JPH07256050A - Non-drainage method of wet exhaust gas desulfurizer - Google Patents

Non-drainage method of wet exhaust gas desulfurizer

Info

Publication number
JPH07256050A
JPH07256050A JP6053558A JP5355894A JPH07256050A JP H07256050 A JPH07256050 A JP H07256050A JP 6053558 A JP6053558 A JP 6053558A JP 5355894 A JP5355894 A JP 5355894A JP H07256050 A JPH07256050 A JP H07256050A
Authority
JP
Japan
Prior art keywords
liquid
dust
exhaust gas
tower
gypsum
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
JP6053558A
Other languages
Japanese (ja)
Inventor
Akira Kumagai
昭 熊谷
Fumiaki Tanaka
文明 田中
Atsushi Fukumoto
淳 福元
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.)
Chiyoda Corp
Chiyoda Chemical Engineering and Construction Co Ltd
Original Assignee
Chiyoda Corp
Chiyoda Chemical Engineering and Construction Co Ltd
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 Chiyoda Corp, Chiyoda Chemical Engineering and Construction Co Ltd filed Critical Chiyoda Corp
Priority to JP6053558A priority Critical patent/JPH07256050A/en
Publication of JPH07256050A publication Critical patent/JPH07256050A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Treating Waste Gases (AREA)
  • Gas Separation By Absorption (AREA)
  • Separation Of Particles Using Liquids (AREA)

Abstract

PURPOSE:To eliminate the drainage of water in a wet exhaust gas desulfurizer by using a liquid used in the extraction of dust as the washing water of gypsum separated in a solid-liquid separation process before circulating and reuse the same for the purpose of the extraction of dust. CONSTITUTION:After combustion exhaust gas is pretreated, the pretreated gas is brought into contact with the liquid circulated in a dust extraction tower 1 to be subjected to the extraction of dust while cooled and humidified. Next, the exhaust gas is sent to an absorbing tower 4 to be brought into contact with an absorbing soln. being a calcium type slurry to absorb and remove sulfur oxide. Thereafter, the formed gypsum-containing slurry is guided to a solid-liquid separator 7 to be separated into a gypsum cake and a mother liquid. The mother liquid is sent to a mother liquid tank 12 and a part of the mother liquid is reused as the supply water to the dust extraction tower 1 while a part thereof is refluxed to the absorbing tower 2 and the remainder thereof is used in the slurrying of a calcium compd. By this constitution, this desulfurizer is stably and continuously operated in a non-drainage state.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は湿式排煙脱硫装置の無排
水化方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for eliminating drainage of a wet flue gas desulfurization apparatus.

【0002】[0002]

【従来の技術】ボイラー、各種加熱炉、焼却炉等からの
燃焼排ガス中に含有される有害な硫黄酸化物主として亜
硫酸ガスは、カルシウム系化合物を吸収剤とする吸収液
と気液接触させることにより該吸収液中に吸収除去し、
次いで酸化し、石膏として固定、回収する湿式排煙脱硫
方法により、無害化除去すると同時に副生する石膏も産
業上利用されている。
2. Description of the Related Art Harmful sulfur oxides contained in combustion exhaust gas from boilers, various heating furnaces, incinerators, etc. Mainly sulfurous acid gas is produced by contacting with an absorbing liquid containing a calcium compound as a gas-liquid contact. Absorbed and removed in the absorbent,
Next, gypsum, which is detoxified and simultaneously produced as a by-product by a wet flue gas desulfurization method of oxidizing, fixing and collecting as gypsum, is also industrially used.

【0003】しかしながら、排ガス中には硫黄酸化物の
他に微量成分例えばダスト、重金属類、塩素化合物、フ
ッ素化合物、アンモニウム塩、等も不純物として含有さ
れており、これら不純物特に塩素化合物やフッ素化合物
等が吸収塔に流入した場合、吸収剤であるカルシウム系
化合物の溶解速度の低下による脱硫率の低下や、装置の
腐食など種々のトラブルを招く恐れがある。
However, in addition to sulfur oxides, trace components such as dust, heavy metals, chlorine compounds, fluorine compounds, ammonium salts, etc. are also contained in the exhaust gas as impurities, and these impurities, particularly chlorine compounds and fluorine compounds, etc. If it flows into the absorption tower, various problems such as a decrease in the desulfurization rate due to a decrease in the dissolution rate of the calcium-based compound that is the absorbent and corrosion of the apparatus may occur.

