JP4652609B2 - Coal combustion ash melting method and melt processing system - Google Patents

Coal combustion ash melting method and melt processing system Download PDF

Info

Publication number
JP4652609B2
JP4652609B2 JP2001156331A JP2001156331A JP4652609B2 JP 4652609 B2 JP4652609 B2 JP 4652609B2 JP 2001156331 A JP2001156331 A JP 2001156331A JP 2001156331 A JP2001156331 A JP 2001156331A JP 4652609 B2 JP4652609 B2 JP 4652609B2
Authority
JP
Japan
Prior art keywords
ash
coal
coal combustion
melting
combustion ash
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
JP2001156331A
Other languages
Japanese (ja)
Other versions
JP2002349834A (en
Inventor
輝幸 岡崎
啓信 小林
琢也 石賀
好友 青木
強 柴田
敬二 石井
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.)
Hitachi Ltd
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
Hitachi 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 Babcock Hitachi KK, Hitachi Ltd filed Critical Babcock Hitachi KK
Priority to JP2001156331A priority Critical patent/JP4652609B2/en
Publication of JP2002349834A publication Critical patent/JP2002349834A/en
Application granted granted Critical
Publication of JP4652609B2 publication Critical patent/JP4652609B2/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
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/12Heat utilisation in combustion or incineration of waste
    • 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
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
    • 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
    • Y02W30/20Waste processing or separation

Landscapes

  • Chimneys And Flues (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は、発電所から多量に排出される石炭燃焼灰の減容化処理に関する。
【0002】
【従来の技術】
石炭は埋蔵量が豊富であり、他の化石燃料に比べ経済性において優れている。石炭を大量に使用する火力発電所は今後、さらに増設・新設が見込まれている。石炭は約10から20%の灰を含んでおり、火力発電所の増設・新設に伴い石炭燃焼灰の排出量も増加することが予想される。よって、発電所から排出する石炭燃焼灰の処理方法は大きな課題になっている。
【0003】
火力発電所から排出する石炭燃焼灰は大きく分けて、火炉内のクリンカホッパより排出されるボトムアッシュ、エコノマイザから回収されるシンダーアッシュ、集塵器で回収されるフライアッシュの三つに大別される。石炭燃焼灰はセメントなどの原材料として有効利用するが、半分以上の石炭燃焼灰はごみとして近隣の海岸などの埋め立てに利用する。埋め立て処分をする場合において、石炭燃焼灰の溶出水は高アルカリのため、環境保全上の問題が生じる可能性がある。そのため、石炭燃焼灰は管理型産業廃棄物に指定されている。また、石炭燃焼灰の処分用地の確保が難しくなっており、灰を埋め立て以外に有効利用することが望まれている。
【0004】
石炭燃焼灰をセメントの原材料として使用するには灰中未燃分をなるべく少なくする必要がある。微粉炭火炉プラントで回収した石炭燃焼灰は、通常、3から5%の未燃分が含まれる。未燃分の多い石炭燃焼灰はセメントなどの原材料とする価値がない。
【0005】
石炭燃焼灰を利用してセメントの混和材やコンクリートの骨材の原料とする石炭焚きボイラに関する技術として特開平10−1339号公報に記載の技術がある。これは火炉と灰溶融炉で構成され、火炉からのボトムアッシュを溶融してスラグにするというものである。また良質なフライアッシュはそのまま利用するシステムである。
【0006】
一方、石炭燃焼灰をガス化炉でスラグ化し、減容化して処理する技術として特開平10−81398号公報に記載の技術がある。これはガス化炉の燃料として火炉で使用する微粉炭を利用するというものである。
【0007】
なお、特開2000−283429号公報、特開2000−283433号公報には、廃棄物から生成した炭化物を火力燃料とする技術が開示されている。
【0008】
また、特開平9−243044号公報には、炭化物を助燃料として石炭燃焼灰を溶融する技術が開示されている。
【0009】
さらに、特開平2−122109号公報には、炭化材を助燃料として都市ごみ焼却灰を溶融する技術が開示されている。
【0010】
【発明が解決しようとする課題】
前記した従来技術のうち、特開2000−283429号公報、特開2000−283433号公報に開示の技術は、廃棄物から生成した炭化物を単にボイラなどの燃料として利用するに止どまり、発電所から多量に排出される石炭燃焼灰の溶融減容化処理に利用する点については認識されていない。
【0011】
また、特開平9−243044号公報には、炭化物を助燃料として石炭燃焼灰を溶融する技術が開示されているが、廃棄物から生成した炭化物を燃料として石炭燃焼灰を溶融する点については認識されていない。
【0012】
さらに、特開平2−122109号公報に記載の技術は、炭化材を助燃料として都市ごみ焼却灰を溶融するというものであって、都市ごみを含む廃棄物そのものから生成した炭化物を燃料として利用し、石炭燃焼灰を溶融する点については認識されていない。
【0013】
ところで、特開平10−1339号、特開平10−81398号のように石炭燃焼灰を溶融させるためには、溶融炉の炉内を灰の融点以上、すなわち約1200〜2500℃以上にしなければならない。しかし、このような高温の状態で溶融炉を運転すると投入熱量(燃料量)も多くなったり、炉体が熱的に厳しい条件にさらされ損傷が早くなるなどの問題がある。
【0014】
そこで、石炭燃焼灰の融点を下げるため、石炭燃焼灰に添加剤を混ぜて溶融させる技術が特開平9−210338号公報に開示されている。この方法によれば、灰の溶融炉内の温度を下げられるので前述のような問題は回避できる。しかし、石炭燃焼灰を溶融するための添加剤や燃料を購入する必要が生じ、灰処理のコストが増加する。
【0015】
本発明の課題は、発電所から多量に排出される石炭燃焼灰の溶融による減容化処理を低コストで実現することにある。
【0016】
【課題を解決するための手段】
前記課題は、微粉炭火炉から排出される排ガス中の石炭燃焼灰を灰溶融炉で溶融して溶融スラグを生成する場合に、廃棄物から生成した炭化物を燃料として(あるいは廃棄物から生成した炭化物と石炭を混合し、この混合物を燃料として)石炭燃焼灰を溶融することによって達成される。
【0017】
【発明の実施の形態】
以下、添付図面に基づいて本発明の実施例を説明する。ただし、本発明は実施例に限定されるものではない。
(実施例1)
本発明の一実施例を図1に示す。
【0018】
石炭1は貯炭場から運炭設備によって石炭粉砕器9に運ばれ、粉砕される。粉砕した石炭は給炭機によって、石炭の搬送空気が流れている石炭搬送管10に供給される。石炭は火炉6に設けたバーナ7に供給され、火炉6内で燃焼する。
【0019】
空気ブロア18は燃焼用空気をバーナ7に供給する。空気ブロア18からの燃焼用空気は空気余熱器14によって暖められ、空気配管19を通り、バーナ7へ向かう。燃焼用空気は約300℃に暖められ、火炉6内を冷やすことなく石炭の燃焼に寄与し、石炭を安定に燃焼する。
【0020】
石炭の燃焼ガスは火炉6の壁面を加熱し、火炉6の下流側に設置した過熱器や再熱器、空気余熱器である節炭器など(共に図示せず)を加熱しながら脱硝装置13に向かう。排気ガス中のNOxは脱硝装置13において規制値以下になるように除去される。脱硝装置13の下流に排気ガスの余熱を利用して燃焼用空気を暖める空気余熱器14がある。さらに排気ガスは空気余熱器14の下流にある集塵器15によって排気ガス中のフライアッシュを脱塵し、脱硫装置16に入る。排気ガスは脱硫装置16で硫黄酸化物を除去してクリーンな排気ガスとなり、煙突17から排出される。
【0021】
集塵器15の前段で回収したフライアッシュ3や火炉6で回収したボトムアッシュ2を灰溶融炉28に供給する。集塵器15の前段で回収したフライアッシュ4は小粒径で、未燃分も少ないのでセメントの材料として利用可能である。この理由により灰溶融炉28で処理しない。
【0022】
灰溶融炉28の燃料は廃棄物を炭化し、炭化物中の異物を取り除いた物か、廃棄物を炭化し、炭化物中の異物を取り除いた物を石炭と混ぜた物を利用すると良い。
【0023】
前者を使用する理由は、発電所で発生する廃棄物を燃料にでき、燃料コストを削減できるからである。また、石炭燃焼灰の溶融温度は約1200℃から2500℃と高く、融点の低い炭化物を混入すれば石炭燃焼灰の融点を降下することもできる。これにより、灰溶融炉28の炉内の温度を約1200〜1800℃程度でも灰を溶融できる。さらに、石炭だけを燃料にする場合に比べ、灰溶融炉28を加熱するのに必要なエネルギーが低減する。一方、後者を使用する理由は、石炭は発熱量が炭化物に比べ安定しているので、石炭を付加することによって燃焼状態を一定に保つ効果があるからである。
【0024】
このように、発電所から多量に排出される石炭燃焼灰の溶融による減容化処理を、廃棄物から生成した炭化物を燃料とすることで低コストで実現することができる。
【0025】
また、廃棄物から生成した炭化物と石炭を混合し、この混合物を燃料として石炭燃焼灰を溶融する場合、石炭に混ぜた炭化物が石炭燃焼灰の融点を低下させるので、溶融に必要なエネルギーが減る。
【0026】
前述のように炭化物は発電所内の廃棄物を利用して生成すると良いが、一般の家庭などのゴミや産業廃棄物などを回収して利用することも可能である。廃棄物を灰溶融28の燃料とするので、灰溶融処理の燃料コストが削減できる。また、炭化装置から排出された炭化物内には金属などが混入しているので選別器で炭化物と分ける。
【0027】
図1において、灰溶融炉28のバーナには、廃棄物から生成した炭化物と石炭1を粉砕器20で粉砕して供給する。粒径は必要に応じて調整する。図1では、ホッパ22、粉砕器20にに炭化物と石炭1を投入しているが、図2のようにホッパ22、粉砕器20に石炭1を単独的に投入し、炭化物は炭化物専用の粉砕器29で予め粉砕して燃料供給配管23に直接供給しても良い。
【0028】
灰溶融炉28における燃焼用空気は必要に応じて暖め、空気搬送管21を通り、空気ノズルに供給する。
【0029】
高温ガス雰囲気に石炭燃焼灰を投入すると、石炭燃焼灰は溶融し、スラグとして回収される。スラグは灰溶融炉28から排出した後、除冷装置で冷却する。除冷したスラグ5は、路盤材などとして幅広い用途がある。また、埋め立てをする場合も石炭燃焼灰の体積を大幅に縮小できるため、最終処分場の省スペース化につながる。
【0030】
しかし、灰溶融炉28の排気ガスはNOxやSOxなどの有害物質を含んでいるため、火炉6の出口に戻し、脱硝装置13や、脱硫装置16を介して排出する。図1では、火炉6と脱硝装置13の間に灰溶融炉28の燃焼排ガスを投入する例を示す。ここで、炭化物中に含まれる塩素分の存在により、灰溶融炉28から排出される燃焼排ガスにはダイオキシン類が含まれていることを考えておかなければならない。これに対し、脱硝装置13上流側に排ガスを投入すれば、燃焼排ガス中のダイオキシンは脱硝装置13において酸化分解される(化学工学64(3)128−130(2000))。排ガス中の飛灰にもダイオキシンが含まれていることを考えておかなければならないが、これは下流に設置された集塵器15で回収される。これらにより、発電所から排出するダイオキシンは確実に環境規制値以下になる。また、排ガスを火炉6の下流に投入するので火炉6自体の構造変更は必要でない。
【0031】
本実施例によれば、灰溶融炉28で発生するダイオキシン類を脱硝装置13と集塵器15で回収できる。
(実施例2)
火炉6の炉底部に灰溶融炉28の燃焼排ガスを投入する例を図3で説明する。従来の微粉炭火炉では火炉6に設置された最下段のバーナ付近は他の下流のバーナに比べて温度が低いので石炭の着火性が悪い。特に負荷が低い時は炉内温度が低下し、一層着火しにくくなる。これに対し、灰溶融炉28からの燃焼排ガスの温度は、灰溶融炉出口において1000〜2000℃程度と高温である。このガスを高温状態で火炉6に投入すると炉底部の温度が上昇し、石炭の着火性能が向上する。従来、炉底部に投入するガスの温度は300〜400℃程度なので、燃焼排ガスの温度はそれ以上であれば良い。
【0032】
本実施例によれば、灰溶融炉28で発生するダイオキシン類を火炉6において再度、高温燃焼して分解できる。
(実施例3)
炭化物に含まれる塩素分を除去する脱塩装置を備えた例を図4で説明する。図中、灰溶融炉28の燃焼排ガスは火炉6と脱硝装置13の間に投入されているが、実施例2のように火炉6の炉底部に投入しても良い。
【0033】
廃棄物中には塩素分が含まれているため、炭化装置で生成された炭化物を燃焼させるとダイオキシンや塩化水素が発生する。しかし、予め脱塩装置で炭化物から塩素分を除去しておけば、灰溶融炉28内での燃焼によるダイオキシンや塩化水素の発生量は減少する。塩化水素の発生量が少なければ、灰溶融炉下流での冷却配管などに生じる塩素腐食の問題もなくなる。
(実施例4)
発電所外で生成された炭化物を利用する例を図5で説明する。
【0034】
図中、灰溶融炉28の燃焼排ガスは火炉6と脱硝装置13の間に投入されているが、実施例2のように火炉6の炉底部に投入しても良い。また、図では脱塩した炭化物を供給しているが、塩化物が存在することによって発生するダイオキシンを廃棄物燃焼の際に十分分解できれば、脱塩装置は必ずしも必要とするものではない。
【0035】
自治体などで生成した炭化物を購入し、燃料として用いれば、発電所内に炭化装置を所有しなくて良いので省スペース化を図れる。廃棄物炭化装置などの機器が不要で設備コストが削減できる。また、発電所内だけで炭化物を賄う場合に比べ、安定に炭化物を供給できる利点がある。
(実施例5)
灰溶融炉28の廃熱を回収する廃熱回収ボイラ30と、廃熱回収ボイラ30で蒸気タービン24を駆動して発電する発電装置25を灰溶融炉28に設置した例を図6で説明する。
【0036】
灰溶融炉28からの燃焼排ガスは、1000〜2000℃程度と高温であるので灰溶融炉28の下流に廃熱回収ボイラ30を取り付け、蒸気タービン24を駆動して発電する。廃熱回収ボイラ30で発生した電気は灰溶融炉システムの動力として利用できる。燃焼排ガスは熱回収の後、さらに灰溶融炉28の燃焼用空気と熱交換し、燃焼ガス中の飛灰を集塵器26で回収した後、煙突27から大気中に放出される。
【0037】
本実施例によれば、既存のボイラシステムを変更することなく灰を溶融処理することができる。また、廃熱回収ボイラ30で発生した電気は灰溶融炉システムの動力として利用できる。
【0038】
【発明の効果】
本発明によれば、発電所から多量に排出される石炭燃焼灰の溶融による減容化処理を、廃棄物から生成した炭化物を燃料とすることで低コストで実現することができる。
【図面の簡単な説明】
【図1】本発明の一実施例を示す微粉炭火炉の系統図である。
【図2】炭化物の灰溶融炉への輸送配管を変更した例を示す図である。
【図3】火炉の炉底部に灰溶融炉の燃焼排ガスを投入する例を示す微粉炭火炉の系統図である。
【図4】脱塩装置を備えた例を示す微粉炭火炉の系統図である。
【図5】発電所外で生成された炭化物を利用する例を示す微粉炭火炉の系統図である。
【図6】灰溶融炉の廃熱を回収する廃熱回収ボイラと、廃熱回収ボイラで蒸気タービンを駆動して発電する発電装置を灰溶融炉に設置した例を示す微粉炭火炉の系統図である。
【符号の説明】
1…石炭、2…ボトムアッシュ、3…集塵器15の前段で回収したフライアッシュ、4…集塵器15の後段で回収したフライアッシュ、5…除冷したスラグ、6…火炉、7…バーナ、8…ホッパ、9…粉砕器、10…石炭搬送管、11…GRポート、12…サイクロン、13…脱硝装置、14…空気熱交換器、15…集塵器、16…脱硫装置、17…煙突、18…ブロア、19…空気搬送管、20…粉砕器、21…空気搬送管、22…ホッパ、23…炭化物供給配管、24…タービン、25…発電機、26…集塵器、27…煙突、28…灰溶融炉、29…粉砕器、30…廃熱回収ボイラ。
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a volume reduction process of coal combustion ash discharged in large quantities from a power plant.
[0002]
[Prior art]
Coal has abundant reserves and is more economical than other fossil fuels. Thermal power plants that use large amounts of coal are expected to be expanded or newly constructed in the future. Coal contains about 10 to 20% ash, and the amount of coal combustion ash emissions is expected to increase with the expansion and construction of thermal power plants. Therefore, a method for treating coal combustion ash discharged from a power plant has become a major issue.
[0003]
Coal-burning ash discharged from thermal power plants can be broadly divided into three categories: bottom ash discharged from the clinker hopper in the furnace, cinder ash recovered from the economizer, and fly ash recovered from the dust collector. The Coal-burning ash is used effectively as raw materials such as cement, but more than half of the coal-burning ash is used as landfill for nearby beaches as waste. In the case of landfill disposal, the elution water of coal combustion ash is highly alkaline, which may cause environmental conservation problems. For this reason, coal-burning ash is designated as managed industrial waste. In addition, it is difficult to secure a land for disposal of coal combustion ash, and it is desired to use the ash effectively other than landfill.
[0004]
In order to use coal-burning ash as a raw material for cement, it is necessary to reduce the unburned content in the ash as much as possible. The coal combustion ash recovered at the pulverized coal furnace plant usually contains 3 to 5% unburned content. Coal ash with a lot of unburned content is not worth using as raw materials such as cement.
[0005]
JP-A-10-1339 discloses a technique related to a coal-fired boiler that uses coal-burning ash as a raw material for cement admixture or concrete aggregate. This consists of a furnace and an ash melting furnace, in which the bottom ash from the furnace is melted into slag. In addition, high-quality fly ash is a system that can be used as it is.
[0006]
On the other hand, there is a technique described in Japanese Patent Application Laid-Open No. 10-81398 as a technique for converting coal combustion ash into slag in a gasification furnace and reducing the volume. This is to use pulverized coal used in the furnace as the fuel for the gasifier.
[0007]
Japanese Patent Application Laid-Open Nos. 2000-283429 and 2000-283433 disclose a technique in which carbide generated from waste is used as thermal fuel.
[0008]
Japanese Patent Application Laid-Open No. 9-243044 discloses a technique for melting coal combustion ash using carbide as an auxiliary fuel.
[0009]
Furthermore, Japanese Patent Application Laid-Open No. 2-122109 discloses a technique for melting municipal waste incineration ash using a carbonized material as an auxiliary fuel.
[0010]
[Problems to be solved by the invention]
Among the above-described conventional techniques, the techniques disclosed in Japanese Patent Application Laid-Open Nos. 2000-283429 and 2000-283433 merely use the carbide generated from the waste as a fuel for a boiler and the like. It is not recognized that it is used for melting and volume reduction processing of coal combustion ash discharged in large quantities.
[0011]
Japanese Patent Laid-Open No. 9-243044 discloses a technique for melting coal combustion ash using carbide as a supplementary fuel. However, it is recognized that coal combustion ash is melted using carbide generated from waste as fuel. It has not been.
[0012]
