JPS63129209A - Utilization of ash of fluidized-bed boiler - Google Patents
Utilization of ash of fluidized-bed boilerInfo
- Publication number
- JPS63129209A JPS63129209A JP27485086A JP27485086A JPS63129209A JP S63129209 A JPS63129209 A JP S63129209A JP 27485086 A JP27485086 A JP 27485086A JP 27485086 A JP27485086 A JP 27485086A JP S63129209 A JPS63129209 A JP S63129209A
- Authority
- JP
- Japan
- Prior art keywords
- ash
- limestone
- granulated
- fluidized bed
- fluidized
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 235000019738 Limestone Nutrition 0.000 claims abstract description 25
- 239000006028 limestone Substances 0.000 claims abstract description 25
- 239000011230 binding agent Substances 0.000 claims abstract description 12
- 238000002485 combustion reaction Methods 0.000 claims abstract description 8
- 239000004449 solid propellant Substances 0.000 claims abstract description 5
- 239000008187 granular material Substances 0.000 claims description 3
- 239000003245 coal Substances 0.000 abstract description 13
- 238000000034 method Methods 0.000 abstract description 7
- 230000000694 effects Effects 0.000 abstract description 6
- 239000002699 waste material Substances 0.000 abstract description 6
- 239000000446 fuel Substances 0.000 abstract description 5
- 239000003921 oil Substances 0.000 abstract description 5
- 239000003350 kerosene Substances 0.000 abstract description 4
- 239000007788 liquid Substances 0.000 abstract description 3
- 239000011280 coal tar Substances 0.000 abstract description 2
- 239000000571 coke Substances 0.000 abstract description 2
- 239000000295 fuel oil Substances 0.000 abstract description 2
- 239000000203 mixture Substances 0.000 abstract description 2
- 239000011295 pitch Substances 0.000 abstract description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 abstract 1
- 235000011941 Tilia x europaea Nutrition 0.000 abstract 1
- 239000004571 lime Substances 0.000 abstract 1
- 239000010721 machine oil Substances 0.000 abstract 1
- 239000002956 ash Substances 0.000 description 31
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 10
- 239000000428 dust Substances 0.000 description 8
- 235000012255 calcium oxide Nutrition 0.000 description 5
- 239000000292 calcium oxide Substances 0.000 description 5
- 238000006477 desulfuration reaction Methods 0.000 description 5
- 230000023556 desulfurization Effects 0.000 description 5
- 238000006243 chemical reaction Methods 0.000 description 4
- 238000005469 granulation Methods 0.000 description 4
- 230000003179 granulation Effects 0.000 description 4
- 239000000843 powder Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- 239000004480 active ingredient Substances 0.000 description 2
- 229910052925 anhydrite Inorganic materials 0.000 description 2
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 238000005192 partition Methods 0.000 description 2
- 235000002918 Fraxinus excelsior Nutrition 0.000 description 1
- 240000003473 Grevillea banksii Species 0.000 description 1
- 241000282485 Vulpes vulpes Species 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 230000003009 desulfurizing effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000001125 extrusion Methods 0.000 description 1
- 230000001771 impaired effect Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000000399 orthopedic effect Effects 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000010913 used oil Substances 0.000 description 1
Landscapes
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
Abstract
Description
【発明の詳細な説明】
〔ti、業主の利用分野〕
本発明は、石炭、コークス等の固体燃料と石灰石とを混
合流動燃焼する流動層ボイラーで発生する灰を回収して
、とれを再び利用する流動わボイラー灰の利用法に関す
る。[Detailed description of the invention] [Ti, field of application for business owners] The present invention is a method for collecting ash generated in a fluidized bed boiler that performs mixed fluidized combustion of solid fuel such as coal or coke and limestone, and reusing the ash. Concerning the use of fluidized boiler ash.
