JP3740081B2 - Fluidized bed incinerator equipped with fluidized medium deposit removal method and fluidized media deposit removal device - Google Patents

Fluidized bed incinerator equipped with fluidized medium deposit removal method and fluidized media deposit removal device Download PDF

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JP3740081B2
JP3740081B2 JP2002059869A JP2002059869A JP3740081B2 JP 3740081 B2 JP3740081 B2 JP 3740081B2 JP 2002059869 A JP2002059869 A JP 2002059869A JP 2002059869 A JP2002059869 A JP 2002059869A JP 3740081 B2 JP3740081 B2 JP 3740081B2
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fluidized bed
fluidized
medium
deposit
deposits
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JP2003262308A (en
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航哉 竹田
昌宏 魚住
康樹 松下
恭司 山本
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Kawasaki Motors Ltd
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Kawasaki Jukogyo KK
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  • Fluidized-Bed Combustion And Resonant Combustion (AREA)
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  • Devices And Processes Conducted In The Presence Of Fluids And Solid Particles (AREA)
  • Crucibles And Fluidized-Bed Furnaces (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は、廃棄物やRDFあるいは石炭等を燃焼させる流動床式焼却炉において、流動媒体の付着物を炉外で除去する方法、及びこの方法に用いる除去装置を備えた流動床式焼却炉に関するものである。
【0002】
【従来の技術】
流動床式焼却設備では、運転中に流動媒体(主として、硅砂)の表面に灰の一部が付着あるいは被覆し、初期投入時に比べて粒子径が増大する傾向にある。肥大化した粒子は流動化開始速度が速くなるので、適切な流動状態を維持するためには、通風量を増やす必要があり、通風系統のユーティリティーの増大を招く。また、通風量が増えると、排ガス量が増加するため、排ガス処理系統のユーティリティーの増大を招く。
【0003】
流動媒体の再生方法に関する従来技術としては、例えば、特開昭56−160513号公報に、重油焚きボイラの流動媒体に付着した灰分に水を浸透させ、水分を含有する灰分を付着した状態のままで流動媒体を流動層炉に戻す技術が記載されている。しかしながら、この方法では、運転中に抜き出した流動媒体は高温となっており、この高温となった流動媒体に水を浸透させることから、熱衝撃による流動媒体自身の破砕を招く恐れがある。また、付着していた物質は炉内に戻されることから、炉内で付着原因物質が濃縮される可能性がある。
【0004】
また、特許第3020464号公報には、スクリューコンベアを備えた砂洗浄装置が開示されている。この技術は洗浄水を使用するもので、排水を処理する装置が必要となる。また、装置内に稼動部があるため、砂との摩耗による稼動部材の損傷が考えられる。
【0005】
また、特表平8−504131号公報には、鋳物砂、特に活性ベントナイトを含有した砂の再生法に関する技術について記載されている。この技術は圧縮空気を層内に吹き込み流動層を形成させるもので、砂中に含まれる有価物の回収を可能とするものである。この技術は、Ca分及び/又はMg分を含有する燃料あるいはCa化合物及び/又はMg化合物を添加して燃焼させる流動床炉における流動媒体の付着物除去技術ではなく、回収した付着物を脱塩剤等の薬剤として利用する技術でもない。
【0006】
【発明が解決しようとする課題】
本発明は上記の諸点に鑑みなされたもので、本発明の目的は、流動床式焼却炉における付着物で肥大化した流動媒体を一旦炉外に抜き出し、流動媒体中に高速空気を吹き込むことで流動媒体に付着した物質を除去し、流動媒体の再生及び粒子径の適正化を行うことにより、流動床式焼却炉で適切な流動状態を維持することが容易となり、かつ、通風系統及び排ガス処理系統のユーティリティーが増大することもない流動媒体付着物の除去方法、及びこの方法に用いる除去装置を備えた流動床式焼却炉を提供することにある。
【0007】
また、本発明の目的は、炉外に抜き出した流動媒体に高速空気を吹き込んで流動媒体に付着した物質を除去することにより、運転中に流動媒体を抜き出した場合でも流動媒体自身が急激な温度変化による熱衝撃を受けることがなく、しかも、炉内に付着原因物質が濃縮することはなく、さらに、除去装置の構成が非常に簡単で、流動媒体による装置の摩耗損傷も少ない流動媒体付着物の除去方法、及びこの方法に用いる除去装置を備えた流動床式焼却炉を提供することにある。
また、本発明の目的は、Ca分及び/又はMg分を含有する燃料あるいはCa化合物及び/又はMg化合物を添加して燃焼させる流動床式焼却炉において、回収した付着物の粉体を薬剤として有効利用できるようにした技術を提供することにある。
【0008】
【課題を解決するための手段】
上記の目的を達成するために、本発明の流動媒体付着物の除去方法は、流動床式焼却炉から付着物により肥大化した流動媒体を抜き出して、炉外に抜き出した流動媒体を付着物除去装置に投入し、該装置内に高速空気を吹き込むことにより流動媒体に付着した物質を除去して、流動媒体の再生及び粒子径の適正化を行い、除去した付着物を集塵装置で捕集するように構成されている。
【0009】
また、本発明の方法は、Ca分及び/もしくはMg分を含有する燃料を投入して又はCa化合物及び/もしくはMg化合物を添加して燃焼させる流動床式焼却炉から付着物により肥大化した流動媒体を抜き出して、炉外に抜き出した流動媒体を付着物除去装置に投入し、該装置内に高速空気を吹き込むことにより流動媒体に付着した物質を除去して、流動媒体の再生及び粒子径の適正化を行い、除去した付着物を集塵装置で捕集し、捕集した付着物を脱塩剤、脱硫剤、吸着剤等の薬剤として利用することを特徴としている。
