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JPS6257888B2 - - Google Patents
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JPS6257888B2 - - Google Patents

Info

Publication number
JPS6257888B2
JPS6257888B2 JP53110712A JP11071278A JPS6257888B2 JP S6257888 B2 JPS6257888 B2 JP S6257888B2 JP 53110712 A JP53110712 A JP 53110712A JP 11071278 A JP11071278 A JP 11071278A JP S6257888 B2 JPS6257888 B2 JP S6257888B2
Authority
JP
Japan
Prior art keywords
temperature
fluidized bed
furnace
combustion
exhaust gas
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
Application number
JP53110712A
Other languages
Japanese (ja)
Other versions
JPS5538418A (en
Inventor
Toshio Uemura
Yoshiki Watabe
Toshiki Furue
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.)
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
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 filed Critical Babcock Hitachi KK
Priority to JP11071278A priority Critical patent/JPS5538418A/en
Publication of JPS5538418A publication Critical patent/JPS5538418A/en
Publication of JPS6257888B2 publication Critical patent/JPS6257888B2/ja
Granted legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/50Control or safety arrangements

Landscapes

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Incineration Of Waste (AREA)
  • Fluidized-Bed Combustion And Resonant Combustion (AREA)
  • Gasification And Melting Of Waste (AREA)

Description

【発明の詳細な説明】 〈産業上の利用分野〉 この発明は発電所のボイラ等で重油、原油を燃
焼させたときの排ガス流路に設けた集塵装置で捕
集した重原油灰(以下EP灰と称す。)を焼却する
流動層燃焼炉の運転方法に関する。
[Detailed Description of the Invention] <Industrial Application Field> This invention uses heavy crude oil ash (hereinafter referred to as This paper relates to a method of operating a fluidized bed combustion furnace for incinerating EP ash.

〈従来の技術及びその問題点〉 近時発電所等のボイラにおいては排ガス中の窒
素酸化物(以下NOxと称す)を低減させるため
にする二段燃焼方法その他の低O2燃焼手段によ
る未燃カーボン量の増大と、またNOxや硫黄酸
化物(SOx)の除去のためにする還元剤、例えば
アンモニア(NH3)の噴霧供給による硫安
〔(NH42SO4〕の量の増大の問題を生じている。従
つてアンモニア成分含有低融点溶融物(その例と
しEP灰を例にする)を焼却炉で焼却処理する必
要があるが、その際硫安が分解の過程で溶融し流
動層炉の場合には流動媒体や炉壁に付着し炉の運
転上の種々の困難な問題を生じている。また炉の
運転条件によつてはNH3の酸化によりNOxを生じ
その処理をせねばならないという問題がある。ま
たこれに加えて系統出口の排ガス中の亜硫酸ガス
がその露点以下(例えば120℃以下)になると結
露によるダクト材料の腐蝕という問題があり炉排
ガス温度はほぼ500℃以上にするという運転がさ
れていた。しかしこの温度では排ガス中に含まれ
る未燃カーボンが排ガスダクトや集塵装置内で赤
熱の状態にある所謂「おき燃焼」(「燠燃焼」)を
し焼損事故を生ずるという問題が生じた。
<Conventional technology and its problems> Recently, in the boilers of power plants, etc., two-stage combustion methods and other low O 2 combustion methods are used to reduce nitrogen oxides (hereinafter referred to as NOx) in the exhaust gas. The problem of increasing the amount of carbon and also increasing the amount of ammonium sulfate [(NH 4 ) 2 SO 4 ] due to the spray supply of reducing agents such as ammonia (NH 3 ) to remove NOx and sulfur oxides (SOx). is occurring. Therefore, it is necessary to incinerate low-melting-point molten materials containing ammonia components (EP ash is an example of this), but at that time, ammonium sulfate melts during the decomposition process, and in the case of a fluidized bed furnace, it becomes fluid. It adheres to the media and the furnace walls, causing various difficult problems in the operation of the furnace. Furthermore, depending on the operating conditions of the furnace, there is a problem in that NOx is generated due to oxidation of NH 3 and must be disposed of. In addition to this, if the sulfur dioxide gas in the exhaust gas at the system outlet falls below its dew point (for example, below 120°C), there is a problem of corrosion of the duct material due to condensation, so the furnace exhaust gas temperature is operated at approximately 500°C or higher. Ta. However, at this temperature, a problem arose in that the unburned carbon contained in the exhaust gas was in a red-hot state in the exhaust gas duct or dust collector, so-called ``open combustion'' (``burnt combustion''), resulting in a burnout accident.

〈発明の目的〉 この発明は第1の問題の低融点溶融物の付着
NH3分解によるNOx発生を解決するとともに第2
の問題である「おき燃焼」を解決する運転方法を
提案することを目的とする。
<Object of the invention> This invention solves the first problem of adhesion of low melting point melts.
In addition to solving the NOx generation caused by NH3 decomposition,
The purpose of this project is to propose an operating method that solves the problem of "open combustion."

〈手段の概要〉 要するにこの発明は、流動層焼却炉で低融点含
有物を燃焼する方法において、空塔部温度を流動
層より高い温度にし炉出口付近で冷却水噴霧する
流動層焼却炉運転方法であることを特徴とする。
<Summary of the Means> In short, the present invention provides a method for operating a fluidized bed incinerator in which the temperature of the empty column is made higher than that of the fluidized bed and cooling water is sprayed near the furnace outlet in a method of burning low-melting-point containing materials in a fluidized bed incinerator. It is characterized by

〈実施例〉 まず前記第1の問題を解決する流動層焼却炉の
運転方法について説明する。第1図において、流
動層焼却炉1は下部に燃焼用と流動用空気を供給
する空気室2をもち、多孔板3上には砂等の流動
媒体4が収容され、流動用空気により流動層5を
形成する。この流動層は図示しない起動バーナに
より加熱され一定温度に達したときEP灰を収容
するホツパ6からフイーダ(ロータリフイーダ
等)7、シユート8、ノズル8aを経由してEP
灰が流動層内に供給される。また助燃バーナ9と
空塔部バーナ10が夫々複数本設けられ、流動層
内温度をほぼ580〜600℃、流動層上面空塔部温度
を層内温度より高く保持し、EP灰中に含まれる
硫安分解によるNH3が酸化されNOx(窒素酸化
物)が発生してもこれを気相還元して無害なN2
にする。
<Example> First, a method of operating a fluidized bed incinerator that solves the first problem will be described. In Fig. 1, a fluidized bed incinerator 1 has an air chamber 2 at the bottom that supplies combustion and fluidizing air, and a fluidized medium 4 such as sand is stored on a perforated plate 3, and the fluidized bed is heated by the fluidizing air. form 5. This fluidized bed is heated by a starting burner (not shown), and when it reaches a certain temperature, the EP ash is passed from a hopper 6 that accommodates the EP ash via a feeder (rotary feeder, etc.) 7, a chute 8, and a nozzle 8a.
Ash is fed into the fluidized bed. In addition, a plurality of auxiliary combustion burners 9 and a plurality of empty column burners 10 are provided, and the temperature inside the fluidized bed is maintained at approximately 580 to 600°C, and the temperature of the upper surface of the fluidized bed in the empty column is maintained higher than the temperature inside the bed. Even if NH 3 is oxidized by ammonium sulfate decomposition and NOx (nitrogen oxides) is generated, this is reduced in the gas phase and converted into harmless N 2
Make it.

このような流動層焼却炉でEP灰を焼却すると
き上記の温度制御を適切にするため流動層の温度
を検知し信号を出す温度発信器11と空塔部の温
度を計測し信号を出す温度発信器12とが流動層
焼却炉の炉壁に設けられ、これらの信号は制御箱
13に送られる。制御箱13は前記の温度信号を
受け、記憶装置により各制御弁の開度、EP灰の
供給量の制御をする。制御指令はホツパ6、フイ
ーダ7、シユート8、ノズル8aよりなるEP灰
の供給装置にあつてはフイーダ7の駆動用モータ
に出される。燃料の供給については空塔バーナ1
0の制御弁15、助燃バーナについては制御弁1
6に指令が出され、施回噴流用空気については制
御弁17、主供給空気量についてはダンパ18に
制御指令が出される。
When incinerating EP ash in such a fluidized bed incinerator, in order to appropriately control the temperature described above, there is a temperature transmitter 11 that detects the temperature of the fluidized bed and outputs a signal, and a temperature transmitter 11 that measures the temperature of the empty column and outputs a signal. A transmitter 12 is provided on the wall of the fluidized bed incinerator, and these signals are sent to a control box 13. The control box 13 receives the temperature signal and controls the opening degree of each control valve and the supply amount of EP ash using a storage device. Control commands are issued to the drive motor of the feeder 7 in the case of the EP ash supply device consisting of the hopper 6, feeder 7, chute 8, and nozzle 8a. For fuel supply, empty tower burner 1
0 control valve 15, control valve 1 for the auxiliary burner
6, a control command is issued to the control valve 17 regarding the circulating jet air, and a control command is issued to the damper 18 regarding the main supply air amount.

また不活性ガスを管路19、制御弁20、より
ミキサ21に供給するときには制御弁20に制御
箱13より制御指令が出される。
Further, when inert gas is supplied to the mixer 21 through the conduit 19 and the control valve 20, a control command is issued to the control valve 20 from the control box 13.

この発明はこのような第1の問題を解決する前
記第1図の装置につきさらに冷却水を噴霧して炉
出口の排ガスを冷却する運転方法を提案するもの
である。「おき燃焼」を防止するために必要とす
る排ガス温度条件は実験によりほぼ350〜450℃で
あることが確められた。第2図はこの発明の実施
にかかる装置の構造を示すものである。第1図の
従来の装置に加えて、排ガス出口部に温度発信器
22を設けその計測した温度の信号は制御箱13
に送られる。この信号は排ガス温度自体のほか、
上昇率、下降率(dT/dt)を含むものでそれら
が計器に分離表示可能なものとして制御箱13に
送られる。これは流動層炉が温度変化が鈍いこと
よりしてdT/dt信号(T=温度t=時間)によ
り各燃料、空気、EP灰の供給量を制御箱13で
記憶により予測をし指令信号とし各制御弁15,
16,17a,20、ダンパ18、ロータリフイ
ーダ7に送りこれ等を制御するものである。同時
に水噴射ノズル23へ冷却噴霧水を供給する流量
制御弁24を制御するものである。なお温度発信
器22は排ガス出口の後流ダクト内でかつ最初の
集じん機例えばシングルサイクロンの入口のガス
温度を計測してもよい。これは冷却水と排ガスの
混合が充分でないと計測される排ガス出口の温度
よりもより後流の方がその測定温度(排ガス)に
ついて変動少なく信頼性が高いとする考えによる
ものである。
This invention proposes an operating method for the apparatus shown in FIG. 1 which solves the first problem, in which cooling water is further sprayed to cool the exhaust gas at the furnace outlet. Experiments have confirmed that the exhaust gas temperature required to prevent "burning" is approximately 350-450°C. FIG. 2 shows the structure of an apparatus according to the present invention. In addition to the conventional device shown in FIG.
sent to. In addition to the exhaust gas temperature itself, this signal
It includes the rate of rise and rate of fall (dT/dt), and is sent to the control box 13 as a display that can be displayed separately on the meter. This is because the fluidized bed furnace has a slow temperature change, so the control box 13 predicts the supply amount of each fuel, air, and EP ash using the dT/dt signal (T = temperature t = time) and uses it as a command signal. Each control valve 15,
16, 17a, 20, the damper 18, and the rotary feeder 7 to control them. At the same time, the flow rate control valve 24 that supplies cooling spray water to the water injection nozzle 23 is controlled. The temperature transmitter 22 may measure the gas temperature in the wake duct of the exhaust gas outlet and at the inlet of the first dust collector, for example, a single cyclone. This is based on the idea that the measured temperature (exhaust gas) in the downstream stream has less fluctuation and is more reliable than the temperature at the exhaust gas outlet, which is measured when the cooling water and exhaust gas are not sufficiently mixed.

流動層焼却炉の各部の温度を規定するに際し考
慮した温度条件につき、これらを第3図に模式に
示す。すなわち流動層の流動媒体を結合し、流動
を阻害する原因をなくすように酸性硫安の生成を
なくすため、第3図の符号Aで示す流動層内につ
いてはその生成温度270〜380℃より層温を高く
し、瞬時にして硫安を分解しNH3とSO3の生成を
させるようにした。
The temperature conditions considered when defining the temperature of each part of the fluidized bed incinerator are schematically shown in FIG. In other words, in order to combine the fluidized medium in the fluidized bed and eliminate the cause of inhibiting the flow, and to eliminate the formation of acidic ammonium sulfate, the temperature in the fluidized bed indicated by the symbol A in Fig. 3 is lower than the formation temperature of 270 to 380°C. The temperature was increased to instantly decompose ammonium sulfate and generate NH 3 and SO 3 .

酸性硫安(NH4HSO4)の生成について簡単に述
べると、温度270〜380℃の範囲で硫安は下記の分
解をする。
To briefly describe the production of acidic ammonium sulfate (NH 4 HSO 4 ), ammonium sulfate undergoes the following decomposition within the temperature range of 270 to 380°C.

(NH42SO4→NH4HSO4+H2O …(1) この酸性硫安は強い粘着性をもち流動媒体を粘
着し小塊化し流動を阻害する。
(NH 4 ) 2 SO 4 →NH 4 HSO 4 +H 2 O...(1) This acidic ammonium sulfate has strong adhesiveness and sticks to the fluid medium, turning it into small agglomerates and inhibiting flow.

従つて符号Aで示す流動層部を380℃より高い
高温にし下記式に示すように分解し発生するNH3
で発生するNOxを瞬時に気相還元させるように
するものである。
Therefore, the fluidized bed section indicated by symbol A is heated to a high temperature higher than 380°C, and NH 3 is decomposed and generated as shown in the following formula.
This is to instantly reduce the NOx generated in the gas phase.

NH3生成の分解は下式で示される。 The decomposition of NH 3 production is shown by the equation below.

NH4HSO4→NH3+SO3+H2O …(2) また生成NH3は流動層上面近傍で空塔部バーナ
10により発生期の活性の高い状態で所謂気相還
元でNOxと結合これを分解するようにした。な
お参考までに記載するとアンモニア(NH3)の500
〜680℃の範囲での分解反応は下式で示される。
NH 4 HSO 4 →NH 3 +SO 3 +H 2 O...(2) In addition, the generated NH 3 is combined with NOx in the highly active state during the generation stage by the overhead burner 10 near the top of the fluidized bed by so-called gas phase reduction. I tried to disassemble it. For reference, ammonia (NH 3 ) is 500
The decomposition reaction in the range of ~680°C is shown by the following formula.

