JPH0679132A - Desulfurizing method and particle fluidized-bed desulfurizing apparatus - Google Patents
Desulfurizing method and particle fluidized-bed desulfurizing apparatusInfo
- Publication number
- JPH0679132A JPH0679132A JP4130715A JP13071592A JPH0679132A JP H0679132 A JPH0679132 A JP H0679132A JP 4130715 A JP4130715 A JP 4130715A JP 13071592 A JP13071592 A JP 13071592A JP H0679132 A JPH0679132 A JP H0679132A
- Authority
- JP
- Japan
- Prior art keywords
- particles
- desulfurizing agent
- fluidized
- desulfurization
- 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.)
- Granted
Links
Landscapes
- Treating Waste Gases (AREA)
- Devices And Processes Conducted In The Presence Of Fluids And Solid Particles (AREA)
Abstract
Description
【０００１】[0001]
【産業上の利用分野】本発明は、各種産業排ガス等に含
まれる亜硫酸ガス（ＳＯ2 ) 又は無水硫酸ガス（Ｓ
Ｏ3 ) を効率的に除去する粉粒流動層脱硫装置に関す
る。BACKGROUND OF THE INVENTION The present invention relates to sulfur dioxide (SO 2 ) or anhydrous sulfuric acid (S) contained in various industrial exhaust gases.
The present invention relates to a powder / fluidized bed desulfurization device for efficiently removing O 3 ).
【０００２】[0002]
【従来の技術】燃焼排ガスや化学工場の排ガスなど各種
産業排ガスの大気中への放出については、公害防止、環
境保全の観点から種々の規制措置がとられている。その
ためＳＯ2 やＳＯ3 及び酸化窒素類の除去は重要な問題
であり、効率的かつ経済的な除去方法の開発が望まれて
いる。なかでもＳＯ2 やＳＯ3 の除去方法として、乾式
の脱硫方法は装置コストが安価であるため、広く産業界
で用いられている。2. Description of the Related Art Regarding the release of various industrial exhaust gases such as combustion exhaust gases and exhaust gases from chemical plants into the atmosphere, various regulatory measures have been taken from the viewpoint of pollution prevention and environmental protection. Therefore, removal of SO 2 , SO 3, and nitric oxides is an important problem, and development of an efficient and economical removal method is desired. Among them, as a method for removing SO 2 and SO 3 , the dry desulfurization method is widely used in the industrial field because the equipment cost is low.
【０００３】[0003]
【発明が解決しようとする課題】ところが上記の乾式脱
硫方法は脱硫効率が低いという欠点を有している。その
理由は、ＳＯｘと脱硫剤である石灰石やドロマイトなど
が反応して石膏などの化合物が脱硫剤表面に形成される
ため、脱硫剤の粒子径を大きくすると脱硫反応速度を著
しく小さくすることになり、また、粒子径の小さい脱硫
剤を用いると、多量のガスの処理が必要な排煙脱硫で
は、粒子の装置内での滞留時間が小さくなり、脱硫効率
が低下してしまうからである。本発明は、この様な従来
の乾式脱硫方法の欠点を解消し、効率的な脱硫を行うこ
とのできる方法及び装置を提供することを目的とする。However, the above-mentioned dry desulfurization method has a drawback that the desulfurization efficiency is low. The reason is that SOx reacts with desulfurizing agents such as limestone and dolomite to form a compound such as gypsum on the surface of the desulfurizing agent. Therefore, increasing the particle size of the desulfurizing agent significantly reduces the desulfurization reaction rate. Further, when a desulfurizing agent having a small particle size is used, in flue gas desulfurization that requires treatment of a large amount of gas, the residence time of the particles in the device becomes short, and desulfurization efficiency decreases. An object of the present invention is to provide a method and an apparatus capable of solving such drawbacks of the conventional dry desulfurization method and performing efficient desulfurization.
【０００４】[0004]
【課題を解決するための手段】本発明は、ＳＯ2 又はＳ
Ｏ3 を含むガスで脱硫剤に関係のない１００〜２０００
μｍ程度の不活性な粒子（媒体粒子）を７００〜１１０
０℃で流動化している装置内に０．１〜２０μｍ程度の
脱硫剤粒子を連続投入し、媒体粒子とともに流動化する
ことによって連続脱硫を行うことを特徴とする脱硫方法
及びＳＯ2 又はＳＯ3 を含むガスで脱硫剤に関係のない
１００〜２０００μｍ程度の不活性な粒子（媒体粒子）
を７００〜１１００℃で流動化している装置内に０．１
〜２０μｍ程度の脱硫剤粒子を脱硫剤供給機より連続投
入し、媒体粒子とともに流動化し、サイクロンでガスと
分離した後、脱硫剤捕集機に回収するようにしたことを
特徴とし、粉粒流動層を主体として構成される連続脱硫
を行うための粉粒流動層脱硫装置に関する。The present invention is based on SO 2 or S
100 to 2000 regardless of the desulfurizing agent with a gas containing O 3.
