JPH0369568B2 - - Google Patents
Info
- Publication number
- JPH0369568B2 JPH0369568B2 JP58130769A JP13076983A JPH0369568B2 JP H0369568 B2 JPH0369568 B2 JP H0369568B2 JP 58130769 A JP58130769 A JP 58130769A JP 13076983 A JP13076983 A JP 13076983A JP H0369568 B2 JPH0369568 B2 JP H0369568B2
- Authority
- JP
- Japan
- Prior art keywords
- liquid
- spray nozzle
- absorption
- absorption liquid
- tower
- 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 - Lifetime
Links
- 238000010521 absorption reaction Methods 0.000 claims description 60
- 239000007788 liquid Substances 0.000 claims description 54
- 239000007789 gas Substances 0.000 claims description 28
- 239000007921 spray Substances 0.000 claims description 27
- 238000001816 cooling Methods 0.000 claims description 17
- 239000000110 cooling liquid Substances 0.000 claims description 15
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 13
- 238000006477 desulfuration reaction Methods 0.000 claims description 13
- 230000023556 desulfurization Effects 0.000 claims description 13
- 239000003546 flue gas Substances 0.000 claims description 13
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 claims description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 6
- 238000011144 upstream manufacturing Methods 0.000 claims description 4
- 235000019738 Limestone Nutrition 0.000 claims description 3
- 239000006028 limestone Substances 0.000 claims description 3
- 239000002002 slurry Substances 0.000 claims description 3
- 239000000428 dust Substances 0.000 description 33
- 239000002826 coolant Substances 0.000 description 8
- 239000006227 byproduct Substances 0.000 description 5
- 238000000605 extraction Methods 0.000 description 5
- 238000010586 diagram Methods 0.000 description 4
- 239000010440 gypsum Substances 0.000 description 4
- 229910052602 gypsum Inorganic materials 0.000 description 4
- 239000002699 waste material Substances 0.000 description 4
- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 3
- 239000002250 absorbent Substances 0.000 description 3
- 230000002745 absorbent Effects 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 2
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 2
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 2
- 229910000040 hydrogen fluoride Inorganic materials 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 239000003595 mist Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 238000005192 partition Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 238000003809 water extraction Methods 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Gas Separation By Absorption (AREA)
Description
【発明の詳細な説明】
本発明は湿式排煙脱硫装置に係り、特に吸収塔
で二酸化イオウ(SO2)の吸収とダストの除去を
行なう湿式排煙脱硫装置に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a wet flue gas desulfurization system, and more particularly to a wet flue gas desulfurization system that uses an absorption tower to absorb sulfur dioxide (SO 2 ) and remove dust.
従来湿式排煙脱硫装置は、第1図に示すよう
に、排ガス2を冷却し、かつその中のダスト、酸
性ミストなどを除去する冷却、除じん塔(以下、
除じん塔と称する)6と、該除じん塔6に連絡ダ
クト18を介して連結された二酸化イオウ吸収塔
(以下、単に吸収塔という)20とから構成され
る。ボイラ等の排ガス2はボイラ煙道4を経て、
除じん塔6に導入され、ここで除じん塔循環タン
ク14からポンプ12、ライン8を介して循環さ
れ、塔頂からスプレーされる循環水と接触し、冷
却されるとともに、排ガス中のダストおよび塩化
水素(HCl)、フツ化水素(HF)等の不純物が除
去される。次いでこのガスは連絡煙道4を経て吸
収塔20に送られ、ここで塔底からポンプ24に
よりライン28を介して塔頂に送られ、塔内にス
プレーされる石灰石スラリーのような吸収液と接
触し、排ガス中のSO2が吸収、除去され、また副
生品としてCaSO2,CaSO4(石こう)等が生成さ
れる。SO2を除去したクリーンな排ガス32は煙
道30から排出される。なお、10は循環水抜き
出し配管、13は冷却、除じん用水配管、22は
吸収液供給配管、26は吸収液抜き出し配管であ
る。 As shown in Fig. 1, conventional wet flue gas desulfurization equipment includes a cooling and dust removal tower (hereinafter referred to as
The dust removal tower 6 is composed of a sulfur dioxide absorption tower 20 (hereinafter simply referred to as an absorption tower) connected to the dust removal tower 6 via a communication duct 18. The exhaust gas 2 from the boiler etc. passes through the boiler flue 4,
It is introduced into the dust removal tower 6, where it is circulated from the dust removal tower circulation tank 14 via the pump 12 and the line 8, and comes into contact with the circulating water sprayed from the top of the tower, where it is cooled and removes the dust and dust in the flue gas. Impurities such as hydrogen chloride (HCl) and hydrogen fluoride (HF) are removed. This gas is then sent via a connecting flue 4 to an absorption tower 20 where it is pumped from the bottom by a pump 24 through a line 28 to the top of the tower where it is mixed with an absorbent liquid, such as limestone slurry, which is sprayed into the tower. Upon contact, SO 2 in the exhaust gas is absorbed and removed, and by-products such as CaSO 2 and CaSO 4 (gypsum) are generated. Clean exhaust gas 32 from which SO 2 has been removed is discharged from the flue 30. In addition, 10 is a circulating water extraction piping, 13 is a water piping for cooling and dust removal, 22 is an absorption liquid supply piping, and 26 is an absorption liquid extraction piping.
