JP2000283404A - How to use waste fuel - Google Patents
How to use waste fuelInfo
- Publication number
- JP2000283404A JP2000283404A JP9166799A JP9166799A JP2000283404A JP 2000283404 A JP2000283404 A JP 2000283404A JP 9166799 A JP9166799 A JP 9166799A JP 9166799 A JP9166799 A JP 9166799A JP 2000283404 A JP2000283404 A JP 2000283404A
- Authority
- JP
- Japan
- Prior art keywords
- waste
- char
- fuel
- transferred
- power plant
- 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.)
- Pending
Links
- 239000002699 waste material Substances 0.000 title claims abstract description 82
- 239000000446 fuel Substances 0.000 title claims abstract description 63
- 238000000197 pyrolysis Methods 0.000 claims abstract description 45
- 239000007787 solid Substances 0.000 claims abstract description 25
- 238000000034 method Methods 0.000 claims abstract description 22
- 239000004568 cement Substances 0.000 claims description 17
- 239000003245 coal Substances 0.000 claims description 17
- 229910052751 metal Inorganic materials 0.000 abstract description 19
- 239000002184 metal Substances 0.000 abstract description 19
- 150000002739 metals Chemical class 0.000 abstract description 14
- 239000011521 glass Substances 0.000 abstract description 13
- 238000004519 manufacturing process Methods 0.000 abstract description 12
- 239000002910 solid waste Substances 0.000 abstract description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 12
- 235000019645 odor Nutrition 0.000 description 10
- 238000006243 chemical reaction Methods 0.000 description 9
- 238000010586 diagram Methods 0.000 description 7
- 239000002956 ash Substances 0.000 description 6
- 229910052742 iron Inorganic materials 0.000 description 6
- 238000010438 heat treatment Methods 0.000 description 5
- 229910052782 aluminium Inorganic materials 0.000 description 4
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 4
- 238000002485 combustion reaction Methods 0.000 description 4
- 239000004449 solid propellant Substances 0.000 description 4
- 238000001035 drying Methods 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 238000005979 thermal decomposition reaction Methods 0.000 description 3
- 229910000831 Steel Inorganic materials 0.000 description 2
- 239000000460 chlorine Substances 0.000 description 2
- 239000010883 coal ash Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000002309 gasification Methods 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 238000011068 loading method Methods 0.000 description 2
- 239000006148 magnetic separator Substances 0.000 description 2
- 239000010813 municipal solid waste Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 238000007711 solidification Methods 0.000 description 2
- 230000008023 solidification Effects 0.000 description 2
- 239000010959 steel Substances 0.000 description 2
- 230000032258 transport Effects 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 101100219325 Phaseolus vulgaris BA13 gene Proteins 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- -1 cans and others Chemical class 0.000 description 1
- 239000003610 charcoal Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000001125 extrusion Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/12—Heat utilisation in combustion or incineration of waste
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/16—Combined cycle power plant [CCPP], or combined cycle gas turbine [CCGT]
- Y02E20/18—Integrated gasification combined cycle [IGCC], e.g. combined with carbon capture and storage [CCS]
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Processing Of Solid Wastes (AREA)
- Coke Industry (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
- Manufacture Of Iron (AREA)
- Solid-Fuel Combustion (AREA)
- Gasification And Melting Of Waste (AREA)
Abstract
(57)【要約】
【課題】 ハンドリング性が非常に良好で悪臭や腐敗の
発生を防止しつつ、廃棄物を燃料として発電所等へ送り
込むことができ、且つゴミ固形燃料の製造に比べ燃料化
に必要なエネルギー並びにコストも少なくでき、経済的
にも有利となり、しかも、廃棄物に含まれる良質な有価
金属やガラス類を回収し得る廃棄物の燃料利用方法を提
供する。
【解決手段】 廃棄物1を破砕機2で破砕し、必要に応
じて乾燥機3で水分除去し、熱分解炉4で熱分解させて
熱分解残渣を生成し、該熱分解残渣からチャーを選別装
置5で選別した後、該チャーを固形化装置22で所要形
状の固形物に固形化し、該固形化したチャーを移送手段
9で移送し、別設備で燃料として燃焼させる。
(57) [Summary] [Problem] To be able to send waste as a fuel to a power plant, etc., while having excellent handling properties and to prevent the generation of bad smell and decay, and to convert it into a fuel as compared to the production of solid waste fuel In addition, the present invention provides a method of using waste fuel that can reduce the energy and cost required for the waste, is economically advantageous, and can collect high-quality valuable metals and glass contained in the waste. SOLUTION: A waste 1 is crushed by a crusher 2, water is removed by a dryer 3 if necessary, and pyrolysis is performed in a pyrolysis furnace 4 to generate a pyrolysis residue, and char is separated from the pyrolysis residue. After sorting by the sorting device 5, the char is solidified into a solid having a required shape by the solidifying device 22, and the solidified char is transferred by the transfer means 9 and burned as fuel in another facility.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、廃棄物の燃料利用
方法に関するものである。[0001] The present invention relates to a method for utilizing waste fuel.
【0002】[0002]
【従来の技術】一般に、都市ゴミ等の廃棄物は焼却処分
されるが、廃棄物のエネルギーとしての有効利用の観点
から、廃棄物をボイラの燃料として利用し、発電する技
術が広く用いられている。2. Description of the Related Art Generally, waste such as municipal waste is incinerated. From the viewpoint of effective use of waste as energy, a technique for generating electricity by using waste as fuel for a boiler has been widely used. I have.
【0003】[0003]
【発明が解決しようとする課題】しかしながら、廃棄物
をボイラの燃料として燃焼させるのでは、廃棄物には塩
素が含まれており、ボイラの伝熱管を腐食させるため、
蒸気条件(蒸気の温度と圧力)をあまり上げることがで
きず、効率のよい発電を行うことができない。廃棄物は
その形状や大きさがまちまちでハンドリング性が悪く、
特に一般家庭から出る生ゴミ等の廃棄物では悪臭や腐敗
に関しても考慮しなければならず、広域で発生する廃棄
物を処理するのは困難であった。However, if the waste is burned as fuel for the boiler, the waste contains chlorine and corrodes the heat transfer tubes of the boiler.
The steam conditions (temperature and pressure of steam) cannot be increased so much that efficient power generation cannot be performed. Waste has various shapes and sizes, and its handling is poor.
In particular, for waste such as garbage from general households, it is necessary to consider the odor and decay, and it is difficult to treat the waste generated in a wide area.
【0004】これらの解決策として、廃棄物を粉砕し、
カルシウム等を加え、10〜20[mm]程度の柱状チ
ップに固めて乾燥させたゴミ固形燃料(RDF:Ref
use Derived Fuel)を製造する技術が
開発されているが、このようなゴミ固形燃料の製造には
多大なエネルギーが必要でコストも多くかかり、経済的
でないという欠点を有していた。[0004] As a solution to these problems, waste is crushed,
Refuse solid fuel (RDF: Ref) which is made by adding calcium and the like, solidifying into a columnar chip of about 10 to 20 [mm] and drying.