4NH3+5O2=4NO+6H2O …(3) 2NH3+3O2=2HNO2+2H2O …(4) NH3+2O2=HNO3+H2O …(5) 第3図に符合Bで示す空塔部では特に流動層上
面に近い部分を空塔部バーナ10で加熱し流動層
内部より高いものにし、発生期の状態にある流動
層からの放出されるNOと、(2)式の分解で生じた
NH3とを気相の状態で反応させる気相還元効果を
大なるものとしている。
4NH 3 +5O 2 =4NO+6H 2 O …(3) 2NH 3 +3O 2 =2HNO 2 +2H 2 O …(4) NH 3 +2O 2 =HNO 3 +H 2 O …(5) Empty tower shown by symbol B in Figure 3 In this section, the part near the top of the fluidized bed is heated by the empty column burner 10 to make it higher than the inside of the fluidized bed, and the NO released from the fluidized bed in the nascent state and the NO generated by the decomposition of equation (2) are heated. Ta
It has a great gas phase reduction effect by reacting with NH 3 in the gas phase.

また第3図に示す符合B部では未燃成分の燃焼
に好適な高い温度と反応時間を保持できるよう未
燃成分の反応時間を保持するため空塔部は比較的
背丈の高いものに形成されている。
In addition, in the section B shown in Fig. 3, the empty column is formed to be relatively tall in order to maintain a high temperature and reaction time suitable for combustion of the unburned components. ing.

また第3図符合Cで示す部分では、高温の燃焼
ガスが流れて後流集じん装置内で“おき燃焼”を
しないように350〜450℃に水スプレーで燃焼ガス
を冷却している。この温度は硫酸の生成される約
120℃よりはるかに高い処を選定しておりダクト
を構成する部材の腐食はない。
In addition, in the part indicated by C in FIG. 3, the combustion gas is cooled to 350 to 450° C. with water spray to prevent the high-temperature combustion gas from flowing and causing "burning" in the wake dust collector. This temperature is approximately the temperature at which sulfuric acid is produced.
The temperature is much higher than 120℃, so there will be no corrosion of the components that make up the duct.

〈発明の効果〉 この発明の実施にかかる前記した制御により流
動層内では窒素成分含有材料としての硫安の分解
が充分にされ粘着性成分の発生による流動媒体の
結合による塊の生成が防止され、安定した流動層
燃焼ができ、空塔バーナのある空塔部では気相還
元反応としてのNH3とNOの反応に好適な程度の
高温となりNOx排出はなく、その高温ガスの滞
留時間が確保され未燃成分ガスの燃焼が充分にさ
れ、さらには「おき燃焼」の防止の炉頂部付近で
の水スプレーで排ガスの冷却がされる。これは水
の流体としての比重が高温ガスの比重よりはるか
に大なることからスプレー水が排ガス流れの中心
の高温ガス流れまで進入し気化することによるも
のである。
<Effects of the Invention> Through the above-described control according to the implementation of the present invention, ammonium sulfate as a nitrogen component-containing material is sufficiently decomposed in the fluidized bed, and the formation of lumps due to the bonding of the fluidized medium due to the generation of sticky components is prevented. Stable fluidized bed combustion is possible, and the space section where the space tower burner is located has a high temperature that is suitable for the reaction of NH 3 and NO as a gas phase reduction reaction, and there is no NOx emission, and the residence time of the high temperature gas is ensured. The unburnt component gas is sufficiently combusted, and the exhaust gas is further cooled by water spray near the top of the furnace to prevent "burning". This is because the specific gravity of water as a fluid is much greater than the specific gravity of high-temperature gas, so the spray water enters the high-temperature gas flow at the center of the exhaust gas flow and vaporizes.

すなわちこの発明の実施により、流動層部にお
ける安定したEP灰の焼却とNOx低減をするとと
もに、排ガス出口後流における「おき燃焼」に原
因する各種の焼損事故を防止し、装置の安定した
連続運転が可能となる等種々の効果を奏するもの
である。
In other words, by implementing this invention, it is possible to stably incinerate EP ash in the fluidized bed section and reduce NOx, and also to prevent various burnout accidents caused by "open combustion" in the wake of the exhaust gas outlet, and to ensure stable continuous operation of the equipment. This has various effects such as making it possible to

