JP2021098619A - Fuel-producing apparatus and fuel-producing method for combustible waste - Google Patents

Fuel-producing apparatus and fuel-producing method for combustible waste Download PDF

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JP2021098619A
JP2021098619A JP2019230296A JP2019230296A JP2021098619A JP 2021098619 A JP2021098619 A JP 2021098619A JP 2019230296 A JP2019230296 A JP 2019230296A JP 2019230296 A JP2019230296 A JP 2019230296A JP 2021098619 A JP2021098619 A JP 2021098619A
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carbonization
combustible waste
flow rate
gas
dry distillation
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慎二 深見
Shinji Fukami
慎二 深見
大桐 哲雄
Tetsuo Ogiri
哲雄 大桐
岡村 聰一郎
Soichiro Okamura
聰一郎 岡村
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Taiheiyo Cement 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding
    • Y02P40/125Fuels from renewable energy sources, e.g. waste or biomass

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  • Curing Cements, Concrete, And Artificial Stone (AREA)

Abstract

To effectively use a combustible waste that is extremely difficult to treat, by stably feeding the combustible waste to a main burner in a cement kiln as an alternate fuel.SOLUTION: A fuel-producing apparatus 1 for a combustible waste includes: carbonization gasification furnaces 2 (2A to 2C), two or more thereof being arranged in parallel, for performing carbonization gasification of the combustible waste; a flow controller 4 for alternately operating two or more carbonization gasification furnaces to control the flow of a carbonization gas (mixed gas) to be discharged from the operating carbonization gasification furnaces; and supplying means (a fan 5 and the like) for supplying the carbonization gasification gas, the flow amount of which is controlled by the flow controller, continuously to a main burner 10a in a cement kiln 10. The carbonization gasification furnace can open a ceiling part 2a and bottom section 2b thereof and can have a capacity of 50 m3 or more. In the supplying means, a differential pressure-type flow amount-measuring apparatus can be mounted on a pipeline in which the carbonization gasification gasses each discharged from the carbonization gasification furnaces are mixed and thereafter go toward the main burner, the flow-amount measuring apparatus measuring a flow amount of the carbonization gasification gas that flows in the pipeline.SELECTED DRAWING: Figure 1

Description

本発明は、可燃性廃棄物の燃料化装置及び燃料化方法に関し、特に、セメント製造工程において処理困難な可燃性廃棄物を燃料化する技術に関する。 The present invention relates to a fuel conversion device and a fuel conversion method for combustible waste, and more particularly to a technique for converting combustible waste that is difficult to process in a cement manufacturing process into fuel.

セメント製造工程には燃焼ゾーンが2つ存在し、1つは炭酸カルシウムからの脱炭酸反応を促進させるための窯尻や仮焼炉であり、もう1つはセメントの中間製品であるクリンカを焼成するセメントキルンである。仮焼炉及びセメントキルンには、各々バーナーが設置され、特にセメントキルンの窯前に設置されるメインバーナーは、クリンカの品質を決定づけるため重要である。 There are two combustion zones in the cement manufacturing process, one is a kiln butt and a calciner for promoting the decarbonization reaction from calcium carbonate, and the other is firing clinker, which is an intermediate product of cement. Cement kiln. Burners are installed in each of the calciner and the cement kiln, and the main burner installed in front of the kiln of the cement kiln is particularly important for determining the quality of the clinker.

上記2つの燃焼ゾーンで用いられる燃料は、オイルショック以前は重油であったが、オイルショック以後は微粉炭が用いられる。また、セメント燃料への廃棄物の活用は、1980年代に廃タイヤの代替燃料化から始まり、1990年代から現在に至るまで多種多様な形で行われている。 The fuel used in the above two combustion zones was heavy oil before the oil crisis, but pulverized coal is used after the oil crisis. In addition, the utilization of waste as cement fuel began in the 1980s as an alternative fuel for waste tires, and has been carried out in various forms from the 1990s to the present.

窯尻や仮焼炉の燃焼ゾーンでは、可燃性廃棄物の投入口を大きくしたり、燃焼時間を長くすることができると共に、クリンカの品質を決定付けないことから、輸送系統に支障を来さない限り可燃性廃棄物の物理性状が限定されない。そのため、現在では窯尻や仮焼炉で用いられた燃料の全量が可燃性廃棄物に置き換わった。 In the combustion zone of kilns and calciners, the input port for combustible waste can be enlarged, the combustion time can be lengthened, and the quality of the clinker cannot be determined, which hinders the transportation system. Unless otherwise, the physical properties of combustible waste are not limited. As a result, all of the fuel used in kilns and calciners has now been replaced by flammable waste.

