JPH05337327A - Wet-type exhaust gas desulfurization device and method for desulfurization - Google Patents

Wet-type exhaust gas desulfurization device and method for desulfurization

Info

Publication number
JPH05337327A
JPH05337327A JP4150880A JP15088092A JPH05337327A JP H05337327 A JPH05337327 A JP H05337327A JP 4150880 A JP4150880 A JP 4150880A JP 15088092 A JP15088092 A JP 15088092A JP H05337327 A JPH05337327 A JP H05337327A
Authority
JP
Japan
Prior art keywords
slurry
exhaust gas
absorption tower
wet
dehydrator
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
JP4150880A
Other languages
Japanese (ja)
Inventor
Kazuo Katsube
和夫 勝部
Masakatsu Nishimura
正勝 西村
Shigeru Nozawa
滋 野沢
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 JP4150880A priority Critical patent/JPH05337327A/en
Publication of JPH05337327A publication Critical patent/JPH05337327A/en
Pending legal-status Critical Current

Links

Landscapes

  • Treating Waste Gases (AREA)

Abstract

PURPOSE:To provide a wet-type exhaust gas desulfurization method by which to reduce the quantity of alkali agent used for separating fluorine and metal ion dissolved in a drained liquid, when discharging a drained absorbent slurry to a drainage treatment device, in a wet-type exhaust gas desulfurization device using a calcium compound absorbent slurry. CONSTITUTION:Part of a calcium compound absorbent slurry which comes in contact with an exhaust gas containing sulfur oxide in an absorption column 2, is extracted through a pump 5, then the extracted slurry is dehydrated using a dehydrator 13 to recover gypsum 14, and part of the water drained by the dehydrator is recycled to the absorption column 2. The other part, of the water drained by the defydrator, which corresponds to the drainage amount of a desulfurization device is supplied to a neutralization tank 6 and an alkali agent 7 is added to adjust the pH value. After that, the drained water with the adjusted pH value is sent to a thickener 8 where a supernatant is discharged to a drainage treatment device. On the other hand, an underflow slurry containing a solid component is supplied to the absorption column or the dehydrator.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は湿式排ガス脱硫装置およ
び脱硫方法に係り、特に脱硫排水中のF(弗素)濃度を
少量の薬剤で低減することができる湿式排ガス脱硫装置
および脱硫方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a wet exhaust gas desulfurization apparatus and a desulfurization method, and more particularly to a wet exhaust gas desulfurization apparatus and a desulfurization method capable of reducing the F (fluorine) concentration in desulfurization effluent with a small amount of chemicals.

【0002】[0002]

【従来の技術】現在ボイラ等の排ガスの処理に使用され
ている排ガス脱硫装置の中では、ボイラ等の排ガス中の
SOxを吸収した後、酸化して硫酸カルシウム、すなわ
ち石膏として回収する、石灰石・石灰等を吸収剤(以
後、石灰石・石灰等を吸収剤と、吸収塔に供給する吸収
剤を含むスラリを吸収液スラリと称する)として用いる
湿式石灰石・石膏法が一般的に用いられている。
2. Description of the Related Art Among exhaust gas desulfurization apparatuses currently used for treating exhaust gas from boilers and the like, after absorbing SOx in the exhaust gas from boilers and the like, they are oxidized and recovered as calcium sulfate, that is, gypsum. A wet limestone / gypsum method is generally used in which lime or the like is used as an absorbent (hereinafter, limestone / lime or the like is referred to as an absorbent, and a slurry containing the absorbent supplied to an absorption tower is referred to as an absorbent slurry).

【0003】従来の湿式排ガス脱硫装置の系統図を図3
に示す。ボイラ等の排ガスは入口煙道1を通って吸収塔
2に導入され、ここで循環ポンプ3により供給される吸
収液スラリスプレ2aとの気液接触により、飽和温度ま
で冷却されると同時に、排ガス中のSOx、ダスト、H
Cl、HF等が除去され、出口煙道4から排出される。
A system diagram of a conventional wet exhaust gas desulfurization apparatus is shown in FIG.
Shown in. Exhaust gas from a boiler or the like is introduced into the absorption tower 2 through the inlet flue 1, where it is cooled to the saturation temperature by gas-liquid contact with the absorbing liquid slurry pre-spray 2a supplied by the circulation pump 3 and, at the same time, in the exhaust gas. SOx, dust, H
Cl, HF, etc. are removed and discharged from the outlet flue 4.

