JPH06312118A - Dry exhaust gas desulfurization and its device - Google Patents

Dry exhaust gas desulfurization and its device

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Publication number
JPH06312118A
JPH06312118A JP5103045A JP10304593A JPH06312118A JP H06312118 A JPH06312118 A JP H06312118A JP 5103045 A JP5103045 A JP 5103045A JP 10304593 A JP10304593 A JP 10304593A JP H06312118 A JPH06312118 A JP H06312118A
Authority
JP
Japan
Prior art keywords
desulfurization
exhaust gas
tower
absorbent
dry
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
Application number
JP5103045A
Other languages
Japanese (ja)
Inventor
Takayuki Ishida
孝行 石田
Yasuki Hashimoto
泰樹 橋本
Hirobumi Yoshikawa
博文 吉川
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 JP5103045A priority Critical patent/JPH06312118A/en
Publication of JPH06312118A publication Critical patent/JPH06312118A/en
Pending legal-status Critical Current

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Abstract

PURPOSE:To obtain a dry exhaust gas desulfurization device which is capable of improving the desulfurization rate of a dry exhaust gas desulfurization device and reducing the consumption of a desulfurization agent, and at the same time, discharging a solid sticking to the wall surface of a desulfurization tower smoothly. CONSTITUTION:The exhaust gas desulfurization device consists of a desulfurization tower 19 with an inlet duct 1 for introducing an exhaust gas 8, an outlet duct 3 for allowing a treated exhaust gas to flow out and a solid discharge device 9 for discharging a solid, an absorbent atomization device 2a for spraying absorbent powder 2, e.g. NaCl, CaCl2 or KCl, to the exhaust gas 8 flowing in from the inlet duct 1, and a moistening water spray nozzle 4 for spraying an atomization water to the desulfurization part of a desulfurization tower 19 from an atomization water tank. In addition, this system is composed of an additive silo 6, an additive feeder 7 for feeding an additive from the additive silo 6 to the atomization water tank 5, a sensor 11 for detecting the thickness of the solid sticking to the inner wall of the desulfurization tower 19, and a hammering control device 12 for controlling a hammering device 10 based on a signal from the sensor 11 to peel the solid off.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、乾式排ガス脱硫方法お
よび装置に係り、特に排ガス中の硫黄酸化物を除去する
乾式排ガス脱硫方法および装置であって、性能向上およ
び装置の安定運転性維持に寄与するに好適な乾式排ガス
脱硫方法および装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a dry exhaust gas desulfurization method and apparatus, and more particularly to a dry exhaust gas desulfurization method and apparatus for removing sulfur oxides in exhaust gas, which is for improving performance and maintaining stable operability of the apparatus. The present invention relates to a dry exhaust gas desulfurization method and apparatus suitable for contributing.

【0002】[0002]

【従来の技術】排ガス中の硫黄酸化物を除去する方法の
一つとして、ダクト中に吸収剤粉末(消石灰等カルシウ
ム系吸収剤)を注入した後、その後流の脱硫塔にて加湿
用の水噴霧を行ない、排ガス中の硫黄酸化物を吸収除去
する乾式排煙脱硫装置の1例を図8に示す。
2. Description of the Related Art As one of the methods for removing sulfur oxides in exhaust gas, after injecting absorbent powder (calcium-based absorbent such as slaked lime) into a duct, water for humidification is provided in a desulfurization tower in the subsequent flow. FIG. 8 shows an example of a dry flue gas desulfurization apparatus that sprays and absorbs and removes sulfur oxides in exhaust gas.

【0003】ボイラ等での燃焼により発生した排ガス8
は、入口ダクト1で脱硫塔19に導かれる。このとき、
吸収剤2が入口ダクト1に噴霧され、排ガス中に浮遊し
た状態で、脱硫塔19に導入される。塔内には、加湿水
噴霧ノズル4が設けてあり、噴霧された微細液滴が塔出
口に到達するまでに蒸発を完了するが、この過程におい
て排ガス中の硫黄酸化物が水を介して吸収剤2に吸収さ
れる。
Exhaust gas 8 generated by combustion in a boiler, etc.
Is guided to the desulfurization tower 19 through the inlet duct 1. At this time,
The absorbent 2 is sprayed on the inlet duct 1 and introduced into the desulfurization tower 19 in a state of being suspended in the exhaust gas. A humidification water spray nozzle 4 is provided in the tower to complete vaporization of the sprayed fine droplets before reaching the tower outlet. In this process, sulfur oxides in the exhaust gas are absorbed through water. It is absorbed by Agent 2.

【0004】この乾式脱硫方法の反応プロセスは、図9
に示すとおりで硫黄酸化物21を含む排ガス8中に噴霧
され浮遊している吸収剤20は脱硫塔において、噴霧水
22と接触すると、吸収剤20の周囲を噴霧水22が覆
い、この周囲を覆った噴霧水22に排ガス中の硫黄酸化
物21が溶解する。また、吸収剤20中のカルシウムが
噴霧水22に溶解し、噴霧水22中に溶解している硫黄
酸化物21と反応する。吸収剤20の表面を覆っている
水22が蒸発した後の反応生成固形物は脱硫塔後流側に
設置された集塵機によって捕集される。
The reaction process of this dry desulfurization method is shown in FIG.
When the absorbent 20 that is sprayed and suspended in the exhaust gas 8 containing the sulfur oxides 21 as shown in FIG. 6 comes into contact with the spray water 22 in the desulfurization tower, the area around the absorbent 20 is covered with the spray water 22, and the surrounding area The sulfur oxide 21 in the exhaust gas is dissolved in the covered spray water 22. Further, the calcium in the absorbent 20 is dissolved in the spray water 22 and reacts with the sulfur oxide 21 dissolved in the spray water 22. The reaction product solid matter after the water 22 covering the surface of the absorbent 20 is evaporated is collected by the dust collector installed on the downstream side of the desulfurization tower.

【0005】この脱硫反応量は、噴霧水22の蒸発時
間、吸収剤20中のカルシウムの噴霧水22への溶解性
および噴霧水22への排ガス中の硫黄酸化物21の溶解
性によって支配される。硫黄酸化物の溶解は塩化物の存
在で促進される。このような現象はスプレードライヤを
用いた湿式脱硫装置においては公知である。しかし、脱
硫剤を粉体で供給する乾式脱硫装置では、脱硫塔の内径
と長さの比が、スプレードライヤを用いた湿式脱硫装置
のそれと比較して小さいため、脱硫剤の付着によるガス
流速の変化(脱硫率の変化)や塔の閉塞が問題となる。
This desulfurization reaction amount is governed by the evaporation time of the spray water 22, the solubility of calcium in the absorbent 20 in the spray water 22 and the solubility of the sulfur oxide 21 in the exhaust gas into the spray water 22. . Dissolution of sulfur oxides is promoted by the presence of chloride. Such a phenomenon is known in a wet desulfurization device using a spray dryer. However, in the dry desulfurization device that supplies the desulfurization agent in powder form, the ratio of the inner diameter to the length of the desulfurization tower is smaller than that of the wet desulfurization device that uses a spray dryer. Changes (changes in desulfurization rate) and blockages of the tower pose problems.

【0006】すなわち、脱硫塔内では、噴霧水滴22が
蒸発するまでの過程で、一部が塔壁に当たって、その部
分で濡れ面を作り固形物の付着成長が生じることを避け
得ない。この付着物を除去する手段として、付着が懸念
される範囲に対し、槌打装置を多数設けて、定期的に壁
面に振動を与え、固形物を除去していた。
That is, in the desulfurization tower, it is unavoidable that a part of the sprayed water droplet 22 hits the wall of the tower during the process of vaporization to form a wetted surface at that portion to cause solid growth. As a means for removing the adhered matter, a large number of hammering devices are provided to the range where the adherence is concerned, and the wall surface is periodically vibrated to remove the solid matter.

【0007】[0007]

【発明が解決しようとする課題】上記した従来の水噴霧
は、図9に示すようなモデルで反応が進むが、噴霧され
た水自体が中性で排ガス中の硫黄酸化物をとり込む能力
が低く、しかも沸点が低いために吸収剤表面を覆う液膜
としての存在時間が短いため硫黄酸化物の吸収能力が低
かった。また、吸収剤中にあるカルシウム化合物の水に
対する溶解度が小さいために、脱硫反応量も少ない状況
にあり、水噴霧による脱硫性能はあまりよくなかった。
このため、所要の性能を維持するためには多くの吸収剤
を必要とし、運転費がかさみ、経済性の低下につながっ
ていた。
In the conventional water spray described above, the reaction proceeds in a model as shown in FIG. 9, but the sprayed water itself is neutral and has the ability to take up the sulfur oxides in the exhaust gas. Since the boiling point is low and the boiling point is low, the existence time as a liquid film covering the surface of the absorbent is short, so that the ability to absorb sulfur oxide is low. Further, since the calcium compound in the absorbent has a low solubility in water, the desulfurization reaction amount is small, and the desulfurization performance by water spray was not so good.
For this reason, a large amount of absorbent is required to maintain the required performance, resulting in high operating costs and reduced economic efficiency.

【0008】また、さきに述べたように脱硫塔内は、吸
収剤の付着成長が避け得ない環境下にある。この付着
は、塔壁へのスプレ液滴の衝突に起因するものであり、
その領域は、塔内のガスの偏流または運転条件の影響を
受けて変化するため、一定時間内でも場所によって付着
成長の度合いが異なる。このため、塔壁に設けた槌打装
置を一定間隔で作動させたときに剥離、落下する固形物
の大きさにはかなりのばらつきがあり、予想外に大きな
固形物が落下したときには、塔下部に設けられた固形物
排出装置をつまらせるなど運転に支障をきたすことがあ
った。
Further, as described above, the inside of the desulfurization tower is in an environment where the adhesive growth of the absorbent cannot be avoided. This adhesion is due to the collision of spray droplets on the tower wall,
Since the region changes due to the influence of the gas drift in the tower or the operating conditions, the degree of adhesion growth varies depending on the place even within a certain time. For this reason, there is a considerable variation in the size of solids that peel and fall when the hammering device provided on the tower wall is operated at regular intervals. There was a case where it interfered with the operation such as blocking the solids discharging device provided in the.

【0009】また、固形物の成長し過ぎを防ぐ方策とし
て槌打装置の作動間隔を短縮することも試したが、不必
要に塔壁に振動を与えすぎることや騒音発生などを考慮
すると、必ずしも好ましい方法ではなかった。本発明は
上記従来技術の問題点を解決し、脱硫塔内での脱硫率を
向上し、脱硫剤の使用量を節減するとともに、脱硫塔内
で生成した固形物を円滑に排出することができる乾式排
ガス脱硫方法および装置を提供することを目的とする。
Also, as a measure to prevent the solids from growing too much, it was tried to shorten the operation interval of the hammering device, but in consideration of unnecessary vibration of the tower wall and noise generation, it is not always necessary. Not the preferred method. The present invention solves the above-mentioned problems of the prior art, improves the desulfurization rate in the desulfurization tower, reduces the amount of desulfurization agent used, and can smoothly discharge the solid matter generated in the desulfurization tower. An object is to provide a dry exhaust gas desulfurization method and apparatus.

【0010】[0010]

【課題を解決するための手段】上記目的を達成するため
本願の第1の発明は、排ガス中に粉末の吸収剤を浮遊さ
せた状態で脱硫塔に流入させ、脱硫部で加湿水噴霧ノズ
ルから加湿水を噴霧して微細液滴が塔内で蒸発を完了す
るまでの間に排ガス中の硫黄酸化物を吸収除去し、反応
生成固形物を脱硫塔より排出する乾式排ガス脱硫方法に
おいて、前記水噴霧ノズルから噴霧する加湿水にNaC
l、CaCl2、KClのうち少なくとも一つ、または
前記塩化物のうち少なくとも一つを含んだ混合物を添加
することを特徴とする乾式排ガス脱硫方法に関する。
In order to achieve the above object, the first invention of the present application is to allow a powdered absorbent to flow into a desulfurization tower in a state of being suspended in exhaust gas, and from a humidification water spray nozzle at a desulfurization section. In a dry exhaust gas desulfurization method of spraying humidifying water to absorb and remove sulfur oxides in the exhaust gas until the fine droplets complete evaporation in the tower, and discharging the reaction product solid matter from the desulfurization tower, NaC in the humidifying water sprayed from the spray nozzle
l, CaCl 2 , KCl, or a mixture containing at least one of the above chlorides is added to the dry exhaust gas desulfurization method.

【0011】第2の発明は、上記第1の発明において、
塩化物としてNaClを水に対して1〜3 %添加するこ
とを特徴とする乾式排ガス脱硫方法に関する。第3の発
明は、硫黄酸化物含有排ガスを脱硫塔内に導入する入口
ダクトと、脱硫塔で処理された排ガスを排出する出口ダ
クトと、入口ダクト内の排ガス中に吸収剤を噴霧する吸
収剤噴霧装置と、脱硫塔内に加湿水を噴霧する加湿水噴
霧ノズルと、脱硫塔内で生成した固形物を排出する固形
物排出装置とを備えた乾式排ガス脱硫装置において、前
記加湿水中に塩化物を添加する塩化物添加装置を設けた
ことを特徴とする乾式排ガス脱硫装置に関する。
A second invention is the same as the first invention,
The present invention relates to a dry exhaust gas desulfurization method, characterized in that NaCl as a chloride is added in an amount of 1 to 3% with respect to water. A third invention is an inlet duct for introducing a sulfur oxide-containing exhaust gas into a desulfurization tower, an outlet duct for discharging the exhaust gas treated in the desulfurization tower, and an absorbent for spraying an absorbent into the exhaust gas in the inlet duct. A spray device, a humidification water spray nozzle for spraying humidification water in a desulfurization tower, and a dry exhaust gas desulfurization apparatus equipped with a solids discharge device for discharging solid matter generated in the desulfurization tower, wherein chloride is added to the humidification water. The present invention relates to a dry-type exhaust gas desulfurization device, which is provided with a chloride addition device for adding.

【0012】第4の発明は、上記第3の発明において、
脱硫塔の塔壁に絶縁体を介して所定間隔を隔てて取り付
けられた複数個のセンサと、該センサからの検出信号に
基いて作動する槌打装置とを設けたことを特徴とする乾
式排ガス脱硫装置に関する。
A fourth invention is the same as the third invention,
Dry exhaust gas, characterized in that a plurality of sensors mounted at predetermined intervals on the tower wall of the desulfurization tower via insulators, and a hammering device that operates based on detection signals from the sensors are provided. Desulfurization equipment

【0013】[0013]

【作用】噴霧水に添加剤を加えることによって噴霧後の
水滴の沸点が上昇し、液滴としての存在時間が長くなる
ので、硫黄酸化物の吸収時間が長くなる。また、前記添
加剤がNaCl等の強電解質であることから、この添加
剤が溶解した陽イオンの働きで排ガス中の硫黄酸化物を
とり込みやすくなると同時に、このような噴霧水で覆わ
れた吸収剤中の、例えばカルシウム化合物の溶解も促進
されるので、脱硫反応量が増大し吸収性能が向上する。
この結果、運転費の低減が可能となる。
By adding the additive to the spray water, the boiling point of the water droplets after spraying rises and the existence time of the water droplets becomes long, so that the absorption time of sulfur oxide becomes long. Further, since the additive is a strong electrolyte such as NaCl, the action of dissolved cations facilitates the incorporation of sulfur oxides in the exhaust gas, and at the same time, the absorption covered with such sprayed water. Since the dissolution of, for example, a calcium compound in the agent is also promoted, the desulfurization reaction amount increases and the absorption performance improves.
As a result, the operating cost can be reduced.

【0014】また、脱硫塔壁30の内側に所定の長さの
絶縁体に覆われたセンサを所定間隔を隔てて複数配置し
たことにより、前記塔壁30に付着した固形物の厚さが
前記絶縁体の長さ(深さ)以上に成長したとき、隣接す
るセンサの先端間に電気が流れる。従って、この通電に
基いて槌打装置を作動させて固形物を剥離することによ
り、前記付着固形物の一定厚以上の成長を防止すること
ができる。前記隣接するセンサの先端間で通電が生じる
のは、上記した強電解質の添加剤が付着物に混在してお
り、該強電解質が付着物の表面水分中でイオン化して流
れ易くなるためである。
Further, by arranging a plurality of sensors covered with an insulator of a predetermined length at a predetermined interval inside the desulfurization tower wall 30, the thickness of the solid matter adhered to the tower wall 30 is the above. When grown over the length (depth) of the insulator, electricity flows between the tips of the adjacent sensors. Therefore, by operating the hammering device based on this energization to peel off the solid matter, it is possible to prevent the adhered solid matter from growing beyond a certain thickness. Electric current is generated between the tips of the adjacent sensors because the above-mentioned strong electrolyte additive is mixed in the deposit, and the strong electrolyte is easily ionized in the surface water of the deposit to flow. .

【0015】[0015]

【実施例】本発明の実施例を図1に示す。この乾式排ガ
ス脱硫装置が図8の従来技術と異なるところは、噴霧水
タンク5に添加剤を供給する添加剤供給フィーダ7と、
添加剤を貯蔵する添加剤サイロ6と、脱硫塔19の塔壁
30に付着した固形物の厚さを検出するセンサ11と、
該付着固形物を払い落とす槌打装置10と、前記センサ
11からの信号に基いて前記槌打装置10を制御する槌
打制御装置12とを設けた点である。なお、1は入口ダ
クト、2は吸収剤、2aは吸収剤噴霧装置、3は出口ダ
クト、4は加湿水噴霧ノズル、8は排ガス、9は固形物
排出装置である。
FIG. 1 shows an embodiment of the present invention. This dry type exhaust gas desulfurization apparatus is different from the conventional technique shown in FIG. 8 in that an additive supply feeder 7 for supplying an additive to the spray water tank 5 and
An additive silo 6 for storing the additive, a sensor 11 for detecting the thickness of the solid matter attached to the tower wall 30 of the desulfurization tower 19, and
The point is that a hammering device 10 for removing the adhered solid matter and a hammering control device 12 for controlling the hammering device 10 on the basis of a signal from the sensor 11 are provided. In addition, 1 is an inlet duct, 2 is an absorbent, 2a is an absorbent spraying device, 3 is an outlet duct, 4 is a humidifying water spraying nozzle, 8 is an exhaust gas, and 9 is a solid matter discharging device.