一方、セメントキルンのメインバーナーは、クリンカの品質を決定付けるものであるから、バーナーフレームが安定しなければならない。そのため、メインバーナーの代替燃料となる可燃性廃棄物の物理性状や、可燃性廃棄物の投入のし易さや燃焼時間等で制約される。現状では、メインバーナーの代替燃料は、投入し易い廃油や、硬質プラスチックのような加工し易い固形物に限られ、メインバーナー燃料の可燃性廃棄物への置換は30%程度に留まっている。 On the other hand, the main burner of the cement kiln determines the quality of the clinker, so the burner frame must be stable. Therefore, it is restricted by the physical properties of combustible waste as an alternative fuel for the main burner, the ease of inputting combustible waste, the combustion time, and the like. At present, the alternative fuel for the main burner is limited to waste oil that is easy to put in and solids that are easy to process such as hard plastic, and the replacement of the main burner fuel with combustible waste is only about 30%.

そこで、例えば特許文献1及び2には、外熱式キルン等で廃プラスチック等を乾留ガス化し、セメントキルンのメインバーナー等の代替燃料として活用する技術が開示される。 Therefore, for example, Patent Documents 1 and 2 disclose a technique for converting waste plastic or the like into dry distillation gas with an external heat type kiln or the like and utilizing it as an alternative fuel for a main burner or the like of a cement kiln.

特開2002−195524号公報JP-A-2002-195524 特開2003−261887号公報Japanese Unexamined Patent Publication No. 2003-261887

しかし、上記特許文献1及び2に記載の発明では、漁網や農業用ビニール等の加工の極めて困難な可燃性廃棄物をセメントキルンのメインバーナーの代替燃料として用いようとすると、乾留ガス化炉内に炭化水素が付着するなどの問題があり、安定して供給することができないおそれがあった。 However, in the inventions described in Patent Documents 1 and 2, when flammable waste such as fishing nets and agricultural vinyl, which is extremely difficult to process, is used as an alternative fuel for the main burner of a cement kiln, the inside of the dry distillation gasification furnace is used. There was a problem that hydrocarbons adhered to the fuel, and there was a risk that it could not be supplied stably.

そこで、本発明は、上記従来の技術における問題点に鑑みてなされたものであって、加工の極めて困難な可燃性廃棄物をセメントキルンのメインバーナーに代替燃料として安定して供給し、有効利用することができる可燃性廃棄物の燃料化装置及び燃料化方法を提供することを目的とする。 Therefore, the present invention has been made in view of the above-mentioned problems in the prior art, and is capable of stably supplying combustible waste, which is extremely difficult to process, to the main burner of a cement kiln as an alternative fuel for effective use. It is an object of the present invention to provide a fuel conversion device and a fuel conversion method for combustible waste that can be used.

上記目的を達成するため、本発明は、可燃性廃棄物の燃料化装置であって、2基以上並列に設置され、可燃性廃棄物を乾留ガス化する乾留ガス化炉と、該2基以上の乾留ガス化炉を交互運転し、運転している乾留ガス化炉から排出される乾留ガスの流量を調整する流量調整器と、該流量調整器によって流量が調整された乾留ガスをセメントキルンのメインバーナーに連続的に供給する供給手段とを備えることを特徴とする。 In order to achieve the above object, the present invention is a carbonization device for combustible waste, in which two or more units are installed in parallel to carbonize combustible waste into a dry distillation gas, and two or more units thereof. A flow controller that alternately operates the carbonization gasification furnaces of the carbonization of the above to adjust the flow rate of the carbonization gas discharged from the carbonization gasification furnace in operation, and the dry distillation gas whose flow rate is adjusted by the flow rate regulator It is characterized by being provided with a supply means for continuously supplying the main burner.