Techniques for producing use-derived fuel have been developed, but the production of such refuse solid fuel requires a large amount of energy, is costly, and is not economical.
【0005】又、廃棄物をボイラの燃料として燃焼させ
た場合、廃棄物に含まれる良質な有価金属は酸化されて
しまうと共に、良質なガラス類は溶融してしまい、いず
れも回収が不可能となっていた。When waste is burned as fuel for a boiler, high-quality valuable metals contained in the waste are oxidized, and high-quality glasses are melted. Had become.
【0006】本発明は、斯かる実情に鑑み、ハンドリン
グ性が良好で悪臭や腐敗の発生を防止しつつ、廃棄物を
燃料として発電所等へ送り込むことができ、且つゴミ固
形燃料の製造に比べ燃料化に必要なエネルギー並びにコ
ストも少なくでき、経済的にも有利となり、しかも、廃
棄物に含まれる良質な有価金属やガラス類を回収し得る
廃棄物の燃料利用方法を提供しようとするものである。[0006] In view of such circumstances, the present invention is capable of sending waste to a power plant or the like as fuel while having good handling properties and preventing the generation of offensive odors and decay, and is more effective than the production of solid fuel. The aim is to provide a method of using waste fuel that can reduce the energy and cost required for fuel conversion, is economically advantageous, and can recover high-quality valuable metals and glass contained in waste. is there.
【0007】[0007]
【課題を解決するための手段】本発明は、廃棄物を破砕
し、熱分解させて熱分解残渣を生成し、該熱分解残渣か
らチャーを選別した後、該チャーを所要形状の固形物に
固形化し、該固形化したチャーを移送し、別設備で燃料
として燃焼させることを特徴とする廃棄物の燃料利用方
法にかかるものである。SUMMARY OF THE INVENTION According to the present invention, waste is crushed and pyrolyzed to generate a pyrolysis residue, and the char is selected from the pyrolysis residue. The present invention relates to a method for utilizing waste fuel, which comprises solidifying, transferring the solidified char, and burning it as fuel in another facility.
【0008】前記廃棄物の燃料利用方法においては、別
設備を発電所とし、該発電所の微粉炭ミルにおいて、移
送されたチャーを石炭と一緒に微粉砕した後、微粉炭焚
ボイラで燃焼させるようにすることができる。In the above-mentioned method of utilizing waste fuel, another facility is used as a power plant, and in a pulverized coal mill of the power plant, the transferred char is pulverized together with coal, and then burnt in a pulverized coal-fired boiler. You can do so.
【0009】前記廃棄物の燃料利用方法においては、別
設備を発電所とし、該発電所の解砕装置において、移送
されたチャーを解砕した後、微粉炭焚ボイラで燃焼させ
るようにすることもできる。[0009] In the above-mentioned method of utilizing waste fuel, another facility is a power plant, and in a crusher of the power plant, the transferred char is crushed and then burned in a pulverized coal-fired boiler. Can also.
【0010】前記廃棄物の燃料利用方法においては、別
設備を発電所とし、該発電所の流動床ボイラにおいて、
移送されたチャーを燃焼させるようにしてもよい。In the above-mentioned method of utilizing waste fuel, another facility is a power plant, and a fluidized-bed boiler of the power plant includes:
The transferred char may be burned.
【0011】前記廃棄物の燃料利用方法においては、別
設備を発電所とし、該発電所の専焼ボイラにおいて、移
送されたチャーを燃焼させて蒸気を発生させ、該蒸気を
主ボイラで発生させた蒸気と一緒に蒸気タービンへ導く
ようにすることもできる。In the above-mentioned method of utilizing waste fuel, another facility is used as a power station, and in a dedicated boiler of the power station, the transferred char is burned to generate steam, and the steam is generated in the main boiler. It can also be guided to a steam turbine together with the steam.
【0012】前記廃棄物の燃料利用方法においては、別
設備を発電所とし、該発電所のガス化炉において、移送
されたチャーをガス化し、該ガス化ガスをボイラで燃焼
させるようにしてもよい。In the above-mentioned method of utilizing waste fuel, another facility may be a power plant, and the transferred char may be gasified in a gasifier of the power plant, and the gasified gas may be burned by a boiler. Good.
【0013】前記廃棄物の燃料利用方法においては、別
設備をセメント工場とし、該セメント工場のセメントキ
ルンにおいて、移送されたチャーを燃焼させるようにす
ることも可能である。[0013] In the above-mentioned method of using waste fuel, it is possible to use a separate facility as a cement factory and burn the transferred char in a cement kiln of the cement factory.
【0014】前記廃棄物の燃料利用方法においては、別
設備を製鉄所とし、該製鉄所の高炉において、移送され
たチャーを燃焼させるようにしてもよい。In the above-mentioned method of using waste fuel, another facility may be a steelworks, and the transferred char may be burned in a blast furnace of the steelworks.
【0015】上記手段によれば、以下のような作用が得
られる。According to the above means, the following effects can be obtained.
【0016】廃棄物は破砕され、熱分解されて熱分解残
渣が生成され、該熱分解残渣からチャーが選別された
後、該チャーが所要形状の固形物に固形化され、該固形
化されたチャーが移送され、別設備で燃料として燃焼さ
れる。The waste is crushed and pyrolyzed to generate a pyrolysis residue. After the char is separated from the pyrolysis residue, the char is solidified into a solid having a required shape, and the solid is formed. The char is transferred and burned as fuel in another facility.
【0017】この結果、廃棄物を熱分解により粉末状の
チャーとし更に所要形状の固形物に固形化して移送する
ため、粉末状のままの場合よりハンドリング性が更によ
くなると共に、悪臭や腐敗が発生する心配もなく、発電
所やセメント工場或いは製鉄所等の別設備へ送り込むこ
とが可能となる。As a result, since the waste is pyrolyzed into a powdery char and solidified into a solid having a required shape and transferred, the handling property is further improved as compared with the case where the waste remains powdery, and the odor and rot are generated. It can be sent to another facility such as a power plant, a cement factory, or a steel mill without worry.
【0018】又、廃棄物の熱分解に必要なエネルギー
は、熱分解の過程で生成される熱分解ガスの燃焼によっ
て得ることができるため、外部からのエネルギー投入が
ほとんど必要なく、ゴミ固形燃料(RDF)を製造する
よりエネルギーが少なくて済み、且つコストも少なくて
済む。Further, since the energy required for the thermal decomposition of waste can be obtained by burning the pyrolysis gas generated in the process of thermal decomposition, almost no external energy input is required, and the waste solid fuel ( RDF) requires less energy and costs.
