JPH10328529A - Flue gas desulfurization equipment - Google Patents
Flue gas desulfurization equipmentInfo
- Publication number
- JPH10328529A JPH10328529A JP9140124A JP14012497A JPH10328529A JP H10328529 A JPH10328529 A JP H10328529A JP 9140124 A JP9140124 A JP 9140124A JP 14012497 A JP14012497 A JP 14012497A JP H10328529 A JPH10328529 A JP H10328529A
- Authority
- JP
- Japan
- Prior art keywords
- absorption tower
- pipe
- slurry
- pump
- flue 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.)
- Pending
Links
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims abstract description 27
- 239000003546 flue gas Substances 0.000 title claims abstract description 27
- 238000006477 desulfuration reaction Methods 0.000 title claims abstract description 25
- 230000023556 desulfurization Effects 0.000 title claims abstract description 25
- 239000002002 slurry Substances 0.000 claims abstract description 76
- 238000010521 absorption reaction Methods 0.000 claims abstract description 66
- 239000007788 liquid Substances 0.000 claims abstract description 38
- 238000004064 recycling Methods 0.000 claims abstract description 11
- 230000002745 absorbent Effects 0.000 claims abstract description 10
- 239000002250 absorbent Substances 0.000 claims abstract description 10
- 239000003513 alkali Substances 0.000 claims abstract description 10
- 238000005507 spraying Methods 0.000 claims abstract description 4
- 239000007789 gas Substances 0.000 description 38
- 230000001590 oxidative effect Effects 0.000 description 8
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 7
- 239000007921 spray Substances 0.000 description 7
- 229910052717 sulfur Inorganic materials 0.000 description 7
- 239000011593 sulfur Substances 0.000 description 7
- 239000000428 dust Substances 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 239000003595 mist Substances 0.000 description 4
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 3
- 239000003245 coal Substances 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- 238000007254 oxidation reaction Methods 0.000 description 3
- 239000000779 smoke Substances 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 2
- 229910052602 gypsum Inorganic materials 0.000 description 2
- 239000010440 gypsum Substances 0.000 description 2
- 230000003009 desulfurizing effect Effects 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-L sulfite Chemical class [O-]S([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-L 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Degasification And Air Bubble Elimination (AREA)
Abstract
(57)【要約】
【課題】 本発明の課題は、吸収塔の液溜部から抜き出
される吸収液から気泡を除去できる排煙脱硫装置を提供
することである。
【解決手段】 アルカリ吸収剤を噴霧して循環するため
のポンプ2を吸収塔1に接続した排煙脱硫装置20にお
いて、ポンプ2を吸収塔1の外側下部に設けると共に該
ポンプ2の出口側配管3bを該吸収塔1の液溜部1a上
方に起立させ、該起立した出口側配管3bと該吸収塔1
の液溜部1aとを結んでスラリを戻すリサイクル配管8
を接続し、且つ該リサイクル配管8と該ポンプ2の入口
側配管3aとを結んで該入口側配管3a上面部からスラ
リに含まれる気泡を該リサイクル配管8に回収する気泡
除去配管9を接続する。
(57) [Summary] An object of the present invention is to provide a flue gas desulfurization apparatus capable of removing air bubbles from an absorbing liquid extracted from a liquid reservoir of an absorption tower. SOLUTION: In a flue gas desulfurization apparatus 20 in which a pump 2 for spraying and circulating an alkali absorbent is connected to an absorption tower 1, the pump 2 is provided at a lower portion outside the absorption tower 1 and an outlet pipe of the pump 2 is provided. 3b is erected above the liquid reservoir 1a of the absorption tower 1, and the erected outlet pipe 3b and the absorption tower 1
Recycling pipe 8 that connects to the liquid reservoir 1a and returns the slurry
And connects the recycling pipe 8 to the inlet pipe 3a of the pump 2 to connect an air bubble removal pipe 9 for collecting bubbles contained in the slurry from the upper surface of the inlet pipe 3a to the recycling pipe 8. .