本発明によれば、乾留ガス化炉を2基以上並列に設置し、これらを交互運転することで、乾留ガス化炉内への炭化水素の付着等を防止することができるため、加工の極めて困難な可燃性廃棄物をセメントキルンのメインバーナーに微粉炭代替燃料として安定して供給することができる。これにより、メインバーナーの燃料代替率を向上させることができ、化石燃料の使用量を低減することができる。 According to the present invention, by installing two or more dry distillation gasification furnaces in parallel and operating them alternately, it is possible to prevent adhesion of hydrocarbons to the inside of the dry distillation gasification furnace. Difficult combustible waste can be stably supplied to the main burner of a cement kiln as an alternative fuel for pulverized carbonization. As a result, the fuel alternative rate of the main burner can be improved, and the amount of fossil fuel used can be reduced.

上記可燃性廃棄物の燃料化装置において、前記乾留ガス化炉を天井部及び炉底部が開放可能で50m以上の容積を有するものとすることで、可燃性廃棄物を効率よく乾留ガス化することができる。 In the above combustible waste fuel conversion device, the dry distillation gasification furnace is capable of opening the ceiling and the bottom of the furnace and having a volume of 50 m 3 or more, so that the combustible waste is efficiently converted into dry distillation gas. be able to.

また、前記供給手段は、前記2基以上の乾留ガス化炉の各々から排出される乾留ガスが合流した後、前記メインバーナーへ向かう配管に、該配管を流れる乾留ガスの流量を測定する差圧型流量測定器を備えることで、メインバーナーへの乾留ガスの供給量を把握することができる。 Further, the supply means is a differential pressure type that measures the flow rate of the dry distillation gas flowing through the pipe toward the main burner after the dry distillation gas discharged from each of the two or more dry distillation gas furnaces merges. By providing a flow rate measuring device, it is possible to grasp the amount of dry distillation gas supplied to the main burner.

さらに、前記乾留ガス化炉の焼却残渣から金属残渣とセメント原料代替物を分別回収する磁力選別機、渦電流選別装置又は/及び風力選別機を設けることで、乾留ガス化炉の焼却残渣を有効利用することができる。 Further, by providing a magnetic force sorter, an eddy current sorter and / or a wind power sorter that separates and recovers the metal residue and the cement raw material substitute from the incinerator residue of the dry distillation gasification furnace, the incinerator residue of the dry distillation gasification furnace is effective. It can be used.

また、前記セメント原料代替物に含まれる塩素を除去する水洗装置を備えることで、セメント原料代替物をセメント原料として利用しても、セメント品質に悪影響を及ぼすことを回避することができる。 Further, by providing a water washing device for removing chlorine contained in the cement raw material substitute, it is possible to avoid adversely affecting the cement quality even if the cement raw material substitute is used as the cement raw material.

また、本発明は、可燃性廃棄物の燃料化方法であって、可燃性廃棄物を乾留ガス化するための乾留ガス化炉を2基以上並列に設置し、該2基以上の乾留ガス化炉を交互運転し、運転している乾留ガス化炉から排出される乾留ガスの流量を調整し、該流量が調整された乾留ガスをセメントキルンのメインバーナーに連続的に供給することを特徴とする。本発明によれば、加工の極めて困難な可燃性廃棄物をメインバーナーに代替燃料として安定して供給することができ、化石燃料の使用量を低減することができる。 Further, the present invention is a method for converting combustible waste into fuel, in which two or more carbonization gasification furnaces for carbonizing combustible waste are installed in parallel to convert the two or more carbonization gas into dry distillation gas. It is characterized by alternately operating the furnaces, adjusting the flow rate of the dry distillation gas discharged from the operating dry distillation gasification furnace, and continuously supplying the adjusted dry distillation gas to the main burner of the cement kiln. To do. According to the present invention, combustible waste that is extremely difficult to process can be stably supplied to the main burner as an alternative fuel, and the amount of fossil fuel used can be reduced.

以上のように、本発明によれば、加工の極めて困難な可燃性廃棄物をセメントキルンのメインバーナーに微粉炭代替燃料として安定して供給し、有効利用することができる。 As described above, according to the present invention, combustible waste that is extremely difficult to process can be stably supplied to the main burner of a cement kiln as an alternative fuel for pulverized coal and can be effectively used.

本発明に係る可燃性廃棄物の燃料化装置の一実施の形態を示す全体構成図である。It is an overall block diagram which shows one Embodiment of the fuel conversion apparatus of combustible waste which concerns on this invention.

