JPH11197450A - Wet desulfurization equipment and its operation method - Google Patents

Wet desulfurization equipment and its operation method

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Publication number
JPH11197450A
JPH11197450A JP10008413A JP841398A JPH11197450A JP H11197450 A JPH11197450 A JP H11197450A JP 10008413 A JP10008413 A JP 10008413A JP 841398 A JP841398 A JP 841398A JP H11197450 A JPH11197450 A JP H11197450A
Authority
JP
Japan
Prior art keywords
tank
absorbing solution
absorption
absorbing
liquid
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
JP10008413A
Other languages
Japanese (ja)
Inventor
Hiroyuki Nosaka
浩之 野坂
Toshio Katsube
利夫 勝部
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 JP10008413A priority Critical patent/JPH11197450A/en
Publication of JPH11197450A publication Critical patent/JPH11197450A/en
Pending legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To provide a flue desulfurization equipment keeping the slurry concentration in an absorbing solution tank and also keeping the absorbing solution level in the absorbing solution tank within the given range when the operation of extracting intermittently an absorbing solution from the absorbing solution tank and also provide an operation method thereof. SOLUTION: An absorbing solution from an absorbing solution tank 1a containing a lime stone slurry storing the absorbing solution is brought into contact with boiler gas introduced into an absorption column 1 to remove sulfur oxide in gas, and the absorbing solution absorbing the sulfur oxide in exhaust gas is returned to the absorbing solution tank 1a. At that time, the specific gravity of the absorbing solution in the absorbing solution tank 1a is sensed by a specific gravity hydrometer 16, and the feed amount of reinforcing water from a reinforcing water feed line 10 into the absorbing solution is adjusted, and also the absorbing solution extraction amount out of an absorbing solution extraction line 9 of the absorbing solution tank 1a is adjusted based on the sensed value of a liquid level indicator 17 for the absorbing solution in the absorbing solution tank 1a.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明はボイラ排ガス中の硫
黄酸化物を除去するのに好適な湿式排煙脱硫装置と方法
に関する。
The present invention relates to a wet flue gas desulfurization apparatus and method suitable for removing sulfur oxides in boiler exhaust gas.

【0002】[0002]

【従来の技術】従来技術からなる排煙脱硫装置の系統図
を図4に示す。ボイラ排ガス14は吸収塔1に導入され
るが、吸収塔1内で吸収塔下部の吸収液タンク1a内の
石灰石スラリを含む吸収液を循環ポンプ2によりスプレ
ノズル3に供給して、該ノズル3から噴霧される吸収液
により、吸収塔1に導入された排ガスは除塵、冷却され
るとともに、該排ガス中に含まれる硫黄酸化物は吸収さ
れる。
2. Description of the Related Art FIG. 4 shows a system diagram of a flue gas desulfurization apparatus according to the prior art. The boiler exhaust gas 14 is introduced into the absorption tower 1. In the absorption tower 1, the absorption liquid containing limestone slurry in the absorption liquid tank 1 a at the lower part of the absorption tower is supplied to the spray nozzle 3 by the circulation pump 2, and from the nozzle 3. The exhaust gas introduced into the absorption tower 1 is removed and cooled by the sprayed absorbing liquid, and the sulfur oxides contained in the exhaust gas are absorbed.

【0003】この排ガス中の硫黄酸化物の除去に使用さ
れる石灰石は、石灰石スラリ供給ライン8から調整弁1
1により、その供給量が調整されて吸収塔1内に導入さ
れる。石灰石スラリの供給量は吸収塔1に導入される排
ガス14中の硫黄酸化物量により制御される。
[0003] Limestone used for removing sulfur oxides from the exhaust gas is supplied from a limestone slurry supply line 8 to a regulating valve 1.
By 1, the supply amount is adjusted and introduced into the absorption tower 1. The supply amount of the limestone slurry is controlled by the amount of sulfur oxide in the exhaust gas 14 introduced into the absorption tower 1.

【0004】吸収液中に吸収された硫黄酸化物は吸収剤
である石灰石と反応し、さらに吸収液中に供給される空
気により酸化されて石膏となる。生成した石膏を含む石
灰石スラリは吸収液タンク1aから吸収液抜出ポンプ4
により抜出され、脱水機6により脱水され、石膏7とし
て回収される。
[0004] The sulfur oxides absorbed in the absorbing solution react with limestone as an absorbing agent, and are further oxidized into gypsum by air supplied into the absorbing solution. The limestone slurry containing the generated gypsum is supplied to the absorption liquid extraction pump 4 from the absorption liquid tank 1a.
, And is dehydrated by the dehydrator 6 and collected as gypsum 7.

【0005】[0005]

【発明が解決しようとする課題】ここで、吸収塔1の脱
硫性能を維持するために、吸収塔1内の石灰石濃度を一
定に保つ必要があり、吸収液の抜出しライン9に設けた
調整弁13により石灰石スラリ供給量に見合った量の吸
収液を抜出す。
Here, in order to maintain the desulfurization performance of the absorption tower 1, it is necessary to keep the concentration of limestone in the absorption tower 1 constant. In step 13, an amount of absorption liquid corresponding to the supply amount of limestone slurry is extracted.

【0006】また吸収塔1において排ガスを冷却するこ
とにより吸収液の蒸発が起こることから、これに見合っ
て補給水配管8に設けた調整弁11により補給水供給し
ている。
[0006] Further, since the absorption liquid is evaporated by cooling the exhaust gas in the absorption tower 1, supply water is supplied by a regulating valve 11 provided in the supply water pipe 8 in accordance with the evaporation.

【0007】これに対し、吸収液(石膏スラリ)の抜出
しライン9の後流側にハイドロサイクロン(図4の排煙
脱硫装置の系統には設置せず)が設置されている場合
は、ハイドロサイクロンアンダーフロー、オーバーフロ
ーのバランスを一定に保つ必要があり、このためには吸
収液の抜出しライン9からの石膏スラリを含む吸収液の
抜出し流量を一定とする必要がある。そのため吸収液タ
ンク1aからの吸収液抜出し量の調整は調整弁12のO
N−OFF制御運転(非連続的な開閉制御)とせざるを
得ない。
On the other hand, when a hydrocyclone (not installed in the flue gas desulfurization system shown in FIG. 4) is installed downstream of the absorption liquid (gypsum slurry) extraction line 9, the hydrocyclone is installed. It is necessary to keep the balance between the underflow and the overflow constant, and for this purpose, it is necessary to keep the flow rate of the absorption liquid containing the gypsum slurry from the absorption liquid extraction line 9 constant. Therefore, the adjustment of the amount of the absorbent to be withdrawn from the absorbent tank 1 a
The N-OFF control operation (discontinuous opening / closing control) must be performed.

【0008】この調整弁12のON−OFF制御(非連
続的な開閉制御)運転において、吸収液タンク1a内の
石膏スラリ濃度に基づくON−OFF制御のみとした場
合、石膏スラリ濃度が高くなると、吸収液タンク1a内
の吸収液を抜出し、吸収液タンク1aには補給水を供給
することになるが、前述の通り、吸収液抜出し量は流入
する硫黄酸化物量に影響されるため、吸収液の抜出し量
と吸収液への補給水の供給量は一定の比率で設定できな
い。
In the ON-OFF control (non-continuous opening / closing control) operation of the regulating valve 12, if only the ON-OFF control based on the gypsum slurry concentration in the absorbent tank 1a is performed, if the gypsum slurry concentration becomes high, The absorption liquid in the absorption liquid tank 1a is withdrawn and replenishment water is supplied to the absorption liquid tank 1a. However, as described above, the absorption liquid withdrawal amount is affected by the amount of sulfur oxide flowing in. The withdrawal amount and the supply amount of make-up water to the absorbent cannot be set at a fixed ratio.

【0009】例えば、ハイドロサイクロン設計値の排ガ
ス中の硫黄酸化物濃度より、低い硫黄酸化物濃度の排ガ
スを処理する場合には石灰石供給量は少なくなり、吸収
液タンク1a内の石灰石及び石膏スラリ濃度を一定にす
るために、それに見合って供給する補給水量も少なくす
る必要がある。したがって、この場合は吸収液タンク1
aの吸収液面レベルは下がる一方になる。
For example, when treating an exhaust gas having a sulfur oxide concentration lower than the sulfur oxide concentration in the exhaust gas of the hydrocyclone design value, the supply amount of limestone is reduced and the limestone in the absorption liquid tank 1a is reduced. In addition, in order to keep the gypsum slurry concentration constant, it is necessary to reduce the amount of makeup water supplied accordingly. Therefore, in this case, the absorbent tank 1
The absorption liquid level of “a” is decreasing.

【0010】また吸収液タンク1aの吸収液面レベルに
基づき吸収液タンク1aからの吸収液抜出し量の調整を
ON−OFF制御運転をした場合、吸収液面レベルが基
準値より高いと吸収液を吸収液タンク1aから抜出し、
これに補給水を供給することなるが、例えば、ハイドロ
サイクロン設計値の排ガス中の硫黄酸化物濃度より、低
い硫黄酸化物濃度の排ガスを処理する場合には石灰石供
給量は少なくなり、石灰石供給量に対して補給水が過剰
となり、スラリ濃度は下がっていく一方となる。
In addition, when the ON-OFF control operation is performed to adjust the amount of the withdrawn liquid from the absorption tank 1a based on the level of the absorption liquid in the absorption tank 1a, the absorption liquid is removed if the absorption liquid level is higher than the reference value. Withdraw from the absorbent tank 1a,
Supply water is supplied to this, for example, when treating the exhaust gas having a lower sulfur oxide concentration than the sulfur oxide concentration in the exhaust gas of the hydrocyclone design value, the supply amount of limestone decreases, and the supply amount of limestone decreases. However, the amount of makeup water becomes excessive, and the slurry concentration decreases.