【0004】吸収塔2には、吸収除去すべきSOx量に
見合う量の吸収剤スラリが吸収剤スラリタンク19から
吸収剤スラリポンプ20を経て供給される。一方、SO
xを吸収し、酸化されて生成した石膏を含有するスラリ
が、吸収塔抜出しポンプ5により、吸収剤スラリの投入
量に見合って抜出され、中和タンク6に供給される。中
和タンク6内では苛性ソーダ等のアルカリ剤溶液7が供
給され、前記抜出された吸収液スラリのpHを4〜6か
ら6以上に上昇させることにより、吸収塔2でSOxと
同時に除去され、吸収液スラリ中に溶解しているF-
よびダスト中の金属イオン(M+ )が、それぞれCaF
2 およびMOHとして析出する。このCaF2 、MOH
を含む石膏スラリは、石膏シックナ8で自然沈降により
石膏、CaF2 、MOHの固形物濃度を上げた濃縮スラ
リと、上澄液とに分離される。濃縮スラリはシックナア
ンダフローポンプ9により脱水機供給タンク10に貯え
られた後、脱水機供給ポンプ11により脱水機13に供
給され、粉末の石膏14として排出される。脱水濾液は
脱水機排水ピット15に貯えられ、脱水機排水ポンプ1
6により石膏シックナ8に戻され、再度濃縮される。一
方、石膏シックナ8からのオーバフロ液はシックナオー
バフロータンク17に貯えられ、シックナオーバフロー
ポンプ18により、一部は系内のCl濃度の濃縮を抑え
るため図示していない排水処理装置へ排出され、残りは
吸収塔2内で再利用される。
The absorber 2 is supplied with an amount of absorbent slurry that corresponds to the amount of SOx to be absorbed and removed from the absorbent slurry tank 19 through the absorbent slurry pump 20. On the other hand, SO
The slurry containing gypsum produced by absorbing x and being oxidized is withdrawn by the absorption tower withdrawing pump 5 in proportion to the amount of the absorbent slurry input, and is supplied to the neutralization tank 6. In the neutralization tank 6, an alkaline agent solution 7 such as caustic soda is supplied, and the pH of the extracted absorbent slurry is increased from 4 to 6 to 6 or more, so that it is simultaneously removed with SOx in the absorption tower 2, Metal ions (M + ) in the F and dust dissolved in the absorbent slurry are CaF
2 and precipitated as MOH. This CaF 2 , MOH
The gypsum slurry containing is separated by the gypsum thickener 8 into a concentrated slurry in which the solid concentration of gypsum, CaF 2 and MOH is increased by natural sedimentation, and a supernatant. The concentrated slurry is stored in the dehydrator supply tank 10 by the thickener underflow pump 9, then supplied to the dehydrator 13 by the dehydrator supply pump 11, and discharged as the powdered gypsum 14. The dehydrated filtrate is stored in the dehydrator drainage pit 15, and the dehydrator drainage pump 1
It is returned to the gypsum thickener 8 by 6 and concentrated again. On the other hand, the overflow liquid from the gypsum thickener 8 is stored in the thickener overflow tank 17, and partly discharged by the thickener overflow pump 18 to a wastewater treatment device (not shown) to suppress the concentration of Cl concentration in the system, and the rest. It is reused in the absorption tower 2.

【0005】上記システムにおいて、中和タンク6にお
いてアルカリ剤7を添加し、溶解しているF- 等を析出
させ石膏シックナ8で分離する目的は、シックナオーバ
フロー水の一部から排水処理装置に排出される排水中の
- 等の濃度を低減することにより、排水処理装置でF
- 等を処理するための薬品量を低減するだけでなく、処
理に伴って発生する産業廃棄物となる汚泥量を低減する
ことである。
In the above system, the purpose of adding the alkaline agent 7 in the neutralization tank 6 to precipitate the dissolved F- and the like and separate it with the gypsum thickener 8 is to discharge a portion of the thickener overflow water to the wastewater treatment equipment. F in wastewater - by reducing the concentration of such, F wastewater treatment apparatus
- not only to reduce the drug amount for processing or the like, is to reduce the amount of sludge to be industrial waste generated by the process.