Inert particles (medium particles) of about μm are 700 to 110
Desulfurization method and SO 2 or SO 3 characterized by continuously introducing desulfurizing agent particles of about 0.1 to 20 μm into a device fluidized at 0 ° C. and fluidizing the particles together with medium particles. Inert particles (medium particles) of about 100 to 2000 μm that are gas-containing and not related to the desulfurizing agent
In a device fluidized at 700-1100 ° C.
Approximately 20 μm of desulfurizing agent particles are continuously charged from a desulfurizing agent feeder, fluidized with medium particles, separated from gas by a cyclone, and then collected by a desulfurizing agent collector, which is a powder particle flow. TECHNICAL FIELD The present invention relates to a powder / fluidized bed desulfurization device for performing continuous desulfurization mainly composed of layers.
【０００５】本発明の方法を実施するのに適する装置
は、例えば、図１に示すように、煙道ガス供給口１、脱
硫剤ホッパー２、脱硫剤供給機３、粉・粒流動層脱硫装
置４、加熱器５、サイクロン６、脱硫剤捕集器７、バッ
クフィルター８及びＳＯ2 メーター９から構成される。
粉・粒流動層脱硫装置４が、本発明の装置本体である。
この装置に適当な大きさの媒体粒子を入れて脱硫に適し
た温度で流動化しておく。流動化ガスとしては煙道ガス
などの通常の排煙脱硫を必要とするガスが使用される。
脱硫剤供給機３より２０μｍ以下の微粒子の脱硫剤を連
続的に供給し、媒体粒子とともに流動化し、脱硫を行
う。脱硫剤は適当な滞留時間、媒体粒子とともに流動化
したのち、ガスとともにこの装置より流出し、サイクロ
ン６、バックフィルター８に捕集される。An apparatus suitable for carrying out the method of the present invention is, for example, as shown in FIG. 1, a flue gas supply port 1, a desulfurizing agent hopper 2, a desulfurizing agent feeder 3, a powder / grain fluidized bed desulfurizing apparatus. 4, a heater 5, a cyclone 6, a desulfurizing agent collector 7, a back filter 8 and an SO 2 meter 9.
The powder / grain fluidized bed desulfurization device 4 is the device body of the present invention.
Medium particles having an appropriate size are put in this apparatus and fluidized at a temperature suitable for desulfurization. As the fluidizing gas, a gas requiring ordinary flue gas desulfurization such as flue gas is used.
The desulfurizing agent feeder 3 continuously supplies a desulfurizing agent having a particle size of 20 μm or less to fluidize with the medium particles and desulfurize. The desulfurizing agent is fluidized with the medium particles for an appropriate residence time, then flows out from this device together with the gas, and is collected by the cyclone 6 and the back filter 8.