上述のように、従来の湿式排煙脱硫装置では、
除じん塔6と吸収塔20を別置して、ガスの冷
却、除じんとSO2の吸収、除去を別々の塔でおこ
なうのが一般的であつた。 As mentioned above, in conventional wet flue gas desulfurization equipment,
It was common practice to separate the dust removal tower 6 and the absorption tower 20 so that gas cooling, dust removal, and SO 2 absorption and removal were performed in separate towers.
しかしながら、このような装置では、2基の塔
を要し、設備コストが高くなるばかりでなく、設
置スペースも大きくなる。 However, such a device requires two towers, which not only increases the equipment cost but also increases the installation space.
本発明の目的は、上記した従来技術の欠点をな
くし、1塔で排ガスの冷却、除じんおよびSO2の
吸収、除去を行ない、且つ冷却、除じんに使用し
た液がSO2の吸収液と混合しないようにした、ダ
スト分離方式の湿式排煙脱硫装置を提供すること
にある。 The purpose of the present invention is to eliminate the above-mentioned drawbacks of the prior art, to perform exhaust gas cooling, dust removal, and SO 2 absorption and removal in one tower, and to provide a system in which the liquid used for cooling and dust removal is an SO 2 absorption liquid. An object of the present invention is to provide a dust separation type wet flue gas desulfurization device that prevents mixing.
本発明は、SO2を含む排ガスの入口ダクトおよ
び処理ガスの出口ダクトを有する塔本体と、塔本
体に入つた排ガスの上流側に設けられた冷却、除
じん用液(以下、冷却液と称する)のスプレノズ
ルと、該スプレノズルの直下に設けられた冷却液
の受け容器と、該受け容器に入つた冷却液を一旦
タンクに貯留した後、ポンプにより前記スプレノ
ズルに循環させる冷却液循環手段と、前記塔本体
に入つた排ガスの下流側に設けられたSO2吸収液
のスプレノズルと、該スプレノズルの直下に設け
られた吸収液の受け容器と、該受け容器に入つた
吸収液を一旦タンクに貯留した後、ポンプにより
前記吸収液のスプレノズルに循環させる吸収液循
環手段とを有することを特徴とする。 The present invention consists of a tower body having an inlet duct for exhaust gas containing SO 2 and an outlet duct for treated gas, and a cooling and dust removal liquid (hereinafter referred to as cooling liquid) provided upstream of the exhaust gas entering the tower body. ), a cooling liquid receiving container provided directly below the spray nozzle, and a cooling liquid circulation means for once storing the cooling liquid in the receiving container in a tank and then circulating it to the spray nozzle by a pump; A spray nozzle for the SO 2 absorption liquid is provided on the downstream side of the exhaust gas that has entered the tower body, a receiving container for the absorption liquid is provided directly below the spray nozzle, and the absorption liquid that has entered the receiving container is temporarily stored in a tank. After that, the absorbent liquid circulating means is configured to circulate the absorbent liquid to the spray nozzle using a pump.