【0006】[0006]

【発明が解決しようとする課題】上述した従来技術にお
いては、中和タンクに供給されるアルカリ剤は排水処理
装置のユーティリティの低減、および発生汚泥量を低減
することを目的とするものであるにもかかわらず、吸収
塔から抜出されるスラリ全量に対し、そのpHを上昇さ
せるために供給されており、さらにそのスラリ全量をシ
ックナ8に入れ、濃縮分離しているので、使用するアル
カリ剤量が過大になるばかりでなく、シックナ8が過剰
に大きくなるという問題があった。
In the above-mentioned prior art, the purpose of the alkaline agent supplied to the neutralization tank is to reduce the utility of the wastewater treatment equipment and to reduce the amount of sludge generated. Nevertheless, the total amount of slurry extracted from the absorption tower is supplied to raise the pH, and the total amount of the slurry is put into the thickener 8 and concentrated and separated, so the amount of alkali agent used is Not only is it too large, but there is also the problem that the thickener 8 becomes too large.

【0007】本発明の目的は、F(弗素)成分除去に必
要なアルカリ剤の量を必要最小限にするとともに、石膏
シックナ8の寸法を小さくすることができる湿式排ガス
脱硫装置および脱硫方法を提供することにある。
An object of the present invention is to provide a wet exhaust gas desulfurization apparatus and a desulfurization method capable of reducing the size of the gypsum thickener 8 while minimizing the amount of the alkaline agent necessary for removing the F (fluorine) component. To do.

【0008】[0008]

【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、硫黄酸化物を含有する排ガスをカ
ルシウム化合物を含む吸収剤スラリと気液接触させる吸
収塔と、気液接触した吸収塔内の吸収剤スラリの一部を
抜出し該スラリ中の石膏を分離して回収する脱水装置と
を備えた湿式排ガス脱硫装置において、脱水装置で石膏
と分離されたスラリの残液の一部を吸収塔へ供給する手
段と、該スラリ残液の他部にアルカリ剤を添加して液中
の溶解物を析出させ濾液と析出固形物濃縮スラリに分離
する手段と、濾液は排出し固形物スラリは脱硫装置へ戻
す手段とを設けたことを特徴とする湿式排ガス脱硫装置
に関する。
In order to achieve the above object, a first invention of the present application is to provide an absorption tower in which exhaust gas containing sulfur oxide is brought into gas-liquid contact with an absorbent slurry containing a calcium compound, and gas-liquid contact is made. In a wet exhaust gas desulfurization device equipped with a dehydrator for extracting a part of the absorbent slurry in the absorption tower and separating and recovering the gypsum in the slurry, one of the residual liquid of the slurry separated from the gypsum by the dehydrator Part to the absorption tower, a means for adding an alkaline agent to the other part of the slurry residual liquid to precipitate a dissolved substance in the liquid and separate it into a filtrate and a precipitated solid concentrated slurry, and the filtrate is discharged and solidified. The present invention relates to a wet exhaust gas desulfurization device, which is provided with means for returning the product slurry to the desulfurization device.

【0009】第2の発明は、吸収塔内で硫黄酸化物含有
排ガスとカルシウム化合物吸収剤スラリと接触させて排
ガス中の硫黄酸化物を吸収除去するとともに、吸収塔内
の吸収剤スラリの一部を抜出しスラリ中の石膏を回収す
る湿式排ガス脱硫装置において、吸収塔から抜出された
スラリを脱水装置により脱水して石膏を回収し、脱水排
液の少なくとも一部にアルカリ剤を添加してpHを上昇
させ、排液中の溶解物を析出させたのち、濾液と析出物
固形物濃縮スラリに分離し、濾液は排水処理装置に排出
し、固形物スラリは脱水装置または吸収塔に供給するこ
とを特徴とする湿式排ガス脱硫方法に関する。
A second aspect of the invention is to bring the sulfur oxide-containing exhaust gas and the calcium compound absorbent slurry into contact with each other in the absorption tower to absorb and remove the sulfur oxide in the exhaust gas, and at the same time, a part of the absorbent slurry in the absorption tower. In a wet exhaust gas desulfurization device for recovering gypsum in the slurry, the slurry extracted from the absorption tower is dehydrated by a dehydrator to recover the gypsum, and an alkaline agent is added to at least a part of the dehydrated effluent to adjust the pH. To precipitate the dissolved matter in the effluent, separate it into a filtrate and precipitate solids concentrated slurry, discharge the filtrate to the wastewater treatment equipment, and supply the solids slurry to the dehydrator or absorption tower. The present invention relates to a wet exhaust gas desulfurization method.

【0010】第3の発明は、上記第2の発明において、
スラリ残液の他部へのアルカリ剤添加量を、アルカリ剤
添加後のスラリ残液のpH値が所定値になるように制御
することを特徴とする湿式排ガス脱硫方法に関する。
A third invention is the above-mentioned second invention,
The present invention relates to a wet exhaust gas desulfurization method, characterized in that the amount of the alkaline agent added to the other part of the slurry residual liquid is controlled so that the pH value of the slurry residual liquid after the addition of the alkaline agent becomes a predetermined value.

【0011】[0011]

【作用】中和タンク6に供給されるスラリ量は脱硫装置
からの必要排水量を確保するための量に限られるため、
pHを上昇するに必要なアルカリ剤添加量は最低限に抑
えられ、またシックナ8への流入スラリ量も減少するた
め、むだな薬品使用および過剰設備となることがない。
Since the amount of slurry supplied to the neutralization tank 6 is limited to the amount required to secure the required amount of waste water from the desulfurization device,
The amount of alkali agent required to raise the pH is kept to a minimum, and the amount of slurry flowing into the thickener 8 is also reduced, so that wasteful use of chemicals and excessive equipment will not occur.

【0012】[0012]

【実施例】本発明になる湿式排ガス脱硫装置の系統を図
1に示す。吸収塔の作用は従来技術と同様であるが、吸
収塔2から抜出されるスラリは脱水機供給タンク10に
貯えられる。このスラリは脱水機供給ポンプ11で脱水
機13に供給され、石膏14は脱水され回収される。一
方、脱水濾液は脱水機排水ピット15に回収され、脱水
機排水ポンプ16により、吸収塔2および吸収剤スラリ
ピット19に補給水として供給されるとともに、一部は
中和タンク6に供給される。中和タンク6では、pH計
12によりpHを計測し、pHが所定値になるよう、ア
ルカリ剤7が添加される。中和タンク6から石膏シック
ナ8に送られ、固形物が分離されたオーバフロー液はシ
ックナオーバフロータンク17に貯えられシックナオー
バフローポンプ18により、排水処理装置に排出され
る。一方、CaF2 等の固形物を含んだスラリは、再度
脱水機供給タンク10に戻される。
EXAMPLE A system of a wet exhaust gas desulfurization apparatus according to the present invention is shown in FIG. The operation of the absorption tower is similar to that of the conventional technology, but the slurry extracted from the absorption tower 2 is stored in the dehydrator supply tank 10. This slurry is supplied to the dehydrator 13 by the dehydrator supply pump 11, and the gypsum 14 is dehydrated and recovered. On the other hand, the dehydrated filtrate is collected in the dehydrator drain pit 15, supplied by the dehydrator drain pump 16 to the absorption tower 2 and the absorbent slurry pit 19 as make-up water, and partly supplied to the neutralization tank 6. In the neutralization tank 6, the pH is measured by the pH meter 12, and the alkaline agent 7 is added so that the pH becomes a predetermined value. The overflow liquid sent from the neutralization tank 6 to the gypsum thickener 8 and separated from the solid matter is stored in the thickener overflow tank 17 and discharged to the wastewater treatment device by the thickener overflow pump 18. On the other hand, the slurry containing solid matter such as CaF 2 is returned to the dehydrator supply tank 10 again.

【0013】上述のとおり、本実施例によれば、中和タ
ンク6への脱水濾液の供給量を低減できるので、アルカ
リ剤7の添加量の低減、石膏シックナ8のコンパクト化
が図れるが、具体的に本発明の効果を従来技術と比較し
てマスバランスを用いて説明する。一例として1000
MW用脱硫プラントの場合について、本発明および従来
技術の中和タンク廻りのマスバランスをそれぞれ図2と
図4に示す。
As described above, according to this embodiment, the supply amount of the dehydrated filtrate to the neutralization tank 6 can be reduced, so that the addition amount of the alkaline agent 7 can be reduced and the gypsum thickener 8 can be made compact. The effect of the present invention will be described in comparison with the prior art using mass balance. 1000 as an example
2 and 4 show the mass balance around the neutralization tank of the present invention and the prior art in the case of the desulfurization plant for MW, respectively.

