JP3021094B2 - Concentration treatment equipment for wastewater discharged from desulfurization equipment - Google Patents

Concentration treatment equipment for wastewater discharged from desulfurization equipment

Info

Publication number
JP3021094B2
JP3021094B2 JP3156460A JP15646091A JP3021094B2 JP 3021094 B2 JP3021094 B2 JP 3021094B2 JP 3156460 A JP3156460 A JP 3156460A JP 15646091 A JP15646091 A JP 15646091A JP 3021094 B2 JP3021094 B2 JP 3021094B2
Authority
JP
Japan
Prior art keywords
wastewater
gas
desulfurization
water
discharged
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP3156460A
Other languages
Japanese (ja)
Other versions
JPH054024A (en
Inventor
英明 堀部
達典 三輪田
弘 吉田
守 鳥屋尾
浩養 筒井
進一郎 小竹
直彦 鵜川
沖野  進
積 中村
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.)
Chubu Electric Power Co Inc
Mitsubishi Heavy Industries Ltd
Original Assignee
Chubu Electric Power Co Inc
Mitsubishi Heavy Industries 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
Family has litigation
First worldwide family litigation filed litigation Critical https://patents.darts-ip.com/?family=15628236&utm_source=google_patent&utm_medium=platform_link&utm_campaign=public_patent_search&patent=JP3021094(B2) "Global patent litigation dataset” by Darts-ip is licensed under a Creative Commons Attribution 4.0 International License.
Application filed by Chubu Electric Power Co Inc, Mitsubishi Heavy Industries Ltd filed Critical Chubu Electric Power Co Inc
Priority to JP3156460A priority Critical patent/JP3021094B2/en
Publication of JPH054024A publication Critical patent/JPH054024A/en
Application granted granted Critical
Publication of JP3021094B2 publication Critical patent/JP3021094B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Treating Waste Gases (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Description

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

【0001】[0001]

【産業上の利用分野】本発明は燃焼排ガス中の二酸化硫
黄ガス(以下、SOxガスと記す)を環境汚染防止の
観点より、石灰石等のアルカリ剤を吸収剤として吸収・
分離する脱硫装置より放出される排水を濃縮し、濃縮排
水を取得する濃縮処理装置に関する。
The present invention relates to a sulfur dioxide gas in the combustion exhaust gas (hereinafter, referred to as SOx gas) absorption and a from the viewpoint of prevention of environmental pollution, an alkali agent such as limestone as an absorbent
Concentrate wastewater discharged from the desulfurizer to separate and concentrate
The present invention relates to a concentration treatment device for obtaining water .

【0002】[0002]

【従来の技術】脱硫装置より放出される排水は該脱硫装
置内で反応生成する石こう及び反応に寄与しなかった石
灰石等の固形成分、排ガス中の塩化水素ガスと吸収剤中
のカルシウム,マグネシウムなどとの反応により生成し
た塩化カルシウム,塩化マグネシウムなどの塩成分、排
ガス中のシリカ,アルミニウムなどの金属の酸化物、ま
た、脱硫装置内で捕獲した燃焼排ガス中の燃焼灰等々種
々雑多な成分を含有しているばかりか、排ガス中のSO
xガス,塩化水素ガスにより排水の液性も酸性となって
おり、同性状のまま公共水域等への放流はできず、通常
以下に述べる如く処理を行っている。
2. Description of the Related Art Waste water discharged from a desulfurization unit includes gypsum produced in the desulfurization unit and solid components such as limestone that did not contribute to the reaction, hydrogen chloride gas in exhaust gas and calcium and magnesium in an absorbent. Contains various components such as calcium chloride, magnesium chloride and other salt components produced by the reaction with the gas, oxides of metals such as silica and aluminum in the exhaust gas, and combustion ash in the combustion exhaust gas captured in the desulfurization unit. Not only SO2 in exhaust gas
The liquid property of the wastewater is also acidic due to x gas and hydrogen chloride gas, and cannot be discharged to public waters or the like with the same properties, and the treatment is usually performed as described below.