【0016】また、図5は、図1の前記センサ11部分
を詳細に示す説明図である。図において、深さTの寸法
まで絶縁体31に覆われた複数のセンサ11が脱硫塔塔
壁30に設けられている。このような構成において、例
えばボイラで発生した燃焼排ガス8は、吸収剤噴霧装置
2aから噴霧される吸収剤、例えば消石灰粉末2を伴っ
て脱硫塔19に流入する。一方、添加剤サイロ6に貯蔵
された添加剤、例えばNaClが添加剤供給フィーダ7
を介して噴霧水タンク5に供給され、噴霧水に溶解す
る。NaClが溶解した噴霧水は加湿水噴霧ノズル4を
経て脱硫塔19の脱硫部に噴霧され、前記吸収剤2を同
伴した燃焼排ガス8と接触する。このようにして燃焼排
ガス、吸収剤およびNaClが添加された噴霧水が接触
し、燃焼排ガス8に含まれる硫黄酸化物が吸収剤に吸収
される。
FIG. 5 is an explanatory view showing the sensor 11 portion of FIG. 1 in detail. In the figure, a plurality of sensors 11 covered with an insulator 31 up to a dimension of a depth T are provided on a desulfurization tower column wall 30. In such a configuration, the combustion exhaust gas 8 generated in the boiler, for example, flows into the desulfurization tower 19 together with the absorbent, for example, slaked lime powder 2, which is sprayed from the absorbent spraying device 2a. On the other hand, the additive stored in the additive silo 6, for example, NaCl is added to the additive supply feeder 7.
It is supplied to the spray water tank 5 via and is dissolved in the spray water. The spray water in which NaCl is dissolved is sprayed to the desulfurization section of the desulfurization tower 19 through the humidification water spray nozzle 4 and comes into contact with the combustion exhaust gas 8 accompanied with the absorbent 2. In this way, the combustion exhaust gas, the absorbent and the spray water to which NaCl is added come into contact with each other, and the sulfur oxides contained in the combustion exhaust gas 8 are absorbed by the absorbent.

【0017】反応プロセスを図2に示す。図において、
硫黄酸化物21を含む排ガス8中に噴霧され浮遊してい
る吸収剤20が脱硫塔19内で噴霧水22と接触する
と、前記吸収剤20の周囲を噴霧水22が覆い、この噴
霧水22に排ガス中の硫黄酸化物21が溶解する。この
とき噴霧水22には添加剤であるNaClが溶解した陰
イオン23および陽イオン24が含まれているので、排
ガス8中の硫黄酸化物21の溶解が促進する。また、吸
収剤20中のカルシウムも同様に噴霧水22に溶解し、
先に溶解した前記硫黄酸化物21と反応する。吸収剤2
0の表面を覆っている噴霧水22が蒸発した後の反応生
成固形物は、図示省略した脱硫塔後流の集塵機によって
捕集される。
The reaction process is shown in FIG. In the figure,
When the absorbent 20 that is sprayed and suspended in the exhaust gas 8 containing the sulfur oxide 21 comes into contact with the spray water 22 in the desulfurization tower 19, the spray water 22 covers the periphery of the absorbent 20 and the spray water 22 The sulfur oxide 21 in the exhaust gas dissolves. At this time, since the spray water 22 contains the anion 23 and the cation 24 in which the additive NaCl is dissolved, the dissolution of the sulfur oxide 21 in the exhaust gas 8 is promoted. Further, the calcium in the absorbent 20 is also dissolved in the spray water 22 in the same manner,
It reacts with the previously dissolved sulfur oxide 21. Absorbent 2
The reaction product solids after the spray water 22 covering the surface of No. 0 is evaporated are collected by a dust collector (not shown) downstream of the desulfurization tower.

【0018】このようにして排ガス8の脱硫操作が進行
する間に、脱硫塔19の塔壁30に固形物33が付着す
る。図6は、塔壁30に固形物33が付着した状況を示
す説明図である。図において、吸収剤による付着固形物
33の厚みtが絶縁体31の深さT以上に成長した際、
センサ11の先端間を付着水34を介して電流が流れ
る。この電流値は図7のように変化する。センサ11
は、例えば電流値=Aを検知すると、その信号を槌打制
御装置12に送る。信号を受けた槌打制御装置12は、
その計測位置に最も近い槌打装置10を適時作動させて
前記固形物33を剥離する。
While the desulfurization operation of the exhaust gas 8 proceeds in this manner, the solid matter 33 adheres to the tower wall 30 of the desulfurization tower 19. FIG. 6 is an explanatory diagram showing a state in which the solid matter 33 adheres to the tower wall 30. In the figure, when the thickness t of the adhered solid matter 33 due to the absorbent grows to be greater than or equal to the depth T of the insulator 31,
An electric current flows between the tips of the sensors 11 via the attached water 34. This current value changes as shown in FIG. Sensor 11
Detects a current value = A, for example, sends the signal to the hammering control device 12. The hammer control device 12, which has received the signal,
The hammering device 10 closest to the measurement position is operated at appropriate times to peel off the solid matter 33.