【0004】そのため湿式排煙脱硫方法では、吸収塔で
排ガスをカルシウム系化合物含有吸収液と気液接触させ
るに先立ち、冷却および除塵のための除塵塔(冷却塔と
も言う)を通常設置し、ここで排ガスを水性の液と接触
させて排ガスの冷却を図ると同時にこれら有害な微量成
分の大部分を捕捉して除去している。この除塵塔で使用
される液は通常循環使用されるため、循環液中に前記不
純物が蓄積し、ダストの堆積、塩類の析出、pH上昇、さ
らには装置の腐食等の問題を発生するので、通常補給水
の1割〜3割程度を排水し、その分工業用水等を補給す
ることにより、運転を継続している。
Therefore, in the wet flue gas desulfurization method, a dust removal tower (also referred to as a cooling tower) for cooling and dust removal is usually installed before the exhaust gas is brought into gas-liquid contact with the calcium compound-containing absorption liquid in the absorption tower. The exhaust gas is contacted with an aqueous liquid to cool the exhaust gas, and at the same time, most of these harmful trace components are captured and removed. Since the liquid used in this dust removal tower is normally circulated, the impurities are accumulated in the circulating liquid, which causes problems such as dust accumulation, salt precipitation, pH increase, and further device corrosion. Normally, about 10 to 30% of makeup water is drained, and industrial water is supplemented by that amount to continue the operation.

【0005】しかしこうして出される排水は前記した不
純物を含有しており、水質汚濁などの環境問題を引き起
こすため、公害防止の観点からそのままでは放流でき
ず、これら有害な不純物を除去もしくは低減させるため
例えばNaOHによる低pH液の中和処理、凝集沈殿、イオン
交換樹脂処理、pH調整、その他の排水処理をしたのち放
流されていた。
However, the wastewater thus discharged contains the above-mentioned impurities and causes environmental problems such as water pollution, so that it cannot be discharged as it is from the viewpoint of pollution prevention, and in order to remove or reduce these harmful impurities, for example, It was discharged after neutralization of low pH liquid with NaOH, coagulation sedimentation, ion exchange resin treatment, pH adjustment, and other wastewater treatment.

【0006】しかし近年、環境問題、水資源の節減など
の理由で、除塵塔からの排水に限らず、排煙脱硫系自体
から排水を出さないで操作するいわゆるクローズ化、無
排水化方法が要求され、種々の方法が提案されている。
例えば、排水をpH調整下に濃縮あるいは濃縮後蒸発乾固
させて除去するか、または排ガス中に噴霧させて得られ
る固形物を捕集除去するか、または排水を濃縮後石灰灰
等に混入し、乾燥除去する方法(特公昭54−1922
6号公報、特公昭63−63248号公報、特開平3−
8411号公報、特開平3−249919号公報、特公
平3−59730号公報)、石膏を加熱乾燥したものに
排水を混入除去する方法(特開昭51−124669号
公報)、排水を中和後固液分離し固相を加熱乾燥したも
のに、濃縮した液相を混入して除去する方法(特公昭5
5−33927号公報)、塩素含有排水を電気透析装置
にかけて得られる塩素濃縮液を石灰または石膏類中に混
入して乾燥固化する方法(特開平4−83586号公
報)、等々があげられる。
However, in recent years, due to environmental problems, reduction of water resources, etc., not only drainage from a dust removal tower, but also a so-called closed or no drainage method of operating without discharging drainage from the flue gas desulfurization system itself is required. , And various methods have been proposed.
For example, the wastewater is concentrated by adjusting the pH or concentrated and then evaporated to dryness to remove, or the solid matter obtained by spraying in the exhaust gas is collected and removed, or the wastewater is concentrated and then mixed with lime ash or the like. , A method of removing by drying (Japanese Patent Publication No. 54-1922)
No. 6, JP-B-63-63248, JP-A-3-
No. 8411, JP-A-3-249919, JP-B-3-59730), a method of removing wastewater by heating and drying gypsum (JP-A-51-124669), and after neutralizing the wastewater. A method in which a concentrated liquid phase is mixed with the solid-liquid separated and the solid phase is heated and dried, and removed (Japanese Patent Publication No.
5-33927), a method of mixing a chlorine-containing wastewater obtained by applying a chlorine-containing wastewater to an electrodialysis device into lime or gypsum to dry and solidify (JP-A-4-83586), and the like.