Description
【0001】[0001]
【発明の属する技術分野】本発明は、アルカリ吸収剤を
含むスラリを吸収塔内で噴霧して排ガスと接触させこれ
を脱硫する排煙脱硫装置に係り、特に、吸収塔の液溜部
に溜まったスラリをポンプで抜き出して吸収塔上部に戻
すスラリ循環手段を改良することにより、ポンプに吸引
されるスラリから気泡を除去できる排煙脱硫装置に関す
る。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a flue gas desulfurization apparatus for spraying a slurry containing an alkali absorbent in an absorption tower, contacting the exhaust gas, and desulfurizing the exhaust gas. The present invention relates to a flue gas desulfurization apparatus capable of removing bubbles from a slurry sucked by a pump by improving a slurry circulation means for extracting the recovered slurry by a pump and returning the slurry to an upper portion of an absorption tower.
【0002】[0002]
【従来の技術】石炭等の燃料を燃焼したとき発生する排
ガス(排煙)には、比較的多くの硫黄分が含まれるた
め、この排ガスを排煙脱硫装置によって脱硫する必要が
ある。2. Description of the Related Art Exhaust gas (smoke exhaust) generated when burning fuel such as coal contains a relatively large amount of sulfur, and it is necessary to desulfurize the exhaust gas with a flue gas desulfurization device.
【0003】図4は、一般的な排煙処理システムの概略
図であり、その一部として、アルカリ吸収剤を含むスラ
リ液(以下、スラリと称する)を排ガスに噴霧して排ガ
スを脱硫する従来の排煙脱硫装置30が示されている。FIG. 4 is a schematic view of a general flue gas treatment system. As a part of the conventional flue gas treatment system, a slurry liquid (hereinafter, referred to as a slurry) containing an alkali absorbent is sprayed on exhaust gas to desulfurize the exhaust gas. Is shown.
【0004】この排煙処理システムは、図示されるよう
に、順に接続されたボイラ10,脱硝装置11,エアヒ
ータ(A/H)12,電気集塵器(EP)13,ガスガ
スヒータ(GGH)14,排煙脱硫装置30,煙突15
から主に構成される。[0004] As shown in the figure, the flue gas treatment system includes a boiler 10, a denitration device 11, an air heater (A / H) 12, an electric dust collector (EP) 13, and a gas gas heater (GGH) 14 which are connected in order. , Flue gas desulfurization equipment 30, chimney 15
Mainly composed of
【0005】排煙脱硫装置30は、吸収塔1と、吸収塔
1にポンプ2を介して接続されたスラリ循環手段3と、
吸収塔1上部にスラリ循環手段3に接続して設けられた
スプレノズル4と、吸収塔1底部に設けられた酸化手段
5(脱硫反応の結果生成した亜硫酸塩等を強制酸化する
ためのもの)と、吸収塔1出口付近に設けられたミスト
エリミネータ6と、吸収塔1にスラリを供給するスラリ
供給手段7とから主に構成される。[0005] The flue gas desulfurization unit 30 comprises an absorption tower 1, a slurry circulation means 3 connected to the absorption tower 1 via a pump 2,
A spray nozzle 4 provided at the top of the absorption tower 1 connected to the slurry circulation means 3; and an oxidizing means 5 provided at the bottom of the absorption tower 1 (for forcibly oxidizing a sulfite or the like generated as a result of the desulfurization reaction). And a mist eliminator 6 provided near the outlet of the absorption tower 1 and a slurry supply means 7 for supplying a slurry to the absorption tower 1.
【0006】吸収塔1は、排ガスがその下部から導入さ
れると共に、上部から排出されるように構成されてい
る。吸収塔1の底部には、スラリが溜まる液溜部1aが
形成される。又、スラリ循環手段3には、図示されない
石膏回収手段が接続される。[0006] The absorption tower 1 is configured such that exhaust gas is introduced from a lower part thereof and discharged from an upper part thereof. At the bottom of the absorption tower 1, there is formed a liquid reservoir 1a in which slurry is stored. Further, a gypsum collecting means (not shown) is connected to the slurry circulating means 3.
【0007】石炭等の燃料がボイラ10で燃焼され、硫
黄分を含んだ排ガスが発生する。硫黄分を含んだ排ガス
は、ボイラ10から脱硝装置11に導入されて脱硝さ
れ、脱硝された排ガスは、エアヒータ12,電気集塵器
13及びガスガスヒータ14を介して吸収塔1の下部に
導入される。[0007] Fuel such as coal is burned in the boiler 10 to generate exhaust gas containing sulfur. Exhaust gas containing sulfur is introduced from the boiler 10 to the denitration device 11 for denitration, and the denitrated exhaust gas is introduced into the lower part of the absorption tower 1 via the air heater 12, the electric dust collector 13 and the gas gas heater 14. You.
【0008】吸収塔1の下部に導入された排ガスは、吸
収塔1内を上昇する。このとき、スプレノズル4を介し
てアルカリ吸収剤を含んだ液(スラリ)が排ガスに噴霧
され、この結果、スラリと排ガスとが気液接触して排ガ
スに含まれる硫黄分がアルカリ吸収剤に吸収され、脱硫
が行われる。The exhaust gas introduced into the lower part of the absorption tower 1 rises in the absorption tower 1. At this time, a liquid (slurry) containing an alkali absorbent is sprayed on the exhaust gas through the spray nozzle 4, and as a result, the slurry and the exhaust gas come into gas-liquid contact, and the sulfur content contained in the exhaust gas is absorbed by the alkali absorbent. , Desulfurization is performed.
【0009】脱硫された排ガスは、ミストエリミネータ
6を介して吸収塔1の頂部から排出され、ガスガスヒー
タ14及び煙突15を介して大気放出される。The desulfurized exhaust gas is discharged from the top of the absorption tower 1 via the mist eliminator 6 and discharged to the atmosphere via the gas gas heater 14 and the chimney 15.
【0010】一方、吸収塔1の液溜部1aに溜まった液
は、ポンプ2によって汲み出されると共に、スラリ循環
手段3によってスプレノズル4に戻されて再び噴霧さ
れ、以下、上記の過程が繰り返される。又、スラリ供給
手段7によって、吸収塔1内にスラリが適宜供給される
と共に、酸化空気が酸化手段5によって吸収塔1の液溜
部1aに送り込まれ、脱硫反応によって生成した亜硫酸
塩(CaSO3 等)が強制的に酸化される。On the other hand, the liquid stored in the liquid storage section 1a of the absorption tower 1 is pumped out by the pump 2 and returned to the spray nozzle 4 by the slurry circulating means 3 to be sprayed again. Thereafter, the above steps are repeated. . Slurry is appropriately supplied into the absorption tower 1 by the slurry supply means 7, and oxidizing air is fed into the liquid reservoir 1a of the absorption tower 1 by the oxidization means 5, and the sulfite (CaSO 3 Etc.) are forcibly oxidized.
【0011】[0011]
【発明が解決しようとする課題】さて、上記の従来の排
煙脱硫装置においては、吸収塔の液溜部に溜まった液に
酸化手段によって酸化空気が多量に吹き込まれるため、
多くの気泡が必然的に液中に発生する。そのため、吸収
塔の液溜部に溜まった液をスラリ循環手段に導入すべく
ポンプによって吸引する際に、スラリと共に気泡がポン
プ内部に導入されてしまい、ポンプの運転に影響を及ぼ
すだけでなく、場合によってはポンプの性能の低下を招
くという問題があった。In the above-mentioned conventional flue gas desulfurization apparatus, a large amount of oxidizing air is blown by the oxidizing means into the liquid stored in the liquid reservoir of the absorption tower.
Many bubbles are necessarily generated in the liquid. Therefore, when the liquid accumulated in the liquid reservoir of the absorption tower is sucked by the pump to be introduced into the slurry circulation means, bubbles are introduced into the pump together with the slurry, which not only affects the operation of the pump, but also affects the operation of the pump. In some cases, there has been a problem that the performance of the pump is reduced.
【0012】そこで、本発明の目的は、吸収塔の液溜部
から抜き出される吸収液から気泡を除去できる排煙脱硫
装置を提供することである。Accordingly, an object of the present invention is to provide a flue gas desulfurization apparatus capable of removing air bubbles from an absorbing liquid extracted from a liquid reservoir of an absorption tower.