【0003】図3に従来の排水処理設備の流れ図の一態
様を示し、同図に基づき従来の排水処理方法を説明す
る。この従来の排水処理設備にて処理する脱硫装置から
の排水、すなわち被処理液はラインaaにより原液タン
ク01に一旦貯蔵される。こののち被処理液はラインb
bにより酸分解槽02に供給され、こゝで同液中に含有
される酸成分を分解したのち、ラインccを介して固形
成分の分離を行う固形分分離槽03に送られる。被処理
液はラインccを流通する間、固形分分離槽03での分
離効率を上昇することを目的として被処理液の水素イオ
ン濃度の調節用アルカリ及び凝集剤等をラインddを介
して注入される。固形分分離槽03では被処理液中の石
灰石,石こう,燃焼灰等の固形分を分離し、固形分が希
薄となった液(以下、清浄液と称す)と固形分が濃厚と
なった液(以下、濃厚懸濁液と称す)を排出する。
FIG. 3 shows one embodiment of a flow chart of a conventional wastewater treatment facility, and a conventional wastewater treatment method will be described with reference to FIG. The wastewater from the desulfurization unit that is treated by the conventional wastewater treatment equipment, that is, the liquid to be treated, is temporarily stored in the stock solution tank 01 by the line aa. Thereafter, the liquid to be treated is placed on line b.
The solution is supplied to the acid decomposing tank 02 by b, and after decomposing the acid component contained in the same solution, is sent to the solid separation tank 03 for separating the solid component via the line cc. While the liquid to be treated flows through the line cc, an alkali and a coagulant for adjusting the hydrogen ion concentration of the liquid to be treated are injected through the line dd for the purpose of increasing the separation efficiency in the solid separation tank 03. You. In the solid separation tank 03, solids such as limestone, gypsum, and combustion ash in the liquid to be treated are separated, and a liquid having a low solids content (hereinafter referred to as a cleaning liquid) and a liquid having a high solids content (Hereinafter referred to as a concentrated suspension).

【0004】濃厚懸濁液はラインeeを介して脱水器0
4に送られ、該脱水器04にて更に水分と固形分に分離
される。脱水器04にて分離された水分及び固形分は各
々ラインff,ggにより該排水処理設備の系外へ排出
される。
The concentrated suspension is supplied to a dehydrator 0 via a line ee.
4 and further separated into water and solids by the dehydrator 04. The water and solids separated by the dehydrator 04 are discharged to the outside of the wastewater treatment facility by lines ff and gg, respectively.

【0005】一方固形分分離槽03からの清浄液はライ
ンhhを介して砂ろ過器等の精密ろ過器05に送られ、
固形分分離槽03にて分離できなかった固形分を更に被
処理液中より分離し、清浄度を向上したのちラインii
を介して処理液タンク06に貯蔵される。処理液タンク
06内の処理後の排水は(排水基準に適合することが確
認されたのち)ラインjjを介して公共水域へ放流され
る。
On the other hand, the cleaning liquid from the solid content separation tank 03 is sent to a fine filter 05 such as a sand filter via a line hh.
The solids that could not be separated in the solids separation tank 03 were further separated from the liquid to be treated to improve cleanliness, and then the line ii.
Is stored in the processing liquid tank 06 via the. The treated wastewater in the treatment liquid tank 06 is discharged to the public water area via the line jj (after it is confirmed that the wastewater meets the wastewater standards).

【0006】[0006]

【発明が解決しようとする課題】従来の排水処理設備で
は前記説明の如く煩雑な装置構成となり、また各装置の
運転制御法も複雑であり、同運転制御法は排水処理設備
から排出される排水の性状に著しい影響を与え、場合に
よっては前記処理液タンク06内の排水の放流が不可能
となり、最悪の場合は排水処理設備全系を停止すること
となる。更に上記の如く装置構成が煩雑であること、運
転制御法が複雑であることなどより、装置費並びに運転
維持費が高価となるばかりか、排水処理設備の設置に要
する敷地面積が広大となる。
As described above, the conventional wastewater treatment equipment has a complicated apparatus configuration, and the operation control method of each apparatus is also complicated. The operation control method is based on the wastewater discharged from the wastewater treatment equipment. In some cases, it is impossible to discharge the wastewater in the treatment liquid tank 06, and in the worst case, the entire system of the wastewater treatment equipment is stopped. Further, as described above, since the apparatus configuration is complicated and the operation control method is complicated, not only the equipment cost and the operation and maintenance cost become expensive, but also the site area required for installing the wastewater treatment equipment becomes large.