(従来の技術)
一級に、流動層ボイラーは、第1図のように構成されて
いる。第1図において、ボイラ一本体(1)は、隔床板
■によって下方の風室a)と上方の流動vg(41に分
割され、風室a)にはその底部から送a機(5)より送
られる法焼用空気が熱交換器(6)によって昇温されて
空気導管■を介して吹込まれる。流動床(4)には、例
えば、粒状の石炭と石灰石が投入され、風室(3)から
の燃焼用空気によって流@府が形成されつつ燃焼し、そ
の内部に配設されたボイラーチューブにより蒸気を得、
排ガスは、流動床(4)の1一方に接続された煙道(8
)に4かれ、順次、粗集塵機(9)、節炭器(ID、熱
交換器(6)、俳風機0δ、集ゆ機03を通って煙突(
141から大気中に放散される。なお、09は石炭投入
Ha 、Of)は石灰石投入装置をそれぞれ示す。(Prior Art) Firstly, a fluidized bed boiler is constructed as shown in FIG. In Fig. 1, the boiler main body (1) is divided into a lower wind chamber a) and an upper flow chamber vg (41) by a partition plate (■). The temperature of the sent calcining air is raised by the heat exchanger (6) and then blown through the air conduit (2). For example, granular coal and limestone are put into the fluidized bed (4), and burned while forming a flow with the combustion air from the wind chamber (3). get steam,
The exhaust gas is passed through a flue (8) connected to one side of the fluidized bed (4).
), and sequentially passes through the coarse dust collector (9), energy saver (ID), heat exchanger (6), haiku fan 0δ, and collector 03 to the chimney (
141 and is emitted into the atmosphere. Note that 09 indicates a coal charging device, and 09 indicates a limestone charging device.
前記流動床(4)内に石炭と同時に石灰石を投入するの
は、下記式に示すように石炭の燃焼によって光生する有
害なSOxの捕捉と、流動層の形成をよくするためであ
る。The reason why limestone is charged into the fluidized bed (4) at the same time as coal is to improve the capture of harmful SOx produced by combustion of coal and the formation of a fluidized bed, as shown in the following formula.
CacOs −Cao + Cow ・−= (
ItCaO+ SOt + 40* →Ca5O<
・−・−■このような流動層ボイラーで生成する灰(粗
集り機(9)及び集塵機OJから回収されるダスト、流
動床14)底部から回収されるアッシュ)は、セメント
産業等で再利用するには運m費が嵩みすぎ、そのままの
杖歯で埋立地に投嚢する以外に有効利用されていない。CacOs −Cao + Cow ・−= (
ItCaO+ SOt + 40* →Ca5O<
・-・- ■The ash produced in such a fluidized bed boiler (dust collected from the coarse collector (9) and dust collector OJ, ash collected from the bottom of the fluidized bed 14) can be reused in the cement industry, etc. It costs too much money to do so, and the only effective use is to throw the cane teeth in a landfill.
ところが、前記石灰石は、SOxをn捉してCaSO4
となる前に、流動床(4)内で粉砕されてCa COs
やCaOの状囮で排ガスといっしょに粗集塵機(9)や
集塵機03に運び出されたり、あるいはCaCO5の状
態で流動床(4)から排出されたりしていた。投入され
る石灰石のうち、有効に反応する石灰石は数%にすぎず
、大部分が未反応の石灰石又は生石灰であり、従って、
析しい石灰石を流動床(4)へ次々と補給せねばならず
、石灰石の使用量は例えば石炭燃tA量の1ハ0〜l/
4にまでおよび流動層ボイラーの運転費が嵩んでいた。However, the limestone captures SOx and converts it into CaSO4.
Ca COs is crushed in a fluidized bed (4) before
It was carried out together with the exhaust gas to the coarse dust collector (9) and dust collector 03 in the form of CaCO and CaO, or was discharged from the fluidized bed (4) in the form of CaCO5. Of the limestone that is introduced, only a few percent of the limestone reacts effectively, and the majority is unreacted limestone or quicklime.
The fluidized bed (4) must be replenished one after another with limestone that is decondensed.
4, and the operating costs of fluidized bed boilers were increasing.
本発明の目的は、有効成分の多い流動層ボイラー灰の有
効利用にあり、該ボイラーの使用石灰石の低減と投棄灰
量の低減を図ることにある。An object of the present invention is to effectively utilize fluidized bed boiler ash containing a large amount of active ingredients, and to reduce the amount of limestone used in the boiler and the amount of ash discarded.