【0011】また、吸収液タンク1aからの吸収液の抜
出し量の調整を吸収液タンク1a内のスラリ濃度制御と
し、また補給水の供給量の調整を吸収液タンク1aの吸
収液面レベル制御とした場合、吸収液を抜出し後、補給
水を吸収液に供給することにより、吸収液面レベルを回
復させた時点で吸収液中のスラリ濃度は低下するが、吸
収液抜出し及び補給水の供給を停止した状態で吸収液面
レベルが低下するようなバランスの運転においては、ス
ラリ濃度が回復する前に吸収液面レベルが低下すること
により、再度補給水が供給され、スラリ濃度がさらに低
くなってしまう。
Adjustment of the amount of the absorbing liquid withdrawn from the absorbing liquid tank 1a is performed by controlling the concentration of the slurry in the absorbing liquid tank 1a. Adjustment of the supply amount of the replenishing water is controlled by controlling the level of the absorbing liquid in the absorbing liquid tank 1a. In this case, the slurry concentration in the absorbing solution is reduced when the level of the absorbing solution is restored by supplying makeup water to the absorbing solution after withdrawing the absorbing solution. In a balanced operation in which the absorption liquid level is reduced in a stopped state, the absorption liquid level is reduced before the slurry concentration is recovered, so that makeup water is supplied again, and the slurry concentration is further reduced. I will.

【0012】また、吸収液抜出し及び補給水の供給を停
止した状態で吸収液面レベルが上昇するバランスでは、
吸収液抜出して液面レベルが低下した状態から液面レベ
ルが回復するまで補給水を供給すると、石灰石スラリ濃
度が低下するが、その後石灰石スラリ濃度が回復するま
での間に吸収液面レベルがさらに上昇してしまう。
[0012] Further, in a balance in which the level of the absorbing liquid rises in a state where the extraction of the absorbing liquid and the supply of the makeup water are stopped,
When the make-up water is supplied until the liquid level recovers from the state in which the liquid level is lowered after the absorption liquid is withdrawn, the limestone slurry concentration decreases, but the absorption liquid level further increases until the limestone slurry concentration recovers. Will rise.

【0013】本発明の課題は吸収液タンクから吸収液を
断続的に抜出す運転を行っても、吸収液タンク内の石灰
石及び石膏からなるスラリの濃度を一定の範囲に保ち、
また吸収液タンク内の吸収液面レベルを一定の範囲に保
つことができる湿式排煙脱硫装置とその運転方法を確立
することにある。
An object of the present invention is to maintain the concentration of the slurry composed of limestone and gypsum in the absorption liquid tank within a certain range even if the operation of intermittently extracting the absorption liquid from the absorption liquid tank is performed.
Another object of the present invention is to establish a wet flue gas desulfurization apparatus capable of maintaining the level of the absorbent in the absorbent tank within a certain range and a method of operating the same.

【0014】[0014]