これらの方法においては、集塵装置から排出される除塵後の空気を流動床式焼却炉の一次空気又は/及び二次空気として利用することができる。
【0010】
流動床式焼却炉が循環流動床炉の場合には、循環流動床炉における収熱用の流動床から付着物により肥大化した流動媒体を抜き出して付着物除去装置に投入する。
【0011】
本発明の流動媒体付着物の除去装置を備えた流動床式焼却炉は、廃棄物やRDF(ごみ固形化燃料)あるいは石炭等の燃料を燃焼させる流動床式焼却炉と、付着物により肥大化した流動媒体を流動床式焼却炉から抜き出す流動媒体抜出手段と、炉外に抜き出した流動媒体を貯留し、この流動媒体群に高速空気を吹き込むことで、流動媒体に付着した物質を除去する付着物除去装置と、付着物除去装置後段に設置された除去した付着物を捕集するための集塵装置と、付着物を除去して粒子径の適正化を行った流動媒体を付着物除去装置から抜き出して流動床式焼却炉又は/及びBM(流動媒体)貯留槽に戻す流動媒体循環系統とを包含してなることを特徴としている。
【0012】
また、本発明の流動媒体付着物の除去装置を備えた流動床式焼却炉は、Ca分及び/もしくはMg分を含有する燃料を投入して又はCa化合物及び/もしくはMg化合物を添加して燃焼させる流動床式焼却炉と、付着物により肥大化した流動媒体を流動床式焼却炉から抜き出す流動媒体抜出手段と、炉外に抜き出した流動媒体を貯留し、この流動媒体群に高速空気を吹き込むことで、流動媒体に付着した物質を除去する付着物除去装置と、付着物除去装置後段に設置された除去した付着物を捕集するための集塵装置と、回収した付着物の粉体を脱塩剤や吸着剤の代替物質として焼却炉の排ガス処理系統に吹き込む回収付着物吹込手段と、付着物を除去して粒子径の適正化を行った流動媒体を付着物除去装置から抜き出して流動床式焼却炉又は/及びBM(流動媒体)貯留槽に戻す流動媒体循環系統とを包含してなることを特徴としている。
【0013】
流動床式焼却炉が循環流動床炉の場合には、循環流動床炉における収熱用の流動床に流動媒体抜出手段を設けて、付着物により肥大化した流動媒体を付着物除去装置に投入する。
【0014】
これらの場合、付着物除去装置は、流動媒体群の下部から散気管により空気を吹き込む構成としても良いし、流動媒体群の下側から分散板上のノズルにより空気を吹き込む構成としても良い。
また、付着物除去装置本体としてBM(流動媒体)貯留槽を用いる場合と、付着物除去装置本体をBM貯留槽とは別に設置する場合がある。
なお、付着物除去装置のBM抜出口は装置底部に限ることなく、装置側面部に設けても良い。
また、集塵装置から排出される除塵後の空気を流動床式焼却炉の一次空気又は/及び二次空気として利用するための空気供給系統を設けることができる。
【0015】
【発明の実施の形態】
以下、本発明の実施の形態について説明するが、本発明は下記の実施の形態に何ら限定されるものではなく、適宜変更して実施することができるものである。図1は、本発明の実施の第1形態による流動媒体付着物の除去装置を備えた流動床式焼却炉の一例を示している。本実施の形態は、一例として、Ca分を含有する燃料(RDFなど)を燃焼させたり、Ca化合物を添加して廃棄物やRDFあるいは石炭等を燃焼させる流動床式焼却炉において、流動媒体に付着した物質を除去するものである。
【0016】
流動床式焼却炉10では、運転中に流動媒体(主として、硅砂)の表面に灰の一部が溶融して付着あるいは被覆し、粒子径が初期投入時に比べて増大する。そこで、この肥大化した流動媒体(BM)を流動床式焼却炉10から抜き出して炉外で付着物の除去処理を行う。流動床式焼却炉10の下部から不燃物等とともに抜き出されたBMは、不燃物をふるい等(図示略)で分離した後、付着物除去装置12に投入される。また、具体的な図示は省略しているが、流動床式焼却炉が循環流動床炉の場合には、循環流動床炉における収熱用の流動床から流動媒体を抜き出して付着物除去装置に投入すればよい。なお、本実施の形態では、付着物除去装置12をBM貯留槽14とは別に設置している。付着物除去装置12内の流動媒体群には高速空気が吹き込まれ、流動媒体同士の摩耗作用で付着物が除去されて、流動媒体の再生及び粒子径の適正化が行われる。この場合、吹込み空気流速は、例えば、100m/s以上である。16はブロワである。
【0017】
付着物除去装置12は、図1、図2に示すように、流動媒体群の下側から分散板18上のノズル20により空気を吹き込む構成とすることができる。ノズル20は、例えば、図2のような構成とすることができる。この場合、空気吹込み方向としては、一例として、図3、図4、図5に示すように、ノズルを備えた分散板18を上から見た状態で、略中心方向又は外側から内側に向かって空気を吹き込む構成とすることができる。図3、図4、図5においては、矢印の始点が吹込み部(ノズル)である。なお、付着物除去装置12は、流動媒体群の下部から散気管により空気を吹き込む構成としても良い。
【0018】
粒子径が適正化された処理後のBMは、付着物除去装置12のBM抜出口22から抜き出され、BM循環ライン24を通って流動床式焼却炉10に戻される。この場合、処理後のBMはBM貯留槽14に戻すこともできる。なお、付着物除去装置12のBM抜出口は装置底部に限ることなく、装置側面部等に設けても良い。また、除去された付着物は付着物除去装置12後段に設置された集塵装置26にて捕集される。集塵装置26としては、一例として、バグフィルタのようなろ過式集塵器が用いられる。集塵装置26から排出される除塵後の空気は、流動床式焼却炉10の一次空気又は/及び二次空気として利用することが可能である。
【0019】
集塵装置26で回収した付着物は、必要に応じて粒度調整などの処理を施した後、薬剤として利用される。試験によると、回収した付着物はそのほとんどが40〜80μm程度の微粉体であって、しかもCa化合物(CaOなど)を含有しており、洗煙用の薬剤、例えば図1に示すように、焼却炉の排ガス処理系統に設置された集塵装置28(バグフィルタ等のろ過式集塵器)の前に吹き込まれている脱塩剤(消石灰等)の代替物質として利用することができる。付着物除去装置12により除去された付着物の粉塵は、その由来が灰であるため、焼却炉からの灰と同様な処理を施す必要がある。灰処理量の増加は処理装置の規模の増大につながり、また、装置のランニングコストも高くなる。そこで、上記のように、回収した付着物の粉塵を脱塩剤の代替物質として利用することは、灰の排出量を抑えることになり、また、薬剤費の低減化につながる。なお、捕集した付着物の薬剤としての利用法としては、上記の脱塩剤に限らず、脱硫剤や吸着剤等としても利用することができる。
【0020】
また、本実施の形態においては、装置の運転中に流動媒体を抜き出して流動媒体の再生及び粒子径の適正化を行う場合と、装置停止時(定期検査時など)に流動媒体を抜き出して流動媒体の再生及び粒子径の適正化を行う場合がある。運転時の場合は、例えば、流動媒体の一部を適量抜き出して除去装置で所定時間処理を行い、流動床炉に循環させるようにする。一方、停止時の場合は、例えば、流動媒体を全量抜き出して、除去装置で付着物がほぼ完全に除去できるまで処理を行った後、流動媒体を流動床炉に戻すようにする。なお、他の運転方法とすることも勿論可能である。
【0021】
