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20080404

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20080507

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20080606

R150 Certificate of patent or registration of utility model

Ref document number: 4139360

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110613

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120613

Year of fee payment: 4

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130613

Year of fee payment: 5

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees