JP4014524B2 - Method for continuous carbonization of waste and its continuous carbonization processing equipment - Google Patents

Method for continuous carbonization of waste and its continuous carbonization processing equipment Download PDF

Info

Publication number
JP4014524B2
JP4014524B2 JP2003068597A JP2003068597A JP4014524B2 JP 4014524 B2 JP4014524 B2 JP 4014524B2 JP 2003068597 A JP2003068597 A JP 2003068597A JP 2003068597 A JP2003068597 A JP 2003068597A JP 4014524 B2 JP4014524 B2 JP 4014524B2
Authority
JP
Japan
Prior art keywords
furnace
waste
carbonization
carbide
melting furnace
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.)
Expired - Fee Related
Application number
JP2003068597A
Other languages
Japanese (ja)
Other versions
JP2004277503A (en
Inventor
豊和 田中
恒夫 小畑
和彦 肥塚
多喜男 住谷
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.)
Kurimoto Ltd
Original Assignee
Kurimoto 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 Kurimoto Ltd filed Critical Kurimoto Ltd
Priority to JP2003068597A priority Critical patent/JP4014524B2/en
Publication of JP2004277503A publication Critical patent/JP2004277503A/en
Application granted granted Critical
Publication of JP4014524B2 publication Critical patent/JP4014524B2/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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/143Feedstock the feedstock being recycled material, e.g. plastics
    • 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