【課題を解決するための手段】本発明の上記課題は次の
構成によって解決される。すなわち、石灰石スラリを含
む吸収液をボイラ排ガスと接触させて、排ガス中の硫黄
酸化物を吸収除去する吸収塔と、排ガス中の硫黄酸化物
を吸収した吸収液を貯留する吸収液タンクと、該吸収液
タンクから吸収液を抜出すための抜出しライン自動開閉
弁を備えた吸収液抜出しラインと、吸収液タンク内に補
給水を供給するための補給水供給ライン自動開閉弁を備
えた補給水供給ラインと、吸収液タンク内の吸収液の比
重を計測する比重計又は吸収液中のスラリ濃度計と吸収
液の液面レベルを計測する液面レベル計と、前記吸収液
の比重計又は吸収液中のスラリ濃度計の検出値に基づき
補給水供給ライン自動開閉弁の開閉制御をし、前記吸収
液の液面レベル計の検出値に基づき抜出しライン自動開
閉弁の開閉制御をする制御装置を設けた湿式排煙脱硫装
置、または、吸収液を貯留する石灰石スラリを含む吸収
液タンクから吸収液を吸収塔内に供給し、吸収塔内に導
入されるボイラ排ガスと接触させて、排ガス中の硫黄酸
化物を吸収除去し、該排ガス中の硫黄酸化物を吸収した
吸収液を吸収液タンクに戻す湿式排煙脱硫方法におい
て、吸収液タンク内の吸収液の比重又はスラリ濃度に基
づき吸収液タンクへの補給水の供給量を調整し、また吸
収液タンク内の吸収液の液面レベルに基づき吸収液タン
クからの吸収液抜出し量を調整する湿式排煙脱硫方法で
ある。
The above object of the present invention is attained by the following constitution. That is, an absorption tower that contacts an absorption liquid containing limestone slurry with boiler exhaust gas to absorb and remove sulfur oxides in the exhaust gas, an absorption liquid tank that stores the absorption liquid that has absorbed sulfur oxides in the exhaust gas, Absorbent extraction line with extraction line automatic opening / closing valve for extracting the absorption liquid from the absorption liquid tank, and make-up water supply line with supply water supply line for supplying makeup water into the absorption liquid tank A line, a hydrometer for measuring the specific gravity of the absorbent in the absorbent tank or a slurry concentration meter in the absorbent and a liquid level meter for measuring the liquid level of the absorbent, and a hydrometer or the absorbent for the absorbent A control device is provided for controlling the opening and closing of the make-up water supply line automatic opening and closing valve based on the detection value of the slurry concentration meter therein, and for controlling the opening and closing of the extraction line automatic opening and closing valve based on the detection value of the liquid level meter for the absorbent. Wet The absorption liquid is supplied into the absorption tower from a smoke desulfurization device or an absorption liquid tank containing limestone slurry for storing the absorption liquid, and is brought into contact with the boiler exhaust gas introduced into the absorption tower to remove sulfur oxides in the exhaust gas. In a wet flue gas desulfurization method for absorbing and removing and absorbing the sulfur oxides contained in the exhaust gas and returning the absorbing solution to the absorbing solution tank, the replenishing water to the absorbing solution tank is determined based on the specific gravity of the absorbing solution in the absorbing solution tank or the slurry concentration. This is a wet type flue gas desulfurization method in which the supply amount of water is adjusted, and the amount of absorption liquid withdrawn from the absorption liquid tank is adjusted based on the level of the absorption liquid in the absorption liquid tank.

【0015】この際、吸収液タンク内の吸収液抜出し開
始の液面レベル、吸収液抜出し停止の液面レベル及び吸
収液タンク内の吸収液への補給水供給開始の吸収液の比
重又はスラリ濃度、吸収液タンク内の吸収液への補給水
供給停止の吸収液の比重又はスラリ濃度を設定する。
At this time, the liquid level at the start of the absorption liquid withdrawal in the absorption liquid tank, the liquid level at the stop of the absorption liquid withdrawal, and the specific gravity or slurry concentration of the absorption liquid at the start of the supply of make-up water to the absorption liquid in the absorption liquid tank. The specific gravity or the slurry concentration of the absorbing liquid when the supply of the replenishing water to the absorbing liquid in the absorbing liquid tank is stopped is set.

【0016】本発明の湿式排煙脱硫装置は吸収液をスプ
レノズルから噴霧するスプレ方式に限らず、濡れ壁を流
れる吸収液に排ガスを接触させる濡れ壁方式、排ガスを
吸収液中にバブリングするバブリング方式の吸収液を備
えたものにも適用できる。また、本発明の吸収液を貯留
する吸収液タンクは吸収塔の下部に設けた構造又は吸収
塔とは別の装置として設けた構造のいずれでも良い。
The wet type flue gas desulfurization apparatus of the present invention is not limited to the spray type in which the absorbent is sprayed from the spray nozzle, but the wet wall type in which the exhaust gas is brought into contact with the absorbent flowing through the wet wall, and the bubbling type in which the exhaust gas is bubbled in the absorbent. Can also be applied to those provided with an absorbing liquid. Further, the absorbing liquid tank for storing the absorbing liquid of the present invention may have either a structure provided below the absorption tower or a structure provided as a separate device from the absorption tower.

【0017】[0017]

【作用】吸収液タンク内の吸収液抜出し量を液面レベル
制御により行い、抜出し停止の液面レベルまで吸収液を
抜出した後でも、吸収液への補給水は吸収液中の所定の
石灰石及び石膏からなるスラリ濃度に相当する吸収液の
比重値になるまで供給しない。この間、新たな石灰石ス
ラリ及び吸収塔廻りの洗浄水は補給されており、吸収塔
下部にある吸収液タンク内の吸収液中のスラリ濃度、吸
収液面レベルも自然に上昇してくる。そして、前記スラ
リ濃度に相当する吸収液の比重値が得られると補給水を
供給開始濃度に相当する値となった時点で補給水を供給
する。
[Action] Even after the absorption liquid is withdrawn to the liquid level at which the withdrawal is stopped, the replenishing water for the absorption liquid is supplied with a predetermined amount of limestone in the absorption liquid. It is not supplied until the specific gravity of the absorbing solution corresponding to the gypsum slurry concentration is reached. During this time, fresh limestone slurry and washing water around the absorption tower are being replenished, and the slurry concentration and the absorption liquid level in the absorption liquid in the absorption tank at the bottom of the absorption tower naturally rise. When the specific gravity of the absorbing liquid corresponding to the slurry concentration is obtained, the supply water is supplied when the supply water reaches the value corresponding to the supply start concentration.