【0019】本実施例において、噴霧水に添加剤を加え
た効果を図3および図4に示す。図3において、吸収剤
のモル比と排ガス中の硫黄酸化物のモル比(以下、Ca
/Sと呼ぶ)を脱硫塔での脱硫率70%ベースで比較す
ると、添加剤を加えることによってCa/S=2をCa
/S=1.5に低減できることが分かった。また、添加
剤(NaCl)の濃度を変化させて試験を行なったとこ
ろ、図4に示す結果が得られた。図において、添加剤と
してNaClを用いた場合の添加剤量は、3wt%以
下、望ましくは1wt%前後であることが分かる。
In this embodiment, the effect of adding the additive to the spray water is shown in FIGS. 3 and 4. In FIG. 3, the molar ratio of the absorbent and the molar ratio of the sulfur oxide in the exhaust gas (hereinafter referred to as Ca
/ S) is compared on the basis of a desulfurization rate of 70% in a desulfurization tower, Ca / S = 2 becomes Ca by adding an additive.
It was found that /S=1.5 can be reduced. Further, when the test was conducted by changing the concentration of the additive (NaCl), the results shown in FIG. 4 were obtained. In the figure, it can be seen that the additive amount when NaCl is used as the additive is 3 wt% or less, preferably around 1 wt%.

【0020】本実施例によれば、噴霧水に添加剤を加え
ることによって、噴霧水の沸点上昇が起こり、液滴蒸発
時間が長くなるので、液滴の硫黄酸化物吸収時間が長く
なる。また、NaCl、CaCl2に代表されるように
塩化物を含む化合物には、水分を保持する能力である潮
解性があり、噴霧水が吸収剤に付着した後、徐々に液滴
が蒸発しても付近の水分をとり込み噴霧水が吸収剤を覆
っている時間が長くなるので、硫黄酸化物の吸収能力が
向上する。
According to the present embodiment, by adding the additive to the spray water, the boiling point of the spray water rises and the droplet evaporation time becomes long, so that the sulfur oxide absorption time of the liquid droplet becomes long. In addition, compounds containing chloride as represented by NaCl and CaCl 2 have a deliquescent property that is an ability to retain water, and after the spray water adheres to the absorbent, the droplets gradually evaporate. In addition, since the time that the water in the vicinity is taken in and the sprayed water covers the absorbent for a long time, the ability to absorb sulfur oxides is improved.

【0021】また、塩化物などの強電解質を含む噴霧水
を噴霧することにより、吸収剤に付着した噴霧水と吸収
剤の表面でイオン緩衝作用が起こり、吸収剤表面のカル
シウムイオンが溶解し易くなると同時に、噴霧水に含ま
れる陽イオンが排ガス中の硫黄酸化物の溶解を促進する
ので、脱硫反応が促され、脱硫性能が向上する。さら
に、噴霧水に塩化物などの強電解質を添加することによ
り、脱硫塔内壁で成長した固形物中の噴霧水を介してセ
ンサ11間に電流が流れるので、この電流に基いて、付
着固形物を剥離する必要性を検出することができる。す
なわち、脱硫塔壁の適切な位置に、成長する固形物の厚
さを検知する複数のセンサ11を設置したことにより、
該固形物が所定の厚さに到達した時点で槌打装置10を
起動して剥離することができる。
By spraying spray water containing a strong electrolyte such as chloride, an ion buffering action occurs between the spray water adhering to the absorbent and the surface of the absorbent, and calcium ions on the surface of the absorbent are easily dissolved. At the same time, the cations contained in the spray water promote the dissolution of the sulfur oxides in the exhaust gas, so that the desulfurization reaction is promoted and the desulfurization performance is improved. Furthermore, by adding a strong electrolyte such as chloride to the spray water, an electric current flows between the sensors 11 through the spray water in the solid matter grown on the inner wall of the desulfurization tower. The need for stripping can be detected. That is, by installing a plurality of sensors 11 that detect the thickness of the growing solid matter at appropriate positions on the desulfurization tower wall,
When the solid material reaches a predetermined thickness, the hammering device 10 can be activated and peeled.

【0022】本実施例によれば、固形物の厚みを検出す
るセンサ11、槌打制御装置12および槌打装置10を
設けたことにより、脱硫塔下部より排出される固形物3
3をある大きさ以下に維持することができるので、固形
物を排出装置9から安定して排出することができる。本
実施例において、噴霧水に加える添加剤として、例えば
海水を使用することもできる。
According to this embodiment, since the sensor 11 for detecting the thickness of the solid matter, the hammering control device 12, and the hammering device 10 are provided, the solid matter 3 discharged from the lower part of the desulfurization tower 3
Since 3 can be maintained below a certain size, solid matter can be stably discharged from the discharging device 9. In this embodiment, for example, seawater can be used as an additive added to the spray water.