Description

【0001】
【発明の属する技術分野】
この発明は、ごみなどの一般廃棄物並びに廃プラスチックなどの産業廃棄物を連続的に炭化処理する方法及びその設備に関する。
【0002】
【従来の技術】
ごみなどの一般廃棄物並びに廃プラスチックなどの産業廃棄物の処理については、近年ダイオキシン類などの環境汚染対策が重要視され、廃棄物を焼却処理せずに加熱によりガス化して乾留ガスと熱分解残渣とに分離する方法がある。
廃棄物のガス化の際には、外熱式ロータリーキルンや流動式又はシャフト式の処理炉が用いられる。
廃棄物を外熱式ロータリーキルンによって処理する場合、加熱によって生成される乾留ガスは、後工程である溶融炉や溶融炉排ガスの二次燃焼室の燃料として使用することができ、効率がよい。
熱分解残渣である炭化物を、金属などの再利用が可能なものを選別除去して粒度調整した後、溶融炉で高温燃焼処理することによって、該炭化物はさらに減容され溶融スラグとなり、またダイオキシン類の発生も低減できる。
しかし、上記設備の溶融炉はその内部が高温であるため消耗が激しく、したがって、定期補修が必要で、年間に数週間の運転停止を余儀なくされる。この間の休止に伴い、日々発生する廃棄物が溜まってしまうため、この期間にも廃棄物の処理を連続して行なうことが望まれている。そこで、溶融炉を複数系統備える方法もあるが、設備費のアップに繋がることになる。
【0003】
上記の要望に応えるために、都市ごみ及び/又は産業廃棄物などの各種廃棄物に含まれる可燃ごみを、砂などの流動媒体を用いて熱分解ガス化する流動床ガス化炉と前記可燃物を熱分解ガス化して得られた固形分を溶融する溶融炉と上記溶融炉で得られる熱ガスを用いて熱回収する熱回収装置と上記装置から排出する排ガスを浄化処理する排ガス浄化装置とからなる流動床式ガス化溶融装置において、前記固形物を含む可燃ごみを、流動媒体を用いて上記流動床式ガス化炉内で熱分解ガス化して生成する熱分解ガスを熱分解ガス燃焼炉で燃焼させ、その得られる燃焼ガスを用いて独立過熱器(又は独立空気予熱器)で熱交換した後、熱交換後の燃焼ガスを流動床ガス化炉の流動媒体の流動化流体として用いることにより、上記流動床ガス化炉を上記溶融炉および熱回収装置から切り離した状態で運転する。すなわち、上記流動床ガス化炉に後続の溶融炉をメンテナンスのためまたは不具合などで運転を停止する場合でも前記流動床ガス化炉を単独に運転継続するものが提案されている(例えば、特許文献1参照)。
【0004】
【特許文献1】
特開昭11−118124号公報(第9頁、図2)
【0005】
【発明が解決しようとする課題】
しかしながら、特許文献1に記載の従来技術は、上記溶融炉と熱回収装置を含む系統とは別に熱分解ガスの熱分解ガス燃焼炉、その得られる燃焼ガスを用いて熱交換用媒体を熱交換する独立過熱器(又は独立空気加熱器)を用い、熱交換後の燃焼ガスを流動床ガス化炉の流動媒体の流動化流体として用いる系統を採用したものであるため、実質的には一系統とは言えないことから構造が複雑である。また、熱交換後の燃焼ガスを流動化流体として直接流動床ガス化炉に供給する方式であるため、上記燃焼ガスの酸素濃度が低くて可燃ごみの部分燃焼が低減し、上記流動媒体の温度維持が難しく、したがって流動床ガス化炉の熱分解ガス化の安定性に欠けるという問題がある。
【0006】
そこで、この発明は外熱式回転型炭化炉とこれに後続する溶融炉との組み合わせからなり、比較的簡単な構造にも係わらず溶融炉が運転停止しても上記炭化炉の継続運転が可能であり、しかも安定した運転を図ることを課題とする。
【0007】
【課題を解決するための手段】
上記の課題を解決するために、この発明は、ごみなどの一般廃棄物ならびに廃プラスチックなどの産業廃棄物を低酸素雰囲気下の外熱式回転型炭化炉で加熱炭化し、その炭化による炭化物をストックタンクに貯溜し、上記ストックタンクの炭化物と上記炭化による可燃性ガスを溶融炉に供給して燃焼・溶融し、その燃焼ガスを二次燃焼室、熱交換器および排ガス処理装置で処理し、上記熱交換器の加熱空気を上記外熱式回転型炭化炉に供給するようにした廃棄物の連続炭化処理方法において、上記溶融炉を補修停止した際、上記外熱式回転型炭化炉の可燃性ガスは上記二次燃焼室に送られて燃焼処理され、その燃焼ガスにより上記熱交換器で熱交換され、熱交換された加熱空気により上記外熱式回転型炭化炉の熱源が担保されるクローズ回路が形成される。この回路は比較的構造が簡単であり、安定した運転を図ることができる。
【0008】
さらに、上記溶融炉の補修停止に伴う上記外熱式回転型炭化炉からの炭化物を上記ストックタンクに貯溜するようにした構成の採用により、上記ストックタンクは大幅に減容化した炭化物であることとあいまって、ごみピットの収容スペースに比べて大幅に小形化されて省スペース化となる。
また、上記溶融炉の補修停止に伴う上記外熱式回転型炭化炉からの炭化物を洗浄・脱水するようにした構成の採用により、炭化物は無害な炭化燃料となる。
【0009】
ごみなどの一般廃棄物ならびに廃プラスチックなどの産業廃棄物を低酸素雰囲気下で加熱して炭化する外熱式回転型炭化炉と、上記炭化による可燃性ガスを燃焼・溶融する溶融炉と、上記溶融炉の燃焼ガスを処理する二次燃焼室、熱交換器および排ガス処理装置と、上記炭化による炭化物を貯溜するストックタンクと、上記ストックタンクの炭化物を上記溶融炉に供給する搬送手段と、上記熱交換器の加熱空気を上記炭化炉に供給する導管と、上記外熱式回転型炭化炉を運転しつつ上記溶融炉を停止した際の上記外熱式回転型炭化炉の可燃性ガスを上記二次燃焼室に供給する導管と、からなるものである。これにより、溶融炉を補修などのため停止した場合でも、別系列の独立過熱器(又は独立空気予熱器)を設けることなく、上記二次燃焼室および熱交換器の稼働により上記外熱式回転型炭化炉の運転ができるから、コンパクトとなる。
また、上記溶融炉の補修停止に伴う上記外熱式回転型炭化炉からの炭化物を貯溜する大きさの上記ストックタンクの構成を採用することができる。
また、上記溶融炉の補修停止に伴う上記外熱式回転型炭化炉からの炭化物を洗浄・脱水する洗浄・脱水機の構成を採用することができる。
【0010】
【発明の実施の形態】
本発明の実施の形態を図面とともに説明する。図1は本発明の実施の形態に係る廃棄物の連続炭化処理設備の概略フローを示し、このフローにおいて、一般廃棄物並びに廃プラスチックなどの産業廃棄物をピット(図示省略)からクレーンなどにより破砕機1に投入して10〜15cm程度に破砕し、次いで前処理装置2である乾燥機に投入して乾燥した後、定量供給機3aを介して外熱式回転型炭化炉3に投入する。外熱式回転型炭化炉3に投入された廃棄物中の可燃物は、低酸素状態、すなわち外気が遮断された空燃比が約0.3程度の略無酸素雰囲気下で400〜500℃程度の外部加熱により、部分燃焼とともに熱分解して炭化される。この熱分解により可燃性ガスと炭化物とが生成され、可燃性ガスはダストとともに導管aを経て溶融炉4に送られる。
一方、外熱式回転型炭化炉3の炭化物、金属や不燃物などの固形物は排出装置3bにより排出され、次いで、例えば水冷手段により約250℃に冷却された後、分別装置10によって金属などの資源化物や不燃物と炭化物とに分別される。分別された炭化物は一旦ストックタンク11に貯溜された後、ストックタンク11下部の定量切り出し装置(図示省略)により定量切り出しされ、ベルトコンベアなどの搬送手段12により溶融炉4に供給される。
【0011】
溶融炉4に供給された炭化物と別途供給された可燃性ガスおよび必要に応じて供給される補助燃料は燃焼し、高熱量の炭化物の燃焼により高温(約1250〜1450℃)となり、この高温下で、燃焼に伴って発生する灰分が溶融してスラグ化し、溶融スラグは水冷式タンク(図示省略)で水冷し、水砕スラグとして回収される。
上記溶融炉4の燃焼ガスは、導管bから二次燃焼室5に入り、導管cを経て減温塔6に導かれて所定の温度に降下され、次いで導管dを経て熱交換器7に導かれて空気の熱交換に利用された後、導管eから排ガス処理装置(バグフィルタ)8に導かれて浄化処理され、清浄化された排ガスは導管fを経て排気筒9から大気中に放出される。
前記熱交換器7で熱交換された加熱空気(熱風)は、導管gを経て外熱式回転型炭化炉3に供給され炭化用熱源として使用される。
また、溶融炉4を補修停止した際、炭化炉3からの可燃性ガスを導管aから分岐して導管bを経て二次燃焼室5に供給して燃焼処理し、その燃焼ガスにより熱交換器7で熱交換した加熱空気を、導管gを経て外熱式回転型炭化炉3に供給することより、溶融炉4を補修停止した場合でも外熱式回転型炭化炉3の連続運転が可能となる。
前記加熱空気は、その一部を導管gから分岐して溶融炉4にも供給して燃焼ガス温度上昇用の熱源としても使用し得る。さにに、加熱空気(熱風)は給湯・冷暖房用の熱源にも利用できる。
【0012】
また、前記燃焼ガスの一部を導管bから分岐した導管hを経て乾燥機2に供給し、廃棄物を所定の含水率に乾燥する熱源として利用し、乾燥機2の乾燥排ガスを導管jを経て溶融炉4に投入する。燃焼ガスを乾燥機2の熱源とすることにより、熱エネルギーの有効利用およびランニングコストの低減になる。
【0013】
また、可燃性ガスの溶融炉4での燃焼に当り、外熱式回転型炭化炉3で発生する可燃性ガスの量や性状が一定しない場合でも、高発熱量の炭化物を溶融炉4に供給して燃焼させるため、安定した高温燃焼が可能となる。これにより、燃焼ガスの温度、ひいては熱交換器7による加熱空気の温度も一定し、外熱式回転型炭化炉3の加熱温度の制御が極めて安定する。
【0014】
外熱式回転型炭化炉3として外熱式のロータリーキルンを用いることにより、可燃物をロータリーキルンの外部からの間接加熱と該キルン内の部分燃焼により炭化させるが、幅広いごみ質、すなわち、一般廃棄物だけでなく産業廃棄物も合わせて処理する場合のごみ質の大きな変動にも対応でき、しかも炭化物の性状を一定化するための加熱温度制御が従来の流動床式ガス化溶融炉に比べて容易である。ごみのロータリーキルン内での滞留時間を1時間程度にとることで、可燃性ガス発生の変動を抑制することができる。なお、前記ロータリーキルン外部に設けた図示しないジャケットに熱交換器7からの加熱空気を送りこんで、キルンを間接加熱することで、キルン内の温度制御が容易となり安定した炭化が行なわれる。
【0015】
可燃性ガスを高発熱量の炭化物とともに溶融炉4(又は二次燃焼室5)で高温燃焼させ、燃焼ガスを排ガス処理装置8で薬剤の投入と共に処理することでダイオキシン類の発生を規制値0.1ng-TEO/m3N以下に低減することができる。
【0016】
上記実施の形態では、ごみなどの一般廃棄物ならびに廃プラスチックなどの産業廃棄物を低酸素雰囲気下の外熱式回転型炭化炉3で加熱炭化し、その炭化による炭化物をストックタンク11に貯溜し、ストックタンク11の炭化物と炭化による可燃性ガスを溶融炉4に供給して燃焼・溶融し、その燃焼ガスを二次燃焼室5、熱交換器7および排ガス処理装置8で処理し、熱交換器7の加熱空気を外熱式回転型炭化炉3に供給するとともに、外熱式回転型炭化炉3を運転しつつ溶融炉4を補修停止した際、外熱式回転型炭化炉3の可燃性ガスを二次燃焼室5で燃焼処理し、その燃焼ガスにより熱交換器7で熱交換した加熱空気を外熱式回転型炭化炉3に供給するようにしたが、上記溶融炉4の補修停止に伴う外熱式回転型炭化炉3の炭化物を上記ストックタンク11に貯溜するようにすることができる。ストックタンク11の容量を溶融炉4の補修停止中分の炭化物が貯溜可能な大きさにしたことにより、溶融炉4の補修停止期間が年間に数週間程度であっても、ごみに対して1/4程度に大幅に減容された炭化物を貯溜するから、ごみを収容する大きなスペースのピットに比べて大幅に小形化され小スペース化する。
また、溶融炉4の補修停止に伴う外熱式回転型炭化炉3の炭化物を洗浄・脱水機13により洗浄・脱水するようにすることもできる。これにより、一系列の溶融炉をメンテナンスなどのため停止した場合でも、二次燃焼室5の稼働により炭化物の製造が可能であり、製造された炭化物は洗浄・脱水処理されて無害な炭化燃料となる。すなわち、塩素濃度0.5%以下および重金属が土壌環境基準以下のクリーンで、しかも、発熱量がRDF(ごみ固形化燃料)に比べて30%も高い高発熱量の付加価値の高いものであるから、本設備および本設備以外への有効利用を図ることができる。この場合のストックタンク11の容量は上記溶融炉補修停止中に製造される炭化物の全量が洗浄・脱水機13に供給されるから、極めて小さいものでよい。
【0017】
また、より低コストでダイオキシン類の削減およびその他の環境汚染の防止、高効率のエネルギー回収と使用エネルギーの削減につながる。また、炭化物の必要時でのオンタイム別途利用も可能となる。