本発明の特徴は、石炭、フークス等の固体燃料と石灰石
とを混合流動燃焼する流動層ボイラーで発生する灰を回
収し、この回収した灰をバインダーで1〜5龍に造粒し
たのち、これを再び流a層内に投入して燃焼することに
ある。The feature of the present invention is that the ash generated in a fluidized bed boiler that mixes solid fuel such as coal and Fuchs with limestone is collected, and the collected ash is granulated with a binder to 1 to 5 grains. The purpose is to re-inject it into the flow a layer and burn it.
回収した灰には、前述の通り有効成分が含有されている
が、このままの状態では、微粉が非常に多いために流1
17層内に滞留することなく再び排ガスにより運び出さ
れることとなる。これを防1ヒするために本発明では、
回収した灰をバインダーで1〜5軸に造粒する。造粒に
際し、11以下では微粉と同様に流動層内に滞留するこ
となく、又、5−1以上では粒子が大きすぎて隔床板り
に積り適正な流動層が得られない。この理由により1〜
51−に造粒することとした。造粒形状は1、球形吠、
あるいは細長く押出し整形袋適当な長さに剪断した円柱
伏、角柱伏等どのような形状でもよい。As mentioned above, the collected ash contains active ingredients, but in its current state, it is difficult to wash it as it contains a very large amount of fine powder.
It will be carried out again by the exhaust gas without staying in the 17th layer. In order to prevent this, in the present invention,
The collected ash is granulated into 1 to 5 axes using a binder. During granulation, if it is less than 11, it will not stay in the fluidized bed like fine powder, and if it is more than 5-1, the particles will be too large and will pile up on the partition plate, making it impossible to obtain a proper fluidized bed. For this reason, 1~
It was decided to granulate to 51-. The granulation shape is 1, spherical,
Alternatively, the extruded orthopedic bag may have any shape, such as a cylindrical shape or a prismatic shape, which is sheared to an appropriate length.
次に、灰を造粒するためのバインダーとしては、用油、
コールタール、灯油、灯油とピッチの混合物、マシ/浦
スピンドル油等の使用後の油いわゆる廃油、等の液体燃
料系のものが好ましい。これは、粘性があり、かつバイ
ンダー自身が燃料きなり得るからである。例えば、バイ
ンダーとして水を使用するのは好ましくない。灰にはC
aO成分が含有しており、水で造粒すると下記(3)式
の反応が起る。Next, as a binder for granulating the ash, commercial oil,
Liquid fuels such as coal tar, kerosene, a mixture of kerosene and pitch, used oil such as Masi/Ura spindle oil, and so-called waste oil are preferred. This is because it is viscous and the binder itself can become a fuel. For example, it is undesirable to use water as a binder. C for ashes
It contains an aO component, and when granulated with water, the following reaction (3) occurs.
C,aO+11.O→Ca(OH)s −−−−−−
(3)この(3)式は、発熱反応であり、水添加時に発
熱して危険であり、又、せっかく生成しているCaOが
無くなってしまい排ガスの脱硫作用がなされないことに
なる。C, aO+11. O→Ca(OH)s --------
(3) Equation (3) is an exothermic reaction, which is dangerous because it generates heat when water is added, and the CaO that has been produced will disappear, meaning that the desulfurization effect of the exhaust gas will not be achieved.
バインダーのみの造粒で造粒灰に強度が得られない場合
は、造粒補助材として粘土の乾燥粉末を2〜10wt%
添加するのがよい。If the strength of the granulated ash cannot be obtained by granulating only the binder, add 2 to 10 wt% of dry clay powder as a granulation aid.
It is good to add it.