【0013】[0013]
【課題を解決するための手段】上記目的を達成するため
に請求項1の発明は、アルカリ吸収剤を噴霧して循環す
るためのポンプを吸収塔に接続した排煙脱硫装置におい
て、ポンプを吸収塔の外側下部に設けると共に該ポンプ
の出口側配管を該吸収塔の液溜部上方に起立させ、該起
立した出口側配管と該吸収塔の液溜部とを結んでスラリ
を戻すリサイクル配管を接続し、且つ該リサイクル配管
と該ポンプの入口側配管とを結んで該入口側配管上面部
からスラリに含まれる気泡を該リサイクル配管に回収す
る気泡除去配管を接続して構成される。In order to achieve the above object, the present invention is directed to a flue gas desulfurization apparatus in which a pump for spraying and circulating an alkali absorbent is connected to an absorption tower. A recycling pipe that is provided at the lower part of the outside of the tower and raises the outlet pipe of the pump above the liquid storage part of the absorption tower, connects the raised outlet pipe to the liquid storage part of the absorption tower, and returns the slurry. The recycling pipe and the inlet pipe of the pump are connected to each other, and a bubble removal pipe for collecting bubbles contained in the slurry from the upper face of the inlet pipe to the recycling pipe is connected.
【0014】[0014]
【発明の実施の形態】以下、本発明の実施の形態を添付
図面により説明する。Embodiments of the present invention will be described below with reference to the accompanying drawings.
【0015】図1に、一般的な排煙処理システムの一部
であり、アルカリ吸収剤を含むスラリ液(以下、スラリ
と称する)を排ガスに噴霧して排ガスを脱硫すると共
に、脱硫後にスラリを抜き出す際、ポンプへの気泡の侵
入を防止可能な本発明の排煙脱硫装置20が示されてい
る。FIG. 1 shows a part of a general flue gas treatment system, in which a slurry liquid (hereinafter, referred to as a slurry) containing an alkali absorbent is sprayed on exhaust gas to desulfurize the exhaust gas. Shown is a flue gas desulfurization device 20 of the present invention that can prevent the intrusion of bubbles into the pump when it is withdrawn.
【0016】この排煙処理システムは、図示されるよう
に、順に接続されたボイラ10,脱硝装置11,エアヒ
ータ(A/H)12,電気集塵器(EP)13,ガスガ
スヒータ(GGH)14,排煙脱硫装置20,煙突15
から主に構成される。As shown in the figure, this smoke exhaust treatment system includes a boiler 10, a denitration device 11, an air heater (A / H) 12, an electric dust collector (EP) 13, and a gas gas heater (GGH) 14, which are connected in this order. , Flue gas desulfurization equipment 20, chimney 15
Mainly composed of
【0017】排煙脱硫装置20は、吸収塔1と、吸収塔
1にポンプ2を介して接続されたスラリ循環手段3と、
吸収塔1上部にスラリ循環手段3に接続して設けられた
スプレノズル4と、吸収塔1の底部に設けられた酸化手
段5(脱硫反応の結果生成した亜硫酸塩等を強制酸化す
るためのもの)と、吸収塔1出口付近に設けられたミス
トエリミネータ6と、吸収塔1にスラリを供給するスラ
リ供給手段7とから主に構成される。The flue gas desulfurization apparatus 20 includes an absorption tower 1, a slurry circulation means 3 connected to the absorption tower 1 via a pump 2,
Spray nozzle 4 provided on top of absorption tower 1 connected to slurry circulation means 3 and oxidation means 5 provided on the bottom of absorption tower 1 (for forcibly oxidizing sulfites and the like generated as a result of desulfurization reaction) And a mist eliminator 6 provided near the outlet of the absorption tower 1 and a slurry supply means 7 for supplying a slurry to the absorption tower 1.
【0018】吸収塔1は、排ガスがその下部から導入さ
れると共に、上部から排出されるように構成されてい
る。吸収塔1の底部には、スラリが溜まる液溜部1aが
形成される。尚、図1において、吸収塔1は、その液溜
部1aにスラリ液が充分に溜まった状態で示されてい
る。スラリ循環手段3には、図示されない石膏回収手段
が接続される。The absorption tower 1 is configured such that exhaust gas is introduced from a lower part thereof and discharged from an upper part thereof. At the bottom of the absorption tower 1, there is formed a liquid reservoir 1a in which slurry is stored. In FIG. 1, the absorption tower 1 is shown in a state where a slurry liquid is sufficiently stored in a liquid storage portion 1a. A gypsum collecting means (not shown) is connected to the slurry circulating means 3.
【0019】尚、図1の吸収塔1の液溜部1a,ポンプ
2及びポンプ2付近のスラリ循環手段3を拡大して示し
たものが、図2である。FIG. 2 is an enlarged view of the liquid reservoir 1a, the pump 2 and the slurry circulation means 3 near the pump 2 of the absorption tower 1 shown in FIG.