【0018】さらに吸収液抜出し開始すべき吸収液面レ
ベルになった時点で吸収液の抜出しを再度開始するとと
もに、スラリ濃度(又は吸収液の比重)が補給水供給停
止濃度(又は吸収液の比重)となった時点で補給水供給
を停止する。このような運転方法により、吸収液タンク
内の吸収液の液面レベル及び石灰石及び石膏からなるス
ラリの濃度を一定の範囲内に制御できる。
Further, at the time when the level of the absorbing liquid to be started is reached, the extraction of the absorbing liquid is started again, and the concentration of the slurry (or the specific gravity of the absorbing liquid) is changed to the concentration at which the supply of the make-up water is stopped (or the specific gravity of the absorbing liquid). ), The supply water supply is stopped. With such an operation method, the liquid level of the absorbent in the absorbent tank and the concentration of the slurry composed of limestone and gypsum can be controlled within a certain range.

【0019】[0019]

【発明の実施の形態】本発明の実施の形態を図1に示す
排煙脱硫装置のフローで説明する。図1に示す排煙脱硫
装置のフローは図4に示す従来技術と基本的構成は同様
のものであるが、排煙脱硫装置を運転する制御装置に特
徴がある。
DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described with reference to a flow chart of a flue gas desulfurization apparatus shown in FIG. Although the flow of the flue gas desulfurization device shown in FIG. 1 is basically the same as that of the conventional technology shown in FIG. 4, it is characterized by a control device for operating the flue gas desulfurization device.

【0020】吸収塔1の下部には石灰石スラリを含む吸
収液タンク1aが配置され、該吸収液タンク1a内の吸
収液は循環ポンプ2により吸収塔1の空塔部に設けられ
たスプレノズル3に吸収液が供給されている。したがっ
て吸収塔1内の導入された排ガス14はスプレノズル3
から噴霧される吸収液中の石灰石スラリと気液接触し
て、排ガス中の硫黄酸化物は石灰石スラリにより吸収さ
れる。吸収液中に吸収された硫黄酸化物は吸収剤である
石灰石と反応し、さらに吸収液中に供給される空気15
により酸化されて石膏となる。生成した石膏を含む石灰
石スラリは吸収液タンク1aから吸収液抜出ポンプ4に
より吸収液抜出しライン9に抜出され、ハイドロサイク
ロン18に送られて濃縮され、次いで脱水機6により脱
水され、石膏7として回収される。このとき、吸収液抜
出しライン9には吸収液抜出弁13を設け、この吸収液
抜出弁13の開閉制御で吸収液の抜出し量が調整され
る。
An absorption liquid tank 1a containing limestone slurry is disposed below the absorption tower 1, and the absorption liquid in the absorption liquid tank 1a is supplied to a spray nozzle 3 provided in an empty tower portion of the absorption tower 1 by a circulation pump 2. Absorbing liquid is being supplied. Therefore, the exhaust gas 14 introduced into the absorption tower 1 is sprayed by the spray nozzle 3
Gas-liquid contact with the limestone slurry in the absorbing liquid sprayed from the mist, the sulfur oxides in the exhaust gas are absorbed by the limestone slurry. The sulfur oxides absorbed in the absorbing solution react with limestone as the absorbing agent, and the air 15 supplied to the absorbing solution further reacts.
Is oxidized into gypsum. The limestone slurry containing the produced gypsum is withdrawn from the absorbing liquid tank 1a by the absorbing liquid extracting pump 4 to the absorbing liquid extracting line 9 and sent to the hydrocyclone 18 where it is concentrated. Will be collected as At this time, an absorption liquid extraction valve 13 is provided in the absorption liquid extraction line 9, and the opening / closing control of the absorption liquid extraction valve 13 adjusts the amount of the absorption liquid extracted.

【0021】また排ガス中の硫黄酸化物の除去に使用さ
れる石灰石は、石灰石スラリ供給ライン8から吸収塔内
に供給されるが、その供給量は調整弁11により吸収塔
1に導入される排ガス14中の硫黄酸化物量に応じて制
御される。
The limestone used for removing sulfur oxides in the exhaust gas is supplied from the limestone slurry supply line 8 into the absorption tower. 14 is controlled in accordance with the amount of sulfur oxide.