次に、本発明を実施するための形態について図面を参照しながら詳細に説明する。 Next, a mode for carrying out the present invention will be described in detail with reference to the drawings.

図1は、本発明に係る可燃性廃棄物の燃料化装置の一実施の形態を示し、この可燃性廃棄物の燃料化装置1は、乾留ガス化炉2(2A〜2C)と、乾留ガス化炉2の出口に設けられるダンパ3(3A〜3C)と、乾留ガス化炉2(2A〜2C)から排出される乾留ガスG1〜G3の合流ガスGの流量を調整する流量調整器4と、合流ガスGをセメントキルン10のメインバーナー10aに連続的に供給するファン(供給手段)5と、合流ガスG乾留ガス化炉2から排出された焼却残渣Rから金属残渣を回収するための金属残渣回収装置6と、金属残渣を回収した後の焼却残渣R1を水洗して脱塩する水洗装置7等で構成される。 FIG. 1 shows an embodiment of a combustible waste fuel conversion device according to the present invention, in which the combustible waste fuel conversion device 1 includes a dry distillation gasification furnace 2 (2A to 2C) and a dry distillation gas. A damper 3 (3A to 3C) provided at the outlet of the chemical furnace 2 and a flow regulator 4 for adjusting the flow rate of the combined gas G of the carbonization gas G1 to G3 discharged from the carbonization gasification furnace 2 (2A to 2C). , A fan (supply means) 5 for continuously supplying the confluent gas G to the main burner 10a of the cement kiln 10 and a metal for recovering the metal residue from the incineration residue R discharged from the carbonization gasization furnace 2 of the confluence gas G. It is composed of a residue recovery device 6 and a water washing device 7 for washing and desalting the incineration residue R1 after recovering the metal residue.

乾留ガス化炉2は、複数(図示例では3基)並列に設置され、各々直径2m以上の円筒状の本体2cを有し、天井部2aと炉底部2bが開閉可能なものあって、魚網、農業用ビニール、フレコン封入物等の加工し難い可燃性廃棄物Wをそのまま投入することができる。乾留ガス化炉2は、少なくとも2基以上、運用面を考慮すると3基以上設置するのが望ましい。乾留ガス化炉2の1基当たりの容量は、可燃性廃棄物Wの燃え切り時間と、乾留ガス化炉2(2A〜2C)の運転切替のタイミングを考慮し、50m以上であることが好ましい。 A plurality of dry distillation gasification furnaces 2 (three in the illustrated example) are installed in parallel, each having a cylindrical main body 2c having a diameter of 2 m or more, and a ceiling portion 2a and a furnace bottom portion 2b can be opened and closed. , Combustible waste W, which is difficult to process, such as agricultural vinyl and flexible container inclusions, can be input as it is. It is desirable to install at least two dry distillation gasification furnaces 2 and three or more in consideration of operation. The capacity per unit of the carbonization gasification furnace 2 should be 50 m 3 or more in consideration of the burnout time of the combustible waste W and the timing of switching the operation of the carbonization gasification furnaces 2 (2A to 2C). preferable.

乾留ガス化炉2(2A〜2C)の各々からメインバーナー10aは配管で接続され、乾留ガス化炉2側が負圧となるように配管の流路の途中にファン5を設置し、乾留ガスGをメインバーナー10aに供給する。 The main burner 10a is connected from each of the carbonization gasification furnaces 2 (2A to 2C) by a pipe, and a fan 5 is installed in the middle of the flow path of the pipe so that the dry distillation gasification furnace 2 side has a negative pressure. Is supplied to the main burner 10a.

流量調整器4は、合流ガスGの流量を調整するために設けられ、合流ガスGが流れる管路に配置された差圧型流量測定器(不図示)によって合流ガスGの流量が測定される。合流ガスGの流量の調整は、図示例のように、乾留ガス化炉2(2A〜2C)の各々の配管に設けたダンパ3(3A〜3C)で行うことも可能であるが、ファン5を設置せずに、各々の乾留ガス化炉2にインバータファンを設置することにより行うことも可能である。 The flow rate regulator 4 is provided to adjust the flow rate of the merging gas G, and the flow rate of the merging gas G is measured by a differential pressure type flow rate measuring device (not shown) arranged in a pipeline through which the merging gas G flows. As shown in the illustrated example, the flow rate of the merged gas G can be adjusted by the dampers 3 (3A to 3C) provided in each pipe of the carbonization gasification furnaces 2 (2A to 2C), but the fan 5 It is also possible to install an inverter fan in each carbonization gasification furnace 2 without installing the above.