上記の実施形態において、洗浄・脱水機13の後に乾燥機14を付加することもできる。
また、減温塔6の冷却水として、本設備から発生する種々の排水を処理する排水処理装置15の排水を利用することにより、排水の外部への放流がなくなる。
【0018】
さらに、他の実施形態として、ストックタンク11の炭化物の一部を溶融炉4に供給し、残部を洗浄・脱水機13に供給するようにしたものにおいて、溶融炉4の補修停止中に外熱式回転型炭化炉3で製造される炭化物の一部をストックタンク11に貯溜するようにすることもできる。これにより、一系列の溶融炉をメンテナンスなどのため停止した場合でも、上記二次燃焼室5の稼働により上記残部の炭化物の製造が可能であり、製造された炭化物は洗浄・脱水機13により洗浄・脱水処理されて無害な炭化燃料となる。また、この場合のストックタンク11の容量は上記溶融炉補修停止中に製造される炭化物の一部を貯溜する大きさでよい。
【0019】
また、他の実施形態として、ストックタンク11の炭化物の一部を溶融炉4に供給し、残部を洗浄・脱水機13に供給するようにしたものにおいて、溶融炉4の補修停止中に外熱式回転型炭化炉3で製造される炭化物の全量をストックタンク11を経て洗浄・脱水機13に供給して洗浄、脱水するようにすることもできる。これにより、一系列の溶融炉をメンテナンスなどのため停止した場合でも、二次燃焼室5の稼働により炭化物の製造が可能であり、製造された炭化物は洗浄・脱水機により洗浄・脱水処理されて無害な炭化燃料となる。また、この場合のストックタンク11の容量は上記溶融炉補修停止中に製造される炭化物の全量が洗浄・脱水機13に供給されるから、極めて小さいものでよい。
前記において、溶融炉4に供給する炭化物の量を一部としたのは、可燃性ガスの燃焼および溶融スラグ化のために高温を維持するとともに加熱空気を得るために必要最小限の量であるが、その量を増やして温水や暖房用などの熱源として利用することができる。
【0020】
【発明の効果】
この発明は、以上のように、上記溶融炉を補修などのため停止した場合、外熱式回転型炭化炉の可燃性ガスを二次燃焼室で燃焼処理し、その燃焼ガスにより熱交換器で熱交換した加熱空気を上記外熱式回転型炭化炉に供給するようにしたので、上記溶融炉の停止時にも外熱式回転型炭化炉を連続して操業でき、また、構造も簡単であり、さらに安定した運転が可能となる。
【図面の簡単な説明】
【図1】本発明の実施の形態に係る廃棄物の連続炭化処理設備のフロー図
【符号の説明】
1 破砕機
2 前処理装置
3 炭化炉
4 溶融炉
5 二次燃焼室
6 減温塔
7 熱交換器
8 排ガス処理装置
9 排気筒
10 分別機(選別機)
11 ストックタンク
12 搬送手段
13 洗浄・脱水機
14 乾燥機
15 排水処理装置
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method and equipment for continuously carbonizing general waste such as garbage and industrial waste such as waste plastic.
[0002]
[Prior art]
Regarding the disposal of general waste such as garbage and industrial waste such as waste plastic, in recent years, environmental pollution countermeasures such as dioxins have been emphasized, and waste is gasified by heating without incineration and pyrolysis and pyrolysis. There is a method of separating into residues.
When waste is gasified, an externally heated rotary kiln or a fluidized or shaft type processing furnace is used.
When waste is processed by an externally heated rotary kiln, the dry distillation gas generated by heating can be used as a fuel for a secondary combustion chamber of a melting furnace or melting furnace exhaust gas, which is a subsequent process, and is efficient.
Carbide, which is a pyrolysis residue, is selectively removed from recyclable carbides such as metal, and then subjected to high-temperature combustion treatment in a melting furnace, whereby the carbide is further reduced in volume to form molten slag, and dioxin The occurrence of odors can also be reduced.
However, the melting furnace of the above equipment is very exhausted because the inside of the melting furnace is high temperature. Therefore, periodic repairs are necessary, and it is forced to shut down for several weeks per year. Since the waste generated every day is accumulated with the suspension during this period, it is desired to continuously treat the waste during this period. Therefore, there is a method of providing a plurality of melting furnaces, but this leads to an increase in equipment costs.
[0003]
In order to meet the above demand, a fluidized bed gasification furnace for pyrolyzing and gasifying combustible waste contained in various types of waste such as municipal waste and / or industrial waste using a fluid medium such as sand and the combustible A melting furnace that melts the solid content obtained by pyrolysis gasification, a heat recovery device that recovers heat using the hot gas obtained in the melting furnace, and an exhaust gas purification device that purifies the exhaust gas discharged from the device In the fluidized bed gasification and melting apparatus, the pyrolysis gas generated by pyrolyzing and gasifying the combustible waste containing the solid matter in the fluidized bed gasification furnace using a fluid medium in the pyrolysis gas combustion furnace. By using the combustion gas obtained from the combustion and exchanging heat with an independent superheater (or an independent air preheater), the combustion gas after the heat exchange is used as a fluidizing fluid for a fluidized medium in a fluidized bed gasifier. , Fluidized bed gasifier It operated in a state disconnected from the melting furnace and a heat recovery device. That is, it has been proposed to continue operation of the fluidized bed gasification furnace independently even when the operation of the subsequent melting furnace to the fluidized bed gasification furnace is stopped for maintenance or due to malfunction (for example, Patent Documents). 1).
[0004]
[Patent Document 1]
JP 11-118124 A (page 9, FIG. 2)
[0005]
[Problems to be solved by the invention]
However, in the prior art described in Patent Document 1, in addition to the system including the melting furnace and the heat recovery device, the pyrolysis gas combustion furnace of the pyrolysis gas, and the heat exchange medium is heat exchanged using the obtained combustion gas. This system employs a system that uses an independent superheater (or an independent air heater) and uses the combustion gas after heat exchange as the fluidizing fluid of the fluidized medium of the fluidized bed gasification furnace. The structure is complicated because it cannot be said. In addition, since the combustion gas after heat exchange is directly supplied to the fluidized bed gasification furnace as a fluidized fluid, the combustion gas has a low oxygen concentration, reducing the partial combustion of combustible waste, and the temperature of the fluidized medium. There is a problem that it is difficult to maintain and therefore lacks the stability of pyrolysis gasification of a fluidized bed gasifier.