本発明は、吸収塔内で排ガスの冷却、除じんと
SO2吸収を同時に行うものであるが、冷却、除じ
んには通常は、水を使用し、洗浄後の廃液は容器
に受けて回収し、タンクにたくわえて、循環、使
用し、一方、SO2吸収、除去に使用する吸収液に
ついても、SO2の吸収後は、吸収液を別の容器に
受けて回収し、吸収塔タンクにたくわえて、循
環、使用するものである。このようにそれぞれの
液の下に別の容器を設置して、塔内で液が混合し
ないようにするとともに、それぞれの液を別のタ
ンクに分離して回収することによつて、1塔で除
じんと吸収という両方の機能をもたせることがで
きる。 The present invention cools exhaust gas and removes dust in an absorption tower.
Although SO 2 absorption is performed at the same time, water is usually used for cooling and dust removal, and the waste liquid after washing is collected in a container and stored in a tank for circulation and use. 2 Regarding the absorption liquid used for absorption and removal, after absorbing SO 2 , the absorption liquid is collected in another container and stored in the absorption tower tank for circulation and use. In this way, by installing separate containers under each liquid to prevent the liquids from mixing within the tower, and by separating and collecting each liquid in separate tanks, one tower can be used. It can have the functions of both dust removal and absorption.
上記吸収液または冷却液の受け容器は、上方か
ら滴下される液を受けとめて下方へ落下させない
ものであればよいが、これらの液のスプレノズル
の直下に、下方からのガス流に対して大きな抵抗
とならないように配置される。好適例としては、
後述の第3図に示すようにトラフ状の容器を多段
に設けたものがあげられる。 The above-mentioned absorbing liquid or cooling liquid receiving container may be one that can catch the liquid dripping from above and prevent it from falling downward, but there is a container directly below the spray nozzle for these liquids that has a large resistance to gas flow from below. It is arranged so that it does not become . A suitable example is
One example is one in which trough-shaped containers are provided in multiple stages, as shown in FIG. 3, which will be described later.
また、容器に受けた液を回収し、一旦貯留する
タンクとしては、取扱い量の多い吸収液を吸収塔
下部タンクに回収し、取扱い量の少ないダストを
含む除じん後の液を別置のタンクに回収するのが
有利であるが、それらの取扱い量を考慮して吸収
塔下部タンクを仕切つて回収することもできる。 In addition, the tank that collects and temporarily stores the liquid received in the container is used to collect the absorbed liquid, which is handled in large quantities, into the lower tank of the absorption tower, and to store the liquid, which contains dust, which is handled in small quantities, in a separate tank. Although it is advantageous to collect the waste in the lower part of the absorption tower, it is also possible to partition the tank at the bottom of the absorption tower and collect the waste in consideration of the amount to be handled.
以下、本発明を図面によりさらに詳細に説明す
る。 Hereinafter, the present invention will be explained in more detail with reference to the drawings.
第2図は、本発明の一実施例を示す湿式脱硝装
置の冷却、除じん兼吸収塔の構成を示す説明図で
ある。この装置は、塔下部に排ガス2の入口ダク
ト4および塔頂部の処理ガス32の出口ダクト3
0を有する塔本体38と、該塔本体下部に一体的
に設けられた吸収液循環タンク34と、塔内上部
に設けられた吸収液のスプレノズル40と、前記
タンク34に貯留された吸収液をポンプ24を介
して吸収液スプレノズル40に循環させる配管系
28と、スプレノズル40の下方に設けられ、該
スプレノズルから散布された吸収液を受けとめる
受け容器44と、該受け容器44の吸収液を前記
循環タンク34に流下させる回収ダクト46と、
排ガス入口ダクト4から導入される排ガスの上流
側で、かつ前記吸収液の受け容器44の下方に設
けられた冷却液のスプレノズル36と、その下方
に設けられ、該スプレノズルから散布された冷却
液を受けとめる受け容器48と、該受け容器48
の冷却液を一旦貯留する冷却液循環タンク54
と、該タンク54の冷却液をポンプ52により前
記冷却液スプレノズル36に循環させる配管系5
0とから主として構成される。なお、22は吸収
液(石灰石スラリ)供給配管、26はその抜き出
し配管、42は塔頂部に設けられたデミスタ、4
5は冷却液供給配管、56はその抜き出し配管を
示す。 FIG. 2 is an explanatory diagram showing the configuration of a cooling and dust removal/absorption tower of a wet denitrification apparatus showing an embodiment of the present invention. This device has an inlet duct 4 for exhaust gas 2 at the bottom of the column and an outlet duct 3 for process gas 32 at the top of the column.