【0019】更に又、廃棄物は、直接燃焼させるのでは
なく、比較的温度の低い熱分解により熱分解残渣を生成
させるようにしているため、廃棄物に含まれる良質な鉄
やアルミ等の有価金属は酸化されないと共に、良質なガ
ラス類は溶融せず、いずれも回収が可能となってリサイ
クルでき、燃焼灰の減少にも役立つこととなる。In addition, waste is not directly burned, but pyrolysis residues are generated by pyrolysis at a relatively low temperature. Therefore, valuable waste such as high-quality iron and aluminum contained in the waste is produced. The metal is not oxidized, and the high-quality glasses do not melt, and all of them can be collected and recycled, which also helps to reduce combustion ash.
【0020】[0020]
【発明の実施の形態】以下、本発明の実施の形態を図示
例と共に説明する。Embodiments of the present invention will be described below with reference to the drawings.
【0021】図1は本発明を実施する形態の第一の例で
あって、1はゴミ等の廃棄物、2は廃棄物1を破砕する
破砕機、3は破砕機2で破砕された破砕廃棄物を乾燥さ
せ水分除去する乾燥機、4は乾燥機3で水分除去された
乾燥廃棄物を熱分解する熱分解炉、5は熱分解炉4で熱
分解され生成された熱分解残渣からチャー(炭化物)を
選別する選別装置、7は熱分解炉4で熱分解され生成さ
れた熱分解ガスを燃料として燃焼させ発生した加熱ガス
を熱分解炉4へ導く熱風炉、8は熱風炉7から熱分解炉
4を経て乾燥機3へ導かれ、該乾燥機3で破砕廃棄物の
乾燥に使用された後の加熱ガスを処理するための排ガス
処理装置であり、廃棄物1を破砕機2で破砕し、乾燥機
3で乾燥させて水分除去し、熱分解炉4で熱分解させて
熱分解残渣を生成し、該熱分解残渣からチャーを選別装
置5で選別した後、該チャーを固形化装置22で所要形
状の固形物に固形化し、該固形化したチャーを移送手段
9で移送し、別設備で燃料として燃焼させるようにした
ものである。FIG. 1 shows a first embodiment of the present invention, wherein 1 is waste such as garbage, 2 is a crusher for crushing waste 1, and 3 is a crusher crushed by a crusher 2. A dryer 4 for drying and removing moisture from the waste, a pyrolysis furnace 4 for thermally decomposing the dried waste from which the moisture has been removed by the dryer 3, and a char 5 from the pyrolysis residue generated by pyrolysis in the pyrolysis furnace 4. A sorting device for sorting (carbide), 7 is a hot blast stove that guides the generated heating gas to the pyrolysis furnace 4 by burning the pyrolysis gas generated by pyrolysis in the pyrolysis furnace 4 as a fuel, and 8 is a hot blast stove 7 This is an exhaust gas treatment device for treating the heated gas that has been guided to the dryer 3 through the pyrolysis furnace 4 and has been used for drying the crushed waste by the dryer 3. Crushed, dried in dryer 3 to remove water, and pyrolyzed in pyrolysis furnace 4 to generate pyrolysis residue After the char is separated from the pyrolysis residue by the separating device 5, the char is solidified into a solid having a required shape by the solidifying device 22, and the solidified char is transferred by the transfer means 9, and the fuel is separated by another facility. It is made to burn as.
【0022】前記熱分解炉4としては、例えば、外筒4
aと内筒4bとを備えたロータリキルン等を用いること
ができ、内筒4b内に乾燥機3からの乾燥廃棄物を投入
すると共に、外筒4aと内筒4bとの間の空間内に熱風
炉7からの加熱ガスを導入することにより、空気を遮断
した状態で前記乾燥廃棄物を加熱ガスによって間接的に
およそ350〜500[℃]程度に加熱し熱分解させ、
熱分解残渣を生成するようにしてある。As the pyrolysis furnace 4, for example, an outer cylinder 4
a and a rotary kiln provided with an inner cylinder 4b can be used, and while the dry waste from the dryer 3 is charged into the inner cylinder 4b, the inside of the space between the outer cylinder 4a and the inner cylinder 4b is By introducing the heating gas from the hot blast stove 7, the dried waste is indirectly heated to about 350 to 500 [° C.] by the heating gas and thermally decomposed in a state where the air is shut off.
A pyrolysis residue is produced.
【0023】前記選別装置5としては、例えば、前記熱
分解炉4で生成された熱分解残渣をスクリーン(篩)に
かけ、缶等の金属類とそれ以外のものとに選別し、金属
類以外のものを風力選別機にかけ、比重の差を利用して
ガラス類とチャーとに選別する一方、前記金属類を磁選
機にかけ、鉄とアルミとに選別するようなものを用いる
ことができる。As the sorting device 5, for example, the pyrolysis residue generated in the pyrolysis furnace 4 is screened (sieved), and sorted into metals such as cans and others, and other than metals. A material which is subjected to a wind separator to separate the materials into glass and char by utilizing a difference in specific gravity and a material which is subjected to a magnetic separator to separate the metals into iron and aluminum can be used.
【0024】前記固形化装置22としては、例えば、チ
ャーを直径がおよそφ20〜30[mm]程度で、長さ
がおよそ50[mm]程度の円柱状の固形物に固形化す
る押出し造粒機等を用いることができる。The solidifying device 22 is, for example, an extrusion granulator that solidifies a char into a columnar solid having a diameter of about φ20 to 30 [mm] and a length of about 50 [mm]. Etc. can be used.
【0025】前記移送手段9としては、チャーを生成す
る設備と別設備との距離に応じて、例えば、固形物に固
形化したチャーを積載して輸送するトラックや列車、或
いは固形物に固形化したチャーを搬送するコンベヤ等を
用いることができる。The transfer means 9 may be, for example, a truck or a train for loading and transporting the solidified solid, or a solidified solid, depending on the distance between the facility for producing the char and another facility. A conveyor or the like that transports the prepared char can be used.
【0026】図1に示す第一の例の場合、別設備を発電
所とし、該発電所の微粉炭ミル10において、移送され
たチャーの固形物を石炭と一緒に微粉砕した後、微粉炭
焚ボイラ11で燃焼させるようにし、該微粉炭焚ボイラ
11で発生させた蒸気を蒸気タービン12へ導き、発電
機13を駆動して発電を行うようにしてある。In the case of the first example shown in FIG. 1, another facility is a power plant, and in a pulverized coal mill 10 of the power plant, the transferred char solids are pulverized together with coal, and then pulverized coal is removed. Combustion is carried out by the boiler 11, and the steam generated by the pulverized coal-fired boiler 11 is guided to a steam turbine 12, and a generator 13 is driven to generate power.