【0014】図4に示す従来の脱硫装置においては、中
和タンク6に流入するスラリ量51は168トン/hで
あり、このスラリのpH上昇に要するアルカリ剤添加量
57は0.16トン/hである。これに対し、図2に示
す本発明においては中和タンク6に流入するスラリ量5
6は26トン/hに低減できることから、アルカリ剤5
7は約0.03トン/hとなり、従来技術の1/5以下
に低減できる。
In the conventional desulfurization apparatus shown in FIG. 4, the slurry amount 51 flowing into the neutralization tank 6 is 168 tons / h, and the addition amount 57 of the alkaline agent required for raising the pH of this slurry is 0.16 tons / h. h. On the other hand, in the present invention shown in FIG. 2, the amount of slurry flowing into the neutralization tank 6 is 5
6 can be reduced to 26 tons / h,
7 is about 0.03 ton / h, which can be reduced to ⅕ or less of the conventional technique.

【0015】さらにシックナ8に流入するスラリ量につ
いても従来技術においては、図4に示すとおり、上記の
吸収塔抜出し量51:168トン/hと、アルカリ剤添
加量57:0.16トン/hと、脱水機排水ポンプ16
から供給される脱水機排水ポンプ出口量55:102ト
ン/hを加えた270トン/hを処理する必要があり、
この量を処理するためにはシックナ8は直径が17mと
非常に大型となる。
Regarding the amount of slurry flowing into the thickener 8, in the prior art, as shown in FIG. 4, the above-mentioned absorption tower withdrawal amount is 51: 168 tons / h and the alkali agent addition amount is 57: 0.16 tons / h. And the dehydrator drainage pump 16
It is necessary to treat 270 tons / h, which is the sum of 55: 102 tons / h of outlet of the dehydrator drain pump supplied from
In order to handle this amount, the thickener 8 becomes very large with a diameter of 17 m.

【0016】これに対し、本発明ではシックナ8に流入
するスラリ量は、図2に示すように、上述の中和タンク
入口流量56:26トン/hと、アルカリ剤添加量5
7:0.03トン/hを加えた約26トン/hとなり、
従来技術の1/10に低減でき、シックナ8も直径5m
以下と非常に小型化が可能である。本発明の他の実施例
としては、図1に示す脱水機供給タンク10、ポンプ1
1を省略し、シックナ8のアンダフロースラリは吸収塔
に戻す方法があるが、同様の効果が得られる。
On the other hand, in the present invention, the amount of slurry flowing into the thickener 8 is, as shown in FIG. 2, the above neutralization tank inlet flow rate of 56:26 tons / h and the amount of alkali agent addition of 5
7: 0.03 ton / h added to about 26 ton / h,
It can be reduced to 1/10 of the conventional technology, and thicker 8 has a diameter of 5 m
It is possible to make the size very small as follows. As another embodiment of the present invention, a dehydrator supply tank 10 and a pump 1 shown in FIG.
Although there is a method of omitting 1 and returning the underflow slurry of the thickener 8 to the absorption tower, the same effect can be obtained.

【0017】[0017]

【発明の効果】本発明によれば、中和タンクおよびシッ
クナへの流入スラリ量を低減できるので、弗素等を除去
するための薬品使用量およびシックナの設備費の低減が
可能である。
According to the present invention, since the amount of slurry flowing into the neutralization tank and thickener can be reduced, the amount of chemicals used to remove fluorine and the like and the equipment cost of thickener can be reduced.

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

【図1】本発明になる湿式排煙脱硫装置の系統図。FIG. 1 is a system diagram of a wet flue gas desulfurization apparatus according to the present invention.

【図2】本発明になる湿式排煙脱硫装置のマスバランス
を示す図。
FIG. 2 is a diagram showing a mass balance of the wet flue gas desulfurization apparatus according to the present invention.

【図3】およびFIG. 3 and

【図4】それぞれ従来技術からなる湿式排煙脱硫装置の
系統図およびそのマスバランスを示す図。
FIG. 4 is a system diagram of a conventional wet flue gas desulfurization apparatus and a diagram showing a mass balance thereof.