【0007】これらの方法はいずれも排水を濃縮または
乾燥するための熱エネルギーを要する。またたとえ熱エ
ネルギー源として排ガスの煙道の熱を利用したとしても
そのための機器を必要とする。その他中和のための薬剤
費、電気透析装置設備費、等の経費に加えそれらの運用
経費などを要する。濃縮を要しない方法として、特公昭
61−16490号公報には吸収塔を2基設置すること
による無排水化方法も開示されているが、吸収塔を1基
余分に設置することで設備費やその敷地面積を必要と
し、運転経費、保守費用も余分にかかる。
All of these methods require heat energy to concentrate or dry the wastewater. Even if the heat of the exhaust gas flue is used as a heat energy source, a device for that purpose is required. In addition to expenses such as drug costs for neutralization, facility costs for electrodialysis equipment, etc., operating costs for these are required. As a method that does not require concentration, Japanese Patent Publication No. 61-16490 discloses a method of eliminating drainage by installing two absorption towers. However, by installing an additional absorption tower, equipment costs are increased. The site area is required, and operating costs and maintenance costs are extra.

【0008】このとおり従来法による無排水化では、排
水処理装置それ自体が不要となってもあらたな機器その
他を必要とし、そのため結局のところあまり工業的に大
きなメリットは期待できなかった。
[0008] As described above, the conventional method without drainage requires new equipment and the like even if the wastewater treatment device itself is not required, and therefore, industrially, no great merit can be expected.

【0009】[0009]

【発明が解決しようとする課題】それゆえ、排水の濃縮
または煙道に戻しての噴霧乾燥を要せず、薬剤費も不要
で、無排水化のためのあらたな機器を設置する必要のな
い方法が開発できれば、工業的のみならず環境上も水資
源節減上も多大の貢献をもたらすことが出来ると期待さ
れる。
Therefore, there is no need for concentrating the waste water or spray-drying it back to the flue, no chemical costs, and no new equipment for draining. If a method can be developed, it is expected to make a great contribution not only in terms of industry but also in terms of environment and water resource conservation.

【0010】本発明者らは、除塵塔からのブリード液に
着目し、その運用方法の工夫による脱硫装置系内での液
の循環使用の可能性について種々検討を重ね、前記した
従来法の欠点を有しない無排水化方法を開発すべく研究
した。前記したとおり湿式排煙脱硫装置においては、吸
収塔に流入した場合に種々のトラブルを招く排ガス中の
不純物である有害な微量成分を捕捉し同時に排ガスを冷
却する目的で、吸収塔の前段に除塵塔(冷却塔とも言
う)を設置している。除塵塔内で循環する液にはこれら
有害成分が比較的多量に蓄積するため、補給水の1割〜
3割程度を排水し、その分工業用水等を補給することに
より運転を継続し、排水は排水処理設備を設けて有害成
分を除去後に放流している。
The inventors of the present invention focused on the bleeding liquid from the dust removing tower, conducted various studies on the possibility of circulating the liquid in the desulfurization system by devising the operating method, and found the drawbacks of the above-mentioned conventional method. Research was conducted to develop a drainage-free method that does not have the As described above, in the wet flue gas desulfurization device, dust is removed in the preceding stage of the absorption tower for the purpose of capturing harmful trace components that are impurities in the exhaust gas that cause various problems when flowing into the absorption tower and simultaneously cooling the exhaust gas. A tower (also called a cooling tower) is installed. Since a relatively large amount of these harmful components accumulates in the liquid circulating in the dust removal tower,
About 30% of the water is drained and the operation is continued by replenishing industrial water, etc., and the wastewater is discharged after removing harmful components by installing wastewater treatment equipment.

【0011】一方吸収塔にて生成する石膏は吸収塔から
石膏スラリーとして固液分離工程にまわされ、そこで脱
水処理により石膏ケーキと母液に固液分離される。この
石膏ケーキには母液が約10重量%程度付着している。
ここで前記除塵塔からの、有害微量成分を比較的多量に
含有するブリード液を用いてこの石膏ケーキの洗浄を行
えば、石膏ケーキの約10重量%程度を占める付着水が
排水とほぼ置換されることを見出した。この置換によ
り、除塵塔からのブリード液に含まれる塩類等は石膏と
共に系外に排出される。
On the other hand, the gypsum produced in the absorption tower is sent from the absorption tower as a gypsum slurry to a solid-liquid separation step, where it is separated into a gypsum cake and a mother liquor by dehydration treatment. About 10% by weight of mother liquor adheres to this gypsum cake.
If the gypsum cake is washed with a bleed solution containing a relatively large amount of harmful trace components from the dust removal tower, the adhered water, which accounts for about 10% by weight of the gypsum cake, is almost replaced with the waste water. I found that. By this replacement, salts and the like contained in the bleeding liquid from the dust removing tower are discharged out of the system together with gypsum.

【0012】これは通常補給水の1割〜3割程度を系外
に排水し、その分工業用水等を補給したのと同じ効果を
生ずることになる。石膏ケーキ洗浄後の濾液は除塵塔に
戻して繰り返し循環使用できる。それにより脱硫装置系
外に排水することなく安定して継続的に運転できる。本
発明はこのような知見に基づき完成されたものである。
This usually produces the same effect as that of supplying 10% to 30% of makeup water to the outside of the system and replenishing industrial water etc. accordingly. The filtrate after washing the gypsum cake can be returned to the dust removing tower and repeatedly used repeatedly. This allows stable and continuous operation without draining to the outside of the desulfurization system. The present invention has been completed based on these findings.

【0013】[0013]

【課題を解決するための手段】すなわち本発明は、硫黄
酸化物および煤塵を含有する燃焼排ガスを、水性の液分
と接触させて除塵する工程、次にカルシウム系化合物含
有吸収液と気液接触させることにより前記燃焼排ガスか
ら硫黄酸化物を吸収除去および酸化する工程、および生
成した石膏を主とする固形物を分離する固液分離工程を
包含する湿式排煙脱硫処理において、前記除塵に使用さ
れた液を前記固液分離工程で分離された石膏の洗浄水と
して使用したのち除塵工程に循環再使用することによ
る、湿式排煙脱硫装置の無排水化方法を要旨とするもの
である。
Means for Solving the Problems That is, the present invention is directed to a step of removing flue gas containing sulfur oxides and dust with an aqueous liquid component to remove dust, and then a liquid absorption containing a calcium compound and gas-liquid contact. In the wet flue gas desulfurization treatment including a step of absorbing and removing sulfur oxides from the combustion exhaust gas and oxidizing it, and a solid-liquid separation step of separating the produced solid mainly composed of gypsum, it is used for the dust removal. The purpose of the present invention is to provide a method for eliminating the drainage of a wet flue gas desulfurization apparatus by using the obtained liquid as washing water for the gypsum separated in the solid-liquid separation process and then reusing it in the dust removal process.

【0014】本発明によれば、除塵塔からのブリード液
を循環再使用できるため、従来の除塵塔からの排水を処
理するための排水処理設備が不要となる。薬剤費も不要
となる。あらたな大型の機器を設置せずとも現在の排煙
脱硫装置に簡単な追加設備を設けるだけで事足りる。従
って設備費、スペース面、運用面、薬剤費さらには環境
面でもすぐれた方法と言える。
According to the present invention, the bleed liquid from the dust removing tower can be circulated and reused, so that the conventional waste water treatment facility for treating the waste water from the dust removing tower is not required. No drug costs are required. It is sufficient to install simple additional equipment to the existing flue gas desulfurization equipment without installing new large equipment. Therefore, it can be said that it is an excellent method in terms of equipment cost, space aspect, operation aspect, drug expense and environmental aspect.