【０００６】一般に粒子径が２０μｍ以下の粒子は、粒
子と粒子の付着凝集性が強くなり、均一にガス−固体系
の流動層で流動化することはできない。しかるにこのよ
うな微粒子でも大きな媒体粒子と一緒なら流動化しうる
ことが発見された。本明細書では、微粒子又は超微粒子
を粗い媒体粒子とともに流動化する装置を「粉粒流動
層」と定義する。この粉粒流動層では連続的に供給され
た微粒子は大きな媒体粒子の表面に付着し、媒体粒子と
ともに流動化するので、微粒子の装置内での滞留時間は
ガスの滞留時間の１００倍以上あるものと考えられる。
したがって、供給した脱硫剤とＳＯｘとを効率よく反応
させることが可能である。上記媒体粒子としては、シリ
カサンド、川砂、アルミナ等無機質の高温に耐える粒子
等を用いるのが好ましい。その粒子径は、１００〜２０
００μｍとするが、その理由は、媒体粒子の粒子径が小
さくて、脱硫剤の粒子径との差が小さくなると脱硫剤と
媒体粒子を効率よく分離することが困難となる。一方、
媒体粒子の粒子径を大きくとりすぎると、流動化に必要
なガス速度が大きくなりすぎたり、媒体粒子の磨耗が激
しくなる為である。又、脱硫剤粒子としては、一般に、
石灰石、ドロマイト、石炭にイオン交換担持したＣａ、
水酸化カルシウム及びそのスラリー等を用いるが、特
に、石灰石及びドロマイトが好ましい。その粒子径は、
０．１〜２０μｍとするが、その理由は、石灰石及びド
ロマイトの単位重量当たりの価格が安価なことによる。
一般にこれら媒体粒子を空筒基準ガス速度で２０〜２０
０ｃｍ／ｓｅｃで高温の一定温度で流動化しているとこ
ろへ、脱硫剤粒子を連続的に投入し、脱硫後のガスと共
に流出する脱硫剤をサイクロン及びバックフィルターで
回収する。In general, particles having a particle diameter of 20 μm or less have a strong adhesion and cohesiveness between particles and cannot be uniformly fluidized in a gas-solid fluidized bed. However, it has been discovered that even such particles can be fluidized with large media particles. In the present specification, an apparatus for fluidizing fine particles or ultrafine particles together with coarse medium particles is defined as a "powder particle fluidized bed". In this powder-particle fluidized bed, the continuously supplied fine particles adhere to the surfaces of large medium particles and fluidize with the medium particles, so the retention time of the fine particles in the device is 100 times or more the retention time of gas. it is conceivable that.
Therefore, it is possible to efficiently react the supplied desulfurizing agent with SOx. As the medium particles, it is preferable to use inorganic particles such as silica sand, river sand, and alumina which can withstand high temperatures. The particle size is 100 to 20
The reason is that the particle size is 00 μm, but the reason is that if the particle size of the medium particles is small and the difference from the particle size of the desulfurizing agent is small, it becomes difficult to efficiently separate the desulfurizing agent and the medium particles. on the other hand,
This is because if the particle size of the medium particles is too large, the gas velocity required for fluidization becomes too high and the wear of the medium particles becomes severe. Further, as the desulfurizing agent particles, generally,
Limestone, dolomite, Ca ion-exchanged on coal,
Calcium hydroxide and its slurry are used, but limestone and dolomite are particularly preferable. The particle size is
The thickness is set to 0.1 to 20 μm because the price of limestone and dolomite per unit weight is low.
Generally, these medium particles are contained in the hollow cylinder reference gas velocity of 20 to 20
Desulfurizing agent particles are continuously charged into a fluidized place at a high temperature of 0 cm / sec, and the desulfurizing agent flowing out together with the gas after desulfurization is collected by a cyclone and a back filter.
【０００７】[0007]
【実施例】以下実施例により本発明の方法をさらに具体
的に説明する。 （実施例１）図１に示される様な装置を用いて、内径８
ｃｍ、高さ１５０ｃｍの装置にシリカサンドを静止層高
さで８０ｃｍ充填し、１０００ｐｐｍのＳＯ2 ガスを含
む空気を９００℃、１気圧で毎分３０００ｃｃ供給し、
３００μｍのシリカサンド粒子を空筒基準ガス速度６０
ｃｍ／ｓｅｃで流動化させる。供給したＳＯ2 ガスに対
して化学量論的に２倍の５μｍの石灰石を連続供給して
脱硫を行ったところ、脱硫率は９０％に達した。脱硫剤
は脱硫後のガスとともに装置外に流出し、サイクロン及
びバッグフィルター内に捕集される。EXAMPLES The method of the present invention will be described in more detail with reference to the following examples. (Example 1) Using an apparatus as shown in FIG.
cm, height 150 cm, filled with silica sand at a height of 80 cm, and air containing 1000 ppm SO 2 gas was supplied at 900 ° C. and 1 atm at 3000 cc / min.
Silica sand particles of 300 μm are used as the standard gas velocity of the hollow cylinder 60
Fluidize at cm / sec. When desulfurization was carried out by continuously supplying 5 μm of limestone that was stoichiometrically double to the supplied SO 2 gas, the desulfurization rate reached 90%. The desulfurizing agent flows out of the device together with the gas after desulfurization, and is collected in the cyclone and the bag filter.
【０００８】[0008]
【発明の効果】本発明によれば、特定の粉粒流動層を用
いることにより、従来、流動化することが困難であった
極めて微細な脱硫剤粒子を安定なガス−固体系の流動層
として流動化することができ、それにより、経済的な乾
式脱硫法をより効率的に実施することを可能とした。According to the present invention, by using a specific powder-grain fluidized bed, extremely fine desulfurizing agent particles, which have been difficult to fluidize in the past, can be used as a stable gas-solid fluidized bed. It can be fluidized, which makes it possible to carry out the economical dry desulfurization process more efficiently.