Furthermore, the technique described in Japanese Patent Laid-Open No. 2-122109 is to melt municipal waste incineration ash using carbonized material as a supplementary fuel, and uses carbide generated from waste itself including municipal waste as fuel. The point of melting coal combustion ash is not recognized.
[0013]
By the way, in order to melt coal combustion ash as disclosed in JP-A-10-1339 and JP-A-10-81398, the inside of the melting furnace must have a melting point of ash or higher, that is, about 1200 to 2500 ° C or higher. . However, when the melting furnace is operated in such a high temperature state, there are problems such that the amount of heat input (fuel amount) increases and the furnace body is exposed to severe thermal conditions and damage is accelerated.
[0014]
Therefore, in order to lower the melting point of coal combustion ash, a technique for mixing and melting the coal combustion ash with an additive is disclosed in Japanese Patent Laid-Open No. 9-210338. According to this method, since the temperature in the ash melting furnace can be lowered, the above-mentioned problems can be avoided. However, it becomes necessary to purchase additives and fuel for melting coal-burning ash, which increases the cost of ash treatment.
[0015]
An object of the present invention is to realize a volume reduction process by melting coal combustion ash discharged in large quantities from a power plant at low cost.
[0016]
[Means for Solving the Problems]
The problem is that when the coal combustion ash in the exhaust gas discharged from the pulverized coal furnace is melted in the ash melting furnace to generate molten slag, the carbide generated from the waste is used as the fuel (or the carbide generated from the waste). Is achieved by melting coal ash with coal and coal as fuel.
[0017]
DETAILED DESCRIPTION OF THE INVENTION
Embodiments of the present invention will be described below with reference to the accompanying drawings. However, the present invention is not limited to the examples.
Example 1
An embodiment of the present invention is shown in FIG.
[0018]
Coal 1 is transported from the coal yard to a coal pulverizer 9 by a coal handling facility and crushed. The pulverized coal is supplied by a coal feeder to a coal conveyance pipe 10 in which coal conveyance air flows. Coal is supplied to a burner 7 provided in the furnace 6 and burns in the furnace 6.
[0019]
The air blower 18 supplies combustion air to the burner 7. Combustion air from the air blower 18 is heated by the air residual heater 14, passes through the air pipe 19, and travels toward the burner 7. The combustion air is heated to about 300 ° C., contributes to the combustion of the coal without cooling the furnace 6 and stably burns the coal.
[0020]
The coal combustion gas heats the wall surface of the furnace 6, and the denitration device 13 while heating a superheater, a reheater installed in the downstream side of the furnace 6, a economizer such as an air after-heater (both not shown). Head for. NOx in the exhaust gas is removed by the denitration device 13 so as to be below the regulation value. Downstream of the denitration device 13, there is an air residual heater 14 that warms the combustion air using the residual heat of the exhaust gas. Further, the exhaust gas is dedusted from fly ash in the exhaust gas by a dust collector 15 located downstream of the air residual heater 14 and enters a desulfurizer 16. The exhaust gas is removed from the sulfur oxide by the desulfurization device 16 to become clean exhaust gas, and is discharged from the chimney 17.
[0021]
The fly ash 3 collected at the front stage of the dust collector 15 and the bottom ash 2 collected by the furnace 6 are supplied to the ash melting furnace 28. The fly ash 4 collected at the front stage of the dust collector 15 has a small particle size and a small amount of unburned matter, and can be used as a cement material. For this reason, no treatment is performed in the ash melting furnace 28.
[0022]
As the fuel of the ash melting furnace 28, it is preferable to use a material obtained by carbonizing waste and removing foreign matters in the carbide, or a product obtained by carbonizing the waste and removing foreign matters in the carbide and mixing with coal.
[0023]
The reason for using the former is that the waste generated at the power plant can be used as fuel, and the fuel cost can be reduced. Also, the melting temperature of coal combustion ash is as high as about 1200 ° C. to 2500 ° C., and the melting point of coal combustion ash can be lowered by mixing a carbide having a low melting point. Thereby, even if the temperature in the furnace of the ash melting furnace 28 is about 1200-1800 degreeC, ash can be fuse | melted. Furthermore, the energy required to heat the ash melting furnace 28 is reduced as compared with the case where only coal is used as fuel. On the other hand, the reason for using the latter is that coal has an effect of keeping the combustion state constant by adding coal, since the calorific value is more stable than that of carbide.