【0022】図1に示すフローの特徴は、吸収液比重信
号器16と吸収塔内の吸収液面レベル信号器17を設け
ることであり、この二つの信号器16、17の出力信号
はそれぞれ制御装置20に入り、ここで、前記2つの出
力信号に基づきそれぞれ補給水供給弁11と給水液抜出
弁13の開閉制御をする。
The feature of the flow shown in FIG. 1 is that an absorption liquid specific gravity signal 16 and an absorption liquid level signal 17 in the absorption tower are provided, and the output signals of these two signals 16 and 17 are controlled respectively. The apparatus 20 enters the apparatus 20 and controls the opening and closing of the makeup water supply valve 11 and the feedwater discharge valve 13 based on the two output signals.

【0023】すなわち、吸収塔補給水供給ライン10か
ら供給される補給水は吸収液(石膏スラリ)比重信号器
16より補給水供給弁11を開閉制御して、その供給量
が調整される。また、石膏スラリ抜出し量、すなわち吸
収液抜出し量は吸収塔内の吸収液面レベルをレベル信号
器17の信号に基づき吸収液抜出弁13を開閉制御して
行われる。
That is, the supply amount of makeup water supplied from the absorption tower makeup water supply line 10 is controlled by opening and closing the makeup water supply valve 11 from the absorption liquid (gypsum slurry) specific gravity signal 16. The amount of gypsum slurry withdrawn, that is, the amount of absorbent absorbed, is determined by controlling the level of the absorbed liquid in the absorption tower based on the signal from the level signal 17 to open and close the absorbent extraction valve 13.

【0024】硫黄酸化物を吸収した吸収液は吸収塔タン
ク1a内に吹き込まれる空気14により酸化され、石膏
が生成されるが、生成された石膏は石膏抜出しライン9
から石膏スラリとしてハイドロサイクロン18へ送られ
る。ハイドロサイクロン18で濃縮された石膏スラリ
は、さらに石膏脱水機6により脱水されて、石膏ケーキ
7として回収される。
The absorbing solution having absorbed the sulfur oxides is oxidized by the air 14 blown into the absorption tower tank 1a to produce gypsum.
Is sent to the hydrocyclone 18 as a gypsum slurry. The gypsum slurry concentrated in the hydrocyclone 18 is further dehydrated by the gypsum dewatering machine 6 and collected as the gypsum cake 7.

【0025】この図1に示す排煙脱硫装置のフローで、
レベル信号器17の信号による吸収液(石膏スラリ)の
抜出し量の制御と吸収液比重信号器16よる補給水供給
量の制御の運転シミュレーション結果を図2に示す。
In the flow of the flue gas desulfurization apparatus shown in FIG.
FIG. 2 shows an operation simulation result of controlling the extraction amount of the absorbing liquid (gypsum slurry) by the signal of the level signal device 17 and controlling the supply amount of the makeup water by the absorbing liquid specific gravity signal device 16.

【0026】図2に示すように、吸収液タンク1a内の
吸収液面レベル制御により、吸収液を抜出し停止のレベ
ルまで抜出した後でも、所定の吸収液の比重になるまで
補給水の供給を開始しない。この間に石灰石スラリ及び
吸収塔廻りの洗浄水は補給されており、吸収液タンク1
a内の吸収液中の石灰石スラリ濃度、吸収液面レベルも
自然に上昇してくる。そして、石灰石及び石膏のスラリ
濃度(吸収液の比重)が補給水供給開始濃度(吸収液の
比重)の値となった時点で補給水の供給を始める。さら
に吸収液の抜出し開始の吸収液面レベルになった時点で
吸収液の抜出しを再度開始するとともに、吸収液の比重
が補給水供給停止のスラリ濃度となった時点で補給水供
給を停止する。このような運転方法を繰り返すことによ
り、吸収塔内の吸収液の液面レベル及びスラリ濃度を一
定の範囲内に制御できる。
As shown in FIG. 2, the supply of make-up water is continued until the specific gravity of the absorbent reaches a predetermined value even after the absorbent is withdrawn to the stop level by controlling the level of the absorbent in the absorbent tank 1a. Do not start. During this time, the limestone slurry and the washing water around the absorption tower have been replenished.
The limestone slurry concentration in the absorbing solution and the level of the absorbing solution in a rise naturally. Then, when the slurry concentration of limestone and gypsum (specific gravity of the absorbing solution) becomes the value of the supply water supply start concentration (specific gravity of the absorbing solution), supply of the makeup water is started. Further, the withdrawal of the absorbing liquid is started again when the level of the absorbing liquid reaches the level of the absorbing liquid at the start of the withdrawal of the absorbing liquid, and the supply of the make-up water is stopped when the specific gravity of the absorbing liquid reaches the slurry concentration at which the supply of the make-up water is stopped. By repeating such an operation method, the liquid level and the slurry concentration of the absorbing liquid in the absorbing tower can be controlled within a certain range.