【図１】図１は本発明の粉粒流動層脱硫装置の一例を示
す概念図である。 １：煙道ガス ２：脱硫剤ホッパー ３：脱硫剤供給機 ４：粉・粒流動層脱硫機 ５：加熱器 ６：サイクロン ７：脱硫剤捕集器 ８：バックフィルター ９：ＳＯ2 メーターFIG. 1 is a conceptual diagram showing an example of a powder / fluidized bed desulfurization apparatus of the present invention. 1: Flue gas 2: Desulfurization agent hopper 3: Desulfurization agent feeder 4: Powder / grain fluidized bed desulfurization machine 5: Heater 6: Cyclone 7: Desulfurization agent collector 8: Back filter 9: SO 2 meter
Claims (2)
関係のない１００〜２０００μｍ程度の不活性な粒子
（媒体粒子）を７００〜１１００℃で流動化している装
置内に０．１〜２０μｍ程度の脱硫剤粒子を連続投入
し、媒体粒子とともに流動化することによって連続脱硫
を行うことを特徴とする脱硫方法。1. A gas containing SO 2 or SO 3 which has an inert particle (medium particle) of about 100 to 2000 μm and which is not related to a desulfurizing agent and which is fluidized at 700 to 1100 ° C. A desulfurization method characterized in that continuous desulfurization is carried out by continuously introducing desulfurization agent particles of about 20 μm and fluidizing them together with medium particles.
関係のない１００〜２０００μｍ程度の不活性な粒子
（媒体粒子）を７００〜１１００℃で流動化している装
置内に０．１〜２０μｍ程度の脱硫剤粒子を脱硫剤供給
機より連続投入し、媒体粒子とともに流動化し、サイク
ロンでガスと分離した後、脱硫剤捕集機に回収するよう
にしたことを特徴とする、連続脱硫を行うための粉粒流
動層脱硫装置。2. An apparatus in which inert particles (medium particles) of about 100 to 2000 μm, which are not related to a desulfurizing agent and which contain a gas containing SO 2 or SO 3, are fluidized at 700 to 1100 ° C. in an apparatus. Continuous desulfurization is characterized in that about 20 μm of desulfurizing agent particles are continuously fed from a desulfurizing agent feeder, fluidized with medium particles, separated from a gas by a cyclone, and then collected by a desulfurizing agent collector. Granular fluidized bed desulfurization equipment for performing.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4130715A JP2524552B2 (en) | 1992-05-22 | 1992-05-22 | Desulfurization method and granular fluidized bed desulfurization device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4130715A JP2524552B2 (en) | 1992-05-22 | 1992-05-22 | Desulfurization method and granular fluidized bed desulfurization device |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0679132A true JPH0679132A (en) | 1994-03-22 |
| JP2524552B2 JP2524552B2 (en) | 1996-08-14 |
Family
ID=15040897
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP4130715A Expired - Fee Related JP2524552B2 (en) | 1992-05-22 | 1992-05-22 | Desulfurization method and granular fluidized bed desulfurization device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2524552B2 (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2017056380A (en) * | 2015-09-14 | 2017-03-23 | 三菱重工業株式会社 | Dry type desulfurization system and exhaust gas treatment equipment |
| JP2017056381A (en) * | 2015-09-14 | 2017-03-23 | 三菱重工業株式会社 | Desulfurization system and exhaust gas treatment equipment |
| JP2018525208A (en) * | 2015-07-02 | 2018-09-06 | 立維 黄 | Nitrogen oxide removing method and nitrogen oxide removing apparatus |
-
1992
- 1992-05-22 JP JP4130715A patent/JP2524552B2/en not_active Expired - Fee Related
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2018525208A (en) * | 2015-07-02 | 2018-09-06 | 立維 黄 | Nitrogen oxide removing method and nitrogen oxide removing apparatus |
| JP2017056380A (en) * | 2015-09-14 | 2017-03-23 | 三菱重工業株式会社 | Dry type desulfurization system and exhaust gas treatment equipment |
| JP2017056381A (en) * | 2015-09-14 | 2017-03-23 | 三菱重工業株式会社 | Desulfurization system and exhaust gas treatment equipment |
Also Published As
| Publication number | Publication date |
|---|---|
| JP2524552B2 (en) | 1996-08-14 |
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