[0024]
Thus, volume reduction processing by melting of coal combustion ash discharged in large quantities from the power plant can be realized at low cost by using carbide generated from waste as fuel.
[0025]
In addition, when coal and coal generated from waste are mixed and coal combustion ash is melted using this mixture as fuel, the carbide mixed with coal lowers the melting point of coal combustion ash, thus reducing the energy required for melting. .
[0026]
As described above, the carbide may be generated by using the waste in the power plant, but it is also possible to collect and use garbage such as ordinary households or industrial waste. Since the waste is used as the fuel for the ash melting 28, the fuel cost of the ash melting process can be reduced. Moreover, since the carbide | carbonized_material discharged | emitted from the carbonization apparatus is mixed with a metal etc., it isolate | separates from a carbide | carbonized_material with a selector.
[0027]
In FIG. 1, carbides generated from waste and coal 1 are pulverized by a pulverizer 20 and supplied to a burner of an ash melting furnace 28. The particle size is adjusted as necessary. In FIG. 1, carbide and coal 1 are charged into the hopper 22 and pulverizer 20. However, as shown in FIG. 2, coal 1 is charged into the hopper 22 and pulverizer 20, and the carbide is pulverized exclusively for carbide. It may be pulverized in advance by the vessel 29 and supplied directly to the fuel supply pipe 23.
[0028]
The combustion air in the ash melting furnace 28 is warmed as necessary, and is supplied to the air nozzle through the air conveyance pipe 21.
[0029]
When coal combustion ash is introduced into a high-temperature gas atmosphere, the coal combustion ash is melted and recovered as slag. The slag is discharged from the ash melting furnace 28 and then cooled by a cooling device. The cooled slag 5 has a wide range of uses as a roadbed material. Also, when landfilling, the volume of coal combustion ash can be greatly reduced, leading to space saving at the final disposal site.
[0030]
However, since the exhaust gas of the ash melting furnace 28 contains harmful substances such as NOx and SOx, it is returned to the outlet of the furnace 6 and discharged through the denitration device 13 and the desulfurization device 16. FIG. 1 shows an example in which the combustion exhaust gas from the ash melting furnace 28 is introduced between the furnace 6 and the denitration apparatus 13. Here, it must be considered that the combustion exhaust gas discharged from the ash melting furnace 28 contains dioxins due to the presence of chlorine contained in the carbide. On the other hand, if exhaust gas is input to the upstream side of the denitration device 13, dioxins in the combustion exhaust gas are oxidized and decomposed in the denitration device 13 (Chemical Engineering 64 (3) 128-130 (2000)). It must be considered that the fly ash in the exhaust gas also contains dioxin, but this is recovered by the dust collector 15 installed downstream. This ensures that dioxins emitted from the power plant are below the environmental regulations. Further, since the exhaust gas is introduced downstream of the furnace 6, there is no need to change the structure of the furnace 6 itself.
[0031]
According to the present embodiment, dioxins generated in the ash melting furnace 28 can be recovered by the denitration device 13 and the dust collector 15.
(Example 2)
An example in which the combustion exhaust gas from the ash melting furnace 28 is introduced into the furnace bottom of the furnace 6 will be described with reference to FIG. In the conventional pulverized coal furnace, the temperature in the vicinity of the lowermost burner installed in the furnace 6 is lower than that of the other downstream burners, so the ignitability of coal is poor. In particular, when the load is low, the temperature in the furnace is lowered, and ignition is more difficult. On the other hand, the temperature of the combustion exhaust gas from the ash melting furnace 28 is as high as about 1000 to 2000 ° C. at the outlet of the ash melting furnace. When this gas is introduced into the furnace 6 at a high temperature, the temperature at the bottom of the furnace rises, and the ignition performance of coal is improved. Conventionally, the temperature of the gas charged into the furnace bottom is about 300 to 400 ° C., so the temperature of the combustion exhaust gas only needs to be higher.
[0032]
According to the present embodiment, the dioxins generated in the ash melting furnace 28 can be decomposed again by high-temperature combustion in the furnace 6.
(Example 3)
An example provided with a desalting apparatus for removing chlorine contained in carbide will be described with reference to FIG. In the figure, the combustion exhaust gas from the ash melting furnace 28 is input between the furnace 6 and the denitration apparatus 13, but may be input to the bottom of the furnace 6 as in the second embodiment.
