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JPH021523B2 - - Google Patents
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JPH021523B2 - - Google Patents

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Publication number
JPH021523B2
JPH021523B2 JP55037896A JP3789680A JPH021523B2 JP H021523 B2 JPH021523 B2 JP H021523B2 JP 55037896 A JP55037896 A JP 55037896A JP 3789680 A JP3789680 A JP 3789680A JP H021523 B2 JPH021523 B2 JP H021523B2
Authority
JP
Japan
Prior art keywords
spray
gas
particle size
tower
stage
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
Application number
JP55037896A
Other languages
Japanese (ja)
Other versions
JPS56136617A (en
Inventor
Noboru Kajimoto
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 JP3789680A priority Critical patent/JPS56136617A/en
Publication of JPS56136617A publication Critical patent/JPS56136617A/en
Publication of JPH021523B2 publication Critical patent/JPH021523B2/ja
Granted legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Gas Separation By Absorption (AREA)

Description

【発明の詳細な説明】 本発明はガス吸収塔に係り、更に詳しくは、排
ガス中の二酸化いおうの吸収等に好適なスプレ式
ガス吸収塔に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a gas absorption tower, and more particularly to a spray type gas absorption tower suitable for absorbing sulfur dioxide in exhaust gas.

従来より、ガス吸収やガス洗浄操作に用いらる
塔形式には、多孔板方式、ラツヒリング(あるに
はサドル)充填方式、スプレ方式等がある。排ガ
ス中の二酸化いおうなどを炭酸カルシウム懸濁液
で吸収する、いわゆる石灰石スラリ脱硫方式のよ
うに、吸収反応の副生物として硫酸カルシウムな
どの結晶生成がある場合には、多孔板方式や充填
方式の吸収塔においては、反応の進行の場である
多孔板、ラツヒリングなどの上に石こうのスケー
ルが生成、付着して成長することになる。多孔板
方式や充填方式の吸収塔におけるこのスケールト
ラブルは、湿式脱硫プロセスの最大の欠点であ
り、高濃度な二酸化いおうを含む排煙脱硫装置で
は年間1〜2回の装置停止時にスケールを完全除
去することによつて閉塞を回避し、かつ脱硫効
率、吸収効率の低下を防いでいる。
Conventionally, tower types used for gas absorption and gas cleaning operations include the perforated plate type, the rutling (sometimes saddle) filling type, and the spray type. In cases where crystals such as calcium sulfate are formed as a by-product of the absorption reaction, such as in the so-called limestone slurry desulfurization method, in which sulfur dioxide and other substances in exhaust gas are absorbed using a calcium carbonate suspension, perforated plate methods and filling methods are recommended. In the absorption tower, gypsum scale forms, adheres, and grows on the perforated plates, Rutsch rings, etc. where the reaction proceeds. This scale problem in perforated plate type and packed type absorption towers is the biggest drawback of the wet desulfurization process, and in flue gas desulfurization equipment that contains a high concentration of sulfur dioxide, the scale is completely removed when the equipment is shut down once or twice a year. This avoids blockage and prevents a decrease in desulfurization efficiency and absorption efficiency.

一方、最近の石灰火力の復活によつて、排ガス
中の二酸化いおう濃度は上昇し、排煙脱硫装置の
スケールトラブルの急激化が予測されるため、今
後の湿式排煙脱硫装置の吸収塔はスケールトラブ
ルの少いスプレ塔構造が採用されるようになつて
きている。スプレ方式では、結晶を生成する反応
の場は、スプレ液滴の粒表面であり、被吸収ガス
の流れに対向又は同伴して通過する塔内の空間で
あることになる。
On the other hand, with the recent revival of lime-fired power generation, the concentration of sulfur dioxide in flue gas is increasing, and scale problems in flue gas desulfurization equipment are predicted to increase rapidly. Spray tower structures that cause fewer problems are being adopted. In the spray method, the reaction site for producing crystals is the particle surface of the spray droplets, and is the space within the tower through which the absorbed gas flows, either opposite to or accompanied by the flow.

従つて、スプレ塔内の吸収反応の高効率化を計
るための塔設計の要点は、良好な微粒を噴霧する
スプレノズルの選定と、噴霧の分布を均一にする
適切なスプレヘツダのレイアウトにあるといえ
る。
Therefore, the key points in tower design to improve the efficiency of the absorption reaction within the spray tower are the selection of a spray nozzle that sprays fine particles and the appropriate layout of the spray header to ensure uniform spray distribution. .

第1図に典型的な湿式排煙脱硫プロセスフロー
シートの一例を示す。プロセスの主要機器は、ガ
ス入口にある冷却ベンチユリ塔2と吸収塔9であ
る。排ガスは矢印の方向より入口ガスダクト1を
通り冷却ベンチユリ塔2に入り、冷却液循環タン
ク6からポンプ5により送られ配管4を通り冷却
スプレ3から噴霧された冷却水により、排ガスの
温度が低下され、かつガス中のばいじんが第1次
的に除去される。ガス冷却を行なつた冷却液は冷
却塔2の塔底より循環タンク6に戻され、ガスに
同伴された冷却液はデミスタ7で捕集され、戻り
管8を通つて循環タンク6に戻される。
FIG. 1 shows an example of a typical wet flue gas desulfurization process flow sheet. The main equipment of the process is a cooling bench tower 2 and an absorption tower 9 at the gas inlet. The exhaust gas passes through the inlet gas duct 1 in the direction of the arrow, enters the cooling bench lily tower 2, is sent from the cooling liquid circulation tank 6 by the pump 5, passes through the piping 4, and is sprayed from the cooling spray 3, which lowers the temperature of the exhaust gas. , and the soot and dust in the gas is primarily removed. The coolant that has undergone gas cooling is returned to the circulation tank 6 from the bottom of the cooling tower 2, and the coolant entrained in the gas is collected by a demister 7 and returned to the circulation tank 6 through a return pipe 8. .

吸収塔9内には複数段にスプレノズル10が設
けられてあり、循環タンク13からポンプ14に
より配管12を通つてスプレノズル10に吸収液
が送られ、噴霧された冷却液は塔底に溜り循環タ
ンクに戻される。冷却塔2で冷却されたガスは吸
収塔9にその下側より入り上昇し、噴霧吸収液と
向流で気液接触し、脱硫反応(SO2吸収反応)が
進められる。脱硫反応を終えたガスは矢印方向へ
塔9から排出される。11は吸収液を捕集するデ
ミスタである。尚、吸収液循環タンク13には、
吸収液のメーキヤツプ、PH制御系として吸収剤タ
ンク15、供給ポンプ16、配管17が付属して
いる。スプレ式吸収塔9は多くの場合空洞とされ
ているが、多孔板構造とする場合もある。
Spray nozzles 10 are provided in multiple stages in the absorption tower 9, and absorption liquid is sent from a circulation tank 13 to the spray nozzle 10 through a pipe 12 by a pump 14, and the sprayed cooling liquid accumulates at the bottom of the tower and is transferred to the circulation tank. will be returned to. The gas cooled in the cooling tower 2 enters the absorption tower 9 from the lower side and rises, comes into gas-liquid contact with the sprayed absorption liquid in countercurrent, and a desulfurization reaction (SO 2 absorption reaction) proceeds. The gas that has completed the desulfurization reaction is discharged from the tower 9 in the direction of the arrow. 11 is a demister that collects the absorption liquid. In addition, in the absorption liquid circulation tank 13,
An absorbent tank 15, supply pump 16, and piping 17 are attached as an absorbent make-up and PH control system. Although the spray absorption tower 9 is often hollow, it may also have a perforated plate structure.

従来建設され、あるいは現在建設中のスプレ吸
収塔の仕様の一例をあげると、塔径が15mφ、ス
プレノズル個数がスプレヘツダ1段につき約100
個、スプレ段間隔が1.5〜2mで5〜6段のスプ
レヘツダを配置し、液ガス比(L/G)20/N
m3以下の二酸化いおう吸収塔がある。
To give an example of the specifications of spray absorption towers that have been constructed in the past or are currently under construction, the diameter of the tower is 15mφ, and the number of spray nozzles is approximately 100 per spray header stage.
5 to 6 stages of spray headers are arranged with a spray stage interval of 1.5 to 2 m, and the liquid-gas ratio (L/G) is 20/N.
There is a sulfur dioxide absorption tower of less than m3 .

スプレ式吸収塔に使用される吸収液スプレノズ
ルには、吊り鐘状の噴霧パターンを示すホローコ
ーン型と、筆毛状の噴霧パターンを示すフルコー
ン型との2つのノズルタイプがある。従来建設さ
れ、あるいは現在建設中のスプレ式吸収塔には、
上述のノズルのいずれかの型式のものを統一して
全数同仕様のノズルが使用されている。
There are two types of absorption liquid spray nozzles used in spray absorption towers: a hollow cone type that exhibits a bell-shaped spray pattern, and a full cone type that exhibits a brush-like spray pattern. Spray absorption towers that have been constructed or are currently being constructed include:
All of the above-mentioned nozzles are of the same type and have the same specifications.

ホローコーン型ノズルの脊圧が1Kg/cm3Gの場
合の噴霧粒径分布の一例を第2図に示す。第2図
にみられる如く、平均粒径は1000〜1100μであつ
て、粒径は100〜2500μの間に正規分布をしてい
る。また、脊圧を3〜5Kg/cm3Gに上げるか、ま
たは噴霧孔径を小さくすると粒径分布のピークは
500〜300μに移り、微細粒子分布形態に変化す
る。逆に脊圧を下げると粒径分布のピークは1500
〜2000μとなり粗粒(大粒径)分布型となる。
FIG. 2 shows an example of the spray particle size distribution when the spinal pressure of the hollow cone nozzle is 1 Kg/cm 3 G. As seen in FIG. 2, the average particle size is 1000 to 1100μ, with a normal distribution between 100 and 2500μ. In addition, when the spinal pressure is increased to 3 to 5 kg/cm 3 G or the spray hole diameter is decreased, the peak of the particle size distribution decreases.
500 to 300μ, and changes to a fine particle distribution form. Conversely, when spinal pressure is lowered, the particle size distribution peaks at 1500.
~2000μ, resulting in a coarse grain (large grain size) distribution type.

第3図に、第2図の粒度分布の噴霧粒子の比表
面積割合を示す。第3図より判るように、粒径分
布が微細粒子に偏向すれば、表面積は激増し、粗
粒子に偏寄すれば激減することになる。したがつ
て、液滴表面において進行するガス吸収反応の割
合は、液滴の粒径と粒の数に大きく依存する。こ
この液滴径と粒数は、ノズルの供給脊圧力に大き
く左右される。この供給脊圧力はポンプの所要動
力に正比例し、脊圧力を2倍にするにはポンプ駆
動モータの所要動力は2倍必要となる。塔内に微
細粒子を充満させておくために、高い供給脊圧力
の微細粒子噴霧用のスプレノズルを設置すること
は、このポンプ所要動力の点からはなはだ不経済
である。
FIG. 3 shows the specific surface area ratio of the sprayed particles having the particle size distribution shown in FIG. As can be seen from FIG. 3, if the particle size distribution is biased toward fine particles, the surface area will increase dramatically, and if the distribution is biased toward coarse particles, it will decrease dramatically. Therefore, the rate of gas absorption reaction that progresses on the surface of the droplet largely depends on the particle size and number of droplets. The droplet size and number of droplets here are highly dependent on the nozzle supply spine pressure. This supplied spinal pressure is directly proportional to the pump power requirement; doubling the spinal pressure requires doubling the pump drive motor power requirement. In order to keep the column filled with fine particles, it is extremely uneconomical to install spray nozzles for fine particle atomization with high feed pressures in view of the power requirements of this pump.

また一方、本発明者の実験によれば、第2図に
示されるような液滴が吸収塔内に噴霧された場
合、(a)塔上段のスプレヘツダのノズルより噴霧さ
れた100〜500μの微粒子は、対向してくる被吸収
ガスに同伴されて、ガスに向流することなくデミ
スタに向い、(b)塔下段のスプレヘツダのノズルよ
り噴霧された500〜2500μの大粒径液滴はガスに
逆流して直ちに塔底に落下していることが明らか
になつた。スプレ塔内の反応の場は液滴表面であ
るため、前述の(a)および(b)の液粒子は吸収効率の
向上へ寄与せず、噴霧動力の損失となつているも
のである。
On the other hand, according to the inventor's experiments, when droplets as shown in Fig. 2 are sprayed into the absorption tower, (a) Fine particles of 100 to 500μ are sprayed from the nozzle of the spray header in the upper stage of the tower. (b) The large droplets of 500 to 2,500μ sprayed from the nozzle of the spray header at the bottom of the tower flow into the gas. It became clear that the water was flowing backwards and immediately falling to the bottom of the tower. Since the reaction site in the spray tower is the droplet surface, the liquid particles (a) and (b) described above do not contribute to improving the absorption efficiency and result in a loss of spray power.

本発明者が行つた実験の結果の一部を第4図に
示す。第4図は塔底から塔頂に向けて流速2〜3
m/Sで通過するガス中での各粒径の粒子の移動
挙動を示すものである。即ち、粒径500μ以下の
粒子は、ガスに同伴し上昇し、粒径800μ以上の
粒子は、ガス流に逆らつて一直線に下降してい
る。
FIG. 4 shows part of the results of experiments conducted by the present inventor. Figure 4 shows a flow rate of 2 to 3 from the bottom of the tower to the top.
It shows the movement behavior of particles of each particle size in a gas passing at m/s. That is, particles with a particle size of 500 μm or less rise together with the gas, and particles with a particle size of 800 μm or more fall in a straight line against the gas flow.

本発明の目的は、上記した従来技術の欠点をな
くし、噴霧動力を増加させることなく高いガス吸
収効率を得ることができるガス吸収塔を提供する
にある。
An object of the present invention is to provide a gas absorption tower that eliminates the above-mentioned drawbacks of the prior art and can obtain high gas absorption efficiency without increasing the spray power.

本発明によるガス吸収塔は、吸収液を噴霧する
複数個のスプレノズルを持つ複数段のスプレ段を
有し、ガスを塔下側より導入し上側より排出する
ガス吸収塔において、前記スプレ段は平均粒径
800〜1500μの液滴を噴霧する上段スプレと、平
均粒径500〜800μの液滴を噴霧する中段スプレ
と、平均粒径100〜500μの液滴を噴霧する下段ス
プレとから成り、前記各段のスプレ毎に流量調節
弁を有し、ガス吸収塔へのガス入口にガス濃度検
知器を備え、該検知器が設定されている高濃度を
検知したとき前記流量調節弁の全てを開とする信
号を出力し、高濃度から低濃度への変化に対して
液滴の平均粒径の大きい側から小さい側に前記各
段のスプレの流量調節弁を順次閉鎖する制御手段
を備えたことを特徴とするものである。
The gas absorption tower according to the present invention has a plurality of spray stages having a plurality of spray nozzles that spray absorption liquid, and in the gas absorption tower in which gas is introduced from the bottom of the tower and discharged from the top, the spray stage has an average particle size of diameter
It consists of an upper stage spray that sprays droplets with an average particle size of 800 to 1500μ, a middle stage spray that sprays droplets with an average particle size of 500 to 800μ, and a lower stage spray that sprays droplets with an average particle size of 100 to 500μ, and each of the above stages. A gas concentration detector is provided at the gas inlet to the gas absorption tower, and when the detector detects a set high concentration, all of the flow rate regulation valves are opened. It is characterized by comprising a control means that outputs a signal and sequentially closes the flow rate control valves of the sprays in each stage from the side where the average particle size of the droplets is large to the side where the average particle size of the droplets changes as the concentration changes from high concentration to low concentration. That is.

本発明者は第4図に示す実験結果等に基いて次
の(i)および(ii)の結論に達した。
The inventor has reached the following conclusions (i) and (ii) based on the experimental results shown in FIG. 4.

(i) 粒径500μ以下の粒子はガスに同伴し上昇す
るので、塔内での長い滞留時間を得、ガスとの
接続時間を延長させるためには、ガス流れの上
流に噴霧しなければならない。
(i) Particles with a particle size of 500 μm or less will accompany the gas and rise, so they must be sprayed upstream of the gas stream in order to obtain a long residence time in the column and extend the connection time with the gas. .

(ii) 粒径800μ以上の粒子はガス流れに逆らつて
一直線に下流するので、塔のできるだけ上方の
スプレヘツダのノズルより噴霧する必要があ
る。
(ii) Particles with a particle size of 800μ or more flow downstream in a straight line against the gas flow, so they must be sprayed from the nozzle of the spray header as high as possible in the column.

今、所要ポンプ動力を一定にして、スプレ圧力
一定で、上記の(i)、(ii)の条件を満足させるには、
下記の処置をとることが必要となる。
Now, in order to satisfy conditions (i) and (ii) above while keeping the required pump power constant and the spray pressure constant,
It is necessary to take the following actions.

(i) 上段のスプレヘツダにはノズル孔径を大と
し、平均粒径800〜1500μの粒子を噴霧するノ
ズルを取付ける。
(i) The upper spray header is equipped with a nozzle with a large nozzle hole diameter that sprays particles with an average particle size of 800 to 1500μ.

(ii) 中間部のスプレヘツダには平均粒径500〜
800μの粒子を噴霧するノズルを取付ける。
(ii) Spray header in the middle has an average particle size of 500~
Install a nozzle that sprays 800μ particles.

(iii) 下段のスプレヘツダには、ノズル孔径を最小
とし、平均粒径が100〜500μ近傍にあるような
微細粒子を噴霧するノズルを取付け、塔下部に
微細粒子の噴霧ゾーンを形成させる。
(iii) The lower spray header is equipped with a nozzle that sprays fine particles with a minimum nozzle hole diameter and an average particle size of around 100 to 500 microns to form a fine particle spray zone at the bottom of the tower.

特に、平均粒径が800μ以上の粒子は可及的に
中下段のスプレヘツダのノズルから噴霧させるこ
となく、専ら上段のスプレヘツダのノズルから噴
霧させることが必要である。
In particular, it is necessary to spray particles having an average particle size of 800 μm or more exclusively from the nozzles of the upper spray headers, without spraying them from the nozzles of the middle or lower spray headers as much as possible.

一方、省動力、高効率運用を考えれば、塔入口
ガス流量に応じて、塔全体の吸収液循環を増減制
御し、かつ、吸収ガスの濃度に応じて、上記の上
段、中段、下段のスプレ群のそれぞれの噴霧量を
制御することが不可欠であるのは云うまでもな
い。例えば、低濃度のガス吸収の際には、上段の
スプレヘツダ群は停止し、中段−下段のみの高い
比表面積をもつ微細粒子雰囲気のみとして、低い
ポンプ動力で運用し、高い吸収効率を確保する。
従来の同型スプレノズル群の場合は、吸収液循環
量を制御すれば、噴霧特性が急変して、低動力高
吸収率運転(絞り運転)はできない。
On the other hand, considering power saving and high efficiency operation, it is possible to increase or decrease the absorption liquid circulation throughout the tower according to the gas flow rate at the tower inlet, and also to control the above-mentioned upper, middle, and lower stages of spraying according to the concentration of the absorbed gas. It goes without saying that it is essential to control the amount of spray for each group. For example, when absorbing a low concentration of gas, the upper spray header group is stopped, and only the middle and lower stages have a fine particle atmosphere with a high specific surface area, and are operated with low pump power to ensure high absorption efficiency.
In the case of conventional spray nozzle groups of the same type, if the absorption liquid circulation amount is controlled, the spray characteristics will change suddenly, making low power, high absorption rate operation (throttle operation) impossible.

第5図に本発明のガス吸収塔の一実施例のフロ
ーシートを示す。ガスが入口18より導入され、
出口19より排出され、吸収液循環タンク13の
吸収液がポンプ14により配管12を通つてスプ
レヘツダに送られ、噴霧液は塔底よりタンク13
に戻されること、および吸収剤タンク15等の付
属設備があることは第1図における場合と全く同
様である。
FIG. 5 shows a flow sheet of an embodiment of the gas absorption tower of the present invention. Gas is introduced from the inlet 18,
The absorption liquid is discharged from the outlet 19, and the absorption liquid in the absorption liquid circulation tank 13 is sent to the spray header through the pipe 12 by the pump 14, and the spray liquid is sent from the bottom of the column to the tank 13.
It is exactly the same as in the case in FIG. 1 that the absorbent tank 15 and other attached equipment are provided.

この装置においては複数段のスプレ段すなわ
ち、スプレヘツダは上段スプレ20、中段スプレ
21、下段スプレ22の3群に大別され、それぞ
れ流量調節弁20A,21A,22Aを介して配
管12に接続されている。各段のスプレ20,2
1,22にはそれぞれ粗粒(800〜1500μ)、微粒
(500〜800μ)、微細粒(100〜500μ)の粒子を噴
霧するスプレノズル20B,21B,22Bが取
付けてある。ガス入口18にはガス流量検知器2
3およびガス濃度検知器24が設けてある。吸収
液配管12には調節弁25が設けてあり、ガス流
量検知器23よりの信号により図示せざる制御手
段により調節弁25が制御される。またガス濃度
検知器24よりの信号は制御手段26に送られ、
制御手段26は各段のスプレヘツダの流量調節弁
20A、21A,22Aを制御する。
In this device, the spray stages, that is, the spray headers, are roughly divided into three groups: an upper spray 20, a middle spray 21, and a lower spray 22, which are connected to the piping 12 via flow rate control valves 20A, 21A, and 22A, respectively. There is. Spray 20,2 for each stage
Spray nozzles 20B, 21B, and 22B for spraying coarse particles (800 to 1500 microns), fine particles (500 to 800 microns), and fine particles (100 to 500 microns) are attached to 1 and 22, respectively. A gas flow rate sensor 2 is installed at the gas inlet 18.
3 and a gas concentration detector 24 are provided. The absorption liquid pipe 12 is provided with a control valve 25, and the control valve 25 is controlled by a control means (not shown) in response to a signal from the gas flow rate detector 23. Further, the signal from the gas concentration detector 24 is sent to the control means 26,
The control means 26 controls the flow control valves 20A, 21A, and 22A of the spray headers at each stage.

下段スプレノズル22Bより噴霧された粒径
500μ以下の微細粒子群は塔下部でガス吸収を行
つた後、塔上部に上昇し、衝突、付着等により大
粒子化して落下し、一部はデミスタ11に捕促さ
れる。微細粒子は比表面積が大であり、塔内にお
ける滞留時間が長いので効果的な吸収を行う。ま
た、上段スプレノズル20Bより噴霧された粒径
800μ以上の粗粒子群は、上段で噴霧されている
ので塔内に比較的長時間滞留し、落下に際して
は、塔内各部のヘツダ上面、ヘツダ支持架構など
に衝突し、清掃、すなわちスケール除去しながら
塔底に向う。このように塔内での液滴挙動に無駄
がなく、高い吸収効率が得られる。
Particle size sprayed from the lower spray nozzle 22B
After the fine particles of 500 μm or less absorb gas at the lower part of the tower, they rise to the upper part of the tower, become larger particles due to collision, adhesion, etc., and fall, and some of them are captured by the demister 11. Fine particles have a large specific surface area and a long residence time in the column, so they perform effective absorption. In addition, the particle size sprayed from the upper spray nozzle 20B
Coarse particles of 800μ or more are sprayed in the upper stage, so they remain in the tower for a relatively long time, and when they fall, they collide with the top of the header, header support frame, etc. in various parts of the tower, and are cleaned, that is, scaled. Heading towards the bottom of the tower. In this way, there is no waste in droplet behavior within the column, and high absorption efficiency can be obtained.

また、入口18のガス濃度検知器24よりの信
号が低ガス濃度を示すときは、制御手段26が上
段スプレ20の調節弁20Aを閉鎖して、上段ス
プレヘツダ20へ吸収液を供給しているポンプの
運転を停止する。従つて、吸収塔内には中段およ
び下段のノズル21Bおよび22Bからの高い比
表面積をもつ微細粒子雰囲気のみとされ、低いポ
ンプ動力(少ないポンプ台数)で運転され、高い
吸収効率を無駄なく確保する。更にガス濃度が低
下したときは中段スプレ21の調節弁21Aも閉
鎖され、中段スプレヘツダ21へ吸収液を供給し
ているポンプの運転を停止する。
Further, when the signal from the gas concentration detector 24 at the inlet 18 indicates a low gas concentration, the control means 26 closes the control valve 20A of the upper spray header 20 to pump the absorbent liquid to the upper spray header 20. stop operating. Therefore, the absorption tower is filled with only a fine particle atmosphere with a high specific surface area from the middle and lower nozzles 21B and 22B, and is operated with low pump power (small number of pumps) to ensure high absorption efficiency without waste. . When the gas concentration further decreases, the control valve 21A of the middle stage spray 21 is also closed, and the operation of the pump supplying the absorption liquid to the middle stage spray header 21 is stopped.

以上の如く、本発明によるガス吸収塔は、上段
スプレに粗粒子(800μ以上)を噴霧するスプレ
ノズルが取付けられ、必要に応じて中段スプレに
微粒子(500〜800μ)を、下段スプレに微細粒子
(100〜500μ)を噴霧するスプレノズルが取付け
られているので、それぞれの粒子の塔内滞留時間
が延長され、効果的なガス吸収を行うことがで
き、高い吸収効率をあげることができる。これに
より吸収液のポンプ供給圧力を低くすることがで
き、これにポンプ動力も正比例するので、同じ吸
収効率で3〜5%の動力を節減することができ
る。更に、ガス濃度に応じて、各段のスプレ毎の
流量がガス濃度が設定されている高濃度から低濃
度への変化に対して平均粒径の大きい液滴を噴霧
するスプレから小さい液滴を噴霧するスプレの方
向に順次絞られて適切に制御されるので、適切な
動力節減と共に常に高い吸収効率をあげることが
できる。また、ガス流量検知器からのガス流量に
対する信号により、調節弁(実施例では第5図の
25)を絞る等の制御が前記各段のスプレ毎の順
次流量調節制御と同時に行なわれるため、ガス流
量及びガス濃度の変化に多面的に対応することが
でき、この点からも一層の動力節減と高い吸収効
率を図ることができる。
As described above, in the gas absorption tower according to the present invention, a spray nozzle for spraying coarse particles (800μ or more) is attached to the upper spray, and if necessary, fine particles (500 to 800μ) are sprayed to the middle spray and fine particles (500 to 800μ) are sprayed to the lower spray. Since a spray nozzle that sprays 100 to 500μ) is installed, the residence time of each particle in the column is extended, effective gas absorption can be performed, and high absorption efficiency can be achieved. This allows the pump supply pressure of the absorption liquid to be lowered, and since the pump power is also directly proportional to this, it is possible to save 3 to 5% of the power with the same absorption efficiency. Furthermore, depending on the gas concentration, the flow rate for each spray at each stage changes from spraying droplets with a large average particle size to spraying small droplets as the gas concentration changes from high concentration to low concentration. Since the spray is sequentially narrowed and appropriately controlled in the direction of the spray, it is possible to achieve high absorption efficiency at all times with appropriate power savings. In addition, control such as throttling the control valve (25 in FIG. 5 in the embodiment) is performed simultaneously with the sequential flow rate adjustment control for each spray at each stage, based on the signal from the gas flow rate detector regarding the gas flow rate. It is possible to respond to changes in flow rate and gas concentration from various angles, and from this point of view, further power savings and high absorption efficiency can be achieved.

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

第1図は従来の典型的な湿式排煙脱硫プロセス
のフローシート、第2図は代表的なスプレノズル
の噴霧粒子の粒径分布図、第3図は第2図の粒子
の比表面積割合を示す線図、第4図は塔内におけ
る液滴の飛行挙動を示す線図、第5図は本発明の
ガス吸収塔の実施例のフローシートである。 2……冷却ベンチエリ塔、9……吸収塔、10
……スプレノズル、13……吸収液循環タンク、
20,21,22……上段、中段、下段スプレヘ
ツダ、20A,21A,22A……上段、中段、
下段流量制御弁、20B,21B,22B……上
段、中段、下段スプレノズル、23……ガス流量
検知器、24……ガス濃度検知器、25……流量
制御弁、26……自動制御手段。
Figure 1 is a flow sheet of a typical conventional wet flue gas desulfurization process, Figure 2 is a particle size distribution diagram of atomized particles from a typical spray nozzle, and Figure 3 shows the specific surface area ratio of the particles in Figure 2. 4 is a diagram showing the flight behavior of droplets in the tower, and FIG. 5 is a flow sheet of an embodiment of the gas absorption tower of the present invention. 2...Cooling Benchelli tower, 9...Absorption tower, 10
... Spray nozzle, 13 ... Absorption liquid circulation tank,
20, 21, 22... Upper stage, middle stage, lower stage spray header, 20A, 21A, 22A... Upper stage, middle stage,
Lower stage flow control valve, 20B, 21B, 22B...Upper stage, middle stage, lower stage spray nozzle, 23...Gas flow rate detector, 24...Gas concentration detector, 25...Flow rate control valve, 26...Automatic control means.

Claims (1)

【特許請求の範囲】[Claims] 1 吸収液を噴霧する複数個のスプレノズルを持
つ複数段のスプレ段を有し、ガスを塔下側より導
入し上側より排出するガス吸収塔において、前記
スプレ段は平均粒径800〜1500μの液滴を噴霧す
る上段スプレと、平均粒径500〜800μの液滴を噴
霧する中段スプレと、平均粒径100〜500μの液滴
を噴霧する下段スプレとから成り、前記各段のス
プレ毎に流量調節弁を有すると共に該流量調節弁
より上流側に他の調節弁を有し、ガス吸収塔への
ガス入口にガス濃度検知器及びガス流量検知器を
備え、該ガス流量検知器からの出力信号により前
記他の調節弁を開閉制御すると共に、前記ガス濃
度検知器が予め設定されている高濃度を検知した
とき前記流量調節弁の全てを開とする信号を出力
し、高濃度から低濃度への変化に対して液滴の平
均粒径の大きい側から小さい側に前記各段のスプ
レの流量調節弁を順次閉鎖する制御手段を備えた
ことを特徴とするガス吸収塔。
1. In a gas absorption tower that has multiple spray stages with a plurality of spray nozzles that spray absorption liquid, and gas is introduced from the bottom of the tower and discharged from the top, the spray stage is configured to spray droplets with an average particle size of 800 to 1500μ. It consists of an upper stage spray that sprays liquid, a middle stage spray that sprays droplets with an average particle size of 500 to 800μ, and a lower stage spray that sprays droplets with an average particle size of 100 to 500μ, and the flow rate is adjusted for each spray in each stage. It has a gas concentration detector and a gas flow rate detector at the gas inlet to the gas absorption tower, and the output signal from the gas flow rate detector In addition to controlling the opening and closing of the other control valves, when the gas concentration detector detects a preset high concentration, it outputs a signal to open all of the flow rate control valves, and changes from high concentration to low concentration. A gas absorption tower characterized by comprising a control means for sequentially closing the flow rate control valves of the sprays in each stage from the side where the average particle size of the droplets is large to the side where the average particle size of the droplets is small.
JP3789680A 1980-03-25 1980-03-25 Gas absorption tower Granted JPS56136617A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3789680A JPS56136617A (en) 1980-03-25 1980-03-25 Gas absorption tower

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3789680A JPS56136617A (en) 1980-03-25 1980-03-25 Gas absorption tower

Publications (2)

Publication Number Publication Date
JPS56136617A JPS56136617A (en) 1981-10-26
JPH021523B2 true JPH021523B2 (en) 1990-01-11

Family

ID=12510298

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3789680A Granted JPS56136617A (en) 1980-03-25 1980-03-25 Gas absorption tower

Country Status (1)

Country Link
JP (1) JPS56136617A (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5693076B2 (en) 2010-07-29 2015-04-01 三菱重工業株式会社 Gas-liquid contact device and CO2 recovery device
JP5817971B2 (en) * 2011-06-22 2015-11-18 三菱日立パワーシステムズ株式会社 Wet flue gas desulfurization apparatus and wet flue gas desulfurization method
WO2021111957A1 (en) * 2019-12-04 2021-06-10 富士電機株式会社 Exhaust gas processing device

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5060477A (en) * 1973-09-28 1975-05-24
JPS5513178A (en) * 1978-07-17 1980-01-30 Babcock Hitachi Kk Gas-liquid contact tower

Also Published As

Publication number Publication date
JPS56136617A (en) 1981-10-26

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