0, an absorption liquid circulation tank 34 provided integrally in the lower part of the column main body, an absorption liquid spray nozzle 40 provided in the upper part of the column, and an absorption liquid stored in the tank 34. A piping system 28 that circulates the absorption liquid to the absorption liquid spray nozzle 40 via the pump 24, a receiving container 44 that is provided below the spray nozzle 40 and receives the absorption liquid sprayed from the spray nozzle, and a receiving container 44 that circulates the absorption liquid in the receiving container 44. a recovery duct 46 that flows down to the tank 34;
A coolant spray nozzle 36 is provided on the upstream side of the exhaust gas introduced from the exhaust gas inlet duct 4 and below the absorption liquid receiving container 44, and a coolant spray nozzle 36 is provided below the coolant spray nozzle 36 to spray the coolant sprayed from the spray nozzle. A receiving container 48 for receiving and the receiving container 48
Coolant circulation tank 54 that temporarily stores the coolant of
and a piping system 5 for circulating the coolant in the tank 54 to the coolant spray nozzle 36 by a pump 52.
It is mainly composed of 0 and 0. In addition, 22 is an absorption liquid (limestone slurry) supply pipe, 26 is its extraction pipe, 42 is a demister provided at the top of the tower, 4
Reference numeral 5 indicates a cooling liquid supply pipe, and reference numeral 56 indicates an extraction pipe thereof.
第3図は、第2図に示された吸収液または冷却
液の受け容器(44または48)の断面図を示し
たもので、この受け容器は、断面U字型の傾斜さ
せたトラフ58A,58Bを千鳥状に2段に配設
したものからなる。上段のトラフ同志の間隔Cは
下段のトラフの開口幅Dよりも狭くなるように配
置され、上方から落下する液滴60が上段のトラ
フ58A間を通過しても下段のトラフ58Bで受
けとめられるようになつている。また上段トラフ
58Aと下段トラフ58Bの間隔はガス62の流
路抵抗が過大にならず、かつ液滴60が誤つてト
ラフ外に落下しないように適宜定められる。トラ
フ58Aおよび58Bに落下した液滴は該トラフ
の傾斜方向、すなわち第2図の受け容器44また
は48の紙面右手方向に流れ、前述のようにタン
ク34または54内に回収される。 FIG. 3 shows a cross-sectional view of the absorption liquid or cooling liquid receiving vessel (44 or 48) shown in FIG. 58B arranged in two stages in a staggered manner. The interval C between the upper troughs is arranged to be narrower than the opening width D of the lower trough, so that even if a droplet 60 falling from above passes between the upper troughs 58A, it is received by the lower trough 58B. It's getting old. Further, the interval between the upper trough 58A and the lower trough 58B is appropriately determined so that the flow path resistance of the gas 62 does not become excessive and the droplets 60 do not fall out of the trough by mistake. The droplets falling into the troughs 58A and 58B flow in the direction of the inclination of the troughs, ie, in the right-hand direction of the receiving container 44 or 48 in FIG. 2, and are collected in the tank 34 or 54 as described above.
上記構成の装置において、排ガス2は、ダクト
4を通つて吸収塔38に入り、まず上流側のスプ
レノズル36から噴霧された冷却液の液滴によつ
て冷却、除じんされるが、その液は受け容器48
によつて受けとめられ、下方に落下することなく
回収される。この液は別置されたタンク54に集
められ、ポンプ52によつて上記スプレノズル3
6に戻され、循環、使用される。このようなトラ
フの組合せによる受け容器を用いると、液の下方
への落下は5%以下に抑えることができる。 In the apparatus configured as described above, the exhaust gas 2 enters the absorption tower 38 through the duct 4, and is first cooled and dusted by droplets of cooling liquid sprayed from the upstream spray nozzle 36; Receiving container 48
The object is caught by the object and recovered without falling downward. This liquid is collected in a separate tank 54, and pumped by a pump 52 to the spray nozzle 3.