【0027】次に、上記図示例の作動を説明する。Next, the operation of the illustrated example will be described.
【0028】廃棄物1は破砕機2でおよそ150[m
m]以下に破砕され、該破砕機2で破砕された破砕廃棄
物は、乾燥機3で乾燥され、水分除去され、該乾燥機3
で水分除去された乾燥廃棄物は、熱分解炉4においてお
よそ350〜500[℃]程度の温度で熱分解され、熱
分解残渣と熱分解ガスとが生成される。The waste 1 is approximately 150 [m
m] or less, and the crushed waste crushed by the crusher 2 is dried by the dryer 3 to remove water, and the crushed waste is crushed by the dryer 3.
The dried waste from which the moisture has been removed is thermally decomposed in the pyrolysis furnace 4 at a temperature of about 350 to 500 [° C.] to generate a pyrolysis residue and a pyrolysis gas.
【0029】ここで、前記熱分解炉4において生成され
た熱分解ガスは、熱風炉7で燃焼され、該熱風炉7で燃
焼して発生した加熱ガスは、前記熱分解炉4の外筒4a
と内筒4bとの間の空間内を通って前記乾燥廃棄物の熱
分解のための間接加熱に利用された後、前記乾燥機3へ
導かれ、該乾燥機3において前記破砕廃棄物の水分除去
に利用され、該破砕廃棄物の水分除去に利用された後の
加熱ガスのうちの一部は、前記熱風炉7へ供給され、熱
分解ガスの燃焼に利用され、循環される一方、それ以外
の加熱ガスは前記乾燥機3から排ガス処理装置8へ送給
され、処理される。Here, the pyrolysis gas generated in the pyrolysis furnace 4 is burned in a hot blast furnace 7, and the heating gas generated by burning in the hot blast furnace 7 is supplied to an outer cylinder 4 a of the pyrolysis furnace 4.
After being used for indirect heating for the thermal decomposition of the dried waste through the space between the inner waste 4b and the inner cylinder 4b, it is guided to the dryer 3, where the moisture of the crushed waste is removed. A portion of the heated gas used for removal and used for removing moisture from the crushed waste is supplied to the hot blast stove 7 and used for combustion of the pyrolysis gas while being circulated. Heated gas other than the above is sent from the dryer 3 to the exhaust gas treatment device 8 and processed.
【0030】前記熱分解炉4において生成された熱分解
残渣は、選別装置5において、例えば、スクリーン
(篩)にかけられ、缶等の金属類とそれ以外のものとに
選別され、金属類以外のものが風力選別機にかけられ、
比重の差を利用してガラス類とチャー(粒径およそ1〜
数10[mm]程度)とに選別される一方、前記金属類
が磁選機にかけられ、鉄とアルミとに選別される。The pyrolysis residue generated in the pyrolysis furnace 4 is, for example, screened (sieved) in a separation device 5 to be separated into metals such as cans and other metals, and other than metals. Things are put on a wind sorter,
Using the difference in specific gravity, glass and char (particle size
(Several tens [mm]), while the metals are subjected to a magnetic separator to be separated into iron and aluminum.
【0031】前記選別装置5において選別されたチャー
は、固形化装置22で所要形状の固形物に固形化され、
該固形化されたチャーを積載して輸送するトラックや列
車、或いは固形化されたチャーを搬送するコンベヤ等の
移送手段9によって移送され、別設備としての発電所の
微粉炭ミル10において、移送されたチャーの固形物が
石炭と一緒に微粉砕された後、微粉炭焚ボイラ11で燃
焼され、該微粉炭焚ボイラ11で発生させた蒸気が蒸気
タービン12へ導かれ、発電機13が駆動されて発電が
行われる。The char sorted in the sorting device 5 is solidified into a solid having a required shape by a solidifying device 22.
The solidified char is transported by a transport means 9 such as a truck or a train for loading and transporting the solidified char, or a conveyor for transporting the solidified char, and is transferred in a pulverized coal mill 10 of a power plant as another facility. After the solid matter of the char is pulverized together with the coal, the char is burned in the pulverized coal-fired boiler 11, and the steam generated in the pulverized coal-fired boiler 11 is guided to the steam turbine 12, and the generator 13 is driven. Power is generated.
【0032】この結果、廃棄物1を熱分解により粒径お
よそ1〜数10[mm]程度の粉末状のチャーとし更に
所要形状の固形物に固形化して移送するため、粉末状の
ままの場合よりハンドリング性が更によくなると共に、
悪臭や腐敗が発生する心配もなく、発電所へ送り込むこ
とが可能となる。As a result, the waste 1 is made into a powdery char having a particle size of about 1 to several tens [mm] by pyrolysis and further solidified into a solid having a required shape. With better handling,
It can be sent to the power plant without fear of bad smell and rot.
【0033】又、廃棄物1の熱分解に必要なエネルギー
は、熱分解の過程で生成される熱分解ガスの燃焼によっ
て得ることができるため、外部からのエネルギー投入が
ほとんど必要なく、ゴミ固形燃料(RDF)を製造する
よりエネルギーが少なくて済み、且つコストも少なくて
済む。The energy required for the pyrolysis of the waste 1 can be obtained by burning the pyrolysis gas generated in the pyrolysis process. Less energy and less cost than manufacturing (RDF).
【0034】更に又、廃棄物1は、直接燃焼させるので
はなく、比較的温度の低い熱分解により熱分解残渣を生
成させるようにしているため、廃棄物1に含まれる良質
な鉄やアルミ等の有価金属は酸化されないと共に、良質
なガラス類は溶融せず、いずれも回収が可能となってリ
サイクルでき、燃焼灰の減少にも役立つこととなる。Further, since the waste 1 is not directly burned, but generates a pyrolysis residue by pyrolysis at a relatively low temperature, high quality iron, aluminum, etc. contained in the waste 1 can be obtained. The valuable metals are not oxidized, and good-quality glasses are not melted, all of which can be recovered and recycled, which also helps to reduce combustion ash.
【0035】こうして、ハンドリング性が非常に良好で
悪臭や腐敗の発生を防止しつつ、廃棄物1を燃料として
発電所へ送り込むことができ、且つゴミ固形燃料の製造
に比べ燃料化に必要なエネルギー並びにコストも少なく
でき、経済的にも有利となり、しかも、廃棄物1に含ま
れる良質な有価金属やガラス類を回収し得る。In this way, the waste 1 can be sent to the power plant as fuel while having very good handling properties and preventing the generation of bad smell and rot, and the energy required for fuel conversion as compared with the production of solid waste fuel In addition, the cost can be reduced, the economical advantage can be obtained, and high quality valuable metals and glasses contained in the waste 1 can be recovered.