【0015】以下図面に基づき本発明を詳細に説明す
る。本発明の除塵水循環使用による無排水化方法の排煙
脱硫工程のフローシートを示せば図1のとおりである。
重油ボイラー、石炭ボイラー、焼結プラント、金属精錬
プラントなどからの燃焼排ガスGは、脱硝、電気集塵等
の予備処理を経た後、冷却および除塵のための除塵塔1
に導かれ、ここでポンプ2により循環されている液と気
液接触して除塵と同時に冷却および増湿される。除塵塔
は通常スプレー式が用いられる。
The present invention will be described in detail below with reference to the drawings. The flow sheet of the flue gas desulfurization process of the drainage-free method by circulating the dust removal water of the present invention is shown in FIG.
Combustion exhaust gas G from a heavy oil boiler, a coal boiler, a sintering plant, a metal refining plant, etc. is subjected to a pretreatment such as denitration and electrostatic dust collection, and then a dust removal tower 1 for cooling and dust removal 1
And is brought into contact with the liquid circulated by the pump 2 here, and is cooled and humidified at the same time as dust is removed. The dust removing tower is usually a spray type.

【0016】こうして除塵および冷却増湿された排ガス
は管路3を通って吸収塔4に送られる。吸収塔4で、カ
ルシウム系化合物のスラリーを含有する吸収液と気液接
触し、硫黄酸化物が吸収除去される。吸収塔での気液接
触方法はガスを吸収液中に吹き込むガスバブリング方
式、吸収液を吸収塔内でスプレーするスプレー方式等、
任意の方法を採用できる。吸収塔内で吸収された硫黄酸
化物は、吸収塔に投入される酸化空気にて酸化された
後、吸収塔内に投入されたカルシウム系化合物により中
和され、石膏として固定化される。酸化は、吸収塔とは
別個に酸化塔を設け、そこで行ってもよい。
The exhaust gas thus dedusted and cooled and humidified is sent to the absorption tower 4 through the pipe line 3. In the absorption tower 4, the sulfur oxide is absorbed and removed by making gas-liquid contact with the absorption liquid containing the calcium compound slurry. The gas-liquid contact method in the absorption tower is a gas bubbling method in which a gas is blown into the absorption liquid, a spray method in which the absorption liquid is sprayed in the absorption tower, and the like.
Any method can be adopted. The sulfur oxide absorbed in the absorption tower is oxidized by the oxidizing air introduced into the absorption tower, and then neutralized by the calcium-based compound introduced into the absorption tower to be fixed as gypsum. The oxidation may be performed there by providing an oxidation tower separately from the absorption tower.

【0017】本発明で使用できるカルシウム系化合物と
しては、炭酸カルシウム、水酸化カルシウム、酸化カル
シウム等をあげることができるが、安価にかつ大量に入
手できる点で炭酸カルシウムの使用が好ましい。前記石
膏含有スラリーはポンプ5により管路6を通って洗浄機
能を有する固液分離装置7に供給し、そこで脱水により
固液分離して石膏ケーキと母液に分離する。固液分離装
置7は必ず洗浄機能を有するものを使用する必要があ
る。
Examples of the calcium compound usable in the present invention include calcium carbonate, calcium hydroxide, calcium oxide and the like, but calcium carbonate is preferably used because it is inexpensive and available in large quantities. The gypsum-containing slurry is supplied from a pump 5 through a pipe 6 to a solid-liquid separator 7 having a cleaning function, where it is solid-liquid separated by dehydration and separated into a gypsum cake and a mother liquor. As the solid-liquid separation device 7, it is necessary to use one having a cleaning function.

【0018】母液は管路9を通って母液槽10に運ば
れ、そこからポンプ11により管路12を通って一部分
は除塵塔1の補給水として再使用され、一部分は吸収塔
2に還流され、他の一部分はカルシウム系化合物のスラ
リー化(図示せず)に使用される。本発明においては、
固液分離装置7で分離後に装置に残留する石膏ケーキ
を、除塵塔1から管路17により導入された液を用いて
洗浄することにより、石膏ケーキの約10重量%を占め
る付着水があらかた洗浄水と置換される。それにより排
ガス中の有害微量成分を含有する排水が石膏8に付着し
て一緒に系外に排出される。石膏ケーキ洗浄後の濾液は
管路13を通って洗浄濾液槽14に送られ、ポンプ15
により管路16を通って除塵塔1に戻して循環再使用さ
れる。
The mother liquor is conveyed to the mother liquor tank 10 through the pipe 9, from which it is reused by the pump 11 through the pipe 12 as a make-up water for the dust removing tower 1 and a part is returned to the absorption tower 2. The other part is used for slurrying the calcium compound (not shown). In the present invention,
By washing the gypsum cake remaining in the apparatus after separation by the solid-liquid separation apparatus 7 with the liquid introduced from the dust removal tower 1 through the pipe line 17, the adhered water occupying about 10% by weight of the gypsum cake is thoroughly washed. Replaced by water. As a result, wastewater containing harmful trace components in the exhaust gas adheres to the gypsum 8 and is discharged together with the gypsum 8. The filtrate after washing the gypsum cake is sent to the washing filtrate tank 14 through the pipe 13, and the pump 15
Thus, it is returned to the dust removing tower 1 through the pipe line 16 and circulated and reused.