[0033]
Since the waste contains chlorine, dioxins and hydrogen chloride are generated when the carbide generated in the carbonizer is burned. However, if chlorine is removed from the carbide in advance using a desalting apparatus, the amount of dioxins and hydrogen chloride generated by combustion in the ash melting furnace 28 is reduced. If the amount of hydrogen chloride generated is small, the problem of chlorine corrosion that occurs in cooling pipes downstream of the ash melting furnace is eliminated.
Example 4
An example of using carbide generated outside the power plant will be described with reference to FIG.
[0034]
In the figure, the combustion exhaust gas from the ash melting furnace 28 is input between the furnace 6 and the denitration apparatus 13, but may be input to the bottom of the furnace 6 as in the second embodiment. In the figure, the desalted carbide is supplied. However, if the dioxin generated by the presence of chloride can be sufficiently decomposed during the combustion of the waste, the desalting apparatus is not necessarily required.
[0035]
If you purchase carbide produced by local governments and use it as fuel, you can save space because you don't have to own a carbonization device in the power plant. Equipment such as waste carbonization equipment is not required and equipment costs can be reduced. In addition, there is an advantage that the carbide can be supplied stably compared to the case where the carbide is provided only within the power plant.
(Example 5)
An example in which a waste heat recovery boiler 30 that recovers waste heat from the ash melting furnace 28 and a power generation device 25 that drives the steam turbine 24 with the waste heat recovery boiler 30 to generate power is installed in the ash melting furnace 28 will be described with reference to FIG. .
[0036]
Since the combustion exhaust gas from the ash melting furnace 28 is as high as about 1000 to 2000 ° C., a waste heat recovery boiler 30 is attached downstream of the ash melting furnace 28 and the steam turbine 24 is driven to generate power. The electricity generated in the waste heat recovery boiler 30 can be used as power for the ash melting furnace system. After the heat recovery, the combustion exhaust gas is further exchanged with the combustion air of the ash melting furnace 28, and the fly ash in the combustion gas is recovered by the dust collector 26 and then released from the chimney 27 to the atmosphere.
[0037]
According to the present embodiment, the ash can be melted without changing the existing boiler system. Further, the electricity generated in the waste heat recovery boiler 30 can be used as power for the ash melting furnace system.
[0038]
【The invention's effect】
ADVANTAGE OF THE INVENTION According to this invention, the volume reduction process by melting of coal combustion ash discharged | emitted in large quantities from a power plant can be implement | achieved at low cost by using the carbide | carbonized_material produced | generated from the waste as a fuel.
[Brief description of the drawings]
FIG. 1 is a system diagram of a pulverized coal furnace showing an embodiment of the present invention.
FIG. 2 is a view showing an example in which a transportation pipe to a carbide ash melting furnace is changed.
FIG. 3 is a system diagram of a pulverized coal furnace showing an example in which combustion exhaust gas from an ash melting furnace is charged into the furnace bottom of the furnace.
FIG. 4 is a system diagram of a pulverized coal furnace showing an example provided with a desalting apparatus.
FIG. 5 is a system diagram of a pulverized coal furnace showing an example in which carbide generated outside a power plant is used.
FIG. 6 is a system diagram of a pulverized coal furnace showing an example in which a waste heat recovery boiler that recovers waste heat of an ash melting furnace and a power generation device that generates power by driving a steam turbine with the waste heat recovery boiler are installed in the ash melting furnace It is.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 ... Coal, 2 ... Bottom ash, 3 ... Fly ash collect | recovered in the front | former stage of the dust collector 15, 4 ... Fly ash collect | recovered in the back | latter stage of the dust collector 15, 5 ... Decooled slag, 6 ... Furnace, 7 ... Burner, 8 ... Hopper, 9 ... Crusher, 10 ... Coal conveying pipe, 11 ... GR port, 12 ... Cyclone, 13 ... Denitration device, 14 ... Air heat exchanger, 15 ... Dust collector, 16 ... Desulfurization device, 17 DESCRIPTION OF SYMBOLS ... Chimney, 18 ... Blower, 19 ... Air conveyance pipe, 20 ... Crusher, 21 ... Air conveyance pipe, 22 ... Hopper, 23 ... Carbide supply piping, 24 ... Turbine, 25 ... Generator, 26 ... Dust collector, 27 ... chimney, 28 ... ash melting furnace, 29 ... pulverizer, 30 ... waste heat recovery boiler.