[0006]
Therefore, the present invention comprises a combination of an externally heated rotary carbonization furnace and a subsequent melting furnace, and the carbonization furnace can be continuously operated even if the melting furnace is shut down despite a relatively simple structure. In addition, an object is to achieve stable operation.
[0007]
[Means for Solving the Problems]
In order to solve the above-mentioned problems, the present invention heats and carbonizes general waste such as garbage and industrial waste such as waste plastic in an externally heated rotary carbonization furnace in a low oxygen atmosphere, It is stored in the stock tank, the carbide of the stock tank and the combustible gas generated by the carbonization are supplied to the melting furnace, burned and melted, and the combustion gas is processed in the secondary combustion chamber, the heat exchanger and the exhaust gas treatment device, In the continuous carbonization treatment method for waste, in which the heating air of the heat exchanger is supplied to the external heating rotary carbonization furnace, when the repair of the melting furnace is stopped, the combustibility of the external heating rotary carbonization furnace The property gas is sent to the secondary combustion chamber for combustion treatment, heat is exchanged by the combustion gas in the heat exchanger, and the heat source of the external heating rotary carbonization furnace is secured by the heat exchanged heat. Closed circuit It is formed. This circuit has a relatively simple structure and can be operated stably.
[0008]
Furthermore, the stock tank is a carbide whose volume has been greatly reduced by adopting a configuration in which the carbide from the external heating type rotary carbonization furnace accompanying the repair stop of the melting furnace is stored in the stock tank. In combination with this, the space for the waste pit is greatly reduced and the space is saved.
Further, by adopting a configuration in which the carbide from the external heating rotary carbonization furnace accompanying the repair stop of the melting furnace is cleaned and dehydrated, the carbide becomes a harmless carbonized fuel.
[0009]
General-purpose waste such as garbage and industrial waste such as waste plastic are heated in a low-oxygen atmosphere and carbonized by heating, a melting furnace that burns and melts the above-mentioned combustible gas, and the above A secondary combustion chamber for treating the combustion gas of the melting furnace, a heat exchanger and an exhaust gas treatment device, a stock tank for storing the carbide by the carbonization, a conveying means for supplying the carbide in the stock tank to the melting furnace, and the above A conduit for supplying the heating air of the heat exchanger to the carbonization furnace, and the combustible gas of the external heating rotary carbonization furnace when the melting furnace is stopped while operating the external heating rotary carbonization furnace And a conduit for supplying the secondary combustion chamber. As a result, even when the melting furnace is stopped for repairs, etc., the external heating type rotation can be performed by operating the secondary combustion chamber and the heat exchanger without providing another series of independent superheaters (or independent air preheaters). Because the type carbonization furnace can be operated, it becomes compact.
Moreover, the structure of the said stock tank of the magnitude | size which stores the carbide | carbonized_material from the said external heating type rotary carbonization furnace accompanying the repair stop of the said melting furnace is employable.
Moreover, the structure of the washing | cleaning and dehydration machine which wash | cleans and spin-dry | dehydrates the carbide | carbonized_material from the said external heating type rotary carbonization furnace accompanying the repair stop of the said melting furnace can be employ | adopted.
[0010]
DETAILED DESCRIPTION OF THE INVENTION
Embodiments of the present invention will be described with reference to the drawings. FIG. 1 shows a schematic flow of a continuous carbonization treatment facility for waste according to an embodiment of the present invention. In this flow, industrial waste such as general waste and waste plastic is crushed from a pit (not shown) by a crane or the like. It is put into the machine 1 and crushed to about 10 to 15 cm, and then put into a dryer which is a pretreatment device 2 and dried, and then put into an external heating rotary carbonization furnace 3 through a quantitative feeder 3a. The combustibles in the waste put into the external heating type rotary carbonization furnace 3 are in a low oxygen state, that is, about 400 to 500 ° C. in a substantially oxygen-free atmosphere having an air-fuel ratio of about 0.3 with the outside air shut off. Due to the external heating, it is pyrolyzed and carbonized with partial combustion. By this pyrolysis, combustible gas and carbide are generated, and the combustible gas is sent to the melting furnace 4 through the conduit a together with dust.