金属残渣回収装置6は、磁力選別機、渦電流選別装置又は/及び風力選別機であって、回収対象の金属残渣の種類や量等に応じて選択的に設置される。また、水洗装置7は、焼却残渣R1に含まれる塩素等を除去するために設けられ、フィルタプレス等が用いられる。 The metal residue recovery device 6 is a magnetic force sorter, an eddy current sorter and / or a wind power sorter, and is selectively installed according to the type and amount of the metal residue to be recovered. Further, the water washing device 7 is provided to remove chlorine and the like contained in the incinerator residue R1, and a filter press or the like is used.

次に、上記構成を有する可燃性廃棄物の燃料化装置1の動作について説明する。 Next, the operation of the combustible waste fuel conversion device 1 having the above configuration will be described.

乾留ガス化炉2の1つである乾留ガス化炉2Aに示すように、天井部2aを開放し、漁網等の可燃性廃棄物Wを投入する。次に、乾留ガス化炉2Bに示すように、天井部2aを閉鎖した後、投入された可燃性廃棄物Wにガス又は灯油バーナ(不図示)で着火し、着火後は自燃させることで乾留ガスG2を発生させ、発生した乾留ガスG2を含む合流ガスGをセメントキルン10のメインバーナー10aにファン5によって誘導する。 As shown in the carbonization gasification furnace 2A, which is one of the carbonization gasification furnaces 2, the ceiling portion 2a is opened and combustible waste W such as a fishing net is charged. Next, as shown in the dry distillation gasification furnace 2B, after closing the ceiling portion 2a, the charged combustible waste W is ignited with a gas or kerosene burner (not shown), and after ignition, it is self-combusted to perform dry distillation. Gas G2 is generated, and the combined gas G containing the generated dry distillation gas G2 is guided by the fan 5 to the main burner 10a of the cement kiln 10.

メインバーナー10aへの合流ガスGの供給量は、3基の乾留ガス化炉2(2A〜2C)を交互運転し、運転している乾留ガス化炉2の出口のダンパ3(3A〜3C)を開き(図1ではダンパ3Bが開となっている。)、差圧型流量測定器によって合流ガスGの流量を測定し、流量調整器4で合流ガスGの流量を調整することで制御する。 The supply amount of the confluent gas G to the main burner 10a is the damper 3 (3A to 3C) at the outlet of the dry distillation gasification furnace 2 which is operating by alternately operating the three dry distillation gasification furnaces 2 (2A to 2C). (Damper 3B is open in FIG. 1), the flow rate of the merging gas G is measured by a differential pressure type flow rate measuring device, and the flow rate of the merging gas G is adjusted by the flow rate regulator 4.

乾留ガス化炉2Cに示すように、可燃性廃棄物Wの自燃完了後は、数時間そのまま自然降温させ、自然降温後は、炉底部2bを開放して焼却残渣Rを排出する。 As shown in the carbonization gasification furnace 2C, after the self-combustion of the combustible waste W is completed, the temperature is naturally lowered for several hours, and after the natural temperature is lowered, the bottom 2b of the furnace is opened to discharge the incinerator residue R.

排出後の焼却残渣Rは、金属残渣回収装置6によって金属残渣Hを回収し、金属残渣Hを回収した後の焼却残渣R1は、水洗装置7で水洗脱塩して塩素Clを除去した後、焼却残渣R2としてセメント原料として利用する。焼却残渣R2は金属残渣や塩素が除去されているため、セメントの品質に悪影響を及ぼすことがない。 The incineration residue R after discharge recovers the metal residue H by the metal residue recovery device 6, and the incineration residue R1 after collecting the metal residue H is washed with water and desalted by the water washing device 7 to remove chlorine Cl. , Used as a cement raw material as incineration residue R2. Since the incinerator residue R2 has metal residue and chlorine removed, it does not adversely affect the quality of cement.