【符号の説明】[Explanation of symbols]

1…入口煙道、2…吸収塔、3…循環ポンプ、4…出口
煙道、5…抜出しポンプ、6…中和タンク、7…アルカ
リ剤、8…石膏シックナ、9…シックナアンダフローポ
ンプ、10…脱水機供給タンク、11…脱水機供給ポン
プ、12…pH計、13…脱水機、14…石膏、15…
脱水機排水ピット、16…脱水機排水ポンプ、17…シ
ックナオーバフロータンク、18…シックナオーバフロ
ーポンプ、19…吸収剤スラリピット、20…吸収剤ス
ラリポンプ、51…吸収塔抜出し量、52…脱水機供給
量、53…石膏生成量、54…脱水濾過量、55…脱水
機排水ポンプ出口量、56…中和タンク入口流量、57
…アルカリ剤添加量、58…シックナオーバフロー量、
59…シックナアンダフロー量、60…排水流量。
1 ... Inlet flue, 2 ... Absorption tower, 3 ... Circulation pump, 4 ... Exit flue, 5 ... Extraction pump, 6 ... Neutralization tank, 7 ... Alkaline agent, 8 ... Gypsum thickener, 9 ... Thickener underflow pump, 10 ... Dehydrator supply tank, 11 ... Dehydrator supply pump, 12 ... pH meter, 13 ... Dehydrator, 14 ... Gypsum, 15 ...
Dewatering machine drainage pit, 16 ... Dewatering machine drainage pump, 17 ... Thickener overflow tank, 18 ... Thickener overflow pump, 19 ... Absorber slurry pit, 20 ... Absorber slurry pump, 51 ... Absorption tower extraction amount, 52 ... Dehydrator supply amount , 53 ... Gypsum production amount, 54 ... Dehydration filtration amount, 55 ... Dehydrator drainage pump outlet amount, 56 ... Neutralization tank inlet flow amount, 57
… Alkaline agent addition amount, 58… Thickener overflow amount,
59 ... Thickener underflow amount, 60 ... Drainage flow rate.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 硫黄酸化物を含有する排ガスをカルシウ
ム化合物を含む吸収剤スラリと気液接触させる吸収塔
と、気液接触した吸収塔内の吸収剤スラリの一部を抜出
し該スラリ中の石膏を分離して回収する脱水装置とを備
えた湿式排ガス脱硫装置において、脱水装置で石膏と分
離されたスラリの残液の一部を吸収塔へ供給する手段
と、該スラリ残液の他部にアルカリ剤を添加して液中の
溶解物を析出させ濾液と析出固形物濃縮スラリに分離す
る手段と、濾液は排出し固形物スラリは脱硫装置へ戻す
手段とを設けたことを特徴とする湿式排ガス脱硫装置。
1. An absorption tower in which an exhaust gas containing sulfur oxides is brought into gas-liquid contact with an absorbent slurry containing a calcium compound, and a part of the absorbent slurry in the gas-liquid contacted absorption tower is extracted to obtain gypsum in the slurry. In a wet exhaust gas desulfurization device equipped with a dehydrating device for separating and recovering, the means for supplying a part of the residual liquid of the slurry separated from the gypsum by the dehydrating device to the absorption tower, and the other part of the residual liquid of the slurry. A wet process characterized in that means for adding an alkaline agent to precipitate a dissolved substance in the liquid to separate it into a filtrate and a precipitated solid concentrated slurry, and means for discharging the filtrate and returning the solid slurry to a desulfurization apparatus are provided. Exhaust gas desulfurization equipment.
【請求項2】 吸収塔内で硫黄酸化物含有排ガスとカル
シウム化合物吸収剤スラリと接触させて排ガス中の硫黄
酸化物を吸収除去するとともに、吸収塔内の吸収剤スラ
リの一部を抜出しスラリ中の石膏を回収する湿式排ガス
脱硫装置において、吸収塔から抜出されたスラリを脱水
装置により脱水して石膏を回収し、脱水排液の少なくと
も一部にアルカリ剤を添加してpHを上昇させ、排液中
の溶解物を析出させたのち、濾液と析出物固形物濃縮ス
ラリに分離し、濾液は排水処理装置に排出し、固形物ス
ラリは脱水装置または吸収塔に供給することを特徴とす
る湿式排ガス脱硫方法。
2. A sulfur oxide-containing exhaust gas and a calcium compound absorbent slurry are brought into contact with each other in the absorption tower to absorb and remove the sulfur oxide in the exhaust gas, and a part of the absorbent slurry in the absorption tower is extracted into the slurry. In the wet exhaust gas desulfurization device for recovering gypsum, the slurry extracted from the absorption tower is dehydrated by a dehydrator to recover gypsum, and the pH is increased by adding an alkaline agent to at least a part of the dehydrated effluent, After the dissolved matter in the effluent is precipitated, it is separated into a filtrate and a precipitate solids concentrated slurry, the filtrate is discharged to a wastewater treatment device, and the solids slurry is supplied to a dehydrator or an absorption tower. Wet exhaust gas desulfurization method.
【請求項3】 請求項2において、スラリ残液の他部へ
のアルカリ剤添加量を、アルカリ剤添加後のスラリ残液
のpH値が所定値になるように制御することを特徴とす
る湿式排ガス脱硫方法。
3. The wet method according to claim 2, wherein the amount of the alkaline agent added to the other part of the residual slurry liquid is controlled so that the pH value of the residual slurry liquid after the alkaline agent is added becomes a predetermined value. Exhaust gas desulfurization method.
JP4150880A 1992-06-10 1992-06-10 Wet-type exhaust gas desulfurization device and method for desulfurization Pending JPH05337327A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4150880A JPH05337327A (en) 1992-06-10 1992-06-10 Wet-type exhaust gas desulfurization device and method for desulfurization