On the other hand, solids such as carbides, metals, and non-combustible materials in the external heating type rotary carbonization furnace 3 are discharged by the discharge device 3b, and then cooled to about 250 ° C. by, for example, water cooling means, and then separated by the separation device 10 It is separated into resources, incombustibles and carbides. The separated carbides are temporarily stored in the stock tank 11 and then quantitatively cut out by a quantitative cutout device (not shown) below the stock tank 11 and supplied to the melting furnace 4 by a conveying means 12 such as a belt conveyor.
[0011]
The carbide supplied to the melting furnace 4, the separately supplied combustible gas, and the auxiliary fuel supplied as necessary burn, and become high temperature (about 1250 to 1450 ° C.) due to the combustion of the high calorie carbide. Thus, the ash generated with combustion is melted to form slag, and the molten slag is cooled with water in a water-cooled tank (not shown) and recovered as granulated slag.
The combustion gas of the melting furnace 4 enters the secondary combustion chamber 5 from the conduit b, is guided to the temperature reducing tower 6 via the conduit c, and is lowered to a predetermined temperature, and then is guided to the heat exchanger 7 via the conduit d. After being used for heat exchange of air, the exhaust gas is introduced into the exhaust gas treatment device (bag filter) 8 through the conduit e and purified, and the purified exhaust gas is discharged from the exhaust tube 9 into the atmosphere through the conduit f. The
The heated air (hot air) heat-exchanged by the heat exchanger 7 is supplied to the externally heated rotary carbonization furnace 3 through the conduit g and used as a heat source for carbonization.
Further, when the melting furnace 4 is repaired and stopped, the combustible gas from the carbonization furnace 3 is branched from the conduit a and supplied to the secondary combustion chamber 5 through the conduit b for combustion treatment, and the heat exchanger uses the combustion gas. By supplying the heated air heat-exchanged in 7 to the external heating rotary carbonization furnace 3 through the conduit g, the continuous operation of the external heating rotary carbonization furnace 3 is possible even when the repair of the melting furnace 4 is stopped. Become.
A part of the heated air may be branched from the conduit g and supplied to the melting furnace 4 to be used as a heat source for increasing the combustion gas temperature. In addition, heated air (hot air) can also be used as a heat source for hot water supply and air conditioning.
[0012]
Further, a part of the combustion gas is supplied to the dryer 2 through a conduit h branched from the conduit b, and the waste is used as a heat source for drying to a predetermined moisture content. Then, it is charged into the melting furnace 4. By using the combustion gas as the heat source of the dryer 2, the thermal energy can be effectively used and the running cost can be reduced.
[0013]
In addition, when burning the combustible gas in the melting furnace 4, even if the quantity and properties of the combustible gas generated in the external heating type rotary carbonization furnace 3 are not constant, high calorific value carbide is supplied to the melting furnace 4. Therefore, stable high-temperature combustion is possible. As a result, the temperature of the combustion gas, and hence the temperature of the heated air by the heat exchanger 7, is also constant, and the control of the heating temperature of the external heating type rotary carbonization furnace 3 is extremely stable.
[0014]
By using an externally heated rotary kiln as the externally heated rotary carbonization furnace 3, combustibles are carbonized by indirect heating from the outside of the rotary kiln and partial combustion in the kiln, but a wide range of garbage, that is, general waste In addition to dealing with large fluctuations in waste quality when processing industrial waste together, it is easier to control the heating temperature to make the properties of the carbide constant compared to conventional fluidized bed gasification and melting furnaces. It is. By taking the residence time of garbage in the rotary kiln to about 1 hour, fluctuations in the generation of combustible gas can be suppressed. In addition, by supplying heated air from the heat exchanger 7 to a jacket (not shown) provided outside the rotary kiln and indirectly heating the kiln, temperature control in the kiln is facilitated and stable carbonization is performed.
[0015]
Combustible gas is combusted at high temperature in the melting furnace 4 (or the secondary combustion chamber 5) together with carbide of high calorific value, and the combustion gas is treated together with the introduction of chemicals in the exhaust gas treatment device 8, thereby controlling the generation of dioxins. It can be reduced to 1 ng-TEO / m 3 N or less.
[0016]
In the above embodiment, general waste such as garbage and industrial waste such as waste plastic are heated and carbonized in the external heating rotary carbonization furnace 3 in a low oxygen atmosphere, and the carbonized carbon is stored in the stock tank 11. Then, the carbide in the stock tank 11 and the combustible gas generated by carbonization are supplied to the melting furnace 4 to be burned and melted, and the combustion gas is processed in the secondary combustion chamber 5, the heat exchanger 7 and the exhaust gas treatment device 8 to exchange heat When the heating air of the vessel 7 is supplied to the external heating rotary carbonization furnace 3 and the repair of the melting furnace 4 is stopped while operating the external heating rotary carbonization furnace 3, the combustibility of the external heating rotary carbonization furnace 3 is reached. Although the property gas is burned in the secondary combustion chamber 5 and the heated air heat-exchanged by the heat exchanger 7 by the combustion gas is supplied to the externally heated rotary carbonization furnace 3, the melting furnace 4 is repaired. The carbide of the externally heated rotary carbonization furnace 3 accompanying the stoppage is increased. It can be made to the reservoir to the stock tank 11. Even if the repair stop period of the melting furnace 4 is several weeks per year, the capacity of the stock tank 11 is made large enough to store the carbide during the repair stop of the melting furnace 4. Since the carbide reduced to about / 4 is stored, it is much smaller and smaller than a large space pit for storing garbage.