図6は、本発明の実施の第2形態による流動媒体付着物の除去装置を備えた流動床式焼却炉の一例を示している。本実施の形態も、一例として、Ca分を含有する燃料(RDFなど)を燃焼させたり、Ca化合物を添加して廃棄物やRDFあるいは石炭等を燃焼させる流動床式焼却炉において、流動媒体に付着した物質を除去するものである。流動床式焼却炉10の下部から不燃物等とともに抜き出されたBMは、不燃物をふるい等(図示略)で分離した後、BM貯留槽を改造して製作した付着物除去装置30に投入される。このように、本実施の形態では、付着物除去装置本体としてBM貯留槽を用いている。付着物除去装置30に貯留された流動媒体群には高速空気が吹き込まれ、流動媒体同士の摩耗作用で付着物が除去されて、流動媒体の再生及び粒子径の適正化が行われる。
【0022】
BM貯留槽を改造して製作した付着物除去装置30は、例えば図6に示すように、散気管32により流動媒体群の下部から空気を吹き込む構成とすることができる。なお、付着物除去装置30は、流動媒体群の下側から分散板上のノズルにより空気を吹き込む構成としても良い。
【0023】
粒子径が適正化された処理後のBMは、付着物除去装置30から抜き出され、BM循環ライン24を通って流動床式焼却炉10に戻される。また、除去された付着物は付着物除去装置30後段に設置された集塵装置26(バグフィルタ等のろ過式集塵器)にて捕集される。集塵装置26から排出される除塵後の空気は、流動床式焼却炉10の一次空気又は/及び二次空気として利用することが可能である。集塵装置26で回収した付着物は、必要に応じて粒度調整などの処理を施した後、薬剤として利用される。具体的には、例えば図6に示すように、焼却炉の排ガス処理系統に設置された集塵装置28(バグフィルタ等のろ過式集塵器)の前に吹き込まれている脱塩剤の代替物質として利用することができる。なお、捕集した付着物の薬剤としての利用法としては、上記の脱塩剤に限らず、脱硫剤や吸着剤等としても利用することができる。
他の構成及び作用等は、実施の第1形態の場合と同様である。
【0024】
図7は、本発明の実施の第3形態による流動媒体付着物の除去装置を備えた流動床式焼却炉の一例を示している。本実施の形態は、一例として、流動床式焼却炉が循環流動床炉の場合であり、Ca分を含有する燃料(RDFなど)を燃焼させたり、Ca化合物を添加して廃棄物やRDFあるいは石炭等を燃焼させる流動床炉において、流動媒体に付着した物質を除去するものである。循環流動床炉34においては、サイクロン36の後段に設置された収熱用の流動床38からBMが抜き出され、抜き出されたBMが付着物除去装置12に投入される。このように、本実施の形態では、付着物除去装置12をBM貯留槽14とは別に設置している。付着物除去装置12内の流動媒体群には高速空気が吹き込まれ、流動媒体同士の摩耗作用で付着物が除去されて、流動媒体の再生及び粒子径の適正化が行われる。
【0025】
粒子径が適正化された処理後のBMは、付着物除去装置12のBM抜出口22から抜き出され、BM循環ライン24を通って流動床炉34に戻される。この場合、処理後のBMはBM貯留槽14に戻すこともできる。なお、付着物除去装置12のBM抜出口は装置底部に限ることなく、装置側面部等に設けても良い。また、除去された付着物は付着物除去装置12後段に設置された集塵装置26にて捕集される。集塵装置26から排出される除塵後の空気は、流動床炉34の一次空気又は/及び二次空気として利用することが可能である。
【0026】
集塵装置26で回収した付着物は、必要に応じて粒度調整などの処理を施した後、薬剤として利用される。回収した付着物はそのほとんどが40〜80μm程度の微粉体であって、しかもCa化合物(CaOなど)を含有しており、洗煙用の薬剤、例えば図7に示すように、焼却炉の排ガス処理系統に設置された集塵装置28(バグフィルタ等のろ過式集塵器)の前に吹き込まれている脱塩剤(消石灰等)の代替物質として利用することができる。なお、捕集した付着物の薬剤としての利用法としては、上記の脱塩剤に限らず、脱硫剤や吸着剤等としても利用することができる。
他の構成及び作用等は、実施の第1形態の場合と同様である。
【0027】
図8は、本発明の実施の第4形態による流動媒体付着物の除去装置を備えた流動床式焼却炉の一例を示している。本実施の形態も、一例として、流動床式焼却炉が循環流動床炉の場合であり、Ca分を含有する燃料(RDFなど)を燃焼させたり、Ca化合物を添加して廃棄物やRDFあるいは石炭等を燃焼させる流動床炉において、流動媒体に付着した物質を除去するものである。循環流動床炉34においては、サイクロン36の後段に設置された収熱用の流動床38からBMが抜き出され、抜き出されたBMがBM貯留槽を改造して製作した付着物除去装置30に投入される。このように、本実施の形態では、付着物除去装置本体としてBM貯留槽を用いている。付着物除去装置30に貯留された流動媒体群には高速空気が吹き込まれ、流動媒体同士の摩耗作用で付着物が除去されて、流動媒体の再生及び粒子径の適正化が行われる。
【0028】
粒子径が適正化された処理後のBMは、付着物除去装置30から抜き出され、BM循環ライン24を通って流動床炉34に戻される。また、除去された付着物は付着物除去装置30後段に設置された集塵装置26(バグフィルタ等のろ過式集塵器)にて捕集される。集塵装置26から排出される除塵後の空気は、流動床炉34の一次空気又は/及び二次空気として利用することが可能である。集塵装置26で回収した付着物は、必要に応じて粒度調整などの処理を施した後、薬剤として利用される。具体的には、例えば図8に示すように、焼却炉の排ガス処理系統に設置された集塵装置28(バグフィルタ等のろ過式集塵器)の前に吹き込まれている脱塩剤の代替物質として利用することができる。なお、捕集した付着物の薬剤としての利用法としては、上記の脱塩剤に限らず、脱硫剤や吸着剤等としても利用することができる。
他の構成及び作用等は、実施の第1形態、第2形態、第3形態の場合と同様である。
【0029】
【発明の効果】
本発明は上記のように構成されているので、つぎのような効果を奏する。
(1) 流動床式焼却炉における付着物で肥大化した流動媒体を一旦炉外に抜き出し、流動媒体中に高速空気を吹き込むことで流動媒体に付着した物質を除去し、流動媒体の再生及び粒子径の適正化を行うので、流動床式焼却炉で適切な流動状態を維持することが容易となる。
(2) 流動化開始速度が大きくならないので、ブロワ等の通風系統のユーティリティーが増大することはない。また、流動床炉からの排ガス量が増加しないので、排ガス処理系統のユーティリティーが増大することはない。
(3) 運転中に抜き出した流動媒体は高速空気のみが吹き込まれるので、流動媒体自身が急激な温度変化による熱衝撃を受けることはなく、流動媒体の破砕等が起こりにくい。
(4) 付着物を炉外で除去するので、炉内に付着原因物質が濃縮することがない。
(5) 除去装置内に稼動部はなく空気吹込み手段のみを設けた構造であるので非常に単純で簡単な構成であり、また、流動媒体による装置の摩耗損傷も受けにくい。
(5) Ca分及び/又はMg分を含有する燃料あるいはCa化合物及び/又はMg化合物を添加して燃焼させる流動床式焼却炉の場合は、回収した付着物の粉体を、例えば、廃棄物焼却炉等の排ガス処理系統で集塵器前に吹き込まれている脱塩剤の代替物質として利用することができる。また、回収した付着物の粉体は、吸着剤や脱硫剤としても利用可能である。