【0020】図2に示されるように、本発明のスラリ循
環手段3は、これに付随のポンプ2よりも上流側(入口
側)の入口側配管3aと、ポンプ2よりも下流側(出口
側)の出口側配管3bとに区分される。一般に、スラリ
循環手段3の入口側配管3aは、吸収塔1の液溜部1a
に設けられたスラリ抜きだし口16とポンプ2とを接続
してほぼ水平方向に構成され、一方、スラリ循環手段3
の出口側配管3bは、ポンプ2から入口側配管3aに対
して垂直に立ち上がると共に、吸収塔1の側部に沿って
延びる。As shown in FIG. 2, the slurry circulating means 3 of the present invention includes an inlet-side pipe 3a upstream (inlet side) of the pump 2 and a downstream side (outlet side) of the pump 2. ) And the outlet side pipe 3b. Generally, the inlet side pipe 3a of the slurry circulation means 3 is connected to the liquid reservoir 1a of the absorption tower 1.
The slurry discharge port 16 and the pump 2 are connected to each other so as to be substantially horizontal by connecting the pump 2 and the slurry circulation means 3.
The outlet side pipe 3b rises perpendicularly to the inlet side pipe 3a from the pump 2 and extends along the side of the absorption tower 1.
【0021】図2に示されるように、スラリ循環手段3
の出口側配管3bからは、ポンプ2上の適当な位置(例
えばポンプ2から約2m立ち上がった地点)で、出口側
配管3bから吸収塔1にスラリの一部を戻すリサイクル
配管8が、出口側配管3bの吸収塔1側の側部と吸収塔
1側部とをほぼ水平方向に接続して設けられる。As shown in FIG. 2, the slurry circulation means 3
From the outlet side pipe 3b, at an appropriate position on the pump 2 (for example, a point where the pump 2 rises by about 2 m), a recycle pipe 8 for returning a part of the slurry from the outlet side pipe 3b to the absorption tower 1 is connected to the outlet side. The side of the pipe 3b on the side of the absorption tower 1 and the side of the absorption tower 1 are connected in a substantially horizontal direction.
【0022】又、スラリ循環手段3の入口側配管3aか
らは、スラリ中の気泡を捕捉してスラリの一部と共に入
口側配管3aからリサイクル配管8に流す気泡除去配管
9が、入口側配管3aの適当な地点の配管上部とリサイ
クル配管8の配管下部とをほぼ垂直に接続して、図2
(及び図3A)に示されるように設けられる。From the inlet side pipe 3a of the slurry circulating means 3, a bubble removing pipe 9 which captures bubbles in the slurry and flows a part of the slurry from the inlet side pipe 3a to the recycle pipe 8 is connected to the inlet side pipe 3a. 2 and the lower part of the recycle pipe 8 is connected almost vertically to the upper part of FIG.
(And FIG. 3A).
【0023】尚、気泡除去配管9の設置位置について
は、スラリ循環手段3の入口側配管3aからの気泡分離
を効果的に行うため、入口側配管3aの配管下部に設け
られたストレーナ部(図示されず)の直上部など、部分
的にスラリの流速が遅くなる箇所に設けてよい。The position of the air bubble removal pipe 9 is determined by a strainer section (shown in the figure) provided below the inlet side pipe 3a in order to effectively separate bubbles from the inlet side pipe 3a of the slurry circulation means 3. However, it may be provided at a location where the flow velocity of the slurry is partially reduced, such as immediately above the location.
【0024】又、同様にスラリ循環手段3の入口側配管
3aからの気泡分離を効果的に行うため、気泡除去配管
9と入口側配管3a上面部との接続部分において、この
部分の入口側配管3a上面部を気泡を集め易い形状(例
えば、図3Bに示される平べったい箱形部分3cなど)
に形成してもよい。Similarly, in order to effectively separate bubbles from the inlet pipe 3a of the slurry circulating means 3, at the connection between the bubble removing pipe 9 and the upper surface of the inlet pipe 3a, the inlet pipe of this portion is connected. The upper surface 3a has a shape that easily collects bubbles (for example, a flat box-shaped portion 3c shown in FIG. 3B).
May be formed.