【0036】図2は本発明を実施する形態の第二の例で
あって、図中、図1と同一の符号を付した部分は同一物
を表わしており、基本的な構成は図1に示すものと同様
であるが、本図示例の特徴とするところは、図2に示す
如く、別設備としての発電所に微粉炭ミル10とは別に
解砕装置14を設け、該解砕装置14において、移送さ
れたチャーの固形物を解砕した後、微粉炭焚ボイラ11
で燃焼させるようにした点にある。FIG. 2 shows a second embodiment of the present invention. In FIG. 2, the portions denoted by the same reference numerals as those in FIG. 1 represent the same components. As shown in FIG. 2, the feature of the illustrated example is that, as shown in FIG. 2, a power plant as a separate facility is provided with a crushing device 14 separately from the pulverized coal mill 10, and the crushing device 14 is provided. In the above, after pulverizing the solid matter of the transferred char, the pulverized coal-fired boiler 11
The point is that it is made to burn.
【0037】図2に示す第二の例においては、別設備と
しての発電所の解砕装置14において、図1に示す第一
の例と同様に移送されたチャーの固形物が解砕された
後、微粉炭と一緒に微粉炭焚ボイラ11で燃焼され、該
微粉炭焚ボイラ11で発生させた蒸気が蒸気タービン1
2へ導かれ、発電機13が駆動されて発電が行われる。In the second example shown in FIG. 2, the solid matter of the transferred char was crushed in the crusher 14 of the power plant as a separate facility in the same manner as in the first example shown in FIG. Thereafter, the steam is burned in the pulverized coal-fired boiler 11 together with the pulverized coal, and the steam generated in the pulverized coal-fired boiler 11 is supplied to the steam turbine 1.
2 and the generator 13 is driven to generate power.
【0038】こうして、図2に示す第二の例の場合にも
図1に示す第一の例の場合と同様に、ハンドリング性が
非常に良好で悪臭や腐敗の発生を防止しつつ、廃棄物1
を燃料として発電所へ送り込むことができ、且つゴミ固
形燃料の製造に比べ燃料化に必要なエネルギー並びにコ
ストも少なくでき、経済的にも有利となり、しかも、廃
棄物1に含まれる良質な有価金属やガラス類を回収し得
る。Thus, in the case of the second example shown in FIG. 2, as in the case of the first example shown in FIG. 1, the handleability is very good, and the generation of odors and decay is prevented. 1
Can be sent to a power plant as fuel, and the energy and cost required for fuel conversion can be reduced as compared with the production of solid waste fuel, which is economically advantageous, and the high-quality valuable metal contained in the waste 1 And glass can be recovered.
【0039】図3は本発明を実施する形態の第三の例で
あって、図中、図1と同一の符号を付した部分は同一物
を表わしており、基本的な構成は図1に示すものと同様
であるが、本図示例の特徴とするところは、図3に示す
如く、別設備としての発電所の流動床ボイラ15におい
て、移送されたチャーの固形物を燃焼させるようにした
点にある。FIG. 3 shows a third embodiment of the present invention. In FIG. 3, the portions denoted by the same reference numerals as those in FIG. 1 represent the same components, and the basic configuration is shown in FIG. It is the same as that shown, but the feature of this illustrated example is that, as shown in FIG. 3, solid matter of the transferred char is burned in a fluidized bed boiler 15 of a power plant as a separate facility. On the point.
【0040】図3に示す第三の例においては、別設備と
して発電所の流動床ボイラ15において、石炭やその他
の燃料と一緒に、図1に示す第一の例と同様に移送され
たチャーの固形物が燃焼され、該流動床ボイラ15で発
生させた蒸気が蒸気タービン12へ導かれ、発電機13
が駆動されて発電が行われる。In the third example shown in FIG. 3, as a separate facility, in a fluidized bed boiler 15 of a power plant, a char transferred together with coal and other fuels in the same manner as in the first example shown in FIG. Solid matter is burned, and the steam generated in the fluidized bed boiler 15 is guided to the steam turbine 12,
Is driven to generate power.
【0041】こうして、図3に示す第三の例の場合にも
図1に示す第一の例の場合と同様に、ハンドリング性が
非常に良好で悪臭や腐敗の発生を防止しつつ、廃棄物1
を燃料として発電所へ送り込むことができ、且つゴミ固
形燃料の製造に比べ燃料化に必要なエネルギー並びにコ
ストも少なくでき、経済的にも有利となり、しかも、廃
棄物1に含まれる良質な有価金属やガラス類を回収し得
る。Thus, in the case of the third example shown in FIG. 3, as in the case of the first example shown in FIG. 1, the handleability is very good, and the generation of odors and decay is prevented. 1
Can be sent to a power plant as fuel, and the energy and cost required for fuel conversion can be reduced as compared with the production of solid waste fuel, which is economically advantageous, and the high-quality valuable metal contained in the waste 1 And glass can be recovered.
【0042】図4は本発明を実施する形態の第四の例で
あって、図中、図1と同一の符号を付した部分は同一物
を表わしており、基本的な構成は図1に示すものと同様
であるが、本図示例の特徴とするところは、図4に示す
如く、別設備としての発電所に、石炭、石油、ガス、或
いはその他の燃料を燃やす主ボイラ16とは別にチャー
の固形物の専焼ボイラ17を設け、該専焼ボイラ17に
おいて、移送されたチャーの固形物を燃焼させて蒸気を
発生させ、該蒸気を主ボイラ16で発生させた蒸気と一
緒に蒸気タービン12へ導くようにした点にある。FIG. 4 shows a fourth embodiment of the present invention. In FIG. 4, the portions denoted by the same reference numerals as those in FIG. 1 represent the same components, and the basic configuration is shown in FIG. It is the same as that shown, but the feature of this illustrated example is that, as shown in FIG. 4, a power plant as a separate facility is provided separately from a main boiler 16 that burns coal, oil, gas, or other fuel. A dedicated boiler 17 for char solids is provided. In the dedicated boiler 17, the transferred solids of the char are burned to generate steam, and the steam is generated together with the steam generated by the main boiler 16 in the steam turbine 12. The point is to lead to.
【0043】図4に示す第四の例においては、別設備と
しての発電所の専焼ボイラ17において、図1に示す第
一の例と同様に移送されたチャーの固形物が燃焼されて
蒸気が発生され、該蒸気が主ボイラ16で発生させた蒸
気と一緒に蒸気タービン12へ導かれ、発電機13が駆
動されて発電が行われる。In the fourth example shown in FIG. 4, in the monofiring boiler 17 of the power plant as a separate facility, the solid matter of the transferred char is burned in the same manner as in the first example shown in FIG. The generated steam is guided to the steam turbine 12 together with the steam generated by the main boiler 16, and the generator 13 is driven to generate power.