【図面の簡単な説明】
【図1】本発明の実施の第1形態による流動媒体付着物の除去装置を備えた流動床式焼却炉を示す概略構成説明図である。
【図2】本発明の実施の第1形態における付着物除去装置の空気吹込構造の一例を示す拡大構成説明図である。
【図3】本発明の実施の第1形態における付着物除去装置の空気吹込方向の一例を示す模式的概略平面説明図である。
【図4】本発明の実施の第1形態における付着物除去装置の空気吹込方向の他の例を示す模式的概略平面説明図である。
【図5】本発明の実施の第1形態における付着物除去装置の空気吹込方向のさらに他の例を示す模式的概略平面説明図である。
【図6】本発明の実施の第2形態による流動媒体付着物の除去装置を備えた流動床式焼却炉を示す概略構成説明図である。
【図7】本発明の実施の第3形態による流動媒体付着物の除去装置を備えた流動床式焼却炉を示す概略構成説明図である。
【図8】本発明の実施の第4形態による流動媒体付着物の除去装置を備えた流動床式焼却炉を示す概略構成説明図である。
【符号の説明】
10 流動床式焼却炉
12、30 付着物除去装置
14 BM貯留槽
16 ブロワ
18 分散板
20 ノズル
22 BM抜出口
24 BM循環ライン
26、28 集塵装置
32 散気管
34 循環流動床炉
36 サイクロン
38 収熱用の流動床
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a fluidized bed incinerator for burning waste, RDF, coal, or the like, and a method for removing deposits of a fluidized medium outside the furnace, and a fluidized bed incinerator equipped with a removing device used in this method. Is.
[0002]
[Prior art]
In the fluidized bed incinerator, a part of the ash adheres or covers the surface of the fluidized medium (mainly dredged sand) during operation, and the particle size tends to increase as compared with the initial charging. Since the enlarged particles have a higher fluidization start speed, it is necessary to increase the amount of ventilation in order to maintain an appropriate flow state, which increases the utility of the ventilation system. Moreover, since the amount of exhaust gas increases when the amount of ventilation increases, the utility of the exhaust gas treatment system increases.
[0003]
As a conventional technique relating to a method for regenerating a fluid medium, for example, in Japanese Patent Application Laid-Open No. Sho 56-160513, water is infiltrated into ash adhering to a fluid medium of a heavy oil-fired boiler, and moisture containing ash is adhered. Describes a technique for returning a fluidized medium to a fluidized bed furnace. However, in this method, the fluid medium extracted during operation is at a high temperature, and water is permeated into the fluid medium at the high temperature, which may cause the fluid medium itself to be crushed by thermal shock. In addition, since the adhered substance is returned to the furnace, there is a possibility that the substance causing the adhesion is concentrated in the furnace.
[0004]
Japanese Patent No. 3020464 discloses a sand cleaning apparatus equipped with a screw conveyor. This technique uses washing water and requires a device for treating waste water. Moreover, since there is an operating part in the apparatus, the operating member may be damaged due to abrasion with sand.
[0005]
Japanese Patent Application Laid-Open No. 8-504131 discloses a technique relating to a method for regenerating foundry sand, particularly sand containing active bentonite. In this technique, compressed air is blown into the bed to form a fluidized bed, which enables recovery of valuable materials contained in the sand. This technology is not a deposit removal technology for fluid media in a fluidized bed furnace in which a fuel containing Ca and / or Mg content or a Ca compound and / or Mg compound is added and burned, but the recovered deposits are desalted. It is not a technology used as a drug such as a drug.