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は前記した第1の問題を解決する流動層
焼却炉の制御系統と装置の配置を示す図面、第2
図はこの発明の一実施例にかかる装置の配置と制
御系統を示す図面、第3図は符合A,B,Cで示
す装置部分における反応の説明用としての模式の
装置の断面図である。 1……流動層焼却炉、2……空気室、3……多
孔板、4……流動媒体、5……流動層、6……ホ
ツパ、7……フイーダ、8……シユート、8a…
…ノズル、9……助燃バーナ、10……空塔部バ
ーナ、11,12……温度発信器、13……制御
箱、18……ダンパ、15,16,17,20…
…制御弁、19……不活性ガスの管路、21……
ミキサ、22……温度発信器、23……水噴射ノ
ズル、24……流量制御弁。
Figure 1 is a diagram showing the control system and equipment arrangement of a fluidized bed incinerator that solves the first problem mentioned above;
The figure is a drawing showing the arrangement and control system of an apparatus according to an embodiment of the present invention, and FIG. 3 is a schematic sectional view of the apparatus for explaining reactions in the parts of the apparatus indicated by symbols A, B, and C. 1... Fluidized bed incinerator, 2... Air chamber, 3... Perforated plate, 4... Fluidized medium, 5... Fluidized bed, 6... Hopper, 7... Feeder, 8... Chute, 8a...
... Nozzle, 9 ... Assist burner, 10 ... Sky tower burner, 11, 12 ... Temperature transmitter, 13 ... Control box, 18 ... Damper, 15, 16, 17, 20 ...
...Control valve, 19...Inert gas pipe, 21...
Mixer, 22...Temperature transmitter, 23...Water injection nozzle, 24...Flow rate control valve.

Claims (1)

【特許請求の範囲】[Claims] 1 流動層部と、該流動層部上部に位置する空塔
部とを有する流動層燃焼炉でアンモニア成分含有
低融点溶融物が含まれた物質を燃焼する方法にお
いて、前記空塔部で空塔部バーナによる燃焼を行
ないこの空塔部の温度を前記流動層の温度より高
く保持し、炉出口の炉頂部付近に冷却流体を噴霧
して火炉出口排ガス温度をおき燃焼温度以下に保
持して運転をすることを特徴とする流動層焼却炉
運転方法。
1. In a method for burning a substance containing an ammonia component-containing low melting point molten material in a fluidized bed combustion furnace having a fluidized bed section and a hollow column section located above the fluidized bed section, The furnace is operated by performing combustion using a partial burner and maintaining the temperature of the empty column higher than the temperature of the fluidized bed, and by spraying cooling fluid near the top of the furnace at the furnace outlet to raise the temperature of the exhaust gas at the furnace outlet and maintain it below the combustion temperature. A method of operating a fluidized bed incinerator, characterized by:
JP11071278A 1978-09-11 1978-09-11 Peration of fluidized layer incinerator Granted JPS5538418A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11071278A JPS5538418A (en) 1978-09-11 1978-09-11 Peration of fluidized layer incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11071278A JPS5538418A (en) 1978-09-11 1978-09-11 Peration of fluidized layer incinerator

Publications (2)

Publication Number Publication Date
JPS5538418A JPS5538418A (en) 1980-03-17
JPS6257888B2 true JPS6257888B2 (en) 1987-12-03

Family

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Family Applications (1)

Application Number Title Priority Date Filing Date
JP11071278A Granted JPS5538418A (en) 1978-09-11 1978-09-11 Peration of fluidized layer incinerator

Country Status (1)

Country Link
JP (1) JPS5538418A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4628838A (en) * 1980-11-19 1986-12-16 Peabody Engineering Corp. Fluidized bed combustion method

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5943682B2 (en) * 1975-05-14 1984-10-24 バブコツク日立株式会社 Fluidized bed furnace for incineration of low melting point compounds
JPS54100164A (en) * 1978-01-24 1979-08-07 Mitsubishi Heavy Ind Ltd Fluidized combustion furnace

Also Published As

Publication number Publication date
JPS5538418A (en) 1980-03-17

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