このようにして得た造粒灰の流動層への投入は、石炭投
入装置から石炭と共に投入してもよ(、石灰石投入装置
から石灰石と共に投入してもよく、あるいは、新たに設
けた投入装置より投入してもよい。第1図には、新たに
造粒灰役人装置■を設け、流動層への投入に石灰石の導
入口を併用する構造を示している。又、投入iは石灰石
全投入樋の80%以下程度なら何の問題も生じない。The granulated ash obtained in this way may be charged into the fluidized bed together with coal from a coal charging device (or may be charged together with limestone from a limestone charging device, or by a newly installed charging device). Figure 1 shows a structure in which a new granulated ash official device (2) is installed and a limestone inlet is used for charging into the fluidized bed. If it is less than 80% of the input gutter, no problem will occur.
又、灰には、前述の0式に示したように排ガス中のSO
xと反応したCaSO4が含有されているので、発生す
る全部を再利用に使用していくと、灰中のCaSO41
O度が上り、これを造粒して再利用すると排ガスの脱硫
効果が低下して来る。従って定期的に又は連続的に排ガ
ス中のSOx 66を測定し、その濃度が高(なった場
合には灰の一部を投棄処理をするか、あるいは比較的に
CaSO41O度の高い微粉の灰(集塵機で回収される
もの)を部分的に投棄処理する等の管理が必要である。In addition, as shown in the above equation 0, the ash contains SO in the exhaust gas.
Since it contains CaSO4 that has reacted with
If the O degree increases and this is granulated and reused, the desulfurization effect of the exhaust gas will decrease. Therefore, we measure SOx 66 in the exhaust gas periodically or continuously, and if the concentration becomes high, we either dispose of some of the ash or dispose of fine ash with a relatively high CaSO41O content. It is necessary to manage the waste by partially dumping the waste (collected by dust collectors).
本文明は、流動床ボイラーで発生した灰をバインダーで
1〜5−嘗に造粒したのち、これを流a層内に投入して
燃焼するものであるから、流a層内で沈降することもな
(、燃焼しない吠囮で排ガスにより導出されることもな
(常に安定した流動0を形成し、 L、Thも灰中に多
量含有するCaO成分は、石灰石の主成分Ca COs
の吸熱反応で生成したものであるから石灰石に比べて吸
a量も少なく排ガスの脱硫反応に寄与し、さらにまた、
バインダーに重油等の液体燃料を使用すると造粒灰は排
ガスの脱硫剤とともに燃料としても作用し、投入石炭量
の低減にもなる。In this civilization, the ash generated in the fluidized bed boiler is granulated with a binder for 1 to 5 times, and then it is put into the a bed and burned, so it does not settle in the a bed. The CaO component, which is a non-burning decoy and is not released by exhaust gas (always forms a stable flow 0, and contains large amounts of L and Th in the ash, is the main component of limestone, CaCOs).
Because it is produced by an endothermic reaction, it absorbs less a than limestone and contributes to the desulfurization reaction of exhaust gas.
When a liquid fuel such as heavy oil is used as a binder, the granulated ash acts as a fuel as well as a desulfurizing agent for exhaust gas, which also reduces the amount of coal input.
ボイラーの仕様として、蒸発量がG OT/llr 1
蒸気圧が90 kg/c+L蒸気温度が515°C1石
炭燃焼量が7〜8 T/llrのもので実施した。As for the specifications of the boiler, the amount of evaporation is G OT/llr 1
The experiment was carried out with a steam pressure of 90 kg/c+L, a steam temperature of 515° C., and a coal combustion amount of 7 to 8 T/llr.
石炭の供給量、石灰石の供給量、利用する灰の量等を従
来例と本発明法を比較して第1表に示した。Table 1 shows a comparison of the amount of coal supplied, the amount of limestone supplied, the amount of ash used, etc. between the conventional example and the method of the present invention.
第 1 表
又、前記ボイラーで発生する灰の成分、粒度は第2表の
通りであり、本発明では流動床底部から回収されたアッ
シュは全量再利用し、集塵機から回収されたダストの一
部を廃却、一部を再利用した。又、造粒条件は第3表に
示した。なお、造粒機は、円板型ダイス水平式押出し造
粒機を使用した。Table 1 In addition, the components and particle size of the ash generated in the boiler are as shown in Table 2. In the present invention, the entire amount of ash recovered from the bottom of the fluidized bed is recycled, and a portion of the dust recovered from the dust collector is recycled. were disposed of and some were reused. The granulation conditions are shown in Table 3. The granulator used was a horizontal extrusion granulator with a disk type die.