[0006]
[Problems to be solved by the invention]
The present invention has been made in view of the above points, and an object of the present invention is to once extract a fluid medium enlarged with deposits in a fluidized bed incinerator and then blow high-speed air into the fluid medium. By removing substances adhering to the fluidized medium, regenerating the fluidized medium and optimizing the particle size, it becomes easy to maintain an appropriate fluidized state in the fluidized bed incinerator, and the ventilation system and exhaust gas treatment It is an object of the present invention to provide a fluidized bed incinerator having a fluidized medium deposit removing method that does not increase the utility of the system, and a removing device used in this method.
[0007]
Another object of the present invention is to blow high-speed air into the fluid medium drawn out of the furnace to remove substances adhering to the fluid medium, so that the fluid medium itself has a rapid temperature even when the fluid medium is withdrawn during operation. Fluidized medium deposits that are not subject to thermal shock due to changes, do not concentrate the causative substances in the furnace, and have a very simple removal device configuration and less wear damage to the device due to fluidized media It is an object to provide a fluidized bed incinerator equipped with a removal method and a removal device used in this method.
Another object of the present invention is to use the collected adhering powder as a chemical in a fluidized bed incinerator in which a fuel containing Ca and / or Mg or a Ca compound and / or Mg compound is added and burned. It is to provide a technology that can be used effectively.
[0008]
[Means for Solving the Problems]
In order to achieve the above-mentioned object, the fluid medium deposit removal method of the present invention extracts a fluid medium enlarged by deposits from a fluidized bed incinerator and removes the fluid medium extracted outside the furnace from the deposit. The substance adhering to the fluidized medium is removed by blowing high-speed air into the device, and the fluidized medium is regenerated and the particle size is optimized, and the removed deposits are collected by the dust collector. Is configured to do.
[0009]
In addition, the method of the present invention is a method in which a fuel containing Ca and / or Mg is added or fluid is enlarged by deposits from a fluidized bed incinerator where a Ca compound and / or Mg compound is added and burned. The medium is extracted, the fluid medium extracted outside the furnace is put into a deposit removing device, and the substance adhering to the fluid medium is removed by blowing high-speed air into the device. It is characterized by optimizing, collecting the removed deposits with a dust collector, and using the collected deposits as chemicals such as a desalting agent, a desulfurizing agent, and an adsorbent.
In these methods, the air after dust removal discharged from the dust collector can be used as primary air and / or secondary air in a fluidized bed incinerator.
[0010]
In the case where the fluidized bed incinerator is a circulating fluidized bed furnace, the fluid medium enlarged by the deposits is extracted from the fluidized bed for heat recovery in the circulating fluidized bed furnace and is put into the deposit removing apparatus.
[0011]
The fluidized bed incinerator equipped with the fluidized medium deposit removal device of the present invention is a fluidized bed incinerator that burns fuel such as waste, RDF (garbage solidified fuel) or coal, and is enlarged by deposits. The fluid medium extraction means for extracting the fluid medium that has been removed from the fluidized bed incinerator and the fluid medium extracted outside the furnace are stored, and high-speed air is blown into the fluid medium group to remove substances adhering to the fluid medium. Adherent removal device, dust collector for collecting the removed adhering matter installed at the latter stage of the adhering matter removal device, and fluid medium that has been optimized for particle size by removing the adhering matter It is characterized by including a fluidized bed incinerator or / and a fluidized medium circulation system that returns to a BM (fluidized medium) storage tank.
[0012]
Moreover, the fluidized bed incinerator equipped with the fluidized medium deposit removal device of the present invention is combusted by adding fuel containing Ca and / or Mg or adding Ca compound and / or Mg compound. Fluidized bed incinerator, fluidized medium extracting means for extracting the fluidized medium enlarged by deposits from the fluidized bed incinerator, and storing the fluidized medium extracted outside the furnace, and storing high-speed air in the fluidized media group. A deposit removing device that removes substances adhering to the fluid medium by blowing, a dust collector for collecting the removed deposit installed downstream of the deposit removing device, and a powder of collected deposit As a substitute for desalting agent and adsorbent, the recovered deposit blowing means that blows into the exhaust gas treatment system of the incinerator and the fluidized medium that has been optimized for particle size by removing the deposit are extracted from the deposit removing device. Fluidized bed incinerator or And BM is characterized by comprising encompass the fluidized medium circulation line back to the (fluidized medium) reservoir.
[0013]
When the fluidized bed incinerator is a circulating fluidized bed furnace, a fluidized medium extraction means is provided in the fluidized bed for heat recovery in the circulating fluidized bed furnace, and the fluidized medium enlarged by the adhered material is used as the adhered material removing device. throw into.
[0014]
In these cases, the deposit removing device may be configured to blow air from the lower part of the fluidized medium group using an air diffuser, or may be configured to blow air from the lower side of the fluidized medium group using a nozzle on a dispersion plate.
Moreover, the case where a BM (fluid medium) storage tank is used as the deposit removal apparatus main body and the deposit removal apparatus main body may be installed separately from the BM storage tank.
The BM outlet of the deposit removing device is not limited to the bottom of the device, but may be provided on the side surface of the device.
Moreover, the air supply system for utilizing the air after dust removal discharged | emitted from a dust collector as primary air and / or secondary air of a fluidized bed incinerator can be provided.
[0015]
DETAILED DESCRIPTION OF THE INVENTION
Embodiments of the present invention will be described below, but the present invention is not limited to the following embodiments, and can be implemented with appropriate modifications. FIG. 1 shows an example of a fluidized bed incinerator equipped with a fluid medium deposit removing device according to a first embodiment of the present invention. In this embodiment, as an example, in a fluidized bed incinerator that burns a fuel containing Ca (such as RDF) or burns waste, RDF, coal, or the like by adding a Ca compound, It removes the adhered substances.