【0025】又、リサイクル配管8と気泡除去配管9と
の直径比その他の具体的な構成に関しては、リサイクル
配管8内を流れるスラリの流速がリサイクル配管8に接
続された気泡除去配管9内の気泡及び(気泡と共に流れ
る)一部のスラリの流速より充分に速く、よってこの流
速差によりこれらの配管8,9にエジェクタ効果が生じ
て、気泡除去配管9を出たスラリが速やかに吸収塔1側
に吸引されるように構成することが望ましい。Further, regarding the specific ratio of the diameter of the recycle pipe 8 to the bubble removal pipe 9 and other specific configurations, the flow rate of the slurry flowing in the recycle pipe 8 is determined by the air bubbles in the bubble removal pipe 9 connected to the recycle pipe 8. In addition, the flow velocity is sufficiently higher than the flow velocity of some of the slurries (flowing together with the bubbles). Therefore, an ejector effect is generated in these pipes 8 and 9 due to the flow velocity difference, and the slurry exiting the bubble removal pipe 9 is quickly moved to the absorption tower 1 side. It is desirable to be configured to be sucked in.
【0026】又、リサイクル配管8及び気泡除去配管9
の両方において、その配管の口径は15A〜25A程度
とし、スラリ循環手段3の循環流量に影響を与えないよ
うに構成する。The recycle pipe 8 and the bubble removal pipe 9
In both cases, the diameter of the pipe is set to about 15A to 25A so that the circulation flow rate of the slurry circulation means 3 is not affected.
【0027】石炭等の燃料がボイラ10で燃焼され、硫
黄分を含んだ排ガスが発生する。硫黄分を含んだ排ガス
は、ボイラ10から脱硝装置11に導入されて脱硝さ
れ、脱硝された排ガスは、エアヒータ12,電気集塵器
13及びガスガスヒータ14を介して吸収塔1の下部に
導入される。Fuel such as coal is burned in the boiler 10 to generate sulfur-containing exhaust gas. Exhaust gas containing sulfur is introduced from the boiler 10 to the denitration device 11 for denitration, and the denitrated exhaust gas is introduced into the lower part of the absorption tower 1 via the air heater 12, the electric dust collector 13 and the gas gas heater 14. You.
【0028】吸収塔1の下部に導入された排ガスは、吸
収塔1内を上昇する。このとき、スプレノズル4を介し
てアルカリ吸収剤を含んだ液(スラリ)が排ガスに噴霧
され、この結果、スラリと排ガスとが気液接触して排ガ
スに含まれる硫黄分がアルカリ吸収剤に吸収され、脱硫
が行われる。The exhaust gas introduced into the lower part of the absorption tower 1 rises in the absorption tower 1. At this time, a liquid (slurry) containing an alkali absorbent is sprayed on the exhaust gas through the spray nozzle 4, and as a result, the slurry and the exhaust gas come into gas-liquid contact, and the sulfur content contained in the exhaust gas is absorbed by the alkali absorbent. , Desulfurization is performed.
【0029】脱硫された排ガスは、ミストエリミネータ
6を介して吸収塔1の頂部から排出され、ガスガスヒー
タ14及び煙突15を介して大気放出される。The desulfurized exhaust gas is discharged from the top of the absorption tower 1 through the mist eliminator 6 and discharged to the atmosphere through the gas gas heater 14 and the chimney 15.
【0030】一方、吸収塔1の液溜部1aに溜まった液
は、ポンプ2によりスラリ循環手段3を介して吸収塔1
の液溜部1aから抜き取られると共にスプレノズル4に
戻されて再び噴霧され、以下、上記の過程が繰り返され
る。又、スラリ供給手段7によって、吸収塔1内にスラ
リが適宜供給されると共に、酸化空気が酸化手段5によ
って吸収塔1の液溜部1aに送り込まれ、脱硫反応によ
って生成した亜硫酸塩(CaSO3 等)が強制的に酸化
される。On the other hand, the liquid collected in the liquid storage section 1 a of the absorption tower 1 is pumped by the pump 2 through the slurry circulation means 3.
And is returned to the spray nozzle 4 and sprayed again, and the above process is repeated thereafter. Slurry is appropriately supplied into the absorption tower 1 by the slurry supply means 7, and oxidizing air is fed into the liquid reservoir 1a of the absorption tower 1 by the oxidization means 5, and the sulfite (CaSO 3 Etc.) are forcibly oxidized.