【0027】また、図3に示す実施の形態は図1に示す
フローで用いたハイドロサイクロン18を使用しないこ
と以外は図1に示すフローと同一のフローである。この
ように吸収塔内の吸収液(石膏スラリ)を断続的に抜出
すことが主目的であり、吸収塔1の後流側の機器がハイ
ドロサイクロンを設置しているかどうかにかかわらず、
また石膏脱水機の型式にかかわらず、本発明の適用が可
能である。
The embodiment shown in FIG. 3 is the same as the flow shown in FIG. 1 except that the hydrocyclone 18 used in the flow shown in FIG. 1 is not used. Thus, the main purpose is to intermittently withdraw the absorbing liquid (gypsum slurry) in the absorption tower, regardless of whether the downstream device of the absorption tower 1 is equipped with a hydrocyclone.
Further, the present invention is applicable regardless of the type of the gypsum dewatering machine.

【発明の効果】本発明によれば、吸収液タンク内の吸収
液(石膏スラリ)の抜出しを断続的運転で行っても、吸
収液タンク内の吸収液レベル及び吸収液中の石膏スラリ
又は石灰石スラリ濃度を一定範囲内に保つことができ
る。
According to the present invention, even if the absorption liquid (gypsum slurry) in the absorption liquid tank is withdrawn intermittently, the level of the absorption liquid in the absorption liquid tank and the gypsum slurry or limestone in the absorption liquid are maintained. The slurry concentration can be kept within a certain range.

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

【図1】 本発明の実施の形態の湿式排煙脱硫装置のフ
ローを示す図である。
FIG. 1 is a diagram showing a flow of a wet flue gas desulfurization device according to an embodiment of the present invention.

【図2】 図1のフローに本発明を適用した場合のシミ
ュレーション結果を示す図である。
FIG. 2 is a diagram showing a simulation result when the present invention is applied to the flow of FIG. 1;

【図3】 本発明の実施の形態の湿式排煙脱硫装置のフ
ローを示す図である。
FIG. 3 is a diagram showing a flow of the wet flue gas desulfurization apparatus according to the embodiment of the present invention.

【図4】 従来技術の湿式排煙脱硫装置のフローを示す
図である。
FIG. 4 is a view showing a flow of a conventional wet flue gas desulfurization apparatus.

【符号の説明】[Explanation of symbols]

1 吸収塔 2 循環ポンプ 3 スプレノズル 4 吸収液抜出ポンプ 6 脱水機 7 石膏ケーキ 8 石灰石供給スラリライン 9 石膏抜出しライン 10 吸収塔補給水供給ライン 11 補給水供給弁 12 調整弁 13 吸収液抜出弁 14 排ガス 15 空気 16 吸収液比重信号
器 17 レベル信号器 18 ハイドロサイク
ロン 20 制御装置
DESCRIPTION OF SYMBOLS 1 Absorption tower 2 Circulation pump 3 Spray nozzle 4 Absorption liquid extraction pump 6 Dehydrator 7 Gypsum cake 8 Limestone supply slurry line 9 Gypsum extraction line 10 Absorption tower supply water supply line 11 Supply water supply valve 12 Adjustment valve 13 Absorption liquid extraction valve 14 Exhaust gas 15 Air 16 Absorbent specific gravity signal 17 Level signal 18 Hydrocyclone 20 Controller