【0007】本発明は上記技術水準に鑑み、上述した従
来技術の不具合を解消しうる排水の処理装置を提供しよ
うとするものである。
The present invention has been made in view of the above-mentioned state of the art, and has as its object to provide a wastewater treatment apparatus capable of solving the above-mentioned disadvantages of the prior art.

【0008】[0008]

【課題を解決するための手段】本発明は次の(1)及び
(2)の構成を有するものである。 (1)燃焼排ガス中の二酸化硫黄ガスをアルカリ剤によ
り吸収分離する脱硫装置より放出される排水の濃縮処理
装置であって、前記脱硫装置より放出される排水を貯蔵
する原水タンクと、該原水タンクからの排水と前記脱硫
装置に通ずる前の前記燃焼排ガスの一部を導入して接触
させ、前記排水を濃縮して濃縮排水を取得する気液接触
装置とを備え、該気液接触装置は底部に溜めた排水を上
部の空間部に循環させ、該空間部において前記燃焼排ガ
スと直接接触させて水分を蒸発させて濃縮し、循環液の
一部を濃縮排水として排出するように構成されてなるこ
とを特徴とする脱硫装置より放出される排水の濃縮処理
装置。
Means for Solving the Problems The present invention provides the following (1) and
It has the configuration of (2). (1) Concentration treatment of wastewater discharged from a desulfurization unit that absorbs and separates sulfur dioxide gas in combustion exhaust gas with an alkaline agent
An apparatus for storing wastewater discharged from the desulfurization apparatus
Raw water tank, waste water from the raw water tank and the desulfurization
Part of the flue gas before passing through the device is introduced and contacted
Gas-liquid contact to concentrate the wastewater and obtain concentrated wastewater
A gas-liquid contacting device, which drains water collected at the bottom.
Circulating in the space of the section, where the combustion exhaust gas is circulated.
Water and evaporate water to concentrate and concentrate the circulating fluid.
Concentration treatment of wastewater discharged from a desulfurization unit, characterized in that part of the wastewater is discharged as concentrated wastewater
apparatus.

【0009】(2)燃焼排ガス中の二酸化硫黄ガスをア
ルカリ剤により吸収分離する脱硫装置より放出される排
水の濃縮処理装置であって、前記脱硫装置より放出され
る排水を貯蔵する原水タンクと、該原水タンクからの排
水を供給して減圧下に水分を蒸発させる蒸発缶、該蒸発
缶内の排水を循環通過させて加熱媒体により温度を上昇
させる排水加熱器、前記蒸発缶から蒸発する水蒸気を凝
縮分離する冷却器、該冷却器の後流に設けられた真空排
気装置とを備え、前記排水を減圧下に維持された前記蒸
発缶内で水分を蒸発させて濃縮し、濃縮排水として排出
するように構成されてなることを特徴とする脱硫装置よ
り放出される排水の濃縮処理装置。
(2) Exhaust gas released from a desulfurization device that absorbs and separates sulfur dioxide gas in combustion exhaust gas with an alkali agent
A water concentration treatment device, which is discharged from the desulfurization device.
A raw water tank for storing wastewater discharged from the
An evaporator for supplying water and evaporating water under reduced pressure;
The wastewater in the can is circulated and the temperature is raised by the heating medium
A drain heater, a condenser for condensing and separating water vapor evaporating from the evaporator, and a vacuum exhaust device provided downstream of the cooler , wherein the drain is maintained under reduced pressure.
Concentrate by evaporating water in the can and discharge as concentrated wastewater
A concentration treatment device for wastewater discharged from a desulfurization device, characterized in that the treatment device is configured to perform the treatment .