【0019】一方、硫黄酸化物が除去された排ガスは管
路18により系外に排出される。除塵塔1では、気液接
触後に水分が蒸発して排ガスに随伴して出てゆくため除
塵塔を循環される液が次第に濃縮されはするが、脱硫処
理装置の運転開始例えば約500時間後に、除塵塔を循
環する液中の不純物濃度がほぼ一定となり、それ以上上
昇することがない。これは、除塵塔内で除去される排ガ
ス中の不純物量と石膏に付着して系外に排出される不純
物量との間にバランスが成立するためである。このよう
にして、脱硫装置を安定して無排水状態で継続運転で
き、系外に排水することはない。
On the other hand, the exhaust gas from which the sulfur oxides have been removed is discharged out of the system through the pipe 18. In the dedusting tower 1, since the water evaporates after the gas-liquid contact and goes out together with the exhaust gas, the liquid circulated in the dedusting tower is gradually concentrated, but after the operation of the desulfurization treatment apparatus starts, for example, about 500 hours, The concentration of impurities in the liquid circulating in the dust removal tower becomes almost constant and does not rise any further. This is because a balance is established between the amount of impurities in the exhaust gas removed in the dust removal tower and the amount of impurities attached to gypsum and discharged outside the system. In this way, the desulfurizer can be stably operated continuously without draining water, and is not drained to the outside of the system.

【0020】[0020]

【実施例】【Example】

実施例1 スプレー式除塵塔を使用し、ガスバブリング方式(空気
導入)によるスート分離式脱硫装置(千代田サラブレッ
ドCT−121型)により、下記排ガス組成および反応
条件で湿式排煙脱硫処理を行った。石膏ケーキは、除塵
塔からの排水を用いて洗浄し、濾液を除塵塔に戻して循
環再使用した。 排ガス組成: 石炭燃焼排ガス:400 NL/h 入口ガス温度 :150 ℃ 入口SO 2濃度 :1000ppm-D 煤塵 :115 mg/m3 N うちCl濃度 :14ppm HF濃度 :35ppm pH :4 カルシウム系化合物:200 メッシュ90%パス、純度95%
の炭酸カルシウム 排水 :なし 除塵塔液ガス比 :2 L/m3 除塵塔液滞留時間:5分(循環液流量に対して) 運転開始約500時間後に、除塵塔を循環する液中の不
純物濃度は、Cl濃度として2.6 重量%、F 濃度として3.
5 重量%でほぼ一定となり、以後はそれ以上上昇しなか
った。系外に排水することなく約96%の脱硫率で継続操
業できた。
Example 1 A spray type dust removing tower was used to perform wet flue gas desulfurization treatment under the following exhaust gas composition and reaction conditions by a soot separation type desulfurization device (Chiyoda Thoroughbred CT-121 type) by a gas bubbling method (air introduction). The gypsum cake was washed with the waste water from the dust removing tower, and the filtrate was returned to the dust removing tower and reused by circulation. Exhaust gas composition: Coal combustion exhaust gas: 400 NL / h Inlet gas temperature: 150 ℃ Inlet SO 2 concentration: 1000 ppm-D Soot dust: 115 mg / m 3 N Of which Cl concentration: 14 ppm HF concentration: 35 ppm pH: 4 Calcium-based compound: 200 90% mesh pass, 95% purity
Calcium carbonate Drainage: None Dust removal tower liquid gas ratio: 2 L / m 3 Dust removal tower liquid retention time: 5 minutes (relative to the circulating liquid flow rate) About 500 hours after the start of operation, the concentration of impurities in the liquid circulating in the dust removal tower Is a Cl concentration of 2.6% by weight and an F concentration of 3.
It became almost constant at 5% by weight, and did not increase further thereafter. It was possible to operate continuously with a desulfurization rate of about 96% without draining outside the system.