6, circulated and used. When a receiving container with such a combination of troughs is used, the downward drop of the liquid can be suppressed to 5% or less.
このようにして、冷却、除じんされた排ガスは
次に塔上部のSO2吸収用スプレノズル30から噴
霧された液滴によつてSO2が吸収、除去された
後、液滴は受け容器44によつて集められ、回収
ダクトト46を経て塔下部のタンク部34に回収
される。この回収液は吸収塔循環ポンプ24によ
つて塔上部に戻され、循環、使用される。 In this way, the cooled and dust-removed exhaust gas is then absorbed and removed by droplets sprayed from the SO 2 absorption spray nozzle 30 at the top of the tower, and then the droplets are transferred to the receiving container 44. The waste is collected through the recovery duct 46 and recovered into the tank section 34 at the bottom of the tower. This recovered liquid is returned to the upper part of the tower by the absorption tower circulation pump 24, and is circulated and used.
SO2を除去した排ガスは塔頂部のデミスタ40
で飛散ミストを除去した後、清浄ガス32として
煙道30から排出される。吸収液は配管22から
供給され、SO2の吸収量に応じて配管26から抜
き出され、酸化塔(図示せず)を経て副生品であ
る石こうが生成、回収される。一方、冷却、除じ
ん用の水は配管45から供給され、タンク54内
のダスト濃度に応じて配管56から抜き出され、
別途処理される。 The exhaust gas from which SO 2 has been removed is sent to the demister 40 at the top of the tower.
After removing the scattered mist, it is discharged from the flue 30 as clean gas 32. The absorption liquid is supplied from a pipe 22, extracted from a pipe 26 according to the amount of SO 2 absorbed, passes through an oxidation tower (not shown), and gypsum as a by-product is produced and recovered. On the other hand, water for cooling and dust removal is supplied from a pipe 45 and extracted from a pipe 56 depending on the dust concentration in the tank 54.
Processed separately.
なお、冷却液と吸収液とを分離することなく、
同一タンクに混合して回収した場合には、塔入口
のガス中のダストの量によつては、副生品である
石こう中のダスト含量が増加し、副生品の品質を
低下させるばかりでなく、石炭燃焼排ガスのよう
にHCl、HFなどを含む排ガスの場合には、吸収
液にこれらの酸性成分が混入し、SO2吸収性能が
低下する。 In addition, without separating the cooling liquid and absorption liquid,
If they are mixed and collected in the same tank, depending on the amount of dust in the gas at the tower inlet, the dust content in the by-product gypsum will increase, which will only deteriorate the quality of the by-product. However, in the case of exhaust gas containing HCl, HF, etc., such as coal combustion exhaust gas, these acidic components are mixed into the absorption liquid, reducing SO 2 absorption performance.
本発明によれば、1塔で冷却、除じんとSO2の
吸収、除去の機能をもたせたために、装置がコン
パクトになり、このため設置面積が少くて済み、
また冷却、除じんと脱硫を完全に分離して行うよ
うにしたため、排ガス中のダストやHCl、HFな
どの不純物が吸収液中に混入せず、吸収液の性能
低下を防止するとともに、副生品である石こうの
品質を高めることができる。また冷却液または吸
収液の受け器を塔内に設けたことにより、排ガス
の分散性が良好になり、気液接触効果が増大し、
脱硫率が向上する効果も得られる。 According to the present invention, since the functions of cooling, dust removal, and SO 2 absorption and removal are provided in one tower, the equipment becomes compact, and therefore the installation area is small.