Claims (11)

微粉炭火炉から排出される排ガス中の石炭燃焼灰を灰溶融炉で溶融して溶融スラグを生成する石炭燃焼灰の溶融方法において、
廃棄物から生成した炭化物を燃料として石炭燃焼灰を溶融することを特徴とする石炭燃焼灰の溶融方法。
In the method for melting coal combustion ash, in which coal combustion ash in the exhaust gas discharged from the pulverized coal furnace is melted in an ash melting furnace to produce molten slag,
A method for melting coal combustion ash, comprising melting coal combustion ash using carbide generated from waste as fuel.
微粉炭火炉から排出される排ガス中の石炭燃焼灰を灰溶融炉で溶融して溶融スラグを生成する石炭燃焼灰の溶融方法において、
廃棄物から生成した炭化物と石炭を混合し、この混合物を燃料として石炭燃焼灰を溶融することを特徴とする石炭燃焼灰の溶融方法。
In the method for melting coal combustion ash, in which coal combustion ash in the exhaust gas discharged from the pulverized coal furnace is melted in an ash melting furnace to produce molten slag,
A method for melting coal combustion ash, comprising mixing carbon generated from waste and coal and melting coal combustion ash using the mixture as fuel.
請求項1または2において、石炭燃焼灰を溶融する燃料として、発電所外で廃棄物から生成した炭化物を使用することを特徴とする石炭燃焼灰の溶融方法。3. The method for melting coal combustion ash according to claim 1, wherein a carbide generated from waste outside the power plant is used as a fuel for melting the coal combustion ash. 微粉炭火炉から排出される排ガス中の石炭燃焼灰を集塵する集塵器と、前記集塵器で回収した石炭燃焼灰を灰溶融炉に供給する搬送系と、前記搬送系から供給された石炭燃焼灰を溶融して溶融スラグを生成する灰溶融炉を有する石炭燃焼灰の溶融処理システムにおいて、
廃棄物を炭化する炭化装置を備え、廃棄物から生成した前記炭化物を燃料として石炭燃焼灰を溶融する工程を有することを特徴とする石炭燃焼灰の溶融処理システム。
A dust collector that collects coal combustion ash in the exhaust gas discharged from the pulverized coal furnace, a transport system that supplies the coal combustion ash collected by the dust collector to the ash melting furnace, and a power supply that is supplied from the transport system In a coal combustion ash melting treatment system having an ash melting furnace that melts coal combustion ash to produce molten slag,
A coal combustion ash melting treatment system comprising a carbonization device for carbonizing waste, and having a step of melting coal combustion ash using the carbide generated from the waste as a fuel.
微粉炭火炉から排出される排ガス中の石炭燃焼灰を集塵する集塵器と、前記集塵器で回収した石炭燃焼灰を灰溶融炉に供給する搬送系と、前記搬送系から供給された石炭燃焼灰を溶融して溶融スラグを生成する灰溶融炉を有する石炭燃焼灰の溶融処理システムにおいて、
廃棄物を炭化する炭化装置を備え、廃棄物から生成した炭化物と石炭を混合し、この混合物を燃料として石炭燃焼灰を溶融する工程を有することを特徴とする石炭燃焼灰の溶融処理システム。
A dust collector that collects coal combustion ash in the exhaust gas discharged from the pulverized coal furnace, a transport system that supplies the coal combustion ash collected by the dust collector to the ash melting furnace, and a power supply that is supplied from the transport system In a coal combustion ash melting treatment system having an ash melting furnace that melts coal combustion ash to produce molten slag,
A coal combustion ash melting treatment system comprising: a carbonization device for carbonizing waste, and mixing carbonized coal generated from the waste with coal, and melting the coal combustion ash using the mixture as a fuel.
請求項4または5において、灰溶融炉から発生した燃焼排ガスを微粉炭火炉と脱硝装置の間に投入する配管を備えたことを特徴とする石炭燃焼灰の溶融処理システム。6. The coal combustion ash melting treatment system according to claim 4 or 5, further comprising a pipe for introducing the combustion exhaust gas generated from the ash melting furnace between the pulverized coal furnace and the denitration device. 請求項4〜6のいずれか1項において、灰溶融炉から発生した燃焼排ガスを微粉炭火炉の炉底に投入する配管を備えたことを特徴とする石炭燃焼灰の溶融処理システム。The coal combustion ash melting treatment system according to any one of claims 4 to 6, further comprising a pipe for introducing the combustion exhaust gas generated from the ash melting furnace to the bottom of the pulverized coal fired furnace. 請求項4〜7のいずれか1項において、炭化物に含まれる塩素分を除去する脱塩装置を備えたことを特徴とする石炭燃焼灰の溶融処理システム。8. The coal combustion ash melting treatment system according to any one of claims 4 to 7, further comprising a desalting apparatus that removes chlorine contained in the carbide. 請求項4〜8のいずれか1項において、石炭燃焼灰を溶融する燃料として、発電所外で廃棄物から生成した炭化物を使用することを特徴とする石炭燃焼灰の溶融処理システム。The coal combustion ash melting treatment system according to any one of claims 4 to 8, wherein a carbide generated from waste outside the power plant is used as a fuel for melting the coal combustion ash. 請求項4,5,8,9のいずれか1項において、灰溶融炉の廃熱を回収する廃熱回収ボイラと、前記廃熱回収ボイラで蒸気タービンを駆動して発電する発電装置と、前記灰溶融炉の排ガス中の飛灰を回収する集塵装置と、前記集塵装置で飛灰を回収した後の排ガスを大気中に放出する煙突を備えたことを特徴とする石炭燃焼灰の溶融処理システム。The waste heat recovery boiler that recovers waste heat of the ash melting furnace, a power generation device that drives a steam turbine with the waste heat recovery boiler to generate electric power, according to any one of claims 4, 5, 8, and 9, Coal combustion ash melting characterized by comprising a dust collector that collects fly ash in the exhaust gas of an ash melting furnace, and a chimney that releases the exhaust gas after the fly ash is collected by the dust collector into the atmosphere Processing system. 請求項4〜10のいずれか1項に記載の溶融処理システムを備えた微粉炭火力発電所。A pulverized coal-fired power plant comprising the melt treatment system according to any one of claims 4 to 10.
JP2001156331A 2001-05-25 2001-05-25 Coal combustion ash melting method and melt processing system Expired - Fee Related JP4652609B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001156331A JP4652609B2 (en) 2001-05-25 2001-05-25 Coal combustion ash melting method and melt processing system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001156331A JP4652609B2 (en) 2001-05-25 2001-05-25 Coal combustion ash melting method and melt processing system