【0044】こうして、図4に示す第四の例の場合にも
図1に示す第一の例の場合と同様に、ハンドリング性が
非常に良好で悪臭や腐敗の発生を防止しつつ、廃棄物1
を燃料として発電所へ送り込むことができ、且つゴミ固
形燃料の製造に比べ燃料化に必要なエネルギー並びにコ
ストも少なくでき、経済的にも有利となり、しかも、廃
棄物1に含まれる良質な有価金属やガラス類を回収し
得、更に、廃棄物の灰と石炭灰を分別することが可能と
なる。Thus, in the case of the fourth example shown in FIG. 4, as in the case of the first example shown in FIG. 1, the handleability is very good, and the generation of odors and decay is prevented. 1
Can be sent to the power plant as fuel, and the energy and cost required for fuel conversion can be reduced as compared with the production of solid waste fuel, which is economically advantageous, and the high quality valuable metal contained in the waste 1 And ash can be recovered, and furthermore, waste ash and coal ash can be separated.
【0045】図5は本発明を実施する形態の第五の例で
あって、図中、図1と同一の符号を付した部分は同一物
を表わしており、基本的な構成は図1に示すものと同様
であるが、本図示例の特徴とするところは、図5に示す
如く、別設備としての発電所に、石炭、石油、ガス、或
いはその他の燃料を燃やすボイラ18とは別にチャーの
固形物のガス化炉19を設け、該ガス化炉19におい
て、移送されたチャーの固形物をガス化し、該ガス化ガ
スをボイラ18で燃焼させるようにした点にある。FIG. 5 shows a fifth embodiment of the present invention. In FIG. 5, the portions denoted by the same reference numerals as those in FIG. 1 represent the same components, and the basic configuration is shown in FIG. As shown in FIG. 5, the present embodiment is characterized in that, as shown in FIG. 5, a power plant as a separate facility is provided with a charcoal separately from a boiler 18 which burns coal, oil, gas or other fuel. The solidification gasification furnace 19 is provided, and in the gasification furnace 19, the transferred solid matter of the char is gasified, and the gasified gas is burned by the boiler 18.
【0046】図5に示す第五の例においては、別設備と
しての発電所のガス化炉19において、図1に示す第一
の例と同様に移送されたチャーの固形物がガス化され、
該ガス化ガスが、石炭、石油、ガス、或いはその他の燃
料と一緒にボイラ18で燃焼され、該ボイラ18で発生
させた蒸気が蒸気タービン12へ導かれ、発電機13が
駆動されて発電が行われる。In the fifth example shown in FIG. 5, in the gasifier 19 of the power plant as a separate facility, the solid matter of the transferred char is gasified in the same manner as in the first example shown in FIG.
The gasified gas is burned in a boiler 18 together with coal, petroleum, gas or other fuel, and the steam generated in the boiler 18 is guided to a steam turbine 12, and a generator 13 is driven to generate power. Done.
【0047】こうして、図5に示す第五の例の場合にも
図1に示す第一の例の場合と同様に、ハンドリング性が
非常に良好で悪臭や腐敗の発生を防止しつつ、廃棄物1
を燃料として発電所へ送り込むことができ、且つゴミ固
形燃料の製造に比べ燃料化に必要なエネルギー並びにコ
ストも少なくでき、経済的にも有利となり、しかも、廃
棄物1に含まれる良質な有価金属やガラス類を回収し
得、更に、廃棄物の灰と石炭灰を分別することが可能と
なる。Thus, in the case of the fifth example shown in FIG. 5, as in the case of the first example shown in FIG. 1, the handleability is extremely good, and the generation of waste and odors is prevented. 1
Can be sent to the power plant as fuel, and the energy and cost required for fuel conversion can be reduced as compared with the production of solid waste fuel, which is economically advantageous, and the high quality valuable metal contained in the waste 1 And ash can be recovered, and furthermore, waste ash and coal ash can be separated.
【0048】図6は本発明を実施する形態の第六の例で
あって、図中、図1と同一の符号を付した部分は同一物
を表わしており、基本的な構成は図1に示すものと同様
であるが、本図示例の特徴とするところは、図6に示す
如く、別設備をセメント工場とし、該セメント工場のセ
メントキルン20において、移送されたチャーの固形物
を燃焼させるようにした点にある。FIG. 6 shows a sixth embodiment of the present invention. In FIG. 6, the portions denoted by the same reference numerals as those in FIG. 1 represent the same components, and the basic configuration is shown in FIG. As shown in FIG. 6, the present embodiment is characterized in that, as shown in FIG. 6, a separate facility is a cement factory, and the cement kiln 20 of the cement factory burns the solids of the transferred char. That's the point.
【0049】図6に示す第六の例においては、別設備と
してのセメント工場のセメントキルン20において、図
1に示す第一の例と同様に移送されたチャーの固形物が
燃焼され、原料であるセメントの焼成が行われ、製品と
してのセメントが生成される。In the sixth example shown in FIG. 6, in a cement kiln 20 of a cement plant as a separate facility, solids transferred from the transferred char are burned in the same manner as in the first example shown in FIG. A certain cement is fired to produce cement as a product.
【0050】こうして、図6に示す第六の例の場合に
は、ハンドリング性が非常に良好で悪臭や腐敗の発生を
防止しつつ、廃棄物1を燃料としてセメント工場へ送り
込むことができ、且つゴミ固形燃料の製造に比べ燃料化
に必要なエネルギー並びにコストも少なくでき、経済的
にも有利となり、しかも、廃棄物1に含まれる良質な有
価金属やガラス類を回収し得る。Thus, in the case of the sixth example shown in FIG. 6, the waste 1 can be sent to the cement plant as fuel while having very good handling properties and preventing the generation of offensive odor and decay. Energy and cost required for fuel conversion can be reduced as compared with the production of solid waste fuel, which is economically advantageous, and high quality valuable metals and glasses contained in the waste 1 can be recovered.
【0051】図7は本発明を実施する形態の第七の例で
あって、図中、図1と同一の符号を付した部分は同一物
を表わしており、基本的な構成は図1に示すものと同様
であるが、本図示例の特徴とするところは、図7に示す
如く、別設備を製鉄所とし、該製鉄所の高炉21におい
て、移送されたチャーの固形物を燃焼させるようにした
点にある。FIG. 7 shows a seventh embodiment of the present invention. In FIG. 7, the parts denoted by the same reference numerals as those in FIG. 1 represent the same parts, and the basic structure is shown in FIG. As shown in FIG. 7, the present embodiment is characterized in that, as shown in FIG. 7, a separate facility is a steelworks, and the transferred char is burned in a blast furnace 21 of the steelworks. It is in the point which was made.
【0052】図7に示す第七の例においては、別設備と
しての製鉄所の高炉21において、図1に示す第一の例
と同様に移送されたチャーの固形物が燃焼され、原料で
ある鉄鉱石等の溶融が行われ、製品としての鉄が製造さ
れる。In the seventh example shown in FIG. 7, in the blast furnace 21 of the steel mill as another facility, the solid matter of the transferred char is burned and used as a raw material in the same manner as in the first example shown in FIG. Melting of iron ore is performed to produce iron as a product.