【0023】[0023]

【発明の効果】本発明によれば、噴霧水に添加剤を加え
ることにより、脱硫用吸収剤の使用量を著しく低減する
ことができる。例えば硫黄酸化物に対する吸収剤のモル
比をCa/Sで表すと、脱硫率=70%ベースで比較し
た場合、従来方法でCa/S=2.0であったものをC
a/S=1.5までに低減することができる。この結
果、本装置の1年間の運転費は添加剤の費用を見込んで
も従来方法に較べて約20%の低減となる。
According to the present invention, the amount of the desulfurization absorbent used can be significantly reduced by adding the additive to the spray water. For example, when the molar ratio of the absorbent to the sulfur oxide is expressed by Ca / S, when comparing on the basis of desulfurization rate = 70%, the value of Ca / S = 2.0 in the conventional method is C
It can be reduced to a / S = 1.5. As a result, the operating cost of this device for one year is reduced by about 20% compared with the conventional method even if the cost of the additive is taken into consideration.

【0024】また、槌打装置を制御することにより、塔
下部の固形物排出装置の運転状態を良好にし、脱硫装置
の安定な連続運転を確保することができる。
Further, by controlling the hammering device, it is possible to improve the operating condition of the solids discharging device at the lower part of the tower and to ensure stable continuous operation of the desulfurization device.

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

【図1】本発明の一実施例を示す乾式排ガス脱硫装置の
フロー図。
FIG. 1 is a flow chart of a dry exhaust gas desulfurization apparatus showing an embodiment of the present invention.

【図2】本発明における脱硫反応のモデル説明図。FIG. 2 is a model explanatory view of a desulfurization reaction in the present invention.

【図3】実施例における乾式排ガス脱硫装置の性能曲線
図。
FIG. 3 is a performance curve diagram of a dry exhaust gas desulfurization device in an example.

【図4】実施例においてCa/S一定とした場合のNa
Cl濃度と、脱硫率の関係を示す図。
FIG. 4 shows Na when Ca / S is constant in the example.
The figure which shows the relationship between Cl density | concentration and a desulfurization rate.

【図5】脱硫塔内に設置されたセンサを示す図。FIG. 5 is a diagram showing a sensor installed in a desulfurization tower.

【図6】脱硫塔内に設置されたセンサとその周りに成長
した固形物を示す図。
FIG. 6 is a view showing a sensor installed in a desulfurization tower and a solid substance grown around the sensor.

【図7】固形物付着量とセンサ間に流れる電流値の関係
を示す図。
FIG. 7 is a diagram showing the relationship between the amount of adhered solid matter and the value of current flowing between sensors.

【図8】従来の乾式排ガス脱硫装置のフロー図。FIG. 8 is a flow chart of a conventional dry exhaust gas desulfurization device.

【図9】水噴霧の際の反応モデルを示す図。FIG. 9 is a diagram showing a reaction model during water spraying.

【符号の説明】[Explanation of symbols]