【0031】さて、吸収塔1の液溜部1aに溜まってい
る(スラリ)液には、上述のように酸化手段5によって
空気が吹き込まれ、この結果、スラリ中に微小な気泡が
発生する。従って、吸収塔1の液溜部1aからスラリが
ポンプ2によって抜き取られ、スラリ循環手段3の入口
側配管3aに導入される際、これらの微小な気泡もスラ
リと共に吸引されて入口側配管3aに入る。As described above, air is blown into the (slurry) liquid stored in the liquid storage section 1a of the absorption tower 1 by the oxidizing means 5 as described above, and as a result, fine bubbles are generated in the slurry. Therefore, when the slurry is withdrawn from the liquid reservoir 1a of the absorption tower 1 by the pump 2 and introduced into the inlet-side pipe 3a of the slurry circulating means 3, these minute bubbles are also sucked together with the slurry and are sent to the inlet-side pipe 3a. enter.
【0032】ところが、気泡は、その比重の関係上、ス
ラリ循環手段3の入口側配管3aの配管の上部をスラリ
の一部と共に流れるので、気泡除去配管9に達するとこ
れにより速やかに捕捉され、該スラリの一部と共に気泡
除去配管9内を上昇する。一方、気泡除去配管9によっ
て気泡を除去された残りのスラリは、ポンプ2を介して
スラリ循環手段3の出口側配管3bに入り、その一部は
リサイクル配管8に分岐すると共にリサイクル配管8を
介して吸収塔1に戻され、残りはそのままスラリ循環手
段3の出口側配管3bを上昇してスプレノズル4に導か
れる。However, due to its specific gravity, the bubbles flow along the upper part of the pipe of the inlet side pipe 3a of the slurry circulating means 3 together with part of the slurry. It rises in the bubble removal pipe 9 together with a part of the slurry. On the other hand, the remaining slurry from which bubbles have been removed by the bubble removing pipe 9 enters the outlet side pipe 3b of the slurry circulating means 3 via the pump 2, and a part of the slurry branches off to the recycling pipe 8 and via the recycling pipe 8. The remainder is returned to the absorption tower 1, and the remainder goes up the outlet side pipe 3 b of the slurry circulation means 3 and is guided to the spray nozzle 4.
【0033】気泡除去配管9に分岐した気泡及びスラリ
は、気泡除去配管9内を上昇してリサイクル配管8に入
る。すると、これらの配管8,9には上述のようにエジ
ェクタ効果が発生しているため、このエジェクタ効果に
より、気泡除去配管9を出た気泡及びスラリが速やかに
吸収塔1側に吸引される。The bubbles and the slurry branched to the bubble removing pipe 9 rise in the bubble removing pipe 9 and enter the recycling pipe 8. Then, since the ejector effect is generated in the pipes 8 and 9 as described above, the bubbles and the slurry that have flowed out of the bubble removing pipe 9 are quickly sucked toward the absorption tower 1 by the ejector effect.
【0034】つまり、気泡除去配管9によって分離され
た気泡は、リサイクル配管8を介して散失することなく
吸収塔1内に戻され、又、このように戻された気泡が吸
収塔1の液溜部1aから再び抜き出されたとしても、こ
れらは気泡除去配管9によって再度確実に捕捉されて吸
収塔1内に戻される。従って、スラリと共にポンプ2に
流入する気泡の量が大幅に減少し、この結果、ポンプ2
に流入する気泡の量をポンプ2の運転に影響を及ぼさな
い程度の量に常に維持できる。That is, the bubbles separated by the bubble removal pipe 9 are returned to the absorption tower 1 through the recycling pipe 8 without being lost, and the bubbles thus returned are collected in the liquid storage of the absorption tower 1. Even if they are extracted again from the section 1a, they are surely captured again by the bubble removal pipe 9 and returned into the absorption tower 1. Therefore, the amount of bubbles flowing into the pump 2 together with the slurry is greatly reduced, and as a result, the pump 2
Can always be maintained at an amount that does not affect the operation of the pump 2.