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 石灰石スラリを含む吸収液をボイラ排ガ
スと接触させて、排ガス中の硫黄酸化物を吸収除去する
吸収塔と、 排ガス中の硫黄酸化物を吸収した吸収液を貯留する吸収
液タンクと、 該吸収液タンクから吸収液を抜出すための抜出しライン
自動開閉弁を備えた吸収液抜出しラインと、 吸収液タンク内に補給水を供給するための補給水供給ラ
イン自動開閉弁を備えた補給水供給ラインと、 吸収液タンク内の吸収液の比重を計測する比重計又は吸
収液中のスラリ濃度計と吸収液の液面レベルを計測する
液面レベル計と、 前記吸収液の比重計又は吸収液中のスラリ濃度計の検出
値に基づき補給水供給ライン自動開閉弁の開閉制御を
し、前記吸収液の液面レベル計の検出値に基づき抜出し
ライン自動開閉弁の開閉制御をする制御装置を設けたこ
とを特徴とする湿式排煙脱硫装置。
1. An absorption tower for contacting an absorbent containing limestone slurry with boiler exhaust gas to absorb and remove sulfur oxides in the exhaust gas, and an absorbent tank for storing the absorbent absorbing the sulfur oxides in the exhaust gas. An absorption liquid extraction line with an extraction line automatic opening / closing valve for extracting the absorption liquid from the absorption liquid tank; and a makeup water supply line automatic opening / closing valve for supplying makeup water into the absorption liquid tank. A makeup water supply line, a hydrometer for measuring the specific gravity of the absorbent in the absorbent tank or a slurry concentration meter in the absorbent and a liquid level meter for measuring the liquid level of the absorbent, and a hydrometer for the absorbent. Or, control for opening / closing a make-up water supply line automatic opening / closing valve based on a detection value of a slurry concentration meter in an absorbing solution, and control for opening / closing control of an extraction line automatic opening / closing valve based on a detection value of a liquid level meter for the absorbing solution. Equipment Wet flue gas desulfurization apparatus characterized by.
【請求項2】 吸収液を貯留する石灰石スラリを含む吸
収液タンクから吸収液を吸収塔内に供給し、吸収塔内に
導入されるボイラ排ガスと接触させて、排ガス中の硫黄
酸化物を吸収除去し、該排ガス中の硫黄酸化物を吸収し
た吸収液を吸収液タンクに戻す湿式排煙脱硫方法におい
て、 吸収液タンク内の吸収液の比重又はスラリ濃度に基づき
吸収液タンクへの補給水の供給量を調整し、また吸収液
タンク内の吸収液の液面レベルに基づき吸収液タンクか
らの吸収液抜出し量を調整することを特徴とする湿式排
煙脱硫方法。
2. An absorption liquid is supplied from an absorption liquid tank containing limestone slurry for storing the absorption liquid into an absorption tower, and brought into contact with boiler exhaust gas introduced into the absorption tower to absorb sulfur oxides in the exhaust gas. In the wet flue gas desulfurization method for removing and absorbing the sulfur oxides contained in the exhaust gas to the absorption tank, the replenishing water to the absorption tank is determined based on the specific gravity or the slurry concentration of the absorption tank in the absorption tank. A wet flue gas desulfurization method comprising adjusting the supply amount and adjusting the amount of the absorbing liquid withdrawn from the absorbing liquid tank based on the level of the absorbing liquid in the absorbing liquid tank.
JP10008413A 1998-01-20 1998-01-20 Wet desulfurization equipment and its operation method Pending JPH11197450A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10008413A JPH11197450A (en) 1998-01-20 1998-01-20 Wet desulfurization equipment and its operation method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10008413A JPH11197450A (en) 1998-01-20 1998-01-20 Wet desulfurization equipment and its operation method

Publications (1)

Publication Number Publication Date
JPH11197450A true JPH11197450A (en) 1999-07-27

Family

ID=11692466

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10008413A Pending JPH11197450A (en) 1998-01-20 1998-01-20 Wet desulfurization equipment and its operation method

Country Status (1)

Country Link
JP (1) JPH11197450A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010196775A (en) * 2009-02-25 2010-09-09 Chugoku Electric Power Co Inc:The Piping structure and desulfurizer
WO2012131951A1 (en) * 2011-03-30 2012-10-04 バブコック日立株式会社 Exhaust gas treatment system and exhaust gas treatment method
WO2016010135A1 (en) * 2014-07-17 2016-01-21 三菱日立パワーシステムズ株式会社 Flue gas desulfurization apparatus and method of operating same
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Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010196775A (en) * 2009-02-25 2010-09-09 Chugoku Electric Power Co Inc:The Piping structure and desulfurizer
WO2012131951A1 (en) * 2011-03-30 2012-10-04 バブコック日立株式会社 Exhaust gas treatment system and exhaust gas treatment method
AU2011364139B2 (en) * 2011-03-30 2014-04-24 Mitsubishi Hitachi Power Systems, Ltd. Exhaust gas treatment system and exhaust gas treatment method
WO2016010135A1 (en) * 2014-07-17 2016-01-21 三菱日立パワーシステムズ株式会社 Flue gas desulfurization apparatus and method of operating same
JP2016022408A (en) * 2014-07-17 2016-02-08 三菱日立パワーシステムズ株式会社 Flue-gas desulfurization device and flue-gas desulfurization device operation method
WO2019138885A1 (en) * 2018-01-10 2019-07-18 株式会社ジャパンエンジンコーポレーション Water treatment apparatus
JP2019118903A (en) * 2018-01-10 2019-07-22 株式会社ジャパンエンジンコーポレーション Water treatment apparatus
CN111566053A (en) * 2018-01-10 2020-08-21 日本发动机股份有限公司 Water treatment device
CN112604448A (en) * 2020-12-17 2021-04-06 宜昌江峡船用机械有限责任公司 Garbage incinerator spray tower and garbage incinerator
CN112807937A (en) * 2020-12-31 2021-05-18 荣成碳纤维科技有限公司 Method and equipment for treating tail gas in carbon fiber precursor production
JP2023110945A (en) * 2022-01-31 2023-08-10 直江津電子工業株式会社 Exhaust gas treatment system and exhaust gas treatment method
JP2023111815A (en) * 2022-01-31 2023-08-10 直江津電子工業株式会社 Exhaust gas treatment system and exhaust gas treatment method

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