【0021】[0021]

【発明の効果】本発明では、除塵塔からのブリード液の
運用方法を工夫することにより、従来の無排水化方法で
必要とした、排水の濃縮、そのための機器、その他薬剤
費、電気透析装置設備費、運用費等の経費を要すること
なく無排水化できる。本発明によれば無排水化のための
あらたな大型の機器を設置する必要がなく、現在の排煙
脱硫装置に簡単な追加設備を設けるだけですみ、設備
費、スペース面、運用面、環境面できわめて有利な方法
である。
According to the present invention, by devising the operation method of the bleed liquid from the dust removal tower, the concentration of waste water required for the conventional non-drainage method, equipment therefor, other drug cost, electrodialysis device No drainage is required without incurring equipment costs, operating costs, etc. According to the present invention, it is not necessary to install a new large-scale device for drainage-free, and it is only necessary to provide a simple additional equipment to the present flue gas desulfurization equipment, and the equipment cost, space aspect, operation aspect, and environment. This is a very advantageous method.

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

【図1】本発明の無排水化方式の排煙脱硫工程のフロー
シートを示す。
FIG. 1 shows a flow sheet of a flue gas desulfurization process of the drainage-free system of the present invention.

【符号の説明】[Explanation of symbols]

1 除塵塔 4 吸収塔 7 固液分離器
8 石膏
1 Dust removal tower 4 Absorption tower 7 Solid-liquid separator
8 plaster

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/14 ZAB C 53/34 ZAB B01D 53/34 125 Q ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location B01D 53/14 ZAB C 53/34 ZAB B01D 53/34 125 Q

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 硫黄酸化物および煤塵を含有する燃焼排
ガスを、水性の液分と接触させて除塵する工程、次にカ
ルシウム系化合物含有吸収液と気液接触させることによ
り前記燃焼排ガスから硫黄酸化物を吸収除去および酸化
する工程、および生成した石膏を主とする固形物を分離
する固液分離工程を包含する湿式排煙脱硫処理におい
て、前記除塵に使用された液を前記固液分離工程で分離
された石膏の洗浄水として使用したのち除塵工程に循環
再使用することを特徴とする、湿式排煙脱硫装置の無排
水化方法。
1. A step of contacting a combustion exhaust gas containing sulfur oxides and dust with an aqueous liquid component to remove dust, and then gas-liquid contacting with a calcium compound-containing absorbing liquid to thereby perform sulfur oxidation from the combustion exhaust gas. In a wet flue gas desulfurization process including a step of absorbing and removing a substance and oxidizing, and a solid-liquid separation step of separating a generated gypsum-based solid matter, a liquid used for the dust removal in the solid-liquid separation step. A method for eliminating the drainage of a wet flue gas desulfurization device, which comprises using the separated gypsum as washing water and then recycling it in a dust removal process.
JP6053558A 1994-03-24 1994-03-24 Non-drainage method of wet exhaust gas desulfurizer Pending JPH07256050A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6053558A JPH07256050A (en) 1994-03-24 1994-03-24 Non-drainage method of wet exhaust gas desulfurizer

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6053558A JPH07256050A (en) 1994-03-24 1994-03-24 Non-drainage method of wet exhaust gas desulfurizer

Publications (1)

Publication Number Publication Date
JPH07256050A true JPH07256050A (en) 1995-10-09

Family

ID=12946147

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6053558A Pending JPH07256050A (en) 1994-03-24 1994-03-24 Non-drainage method of wet exhaust gas desulfurizer

Country Status (1)

Country Link
JP (1) JPH07256050A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2014516308A (en) * 2011-04-08 2014-07-10 エネル プロドゥツィオーネ ソシエタ ペル アチオニ Method for monitoring and controlling the chemical reaction of a ZLD process in a power plant

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2014516308A (en) * 2011-04-08 2014-07-10 エネル プロドゥツィオーネ ソシエタ ペル アチオニ Method for monitoring and controlling the chemical reaction of a ZLD process in a power plant

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