In addition, since cooling, dust removal, and desulfurization are completely separated, impurities such as dust, HCl, and HF in the flue gas do not mix into the absorption liquid, preventing deterioration in the performance of the absorption liquid and preventing by-products. The quality of the gypsum product can be improved. In addition, by providing a receiver for the cooling liquid or absorption liquid in the tower, the dispersibility of the exhaust gas is improved and the gas-liquid contact effect is increased.
The effect of improving the desulfurization rate can also be obtained.
第1図は、従来の湿式排煙脱硫装置の構成を示
す図、第2図は、本発明の湿式排煙脱硫装置の構
成を示す図、第3図は、本発明に用いる吸収また
は冷却、除じん後の液の受け容器の配置を模式的
に示す図である。
2……排ガス、4……排ガス煙道(ダクト)、
22……吸収液供給配管、24……吸収用ポン
プ、26……吸収液抜出し配管、34……吸収液
タンク、36……冷却、除じん用スプレノズル、
40……吸収用スプレノズル、42……デミス
タ、44……吸収用受け容器、45……冷却、除
じん用水、46……吸収用回収ダクト、48……
冷却、除じん用受け容器、54……冷却、除じん
用タンク、56……除じん後抜出し配管。
FIG. 1 is a diagram showing the configuration of a conventional wet flue gas desulfurization device, FIG. 2 is a diagram showing the configuration of a wet flue gas desulfurization device of the present invention, and FIG. 3 is a diagram showing the absorption or cooling system used in the present invention. It is a figure which shows typically the arrangement|positioning of the receiving container of the liquid after dust removal. 2...Exhaust gas, 4...Exhaust gas flue (duct),
22...Absorption liquid supply piping, 24...Absorption pump, 26...Absorption liquid extraction pipe, 34...Absorption liquid tank, 36...Spray nozzle for cooling and dust removal,
40... Spray nozzle for absorption, 42... Demister, 44... Receiving container for absorption, 45... Water for cooling and dust removal, 46... Recovery duct for absorption, 48...
Receiving container for cooling and dust removal, 54...Tank for cooling and dust removal, 56...Piping for extraction after dust removal.
Claims (1)
クトおよび処理ガスの出口ダクトを有する塔本体
と、塔本体に入つた排ガスの上流側に設けられた
冷却液のスプレノズルと、該スプレノズルの直下
に設けられた冷却液の受け容器と、該受け容器に
入つた冷却液を一旦タンクに貯留した後、ポンプ
により前記スプレノズルに循環させる冷却液循環
手段と、前記塔本体に入つた排ガスの下流側に設
けられたSO2吸収液のスプレノズルと、該スプレ
ノズルの直下に設けられた吸収液の受け容器と、
該受け容器に入つた吸収液を一旦タンクに貯留し
た後、ポンプにより前記吸収液のスプレノズルに
循環させる吸収液循環手段とを有することを特徴
とする湿式排煙脱硫装置。 2 特許請求の範囲1において、前記受け容器
は、トレー状容器を千鳥状に多段配置したもので
あることを特徴とする湿式排煙脱硫装置。 3 特許請求の範囲1または2において、前記冷
却液は水であり、前記SO2吸収液は石灰石スラリ
であることを特徴とする湿式排煙脱硫装置。 4 特許請求の範囲1ないし3のいずれかにおい
て、前記吸収液のタンクは塔本体の下部に一体的
に設けられ、前記冷却後のタンクは塔本体外に配
置されていることを特徴とする湿式排煙脱硫装
置。[Scope of Claims] 1. A tower body having an inlet duct for exhaust gas containing sulfur dioxide (SO 2 ) and an outlet duct for treated gas, and a cooling liquid spray nozzle provided on the upstream side of the exhaust gas entering the tower body; a cooling liquid receiving container provided directly below the spray nozzle; a cooling liquid circulating means for once storing the cooling liquid in the receiving container in a tank and then circulating it to the spray nozzle by a pump; A spray nozzle for an SO 2 absorption liquid provided on the downstream side of the exhaust gas, a receiving container for the absorption liquid provided directly below the spray nozzle,
A wet flue gas desulfurization device comprising an absorption liquid circulation means that once stores the absorption liquid in the receiving container in a tank and then circulates the absorption liquid to a spray nozzle using a pump. 2. The wet flue gas desulfurization apparatus according to claim 1, wherein the receiving container is a tray-shaped container arranged in multiple stages in a staggered manner. 3. The wet flue gas desulfurization device according to claim 1 or 2, wherein the cooling liquid is water, and the SO 2 absorption liquid is limestone slurry. 4. The wet type according to any one of claims 1 to 3, characterized in that the absorption liquid tank is provided integrally at the lower part of the tower main body, and the tank after cooling is arranged outside the tower main body. Flue gas desulfurization equipment.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58130769A JPS6022921A (en) | 1983-07-20 | 1983-07-20 | Wet desulfurizing apparatus of waste gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58130769A JPS6022921A (en) | 1983-07-20 | 1983-07-20 | Wet desulfurizing apparatus of waste gas |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6022921A JPS6022921A (en) | 1985-02-05 |