Publications (2)

Publication Number Publication Date
JP2002349834A JP2002349834A (en) 2002-12-04
JP4652609B2 true JP4652609B2 (en) 2011-03-16

Family

ID=19000353

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001156331A Expired - Fee Related JP4652609B2 (en) 2001-05-25 2001-05-25 Coal combustion ash melting method and melt processing system

Country Status (1)

Country Link
JP (1) JP4652609B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110887049A (en) * 2019-11-22 2020-03-17 深圳市群卜鸿科技有限公司 A burn burning furnace that is used for refuse treatment to throw material safety
CN113020229A (en) * 2021-05-27 2021-06-25 中国恩菲工程技术有限公司 Fly ash sulfur fixation melting harmless treatment method

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4472380B2 (en) * 2004-02-27 2010-06-02 住友大阪セメント株式会社 Method and apparatus for producing biomass semi-carbonized fuel
JP4711865B2 (en) * 2006-03-24 2011-06-29 中国電力株式会社 Elution inhibitor purchasing system
CN100445352C (en) * 2006-06-24 2008-12-24 中国科学院山西煤炭化学研究所 A method for preparing fuel gas by co-gasification of biomass and coal fluidized bed
CN105042600B (en) * 2015-07-07 2017-08-04 义马环保电力有限公司 Treatment methods of heavy metals and dioxins in garbage power plant ash and medical incineration ash
CN112207115B (en) * 2020-09-22 2022-04-08 武汉科技大学 A process for co-processing medical waste using hot flue gas low-temperature pyrolysis dechlorination and upgrading coupled with cement kiln
CN114685054B (en) * 2020-12-30 2024-04-19 北京科立科盈科技有限公司 Method for preparing basalt fiber by using gas slag
CN217715435U (en) * 2022-05-06 2022-11-01 天津大学滨海工业研究院有限公司 Environment-friendly coal boiler
CN115138658A (en) * 2022-07-21 2022-10-04 北京中科润宇环保科技股份有限公司 Harmless reduction method and device for fly ash of waste incineration power plant

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0824902B2 (en) * 1985-11-25 1996-03-13 三菱重工業株式会社 Fly ash processing equipment
JPH10148307A (en) * 1996-11-20 1998-06-02 Ishikawajima Harima Heavy Ind Co Ltd Boiler exhaust gas recirculation system
JP2000274646A (en) * 1999-03-24 2000-10-03 Nkk Plant Engineering Corp Melting method for coal ash and fly ash of refuse incineration
JP2000283433A (en) * 1999-03-31 2000-10-13 Ishikawajima Harima Heavy Ind Co Ltd Waste treatment method and waste treatment system
JP2000283437A (en) * 1999-03-31 2000-10-13 Ishikawajima Harima Heavy Ind Co Ltd Waste treatment method and waste treatment system

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110887049A (en) * 2019-11-22 2020-03-17 深圳市群卜鸿科技有限公司 A burn burning furnace that is used for refuse treatment to throw material safety
CN110887049B (en) * 2019-11-22 2021-11-09 深圳市群卜鸿科技有限公司 A burn burning furnace that is used for refuse treatment to throw material safety
CN113020229A (en) * 2021-05-27 2021-06-25 中国恩菲工程技术有限公司 Fly ash sulfur fixation melting harmless treatment method

Also Published As

Publication number Publication date
JP2002349834A (en) 2002-12-04

Similar Documents

Publication Publication Date Title
KR100770797B1 (en) Methods and processes for co-burning in energy recovery waste treatment plants
EP0767343A2 (en) Heat recovery system and power generation system
JP4652609B2 (en) Coal combustion ash melting method and melt processing system
CN111895424A (en) A coupling power generation system for garbage disposal and generator set
JP5963239B2 (en) Coal gasification facility and coal gasification power generation system
CN113915619A (en) Waste fan blade treatment device for rotary kiln and plasma melting furnace
JP3964043B2 (en) Waste disposal method
CN110822441A (en) Efficient low-pollution combustion system of cyclone melting furnace for co-combustion of urban solid wastes
CN112143530A (en) Environment-friendly and efficient coupling power generation system and method for refuse derived fuel gasification and large coal-fired unit
KR101153930B1 (en) The method and system to burn petroleum coke
KR101309279B1 (en) All fluidize bed that phlogiston device and produce steam resource
JPH0849822A (en) Waste treatment device and method
JP3707754B2 (en) Waste treatment system and method and cement produced thereby
JP2740644B2 (en) Ash melting apparatus and method
JP3048968B2 (en) Waste treatment method using waste plastic gasification and ash melting
JP4089079B2 (en) Waste treatment method and waste treatment system
CN212362044U (en) Garbage disposal and generator set coupling power generation system
JP3732640B2 (en) Waste pyrolysis melting combustion equipment
JP2977784B2 (en) Power generation method using waste plastic gasification and ash melting
JP4264862B2 (en) A pulverized coal boiler, its operating method, and a modification method of a pulverized coal boiler
KR100387732B1 (en) Circulation Fluidized Bed Boiler System Mounted with Pelletizer for Anthracite
JP4161462B2 (en) Waste treatment method and waste treatment system
JP2003294205A (en) Coal-fired boiler, organic waste gasifier and coal ash treatment plant
JP4089080B2 (en) Waste treatment method and waste treatment system
CN115789662B (en) A waste pyrolysis gasification coupled cyclone furnace co-firing system and method

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20080515

RD02 Notification of acceptance of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7422

Effective date: 20080515

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20101202

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: 20101214

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

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20101216

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

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

Free format text: PAYMENT UNTIL: 20131224

Year of fee payment: 3

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313117

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

Free format text: PAYMENT UNTIL: 20131224

Year of fee payment: 3

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313111

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

LAPS Cancellation because of no payment of annual fees