以上のように、本実施の形態によれば、乾留ガス化炉2を2基以上並列に設置し、これらを交互運転することで、漁網等の加工し難い可燃性廃棄物Wを燃料化する場合であっても、各々の乾留ガス化炉2内で可燃性廃棄物Wが燃え切るため、乾留ガス化炉2内への炭化水素の付着等を防止することができるため、セメントキルン10のメインバーナー10aに安定して供給することができる。これにより、これまで焼却処理以外の処分方法がなかった可燃性廃棄物Wの保有熱をセメント製造に有効活用することができ、メインバーナー10aの燃料代替率を向上させることができ、化石燃料の使用量を低減することができる。また、可燃性廃棄物Wを処理した際に発生する排ガスや焼却灰の負担もほぼなくなる。尚、合流ガスGの供給量に余裕がある場合には、メインバーナー10a以外に窯尻や仮焼炉の代替燃料として利用してもよい。 As described above, according to the present embodiment, two or more carbonization gasification furnaces 2 are installed in parallel, and these are operated alternately to convert combustible waste W such as a fishing net, which is difficult to process, into fuel. Even in this case, since the flammable waste W burns out in each carbonization gasification furnace 2, it is possible to prevent adhesion of hydrocarbons into the carbonization gasification furnace 2 and the like. It can be stably supplied to the main burner 10a. As a result, the heat possessed by the combustible waste W, which has not been disposed of other than incineration, can be effectively utilized for cement production, the fuel alternative rate of the main burner 10a can be improved, and the fossil fuel The amount used can be reduced. In addition, the burden of exhaust gas and incinerator ash generated when the combustible waste W is treated is almost eliminated. If there is a margin in the supply amount of the combined gas G, it may be used as an alternative fuel for the kiln tail or the calcining furnace in addition to the main burner 10a.

以上、本発明の一実施の形態について説明したが、本発明は、上述した本発明の実施形態に限定されるものではなく、本発明の要旨を逸脱しない範囲内で様々な変形や応用が可能である。 Although one embodiment of the present invention has been described above, the present invention is not limited to the above-described embodiment of the present invention, and various modifications and applications can be made without departing from the gist of the present invention. Is.

1 可燃性廃棄物の燃料化装置
2(2A〜2C) 乾留ガス化炉
2a 天井部
2b 炉底部
2c 本体
3(3A〜3C) ダンパ
4 流量調整器
5 ファン
6 金属残渣回収装置
7 水洗装置
10 セメントキルン
10a メインバーナー
Cl 塩素
G 合流ガス
G1〜G3 乾留ガス
H 金属残渣
R、R1、R2 焼却残渣
W 可燃性廃棄物
1 Combustible waste fueling device 2 (2A-2C) Carbonization gasifier 2a Ceiling 2b Furnace bottom 2c Main body 3 (3A-3C) Damper 4 Flow regulator 5 Fan 6 Metal residue recovery device 7 Water washing device 10 Cement Kiln 10a Main burner Cl Chlorine G Combined gas G1 to G3 Carbonization gas H Metal residue R, R1, R2 Incinerator residue W Combustible waste

Claims (6)