【0053】こうして、図7に示す第七の例の場合に
は、ハンドリング性が非常に良好で悪臭や腐敗の発生を
防止しつつ、廃棄物1を燃料として製鉄所へ送り込むこ
とができ、且つゴミ固形燃料の製造に比べ燃料化に必要
なエネルギー並びにコストも少なくでき、経済的にも有
利となり、しかも、廃棄物1に含まれる良質な有価金属
やガラス類を回収し得る。Thus, in the case of the seventh example shown in FIG. 7, the waste 1 can be sent to the steelworks as a fuel while having very good handling properties and preventing the generation of offensive odors and putrefaction. Energy and cost required for fuel conversion can be reduced as compared with the production of solid waste fuel, which is economically advantageous, and high quality valuable metals and glasses contained in the waste 1 can be recovered.
【0054】尚、本発明の廃棄物の燃料利用方法は、上
述の図示例にのみ限定されるものではなく、廃棄物が水
分を含んでいないものである場合には、乾燥機による水
分除去は省略できること等、その他、本発明の要旨を逸
脱しない範囲内において種々変更を加え得ることは勿論
である。The method of using fuel for waste according to the present invention is not limited to the above-described example, and if the waste does not contain moisture, the removal of moisture by a dryer is not required. It goes without saying that various changes can be made without departing from the spirit of the present invention, such as omission.
【0055】[0055]
【発明の効果】以上、説明したように本発明の廃棄物の
燃料利用方法によれば、ハンドリング性が非常に良好で
悪臭や腐敗の発生を防止しつつ、廃棄物を燃料として発
電所やセメント工場或いは製鉄所等へ送り込むことがで
き、且つゴミ固形燃料の製造に比べ燃料化に必要なエネ
ルギー並びにコストも少なくでき、経済的にも有利とな
り、しかも、廃棄物に含まれる良質な有価金属やガラス
類を回収し得るという優れた効果を奏し得る。As described above, according to the method of using waste fuel according to the present invention, the handling efficiency is very good and the generation of bad odors and decay is prevented, while the waste is used as fuel for power plants and cement. It can be sent to factories or steelworks, etc., and the energy and cost required for fuel conversion can be reduced compared to the production of solid waste fuel, which is economically advantageous. An excellent effect that glass can be recovered can be obtained.
【図1】本発明を実施する形態の第一の例の全体概要構
成図である。FIG. 1 is an overall schematic configuration diagram of a first example of an embodiment of the present invention.
【図2】本発明を実施する形態の第二の例の全体概要構
成図である。FIG. 2 is an overall schematic configuration diagram of a second example of an embodiment of the present invention.
【図3】本発明を実施する形態の第三の例の全体概要構
成図である。FIG. 3 is an overall schematic configuration diagram of a third example of an embodiment of the present invention.
【図4】本発明を実施する形態の第四の例の全体概要構
成図である。FIG. 4 is an overall schematic configuration diagram of a fourth embodiment of the present invention.
【図5】本発明を実施する形態の第五の例の全体概要構
成図である。FIG. 5 is an overall schematic configuration diagram of a fifth example of an embodiment of the present invention.
【図6】本発明を実施する形態の第六の例の全体概要構
成図である。FIG. 6 is an overall schematic configuration diagram of a sixth example of an embodiment of the present invention.
【図7】本発明を実施する形態の第七の例の全体概要構
成図である。FIG. 7 is an overall schematic configuration diagram of a seventh embodiment of the present invention.
1 廃棄物 2 破砕機 3 乾燥機 4 熱分解炉 4a 外筒 4b 内筒 5 選別装置 7 熱風炉 8 排ガス処理装置 9 移送手段 10 微粉炭ミル 11 微粉炭焚ボイラ 12 蒸気タービン 13 発電機 14 解砕装置 15 流動床ボイラ 16 主ボイラ 17 専焼ボイラ 18 ボイラ 19 ガス化炉 20 セメントキルン 21 高炉 22 固形化装置 DESCRIPTION OF SYMBOLS 1 Waste 2 Crusher 3 Dryer 4 Pyrolysis furnace 4a Outer cylinder 4b Inner cylinder 5 Sorting device 7 Hot blast furnace 8 Exhaust gas treatment device 9 Transfer means 10 Pulverized coal mill 11 Pulverized coal fired boiler 12 Steam turbine 13 Generator 14 Crushing Apparatus 15 Fluidized bed boiler 16 Main boiler 17 Fired boiler 18 Boiler 19 Gasifier 20 Cement kiln 21 Blast furnace 22 Solidification device
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C21B 5/00 319 F23G 5/027 ZABZ 4K012 F23G 5/027 ZAB B09B 3/00 302E (72)発明者 中村 元哉 東京都江東区豊洲三丁目2番16号 石川島 播磨重工業株式会社豊洲総合事務所内 Fターム(参考) 3K046 AA02 AA11 AA20 CA02 FA00 FA06 3K061 AA07 AA11 AA24 AB01 AB02 AC01 BA01 EA01 FA10 4D004 AA03 AA46 BA03 CA04 CA08 CA09 CA24 CA26 CA42 CA45 4H012 HA03 4H015 AA01 AB01 BA06 BA13 BB03 BB06 CA03 CB01 4K012 BE01 BE05 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C21B 5/00 319 F23G 5/027 ZABZ 4K012 F23G 5/027 ZAB B09B 3/00 302E (72) Inventor Nakamura Motoya 3-2-16 Toyosu, Koto-ku, Tokyo Ishikawajima Harima Heavy Industries, Ltd. Toyosu General Office F-term (reference) 3K046 AA02 AA11 AA20 CA02 FA00 FA06 3K061 AA07 AA11 AA24 AB01 AB02 AC01 BA01 EA01 FA10 4D004 AA03 AA46 BA09 CA08 CA24 CA26 CA42 CA45 4H012 HA03 4H015 AA01 AB01 BA06 BA13 BB03 BB06 CA03 CB01 4K012 BE01 BE05
Claims (8)
渣を生成し、該熱分解残渣からチャーを選別した後、該
チャーを所要形状の固形物に固形化し、該固形化したチ
ャーを移送し、別設備で燃料として燃焼させることを特
徴とする廃棄物の燃料利用方法。Claims 1. A waste is crushed and pyrolyzed to generate a pyrolysis residue, a char is selected from the pyrolysis residue, the char is solidified into a solid having a required shape, and the solidified char is formed. A method for utilizing waste fuel, comprising transporting fuel and burning it as fuel in another facility.