[0016]
In the fluidized bed incinerator 10, a part of the ash melts and adheres to or covers the surface of the fluidized medium (mainly dredged sand) during operation, and the particle size increases compared to the initial charging time. Therefore, the enlarged fluidized medium (BM) is extracted from the fluidized bed incinerator 10 and the deposits are removed outside the furnace. The BM extracted from the lower part of the fluidized bed incinerator 10 together with incombustibles and the like is separated into the incombustibles with a sieve or the like (not shown), and then introduced into the deposit removing device 12. In addition, although the illustration is omitted, when the fluidized bed incinerator is a circulating fluidized bed furnace, the fluidized medium is extracted from the fluidized bed for heat recovery in the circulating fluidized bed furnace, and the adhering substance removing device is removed. Just put it in. In the present embodiment, the deposit removal device 12 is installed separately from the BM storage tank 14. High-speed air is blown into the fluid medium group in the deposit removal device 12, the deposits are removed by the wear action of the fluid media, and the fluid medium is regenerated and the particle diameter is optimized. In this case, the blown air flow velocity is, for example, 100 m / s or more. 16 is a blower.
[0017]
As shown in FIGS. 1 and 2, the deposit removing device 12 can be configured to blow air from the lower side of the fluid medium group through the nozzles 20 on the dispersion plate 18. The nozzle 20 can be configured as shown in FIG. 2, for example. In this case, as an example, as shown in FIGS. 3, 4, and 5, the air blowing direction may be directed substantially in the center direction or from the outside to the inside with the dispersion plate 18 provided with the nozzle viewed from above. The air can be blown. 3, 4, and 5, the starting point of the arrow is the blowing portion (nozzle). In addition, the deposit removing device 12 may be configured to blow air from the lower part of the fluid medium group through an air diffuser.
[0018]
The treated BM having an optimized particle diameter is extracted from the BM outlet 22 of the deposit removing device 12 and returned to the fluidized bed incinerator 10 through the BM circulation line 24. In this case, the treated BM can be returned to the BM storage tank 14. The BM outlet of the deposit removing device 12 is not limited to the bottom of the device, but may be provided on the side surface of the device. Further, the removed deposits are collected by a dust collecting device 26 installed at the rear stage of the deposit removing device 12. As an example of the dust collector 26, a filtration type dust collector such as a bag filter is used. The air after dust discharged from the dust collector 26 can be used as primary air and / or secondary air of the fluidized bed incinerator 10.
[0019]
The deposit collected by the dust collector 26 is used as a drug after being subjected to processing such as particle size adjustment as necessary. According to the test, most of the collected deposits are fine powder of about 40 to 80 μm and contain Ca compound (CaO etc.), and as shown in FIG. It can be used as a substitute for a desalting agent (such as slaked lime) blown in front of a dust collector 28 (filtered dust collector such as a bag filter) installed in an exhaust gas treatment system of an incinerator. Since the dust of the deposit | attachment removed by the deposit | attachment removal apparatus 12 originates in ash, it is necessary to perform the process similar to the ash from an incinerator. An increase in the amount of ash treatment leads to an increase in the scale of the processing apparatus, and the running cost of the apparatus also increases. Therefore, as described above, using collected dust collected as a substitute for a desalting agent suppresses the amount of ash discharged and leads to a reduction in drug costs. In addition, as a utilization method as a chemical | medical agent of the collected deposit | attachment, it can utilize not only as said desalting agent but as a desulfurization agent, an adsorption agent, etc.
[0020]
In the present embodiment, the fluidized medium is extracted during operation of the apparatus to regenerate the fluidized medium and optimize the particle size, and the fluidized medium is extracted when the apparatus is stopped (such as during periodic inspection). There are cases where the medium is regenerated and the particle size is optimized. In the case of operation, for example, an appropriate amount of a fluid medium is extracted, treated with a removing device for a predetermined time, and circulated in a fluidized bed furnace. On the other hand, at the time of stopping, for example, the entire amount of the fluidized medium is extracted, and after the processing is performed until the deposits can be almost completely removed by the removing device, the fluidized medium is returned to the fluidized bed furnace. Of course, other operation methods are possible.
[0021]
FIG. 6 shows an example of a fluidized bed incinerator equipped with a fluid medium deposit removing device according to a second embodiment of the present invention. In the fluidized bed incinerator where the fuel containing the Ca component (RDF or the like) is combusted or the Ca compound is added to combust waste, RDF, coal, etc. It removes the adhered substances. The BM extracted from the lower part of the fluidized bed incinerator 10 together with incombustibles is separated into incombustibles with a sieve (not shown), and then put into a deposit removal device 30 that is manufactured by modifying the BM storage tank. Is done. Thus, in this Embodiment, BM storage tank is used as a deposit removal apparatus main body. High-speed air is blown into the fluid medium group stored in the adhering substance removing device 30, and the adhering substance is removed by the wear action between the fluid media, so that the fluid medium is regenerated and the particle diameter is optimized.
[0022]
For example, as shown in FIG. 6, the deposit removing device 30 manufactured by modifying the BM storage tank can be configured to blow air from the lower portion of the fluid medium group through the air diffuser 32. The deposit removing device 30 may be configured to blow air from the lower side of the fluid medium group using a nozzle on the dispersion plate.
[0023]
The treated BM having an optimized particle diameter is extracted from the deposit removing device 30 and returned to the fluidized bed incinerator 10 through the BM circulation line 24. Further, the removed deposit is collected by a dust collector 26 (a filtration type dust collector such as a bag filter) installed at the rear stage of the deposit removing device 30. The air after dust discharged from the dust collector 26 can be used as primary air and / or secondary air of the fluidized bed incinerator 10. The deposit collected by the dust collector 26 is used as a drug after being subjected to processing such as particle size adjustment as necessary. Specifically, for example, as shown in FIG. 6, an alternative to a desalting agent blown in front of a dust collector 28 (filtered dust collector such as a bag filter) installed in an exhaust gas treatment system of an incinerator. It can be used as a substance. In addition, as a utilization method as a chemical | medical agent of the collected deposit | attachment, it can utilize not only as said desalting agent but as a desulfurization agent, adsorption agent, etc.
Other configurations and operations are the same as those in the first embodiment.