【0035】[0035]
【発明の効果】以上、要するに、本発明に係る排煙脱硫
装置によれば、吸収塔からポンプによってスラリを抜き
出して循環させるスラリ循環手段の配管を改良すること
により、吸収塔から抜き出されたスラリに含まれる気泡
を比較的単純な方法で確実に分離して吸収塔に戻せるの
で、ポンプに流入する気泡の量を大幅に減少可能であ
り、従って、気泡がポンプの運転に及ぼす好ましくない
影響を確実に防止できる。In summary, according to the flue gas desulfurization apparatus of the present invention, the slurry is extracted from the absorption tower by improving the piping of the slurry circulating means for extracting and circulating the slurry from the absorption tower. Since the bubbles contained in the slurry can be reliably separated and returned to the absorption tower in a relatively simple manner, the amount of bubbles flowing into the pump can be significantly reduced, and therefore, the undesirable effects of the bubbles on the operation of the pump. Can be reliably prevented.
【図1】本発明の排煙脱硫装置を含む一般的な排煙処理
システムの概略図である。FIG. 1 is a schematic view of a general flue gas treatment system including a flue gas desulfurization device of the present invention.
【図2】図1の排煙脱硫装置の部分拡大図である。FIG. 2 is a partially enlarged view of the flue gas desulfurization device of FIG.
【図3A】図2の入口側配管と気泡除去配管との接続部
分の拡大側断面図である。FIG. 3A is an enlarged side sectional view of a connection portion between an inlet-side pipe and a bubble removing pipe in FIG. 2;
【図3B】図2の入口側配管と気泡除去配管との接続部
分の別の拡大側断面図である。FIG. 3B is another enlarged sectional side view of a connection portion between the inlet-side pipe and the bubble removing pipe in FIG. 2;
【図4】従来の排煙脱硫装置を含む一般的な排煙処理シ
ステムの概略図である。FIG. 4 is a schematic view of a general flue gas treatment system including a conventional flue gas desulfurization device.
1 吸収塔 1a 液溜部 2 ポンプ 3a 入口側配管 3b 出口側配管 8 リサイクル配管 9 気泡除去配管 20 排煙脱硫装置 DESCRIPTION OF SYMBOLS 1 Absorption tower 1a Liquid storage part 2 Pump 3a Inlet side piping 3b Outlet side piping 8 Recycle piping 9 Air bubble removal piping 20 Smoke flue gas desulfurization equipment
Claims (1)
のポンプを吸収塔に接続した排煙脱硫装置において、ポ
ンプを吸収塔の外側下部に設けると共に該ポンプの出口
側配管を該吸収塔の液溜部上方に起立させ、該起立した
出口側配管と該吸収塔の液溜部とを結んでスラリを戻す
リサイクル配管を接続し、且つ該リサイクル配管と該ポ
ンプの入口側配管とを結んで該入口側配管上面部からス
ラリに含まれる気泡を該リサイクル配管に回収する気泡
除去配管を接続したことを特徴とする排煙脱硫装置。In a flue gas desulfurization apparatus in which a pump for spraying and circulating an alkali absorbent is connected to an absorption tower, a pump is provided at a lower portion outside the absorption tower and an outlet pipe of the pump is connected to the absorption tower. A recycle pipe for returning the slurry by connecting the outlet pipe that has been raised up to the upper part of the liquid reservoir and the liquid reservoir of the absorption tower is connected, and connecting the recycle pipe to the inlet pipe of the pump. A flue gas desulfurization apparatus, wherein a bubble removal pipe for collecting bubbles contained in the slurry from the upper surface of the inlet side pipe to the recycling pipe is connected.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9140124A JPH10328529A (en) | 1997-05-29 | 1997-05-29 | Flue gas desulfurization equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9140124A JPH10328529A (en) | 1997-05-29 | 1997-05-29 | Flue gas desulfurization equipment |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH10328529A true JPH10328529A (en) | 1998-12-15 |
Family
ID=15261465
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9140124A Pending JPH10328529A (en) | 1997-05-29 | 1997-05-29 | Flue gas desulfurization equipment |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH10328529A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002248319A (en) * | 2001-02-23 | 2002-09-03 | Ishikawajima Harima Heavy Ind Co Ltd | Wet flue gas desulfurization equipment |
-
1997
- 1997-05-29 JP JP9140124A patent/JPH10328529A/en active Pending
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002248319A (en) * | 2001-02-23 | 2002-09-03 | Ishikawajima Harima Heavy Ind Co Ltd | Wet flue gas desulfurization equipment |
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