In addition, the carbide in the external heating type rotary carbonization furnace 3 accompanying the repair stop of the melting furnace 4 can be cleaned and dehydrated by the cleaning / dehydrating machine 13. As a result, even when a series of melting furnaces are stopped for maintenance, carbide can be produced by operating the secondary combustion chamber 5, and the produced carbide is washed and dehydrated to produce harmless carbonized fuel. Become. In other words, the chlorine concentration is 0.5% or less and the heavy metal is clean below the soil environmental standard, and the calorific value is 30% higher than that of RDF (garbage solidified fuel) and has a high calorific value and high added value. Therefore, it is possible to effectively use the equipment and the equipment other than the equipment. In this case, the capacity of the stock tank 11 may be very small because the entire amount of carbide produced during the repair of the melting furnace is stopped and supplied to the washing / dehydrating machine 13.
[0017]
In addition, it reduces dioxins and other environmental pollution at a lower cost, leading to highly efficient energy recovery and energy use reduction. In addition, the on-time can be separately used when the carbide is required.
In the above embodiment, the dryer 14 may be added after the washing / dehydrating machine 13.
Further, by using the waste water of the waste water treatment device 15 that treats various waste water generated from this facility as the cooling water of the temperature reducing tower 6, the waste water is not discharged to the outside.
[0018]
Furthermore, in another embodiment, a part of the carbide in the stock tank 11 is supplied to the melting furnace 4 and the remaining part is supplied to the cleaning / dehydrating machine 13. A part of the carbide produced in the rotary rotary carbonization furnace 3 can be stored in the stock tank 11. Thus, even when a series of melting furnaces are stopped for maintenance, the remaining carbide can be produced by operating the secondary combustion chamber 5, and the produced carbide is washed by the washing / dehydrating machine 13.・ Dehydrated to become harmless carbonized fuel. Further, the capacity of the stock tank 11 in this case may be large enough to store a part of the carbide produced during the melting furnace repair stop.
[0019]
In another embodiment, a part of the carbide in the stock tank 11 is supplied to the melting furnace 4 and the remaining part is supplied to the cleaning / dehydrating machine 13. The entire amount of carbide produced in the rotary rotary carbonization furnace 3 can be supplied to the washing / dehydrating machine 13 via the stock tank 11 to be washed and dehydrated. Thereby, even when a series of melting furnaces are stopped for maintenance, carbide can be produced by operating the secondary combustion chamber 5, and the produced carbide is washed and dehydrated by a washing and dehydrating machine. It becomes harmless carbonized fuel. Further, the capacity of the stock tank 11 in this case may be extremely small since the entire amount of carbide produced during the melting furnace repair stop is supplied to the washing / dehydrating machine 13.
In the above description, the amount of carbide supplied to the melting furnace 4 is a part of the minimum amount necessary for obtaining heated air while maintaining high temperature for combustion of combustible gas and melting slag. However, the amount can be increased and used as a heat source for hot water or heating.
[0020]
【The invention's effect】
As described above, when the melting furnace is stopped for repair or the like as described above, the combustible gas of the externally heated rotary carbonization furnace is combusted in the secondary combustion chamber, and the combustion gas is used in the heat exchanger. Heat-exchanged heated air is supplied to the external heating rotary carbonization furnace so that the external heating rotary carbonization furnace can be operated continuously even when the melting furnace is stopped, and the structure is simple. In addition, more stable operation is possible.
[Brief description of the drawings]
FIG. 1 is a flow diagram of a continuous carbonization treatment facility for waste according to an embodiment of the present invention.
DESCRIPTION OF SYMBOLS 1 Crusher 2 Pretreatment device 3 Carbonization furnace 4 Melting furnace 5 Secondary combustion chamber 6 Temperature reducing tower 7 Heat exchanger 8 Exhaust gas treatment device 9 Exhaust tube 10 Sorting machine (sorter)
11 Stock tank 12 Conveying means 13 Washing / dehydrating machine 14 Drying machine 15 Waste water treatment device