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4150880A JPH05337327A (en) 1992-06-10 1992-06-10 Wet-type exhaust gas desulfurization device and method for desulfurization

Publications (1)

Publication Number Publication Date
JPH05337327A true JPH05337327A (en) 1993-12-21

Family

ID=15506406

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4150880A Pending JPH05337327A (en) 1992-06-10 1992-06-10 Wet-type exhaust gas desulfurization device and method for desulfurization

Country Status (1)

Country Link
JP (1) JPH05337327A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012020216A (en) * 2010-07-13 2012-02-02 Babcock Hitachi Kk Wet-type apparatus for desulfurizing flue gas

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012020216A (en) * 2010-07-13 2012-02-02 Babcock Hitachi Kk Wet-type apparatus for desulfurizing flue gas

Similar Documents

Publication Publication Date Title
US4859440A (en) Method of treating flue gases and combustion residues
US4000991A (en) Method of removing fly ash particulates from flue gases in a closed-loop wet scrubbing system
KR101835837B1 (en) Calcium removal method
CN109399855A (en) A kind of zero emission treatment of desulfured waste water
CN205974125U (en) Desulfurization waste water zero release processing system
JP3066403B2 (en) Method for removing sulfur dioxide from flue gas
JP2740533B2 (en) Wet exhaust gas desulfurization method
JPH05337327A (en) Wet-type exhaust gas desulfurization device and method for desulfurization
CN109529588A (en) A kind of anhydrous hydrogen fluoride production technology tail gas absorption method and device
JPS61129090A (en) Removal of fluorine from waste water of waste gas desulfurization apparatus
JP3526975B2 (en) Coal ash solidification treatment method for desulfurization wastewater
CA1099491A (en) Process for removing chlorine ions from the wet flue- gas processing system
CN207537295U (en) A kind of high-salt wastewater treatment process system
JPH08299754A (en) Wet flue gas desulfurization method and device therefor
JP4347097B2 (en) Waste water treatment system and exhaust gas treatment system using the same
JPS5715886A (en) Method for removing heavy metal in waste water of stack gas treatment
JPH0338294A (en) Method for flocculation treatment of waste water
JP3727366B2 (en) Method and apparatus for purifying gases containing sulfur dioxide
CN109205895A (en) A kind of high-salt wastewater treatment process system and method
JP2691036B2 (en) Method for removing impurities from solution after gypsum separation
JP2002336642A (en) Wet type waste gas desulfurizing method and apparatus
JP2608067B2 (en) COD treatment control equipment for wet flue gas desulfurization equipment wastewater
JPS625027B2 (en)
JP3232513B2 (en) Wet flue gas desulfurization device and method for collecting effluent from centrifugal separator
CN109939554A (en) A kind of white clay desulphurization system and its sulfur method