1…入口ダクト、2…吸収剤、2a…吸収剤噴霧装置、
3…出口ダクト、4…加湿式噴霧ノズル、5…噴霧水タ
ンク、6…添加剤サイロ、7…添加剤供給フィーダ、8
…排ガス、9…固形物排出装置、10…槌打装置、11
…センサ、12…槌打制御装置、19…脱硫塔、20…
吸収剤、21…硫黄酸化物、22…噴霧水水滴、23…
塩化物中の陰イオン、24…塩化物中の陽イオン、25
…硫酸カルシウム、30…脱硫塔塔壁、31…絶縁体、
33…固形物、34…付着水。
1 ... Inlet duct, 2 ... Absorbent, 2a ... Absorbent spraying device,
3 ... Exit duct, 4 ... Wet spray nozzle, 5 ... Spray water tank, 6 ... Additive silo, 7 ... Additive supply feeder, 8
... Exhaust gas, 9 ... Solids discharging device, 10 ... Hammering device, 11
... Sensor 12, 12 Hammering control device 19, 19 Desulfurization tower, 20 ...
Absorbent, 21 ... Sulfur oxide, 22 ... Spray water droplets, 23 ...
Anion in chloride, 24 ... Cation in chloride, 25
... calcium sulfate, 30 ... desulfurization tower tower wall, 31 ... insulator,
33 ... Solid matter, 34 ... Adhering water.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 排ガス中に粉末の吸収剤を浮遊させた状
態で脱硫塔に流入させ、脱硫部で加湿水噴霧ノズルから
加湿水を噴霧して微細液滴が塔内で蒸発を完了するまで
の間に排ガス中の硫黄酸化物を吸収除去し、反応生成固
形物を脱硫塔より排出する乾式排ガス脱硫方法におい
て、前記水噴霧ノズルから噴霧する加湿水にNaCl、
CaCl2、KClのうち少なくとも一つ、または前記
塩化物のうち少なくとも一つを含んだ混合物を添加する
ことを特徴とする乾式排ガス脱硫方法。
1. A method in which a powdered absorbent is suspended in exhaust gas and flowed into a desulfurization tower, and humidification water is sprayed from a humidification water spray nozzle in the desulfurization section until fine droplets are completely evaporated in the tower. In the dry exhaust gas desulfurization method of absorbing and removing the sulfur oxides in the exhaust gas during the period and discharging the reaction product solid matter from the desulfurization tower, NaCl is added to the humidification water sprayed from the water spray nozzle.
A dry exhaust gas desulfurization method, comprising adding a mixture containing at least one of CaCl 2 and KCl, or at least one of the above chlorides.
【請求項2】 請求項1において、塩化物としてNaC
lを水に対して1〜3 %添加することを特徴とする乾式
排ガス脱硫方法。
2. The NaC as chloride according to claim 1.
A method for desulfurization of exhaust gas of dry type, characterized in that 1 to 3% of 1 is added to water.
【請求項3】 硫黄酸化物含有排ガスを脱硫塔内に導入
する入口ダクトと、脱硫塔で処理された排ガスを排出す
る出口ダクトと、入口ダクト内の排ガス中に吸収剤を噴
霧する吸収剤噴霧装置と、脱硫塔内に加湿水を噴霧する
加湿水噴霧ノズルと、脱硫塔内で生成した固形物を排出
する固形物排出装置とを備えた乾式排ガス脱硫装置にお
いて、前記加湿水中に塩化物を添加する塩化物添加装置
を設けたことを特徴とする乾式排ガス脱硫装置。
3. An inlet duct for introducing the sulfur oxide-containing exhaust gas into the desulfurization tower, an outlet duct for discharging the exhaust gas treated in the desulfurization tower, and an absorbent spray for spraying an absorbent into the exhaust gas in the inlet duct. Apparatus, a humidification water spray nozzle for spraying humidification water in the desulfurization tower, in a dry exhaust gas desulfurization apparatus equipped with a solid matter discharge device for discharging the solid matter generated in the desulfurization tower, chloride in the humidification water A dry-type exhaust gas desulfurization device, which is provided with a chloride addition device for addition.
【請求項4】 請求項3において、脱硫塔の塔壁に絶縁
体を介して所定間隔を隔てて取り付けられた複数個のセ
ンサと、該センサからの検出信号に基いて作動する槌打
装置とを設けたことを特徴とする乾式排ガス脱硫装置。
4. The plurality of sensors mounted on the tower wall of the desulfurization tower at a predetermined interval via an insulator, and a hammering device which operates based on a detection signal from the sensors according to claim 3. A dry type exhaust gas desulfurization device characterized by being provided.
JP5103045A 1993-04-28 1993-04-28 Dry exhaust gas desulfurization and its device Pending JPH06312118A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5103045A JPH06312118A (en) 1993-04-28 1993-04-28 Dry exhaust gas desulfurization and its device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5103045A JPH06312118A (en) 1993-04-28 1993-04-28 Dry exhaust gas desulfurization and its device

Publications (1)

Publication Number Publication Date
JPH06312118A true JPH06312118A (en) 1994-11-08

Family

ID=14343702

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5103045A Pending JPH06312118A (en) 1993-04-28 1993-04-28 Dry exhaust gas desulfurization and its device

Country Status (1)

Country Link
JP (1) JPH06312118A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AT504426B1 (en) * 2006-10-24 2008-05-15 Scheuch Gmbh APPARATUS FOR MOISTURIZING A SORPTION AGENT
CN103525493A (en) * 2013-10-23 2014-01-22 杨解定 Desulfurization device capable of producing methane from kitchen waste
JP2016530981A (en) * 2013-06-25 2016-10-06 エス.ア.ロイスト ルシェルシュ エ デヴロップマン Method and apparatus for treating a gas by injecting a powdery compound
CN106422748A (en) * 2016-09-05 2017-02-22 光大环保(中国)有限公司 Dry denitrification system

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AT504426B1 (en) * 2006-10-24 2008-05-15 Scheuch Gmbh APPARATUS FOR MOISTURIZING A SORPTION AGENT
JP2016530981A (en) * 2013-06-25 2016-10-06 エス.ア.ロイスト ルシェルシュ エ デヴロップマン Method and apparatus for treating a gas by injecting a powdery compound
CN103525493A (en) * 2013-10-23 2014-01-22 杨解定 Desulfurization device capable of producing methane from kitchen waste
CN106422748A (en) * 2016-09-05 2017-02-22 光大环保(中国)有限公司 Dry denitrification system

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