Claims (6)

ごみなどの一般廃棄物ならびに廃プラスチックなどの産業廃棄物を低酸素雰囲気下の外熱式回転型炭化炉3で加熱炭化し、その炭化による炭化物をストックタンク11に貯溜し、上記ストックタンク11の炭化物と上記炭化による可燃性ガスを溶融炉4に供給して燃焼・溶融し、その燃焼ガスを二次燃焼室5、熱交換器7および排ガス処理装置8で処理し、上記熱交換器7の加熱空気を上記外熱式回転型炭化炉3に供給するようにした廃棄物の連続炭化処理方法において、上記溶融炉4を補修停止した際、上記外熱式回転型炭化炉3の可燃性ガスを上記二次燃焼室5に送り込んで燃焼処理し、その燃焼ガスにより上記熱交換器7で熱交換した加熱空気を上記外熱式回転型炭化炉3に供給して上記外熱式回転型炭化炉3を運転するようにしたことを特徴とする廃棄物の連続炭化処理方法。General waste such as garbage and industrial waste such as waste plastic are heated and carbonized in an externally heated rotary carbonization furnace 3 in a low oxygen atmosphere, and the carbonized carbon is stored in the stock tank 11 and stored in the stock tank 11. Carbide and combustible gas from the carbonization are supplied to the melting furnace 4 to be burned and melted, and the combustion gas is treated in the secondary combustion chamber 5, the heat exchanger 7 and the exhaust gas treatment device 8, and the heat exchanger 7 In the continuous carbonization treatment method for waste, in which heated air is supplied to the external heating rotary carbonization furnace 3, when the melting furnace 4 is repaired and stopped, the combustible gas of the external heating rotary carbonization furnace 3 is used. Is sent to the secondary combustion chamber 5 for combustion treatment, and the heated air heat-exchanged by the heat exchanger 7 by the combustion gas is supplied to the external heating rotary carbonization furnace 3 to supply the external heating rotary carbonization. The furnace 3 was operated Continuous carbonization treatment method of waste characterized. 上記溶融炉4の補修停止に伴う上記外熱式回転型炭化炉3からの炭化物を上記ストックタンクに貯溜するようにしてなる請求項1に記載の廃棄物の連続炭化処理方法。The waste carbonization method according to claim 1, wherein the carbide from the external heating type rotary carbonization furnace 3 accompanying the repair stop of the melting furnace 4 is stored in the stock tank. 上記溶融炉4の補修停止に伴う上記外熱式回転型炭化炉3の炭化物を洗浄・脱水するようにしてなる請求項1又は2に記載の廃棄物の連続炭化処理方法。The method for continuous carbonization of waste according to claim 1 or 2, wherein the carbide in the externally heated rotary carbonization furnace 3 accompanying the repair stop of the melting furnace 4 is cleaned and dehydrated. ごみなどの一般廃棄物ならびに廃プラスチックなどの産業廃棄物を低酸素雰囲気下で加熱して炭化する外熱式回転型炭化炉3と、上記炭化による可燃性ガスを燃焼・溶融する溶融炉4と、上記溶融炉4の燃焼ガスを処理する二次燃焼室5、熱交換器7および排ガス処理装置8と、上記炭化による炭化物を貯溜するストックタンク11と、上記ストックタンク11の炭化物を上記溶融炉4に供給する搬送手段12と、上記熱交換器7の加熱空気を上記炭化炉3に供給する導管gと、上記溶融炉4を停止した際に上記外熱式回転型炭化炉3の可燃性ガスを上記二次燃焼室5に供給する導管aと、からなる廃棄物の連続炭化処理設備。An external heating rotary carbonization furnace 3 for heating and carbonizing general waste such as garbage and industrial waste such as waste plastic in a low oxygen atmosphere, and a melting furnace 4 for combusting and melting combustible gas by the carbonization The secondary combustion chamber 5 for processing the combustion gas of the melting furnace 4, the heat exchanger 7 and the exhaust gas processing device 8, the stock tank 11 for storing the carbonized carbide, and the carbide in the stock tank 11 for the melting furnace 4, a conveying means 12 for supplying the heated air from the heat exchanger 7 to the carbonization furnace 3, and the combustibility of the external heating rotary carbonization furnace 3 when the melting furnace 4 is stopped. A conduit a for supplying gas to the secondary combustion chamber 5 and a continuous carbonization treatment facility for waste. 上記溶融炉4の補修停止に伴う上記外熱式回転型炭化炉3からの炭化物を貯溜する大きさの上記ストックタンク11と、からなる請求項4に記載の廃棄物の連続炭化処理設備。The waste continuous carbonization facility according to claim 4, comprising the stock tank 11 having a size for storing the carbide from the external heating rotary carbonization furnace 3 when the repair of the melting furnace 4 is stopped. 上記溶融炉4の補修停止に伴う上記外熱式回転型炭化炉3からの炭化物を洗浄・脱水する洗浄・脱水機13と、からなる請求項4又は5に記載の廃棄物の連続炭化処理設備。The waste carbonization treatment facility according to claim 4 or 5, comprising a cleaning / dehydrating machine 13 for cleaning / dehydrating the carbide from the external heating rotary carbonization furnace 3 when the repair of the melting furnace 4 is stopped. .
JP2003068597A 2003-03-13 2003-03-13 Method for continuous carbonization of waste and its continuous carbonization processing equipment Expired - Fee Related JP4014524B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2003068597A JP4014524B2 (en) 2003-03-13 2003-03-13 Method for continuous carbonization of waste and its continuous carbonization processing equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2003068597A JP4014524B2 (en) 2003-03-13 2003-03-13 Method for continuous carbonization of waste and its continuous carbonization processing equipment