2基以上並列に設置され、可燃性廃棄物を乾留ガス化する乾留ガス化炉と、
該2基以上の乾留ガス化炉を交互運転し、運転している乾留ガス化炉から排出される乾留ガスの流量を調整する流量調整器と、
該流量調整器によって流量が調整された乾留ガスをセメントキルンのメインバーナーに連続的に供給する供給手段とを備えることを特徴とする可燃性廃棄物の燃料化装置。
Two or more carbonization gasifiers installed in parallel to convert combustible waste into carbonization gas, and
A flow rate regulator that alternately operates the two or more carbonization gasifiers and adjusts the flow rate of the carbonization gas discharged from the operating carbonization gasifiers.
A combustible waste fueling device comprising a supply means for continuously supplying a dry distillation gas whose flow rate has been adjusted by the flow rate regulator to a main burner of a cement kiln.
前記乾留ガス化炉は、天井部及び炉底部が開放可能で50m以上の容積を有することを特徴とする請求項1に記載の可燃性廃棄物の燃料化装置。 The combustible waste fuel conversion device according to claim 1, wherein the dry distillation gasification furnace has a ceiling portion and a furnace bottom portion that can be opened and has a volume of 50 m 3 or more. 前記供給手段は、前記2基以上の乾留ガス化炉の各々から排出される乾留ガスが合流した後、前記メインバーナーへ向かう配管に、該配管を流れる乾留ガスの流量を測定する差圧型流量測定器を備えることを特徴とする請求項1又は2に記載の可燃性廃棄物の燃料化装置。 The supply means is a differential pressure type flow rate measurement for measuring the flow rate of the dry distillation gas flowing through the pipe toward the main burner after the dry distillation gas discharged from each of the two or more carbonization gas furnaces merges. The combustible waste fueling device according to claim 1 or 2, further comprising a container. 前記乾留ガス化炉の焼却残渣から金属残渣とセメント原料代替物を分別回収する磁力選別機、渦電流選別装置又は/及び風力選別機を備えることを特徴とする請求項1、2又は3に記載の可燃性廃棄物の燃料化装置。 The invention according to claim 1, 2 or 3, further comprising a magnetic force sorter, an eddy current sorter and / and a wind sorter for separating and recovering the metal residue and the cement raw material substitute from the incinerator residue of the carbonization gasification furnace. Combustible waste fueling equipment. 前記セメント原料代替物に含まれる塩素を除去する水洗装置を備えることを特徴とする請求項4に記載の可燃性廃棄物の燃料化装置。 The fuel conversion device for combustible waste according to claim 4, further comprising a water washing device for removing chlorine contained in the cement raw material substitute. 可燃性廃棄物を乾留ガス化するための乾留ガス化炉を2基以上並列に設置し、
該2基以上の乾留ガス化炉を交互運転し、運転している乾留ガス化炉から排出される乾留ガスの流量を調整し、
該流量が調整された乾留ガスをセメントキルンのメインバーナーに連続的に供給することを特徴とする可燃性廃棄物の燃料化方法。
Two or more dry distillation gasifiers for carbonizing combustible waste into dry distillation gas were installed in parallel.
The two or more carbonization gasifiers are operated alternately to adjust the flow rate of the carbonization gas discharged from the operating carbonization gasifiers.
A method for fueling combustible waste, which comprises continuously supplying the dry distillation gas having an adjusted flow rate to the main burner of a cement kiln.
JP2019230296A 2019-12-20 2019-12-20 Fuel-producing apparatus and fuel-producing method for combustible waste Pending JP2021098619A (en)

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WO2024047684A1 (en) * 2022-08-29 2024-03-07 太平洋エンジニアリング株式会社 Combustible waste material processing device and processing method

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JPH0894043A (en) * 1994-09-22 1996-04-12 Kinsei Sangyo:Kk Dry distillation gasification incinerating method for waste
JPH08334218A (en) * 1995-06-08 1996-12-17 Kinsei Sangyo:Kk Dry-distillation incinerator
JPH10113646A (en) * 1996-10-08 1998-05-06 Heiwa Corp Treatment of game machine and recycling method
JP2002195524A (en) * 2000-12-21 2002-07-10 Ishikawajima Harima Heavy Ind Co Ltd Waste treatment facility for sintering cement
JP2002274900A (en) * 2001-03-14 2002-09-25 Taiheiyo Cement Corp Method of producing cement raw material and the cement raw material
JP2005345078A (en) * 2004-06-07 2005-12-15 Kinsei Sangyo:Kk Dry distillation gasification and incineration processing device
JP2014034603A (en) * 2012-08-07 2014-02-24 Kinsei Sangyo:Kk Apparatus for gasification by carbonization

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JPH0894043A (en) * 1994-09-22 1996-04-12 Kinsei Sangyo:Kk Dry distillation gasification incinerating method for waste
JPH08334218A (en) * 1995-06-08 1996-12-17 Kinsei Sangyo:Kk Dry-distillation incinerator
JPH10113646A (en) * 1996-10-08 1998-05-06 Heiwa Corp Treatment of game machine and recycling method
JP2002195524A (en) * 2000-12-21 2002-07-10 Ishikawajima Harima Heavy Ind Co Ltd Waste treatment facility for sintering cement
JP2002274900A (en) * 2001-03-14 2002-09-25 Taiheiyo Cement Corp Method of producing cement raw material and the cement raw material
JP2005345078A (en) * 2004-06-07 2005-12-15 Kinsei Sangyo:Kk Dry distillation gasification and incineration processing device
JP2014034603A (en) * 2012-08-07 2014-02-24 Kinsei Sangyo:Kk Apparatus for gasification by carbonization

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2024047684A1 (en) * 2022-08-29 2024-03-07 太平洋エンジニアリング株式会社 Combustible waste material processing device and processing method

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