ミルにおいて、移送されたチャーを石炭と一緒に微粉砕
した後、微粉炭焚ボイラで燃焼させるようにした請求項
1記載の廃棄物の燃料利用方法。2. The pulverized coal mill of the power plant, wherein the transferred char is pulverized together with coal and then burned in a pulverized coal-fired boiler. How to use fuel for waste.
置において、移送されたチャーを解砕した後、微粉炭焚
ボイラで燃焼させるようにした請求項1記載の廃棄物の
燃料利用方法。3. The waste fuel according to claim 1, wherein a separate facility is a power plant, and the transferred char is crushed in a crushing device of the power plant and then burnt in a pulverized coal-fired boiler. How to Use.
ボイラにおいて、移送されたチャーを燃焼させるように
した請求項1記載の廃棄物の燃料利用方法。4. The method according to claim 1, wherein a separate facility is a power station, and the transferred char is burned in a fluidized-bed boiler of the power station.
イラにおいて、移送されたチャーを燃焼させて蒸気を発
生させ、該蒸気を主ボイラで発生させた蒸気と一緒に蒸
気タービンへ導くようにした請求項1記載の廃棄物の燃
料利用方法。5. A separate facility is defined as a power plant, and in a dedicated boiler of the power plant, the transferred char is burned to generate steam, and the steam is guided to a steam turbine together with the steam generated by the main boiler. The method for utilizing waste fuel according to claim 1.
炉において、移送されたチャーをガス化し、該ガス化ガ
スをボイラで燃焼させるようにした請求項1記載の廃棄
物の燃料利用方法。6. The waste fuel according to claim 1, wherein the separate facility is a power plant, and the transferred char is gasified in a gasifier of the power plant, and the gasified gas is burned by a boiler. How to Use.
工場のセメントキルンにおいて、移送されたチャーを燃
焼させるようにした請求項1記載の廃棄物の燃料利用方
法。7. The method according to claim 1, wherein a separate facility is a cement plant, and the transferred char is burned in a cement kiln of the cement plant.
おいて、移送されたチャーを燃焼させるようにした請求
項1記載の廃棄物の燃料利用方法。8. The method according to claim 1, wherein a separate facility is a steelworks, and the transferred char is burned in a blast furnace of the steelworks.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9166799A JP2000283404A (en) | 1999-03-31 | 1999-03-31 | How to use waste fuel |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9166799A JP2000283404A (en) | 1999-03-31 | 1999-03-31 | How to use waste fuel |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JP2000283404A true JP2000283404A (en) | 2000-10-13 |
Family
ID=14032844
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9166799A Pending JP2000283404A (en) | 1999-03-31 | 1999-03-31 | How to use waste fuel |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2000283404A (en) |
Cited By (15)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002138285A (en) * | 2000-11-06 | 2002-05-14 | Shin Nihonkai Jukogyo Kk | Animal dung carbonization equipment |
| KR20030084339A (en) * | 2002-04-26 | 2003-11-01 | 김진택 | A macromolecule waste system |
| JP2007091893A (en) * | 2005-09-29 | 2007-04-12 | Ube Machinery Corporation Ltd | Woody biomass fuel supply system |
| JP2007091892A (en) * | 2005-09-29 | 2007-04-12 | Ube Machinery Corporation Ltd | Manufacturing system of boiler fuel from ligneous biomass |
| JP2007145968A (en) * | 2005-11-28 | 2007-06-14 | Kohei Matsushita | Waste utilization system |
| JP2007169484A (en) * | 2005-12-22 | 2007-07-05 | Saitama Univ | Biomass-coal fusion fine powder fuel, combustible gas, and method for producing combustible gas and char from coal powder and / or waste carbide, and plant polymer organic powder |
| JP2007169398A (en) * | 2005-12-20 | 2007-07-05 | Shigenka System Kk | Solidified fuel, system for manufacturing solidified fuel and method for manufacturing solidified fuel |
| JP2009019156A (en) * | 2007-07-13 | 2009-01-29 | Victory:Kk | Carbonization-processing method |
| JP2010107165A (en) * | 2008-10-31 | 2010-05-13 | Miike Iron Works Co Ltd | Biomass fuel burner |
| JP2011068824A (en) * | 2009-09-28 | 2011-04-07 | Maywa Co Ltd | Carbonization facility for organic water-containing waste |
| JP2013209526A (en) * | 2012-03-30 | 2013-10-10 | Ihi Corp | Apparatus and method for producing fuel |
| JP2013539813A (en) * | 2010-10-11 | 2013-10-28 | コルトゥス アーベー | Method and equipment for producing coke during indirect heating gasification |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002138285A (en) * | 2000-11-06 | 2002-05-14 | Shin Nihonkai Jukogyo Kk | Animal dung carbonization equipment |
| KR20030084339A (en) * | 2002-04-26 | 2003-11-01 | 김진택 | A macromolecule waste system |
| JP2007091893A (en) * | 2005-09-29 | 2007-04-12 | Ube Machinery Corporation Ltd | Woody biomass fuel supply system |
| JP2007091892A (en) * | 2005-09-29 | 2007-04-12 | Ube Machinery Corporation Ltd | Manufacturing system of boiler fuel from ligneous biomass |
| JP2007145968A (en) * | 2005-11-28 | 2007-06-14 | Kohei Matsushita | Waste utilization system |
| JP2007169398A (en) * | 2005-12-20 | 2007-07-05 | Shigenka System Kk | Solidified fuel, system for manufacturing solidified fuel and method for manufacturing solidified fuel |
| JP2007169484A (en) * | 2005-12-22 | 2007-07-05 | Saitama Univ | Biomass-coal fusion fine powder fuel, combustible gas, and method for producing combustible gas and char from coal powder and / or waste carbide, and plant polymer organic powder |
| JP2009019156A (en) * | 2007-07-13 | 2009-01-29 | Victory:Kk | Carbonization-processing method |
| JP2010107165A (en) * | 2008-10-31 | 2010-05-13 | Miike Iron Works Co Ltd | Biomass fuel burner |
| JP2011068824A (en) * | 2009-09-28 | 2011-04-07 | Maywa Co Ltd | Carbonization facility for organic water-containing waste |
| JP2013539813A (en) * | 2010-10-11 | 2013-10-28 | コルトゥス アーベー | Method and equipment for producing coke during indirect heating gasification |
| JP2013209526A (en) * | 2012-03-30 | 2013-10-10 | Ihi Corp | Apparatus and method for producing fuel |
| CN108580511A (en) * | 2018-04-04 | 2018-09-28 | 杭州瑞赛可环境工程有限公司 | It is a kind of to utilize ultrasound-enhanced organic waste pyrolytic gasification equipment |
| CN110425540A (en) * | 2019-08-30 | 2019-11-08 | 西安西热锅炉环保工程有限公司 | A kind of pulverized-coal fired boiler mixes the system and method for burning rubbish |
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