[0024]
FIG. 7 shows an example of a fluidized bed incinerator equipped with a fluid medium deposit removing device according to a third embodiment of the present invention. As an example, this embodiment is a case where the fluidized bed incinerator is a circulating fluidized bed furnace, in which a fuel containing Ca (such as RDF) is burned, or a Ca compound is added to produce waste or RDF or In a fluidized bed furnace for burning coal or the like, a substance attached to the fluidized medium is removed. In the circulating fluidized bed furnace 34, BM is extracted from the heat collecting fluidized bed 38 installed at the subsequent stage of the cyclone 36, and the extracted BM is supplied to the deposit removing device 12. Thus, in this Embodiment, the deposit | attachment removal apparatus 12 is installed separately from the BM storage tank 14. FIG. High-speed air is blown into the fluid medium group in the deposit removal device 12, the deposits are removed by the wear action of the fluid media, and the fluid medium is regenerated and the particle diameter is optimized.
[0025]
The treated BM having an optimized particle size is extracted from the BM outlet 22 of the deposit removing device 12 and returned to the fluidized bed furnace 34 through the BM circulation line 24. In this case, the treated BM can be returned to the BM storage tank 14. The BM outlet of the deposit removing device 12 is not limited to the bottom of the device, but may be provided on the side surface of the device. Further, the removed deposits are collected by a dust collecting device 26 installed at the rear stage of the deposit removing device 12. The dust-removed air discharged from the dust collector 26 can be used as primary air and / or secondary air in the fluidized bed furnace 34.
[0026]
The deposit collected by the dust collector 26 is used as a drug after being subjected to processing such as particle size adjustment as necessary. Most of the collected deposits are fine powders of about 40 to 80 μm and contain Ca compounds (CaO, etc.), and smoke cleaning chemicals such as exhaust gas from incinerators as shown in FIG. It can be used as a substitute for a desalting agent (slaked lime, etc.) blown in front of a dust collector 28 (filter type dust collector such as a bag filter) installed in the treatment system. In addition, as a utilization method as a chemical | medical agent of the collected deposit | attachment, it can utilize not only as said desalting agent but as a desulfurization agent, an adsorption agent, etc.
Other configurations and operations are the same as those in the first embodiment.
[0027]
FIG. 8 shows an example of a fluidized bed incinerator equipped with a fluidized medium deposit removing device according to a fourth embodiment of the present invention. This embodiment is also an example in which the fluidized bed incinerator is a circulating fluidized bed furnace, in which a fuel containing Ca content (such as RDF) is burned, or a Ca compound is added to produce waste or RDF. In a fluidized bed furnace for burning coal or the like, a substance attached to the fluidized medium is removed. In the circulating fluidized bed furnace 34, BM is extracted from a fluidized bed 38 for heat collection installed at the subsequent stage of the cyclone 36, and the extracted BM modifies the BM storage tank to produce the deposit removing device 30. It is thrown into. Thus, in this Embodiment, BM storage tank is used as a deposit removal apparatus main body. High-speed air is blown into the fluid medium group stored in the adhering substance removing device 30, and the adhering substance is removed by the wear action between the fluid media, so that the fluid medium is regenerated and the particle diameter is optimized.
[0028]
The treated BM having an optimized particle size is extracted from the deposit removing device 30 and returned to the fluidized bed furnace 34 through the BM circulation line 24. Further, the removed deposit is collected by a dust collector 26 (a filtration type dust collector such as a bag filter) installed at the rear stage of the deposit removing device 30. The dust-removed air discharged from the dust collector 26 can be used as primary air and / or secondary air in the fluidized bed furnace 34. The deposit collected by the dust collector 26 is used as a drug after being subjected to processing such as particle size adjustment as necessary. Specifically, for example, as shown in FIG. 8, an alternative to a desalting agent blown in front of a dust collector 28 (filtered dust collector such as a bag filter) installed in an exhaust gas treatment system of an incinerator. It can be used as a substance. In addition, as a utilization method as a chemical | medical agent of the collected deposit | attachment, it can utilize not only as said desalting agent but as a desulfurization agent, an adsorption agent, etc.
Other configurations and operations are the same as those in the first, second, and third embodiments.
[0029]
【The invention's effect】
Since this invention is comprised as mentioned above, there exist the following effects.
(1) The fluidized medium enlarged with deposits in the fluidized bed incinerator is once extracted out of the furnace, and high-speed air is blown into the fluidized medium to remove the substances adhering to the fluidized medium. Since the diameter is optimized, it is easy to maintain an appropriate fluid state in the fluidized bed incinerator.
(2) Since the fluidization start speed does not increase, the utility of ventilation systems such as blowers will not increase. Moreover, since the amount of exhaust gas from the fluidized bed furnace does not increase, the utility of the exhaust gas treatment system does not increase.
(3) Since only high-speed air is blown into the fluid medium extracted during operation, the fluid medium itself is not subjected to thermal shock due to a rapid temperature change, and the fluid medium is not easily crushed.
(4) Since the deposits are removed outside the furnace, the causative substances are not concentrated in the furnace.
(5) Since there is no moving part in the removing apparatus and only air blowing means is provided, the structure is very simple and simple, and the apparatus is not easily damaged by the fluid medium.
(5) In the case of a fluidized bed incinerator in which a fuel containing Ca and / or Mg or a Ca compound and / or Mg compound is added and combusted, the collected deposit powder is, for example, waste It can be used as a substitute for a desalting agent blown before a dust collector in an exhaust gas treatment system such as an incinerator. The collected deposit powder can also be used as an adsorbent or a desulfurizing agent.
[Brief description of the drawings]
FIG. 1 is a schematic configuration explanatory view showing a fluidized bed incinerator equipped with a fluidized medium deposit removal device according to a first embodiment of the present invention.
FIG. 2 is an enlarged configuration explanatory view showing an example of an air blowing structure of the deposit removing apparatus according to the first embodiment of the present invention.
FIG. 3 is a schematic schematic plan view illustrating an example of an air blowing direction of the deposit removing apparatus according to the first embodiment of the present invention.
FIG. 4 is a schematic schematic plan view illustrating another example of the air blowing direction of the deposit removing apparatus according to the first embodiment of the present invention.