| JPH0369568B2 true JPH0369568B2 (en) | 1991-11-01 |
Family
ID=15042218
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP58130769A Granted JPS6022921A (en) | 1983-07-20 | 1983-07-20 | Wet desulfurizing apparatus of waste gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6022921A (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2014188406A (en) * | 2013-03-26 | 2014-10-06 | Babcock-Hitachi Co Ltd | Sea water flue gas desulfurization equipment and operation method thereof |
| CN104208966B (en) * | 2014-08-15 | 2016-01-20 | 杭州中环化工设备有限公司 | Process alloy converting furnace is containing the technique of selenium flue gas |
| CN107774082B (en) * | 2016-08-31 | 2020-10-16 | 中国石油化工股份有限公司 | Method and device for flue gas desulfurization |
| CN108905532A (en) * | 2018-07-31 | 2018-11-30 | 太仓市宇格明叶环保设备有限公司 | A kind of scrubbing tower that the acid-base property for semiconductor workshop is vented |
-
1983
- 1983-07-20 JP JP58130769A patent/JPS6022921A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6022921A (en) | 1985-02-05 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| RU2166355C2 (en) | Plant for withdrawal of so2 from flue gases and production of ammonium sulfate solution | |
| KR100382444B1 (en) | Flue gas cleaning device | |
| US4469493A (en) | Method and apparatus for the purification of gases which contain solid and gaseous impurities | |
| US4039307A (en) | Countercurrent flow horizontal spray absorber | |
| US5413626A (en) | Process for the wet cleaning of gases | |
| RU2038130C1 (en) | Method and equipment for cleaning waste gases | |
| CA2210981A1 (en) | Horizontal multi-washer and method of total cleaning of synthesis gases obtained from the gasification of wastes of the most varied composition | |
| EP0162536A1 (en) | Apparatus for wet type flue gas desulfurization | |
| JPS6336817A (en) | Wet flue gas purifying method and device therefor | |
| JP2001520107A (en) | Flue gas treatment scrubber | |
| PL165481B1 (en) | Method of and apparatus for treating waste gases containing dusty matter and chemical pollutants | |
| PL149355B1 (en) | Method of cooling and dedusting gases and apparatus therefor | |
| JPH06254345A (en) | Horizontal wet type cleaning device and method for removing sulfur dioxide from gaseous stream | |
| JP2014188406A (en) | Sea water flue gas desulfurization equipment and operation method thereof | |
| JPH08281049A (en) | Gas purification method by water | |
| CN104548881A (en) | Method and apparatus for wet desulfurization spray towers | |
| SI9520071A (en) | Improved wet scrubbing method and apparatus for removing sulfur oxides from combustion effluents | |
| CN107690511A (en) | Inline washer with dual water system | |
| EP0879632B1 (en) | Gas-liquid contact apparatus | |
| JPH0369568B2 (en) | ||
| JPH0788325A (en) | Treatment of waste gas and device therefor | |
| US7306776B2 (en) | Method and an apparatus for processing flue gas scrubber material flows | |
| CN106000045B (en) | Boiler smoke depth dust-removal and desulfurizing denitration device | |
| JP3322455B2 (en) | Water spray type air purification device | |
| FI126920B (en) | Exhaust washers and vessels with exhaust washers |