第2表
第 3 表
第1表に示す本発明法は、第3表に示す各種造粒灰の使
用平均値であり、この発明法と従来法を比較すると、第
2表に示す化学成分中のCaO量(Ca COs も含
む)、 C量が有効利用されたことにより、石炭で数%
、石灰石で約60%の低減及び廃却灰で約40%の低減
が可能となり、また、排ガス中のSOx含有量もほぼ同
じ値であって、脱硫性がそこなわれていないことがわか
る。The method of the present invention shown in Table 1 is the average value used for the various granulated ash shown in Table 3. Comparing this method of the invention with the conventional method, the chemical components shown in Table 2 are The amount of CaO (including CaCOs) and the amount of C have been effectively utilized, resulting in a reduction of several % in coal.
It can be seen that a reduction of about 60% with limestone and a reduction of about 40% with waste ash is possible, and the SOx content in the exhaust gas is almost the same, indicating that the desulfurization property is not impaired.
なお、本発明法では、排ガスの脱硫維持のために発生す
る灰の全量を必ずしも使用する必要がなく、発生する灰
の一部を廃却して新しい石灰りとの併用が望ましい。In addition, in the method of the present invention, it is not necessarily necessary to use the entire amount of ash generated in order to maintain desulfurization of exhaust gas, and it is preferable to discard a portion of the ash generated and use it in combination with new limescale.
本発明法は、流*aボイラーで発生する灰を回収して造
粒し、これを流動層ボイラーに再利用することにより、
石灰石の低減、廃却灰量の低減か可能となり、しかも排
ガス中のSOx は従来法と同程度に脱硫がなされ、多
大の効果かある。The method of the present invention collects and granulates the ash generated in the flow*a boiler, and reuses it in the fluidized bed boiler.
It is possible to reduce the amount of limestone and waste ash, and moreover, the SOx in the exhaust gas is desulfurized to the same extent as the conventional method, so it has great effects.
第1図は、流vI層ボイラーの概略説明図でよ古。 Figure 1 is an old schematic diagram of a flow VI layer boiler.
Claims (1)
で発生する灰を回収し、この回収した灰をバインダーで
1〜5mmに造粒したのち、これを再び流動層内に投入
して燃焼する流動層ボイラー灰の利用法。A fluidized bed boiler that collects ash generated in a fluidized bed boiler that performs mixed fluidized combustion of solid fuel and limestone, granulates the collected ash with a binder to a size of 1 to 5 mm, and then feeds it back into the fluidized bed for combustion. How to use bed boiler ash.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP27485086A JPS63129209A (en) | 1986-11-18 | 1986-11-18 | Utilization of ash of fluidized-bed boiler |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP27485086A JPS63129209A (en) | 1986-11-18 | 1986-11-18 | Utilization of ash of fluidized-bed boiler |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS63129209A true JPS63129209A (en) | 1988-06-01 |
Family
ID=17547446
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP27485086A Pending JPS63129209A (en) | 1986-11-18 | 1986-11-18 | Utilization of ash of fluidized-bed boiler |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS63129209A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB2276377A (en) * | 1991-12-12 | 1994-09-28 | United Distillers Plc | Method and apparatus for securing one body with respect to another |
JP2008503707A (en) * | 2004-06-23 | 2008-02-07 | フォスター ホイーラー エナージア オサケ ユキチュア | Method for reducing sulfur dioxide emissions from circulating fluidized bed boilers. |
-
1986
- 1986-11-18 JP JP27485086A patent/JPS63129209A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB2276377A (en) * | 1991-12-12 | 1994-09-28 | United Distillers Plc | Method and apparatus for securing one body with respect to another |
JP2008503707A (en) * | 2004-06-23 | 2008-02-07 | フォスター ホイーラー エナージア オサケ ユキチュア | Method for reducing sulfur dioxide emissions from circulating fluidized bed boilers. |
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