FIG. 5 is a schematic schematic plan view showing still another example of the air blowing direction of the deposit removing apparatus according to the first embodiment of the present invention.
FIG. 6 is a schematic configuration explanatory view showing a fluidized bed incinerator equipped with a fluid medium deposit removal device according to a second embodiment of the present invention.
FIG. 7 is a schematic configuration explanatory view showing a fluidized bed incinerator equipped with a fluid medium deposit removing device according to a third embodiment of the present invention.
FIG. 8 is a schematic configuration explanatory view showing a fluidized bed incinerator equipped with a fluid medium deposit removing device according to a fourth embodiment of the present invention.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 10 Fluidized bed incinerator 12, 30 Deposit removal apparatus 14 BM storage tank 16 Blower 18 Dispersion plate 20 Nozzle 22 BM outlet 24 BM circulation line 26, 28 Dust collector 32 Aeration pipe 34 Circulating fluidized bed furnace 36 Cyclone 38 Collection Fluidized bed for heat

Claims (6)

Ca分及び/もしくはMg分を含有する燃料を投入して又はCa化合物及び/もしくはMg化合物を添加して燃焼させる流動床式焼却炉から付着物により肥大化した流動媒体を抜き出して、炉外に抜き出した流動媒体を付着物除去装置に投入し、該装置内に空気を吹き込むことにより流動媒体に付着した物質を除去して、流動媒体の再生及び粒子径の適正化を行い、除去した付着物を集塵装置で捕集し、捕集した付着物を脱塩剤、脱硫剤及び吸着剤のいずれかの薬剤として利用することを特徴とする流動媒体付着物の除去方法 The fluid medium enlarged by deposits is extracted from the fluidized bed incinerator in which fuel containing Ca and / or Mg is added or Ca compound and / or Mg compound is added and burned. The extracted fluidized medium is put into a deposit removal device, and air is blown into the device to remove substances adhered to the fluidized medium, and the fluidized medium is regenerated and the particle size is optimized. A method for removing deposits from a fluid medium, characterized in that the collected deposits are collected by a dust collector, and the collected deposits are used as any one of a desalting agent, a desulfurizing agent and an adsorbent . 流動床式焼却炉が循環流動床炉であり、循環流動床炉における収熱用の流動床から付着物により肥大化した流動媒体を抜き出して付着物除去装置に投入する請求項1記載の流動媒体付着物の除去方法。  2. The fluidized medium according to claim 1, wherein the fluidized bed incinerator is a circulating fluidized bed furnace, and the fluidized medium enlarged by deposits is extracted from the fluidized bed for heat recovery in the circulating fluidized bed furnace and is put into the deposit removing device. How to remove deposits. 集塵装置から排出される除塵後の空気を流動床式焼却炉の一次空気又は/及び二次空気として利用する請求項1又は2記載の流動媒体付着物の除去方法。  The removal method of the deposit | attachment of the fluid medium of Claim 1 or 2 using the air after dust removal discharged | emitted from a dust collector as primary air and / or secondary air of a fluidized bed incinerator. Ca分及び/もしくはMg分を含有する燃料を投入して又はCa化合物及び/もしくはMg化合物を添加して燃焼させる流動床式焼却炉と、
付着物により肥大化した流動媒体を流動床式焼却炉から抜き出す流動媒体抜出手段と、
炉外に抜き出した流動媒体を貯留し、この流動媒体群に空気を吹き込むことで、流動媒体に付着した物質を除去する付着物除去装置と、
付着物除去装置後段に設置された除去した付着物を捕集するための集塵装置と、
回収した付着物の粉体を脱塩剤や吸着剤の代替物質として焼却炉の排ガス処理系統に吹き込む回収付着物吹込手段と、
付着物を除去して粒子径の適正化を行った流動媒体を付着物除去装置から抜き出して流動床式焼却炉又は/及び流動媒体貯留槽に戻す流動媒体循環系統とを包含してなることを特徴とする流動媒体付着物の除去装置を備えた流動床式焼却炉。
A fluidized bed incinerator in which a fuel containing Ca and / or Mg is charged or burned by adding a Ca compound and / or Mg compound;
Fluid medium extraction means for extracting the fluid medium enlarged by deposits from the fluidized bed incinerator;
A deposit removing device that removes a substance attached to the fluid medium by storing the fluid medium extracted outside the furnace and blowing air into the fluid medium group;
A dust collecting device for collecting the removed deposits installed downstream of the deposit removing device;
Collected deposit blowing means for blowing the collected deposit powder into the exhaust gas treatment system of the incinerator as a substitute for desalting agent and adsorbent,
Including a fluidized medium circulation system for removing the deposits and optimizing the particle size and extracting the fluidized medium from the deposit removing device and returning it to the fluidized bed incinerator and / or the fluidized medium storage tank. A fluidized bed incinerator equipped with a fluidized medium deposit removing device.
流動床式焼却炉が循環流動床炉であり、循環流動床炉における収熱用の流動床に流動媒体抜出手段を設け、付着物により肥大化した流動媒体を付着物除去装置に投入するようにした請求項記載の流動媒体付着物の除去装置を備えた流動床式焼却炉。The fluidized bed incinerator is a circulating fluidized bed furnace, and a fluidized medium extraction means is provided in the fluidized bed for heat recovery in the circulating fluidized bed furnace so that the fluidized medium enlarged by the deposits is put into the deposit removing device. A fluidized bed incinerator comprising the fluid medium deposit removing device according to claim 4 . 集塵装置から排出される除塵後の空気を流動床式焼却炉の一次空気又は/及び二次空気として利用するための空気供給系統を設けた請求項4又は5記載の流動媒体付着物の除去装置を備えた流動床式焼却炉。  6. Removal of fluid medium deposits according to claim 4 or 5, further comprising an air supply system for using the air after dust removal discharged from the dust collector as primary air and / or secondary air in a fluidized bed incinerator. Fluidized bed incinerator equipped with equipment.
JP2002059869A 2002-03-06 2002-03-06 Fluidized bed incinerator equipped with fluidized medium deposit removal method and fluidized media deposit removal device Expired - Fee Related JP3740081B2 (en)

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