Publications (2)

Publication Number Publication Date
JP2004277503A JP2004277503A (en) 2004-10-07
JP4014524B2 true JP4014524B2 (en) 2007-11-28

Family

ID=33285882

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2003068597A Expired - Fee Related JP4014524B2 (en) 2003-03-13 2003-03-13 Method for continuous carbonization of waste and its continuous carbonization processing equipment

Country Status (1)

Country Link
JP (1) JP4014524B2 (en)

Also Published As

Publication number Publication date
JP2004277503A (en) 2004-10-07

Similar Documents

Publication Publication Date Title
JP5521187B2 (en) Combustible gas generator for gasifying waste and method for producing combustible gas
JP2005319374A (en) Method and apparatus for converting sludge into fuel
US20070294937A1 (en) Gasifier
JP2001342476A (en) Method and facility for producing carbonized waste
JPH11173520A (en) Method and device for fluidized bed type thermal decomposition
KR100856677B1 (en) Treatment apparatus of food rubbish
JP4156483B2 (en) Gasification and melting method of sludge
JP4910431B2 (en) Method and apparatus for pyrolysis gasification of waste
JP4014524B2 (en) Method for continuous carbonization of waste and its continuous carbonization processing equipment
JP3707754B2 (en) Waste treatment system and method and cement produced thereby
JP4089079B2 (en) Waste treatment method and waste treatment system
JP4161462B2 (en) Waste treatment method and waste treatment system
JP3836582B2 (en) Fluidized bed gasification melting apparatus and method
JPH11159719A (en) Incinerating method of waste
US7063026B1 (en) Waste carbonizing and energy utilizing system
JP2006170609A (en) Gasification and gasification combustion method of solid waste
JP2898625B1 (en) Method and apparatus for removing and decomposing dioxins with unburned ash
JP2002235913A (en) Method and apparatus for mixing wastes with sludge
JP2001289413A (en) Waste treatment facility
JP4089080B2 (en) Waste treatment method and waste treatment system
JP2001280615A (en) Melting furnace
JP2005077059A (en) Waste carbonization/energy using system
JP3876502B2 (en) Waste pyrolysis gasification melting equipment
JP2000283431A (en) Method and system for treating waste
JPH10205731A (en) Thermal decomposition reactor and waste treatment device

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20050119

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: 20070828

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20070911

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

Free format text: PAYMENT UNTIL: 20100921

Year of fee payment: 3

R150 Certificate of patent or registration of utility model

Ref document number: 4014524

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: 20100921

Year of fee payment: 3

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313113

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

Free format text: PAYMENT UNTIL: 20100921

Year of fee payment: 3

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

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

Free format text: PAYMENT UNTIL: 20100921

Year of fee payment: 3

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

Free format text: PAYMENT UNTIL: 20110921

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: 20120921

Year of fee payment: 5

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: 20130921

Year of fee payment: 6

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