【0010】すなわち、本発明は燃焼排ガス中のSOx
ガスを環境汚染防止の観点より石灰石等のアルカリ剤を
吸収剤として排ガスよりSOxガスを吸収分離する脱硫
装置より放出される排水の処理装置であって、前記脱硫
装置より放出される排水を燃焼排ガス、若しくは蒸気そ
の他の加熱媒体を用いて蒸発・濃縮し、該排水を固形分
及び溶解分を多量に含有する濃縮排水と蒸発凝縮水(以
下単に回収水と称す)または前記濃縮排水を更に濃縮し
て得た固形分と回収水とに分別回収するようにした排水
処理装置である。
That is, the present invention relates to SOx in combustion exhaust gas.
A treatment device for waste water discharged from a desulfurization device that absorbs and separates SOx gas from exhaust gas using an alkaline agent such as limestone as an absorbent from the viewpoint of preventing environmental pollution of the gas , wherein the waste water released from the desulfurization device is a combustion exhaust gas. Or concentrated using steam or other heating medium, and the waste water is further concentrated by condensing waste water containing a large amount of solids and dissolved matter and evaporating condensed water (hereinafter simply referred to as recovered water) or the concentrated waste water. This is a wastewater treatment device that separates and collects the solids obtained and the collected water.

【0011】本発明において脱硫装置から放出される排
水の蒸発・濃縮に燃焼排ガスを用いる場合は、燃焼排ガ
スとしては脱硫装置にて処理する前の燃焼排ガスの一部
を用い、脱硫装置より放出される排水と気液接触装置内
で直接接触させ、排ガスの顕熱により排水中の水分を蒸
発させることにより排水を濃縮するものである。
In the present invention, when flue gas is used for evaporating and condensing wastewater discharged from the desulfurization unit, a part of the flue gas before being treated by the desulfurization unit is used as the flue gas and is discharged from the desulfurization unit. that drainage and in direct contact with the gas-liquid contact device, is to concentrate the waste water by evaporating the moisture in the waste water by the sensible heat of the flue gas.

【0012】一方蒸気その他の加熱媒体を用いる場合
は、他の蒸気発生装置等にて発生した加熱媒体を用い、
装置内を減圧とした蒸発缶に本発明の濃縮対象である排
水を投入し、前記加熱媒体にて排水を上昇することによ
り排水中水分を蒸発させ、排水を濃縮するものである。
On the other hand, when steam or other heating medium is used, a heating medium generated by another steam generator or the like is used.
The wastewater to be concentrated according to the present invention is charged into an evaporator in which the pressure in the apparatus is reduced, and the wastewater is evaporated by raising the wastewater with the heating medium to concentrate the wastewater.

【0013】[0013]

【作用】本発明は燃焼排ガス若しくは蒸気その他の加熱
媒体で排水を蒸発・濃縮し、濃縮排水または固形分及び
回収水に分別する排水処理装置であり、従来の排水処理
設備にて処理の対象となっていた固形成分,塩成分,金
属の酸化物及び燃焼排ガス中の燃焼灰等を全て濃縮排水
または固形分中に減容化して濃縮するものである。
The present invention is a wastewater treatment apparatus for evaporating and condensing wastewater with combustion exhaust gas or steam or other heating medium and separating the wastewater into concentrated wastewater or solids and recovered water. The solid components, salt components, metal oxides, combustion ash and the like in the combustion exhaust gas, which have been formed, are all reduced in concentrated wastewater or solid content and concentrated.

【0014】[0014]

【実施例】以下、本発明の実施態様を図1及び図2によ
って詳細に説明する。図1は排水を濃縮するための熱源
として燃焼排ガスを用いる場合、図2は前記熱源として
蒸気を用いる場合の一実施態様を示す説明図である。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below in detail with reference to FIGS. FIG. 1 is an explanatory diagram showing an embodiment in which combustion exhaust gas is used as a heat source for condensing wastewater, and FIG. 2 is an embodiment showing a case in which steam is used as the heat source.

【0015】図1において、1は脱硫装置(図示なし)
から放出される排水を一旦貯蔵するための原水タンク、
2は排水と燃焼排ガスを直接接触させる気液接触装置、
3は前記気液接触装置内の排水を同装置内で燃焼排ガス
と接触させるために循環する循環ポンプである。
In FIG. 1, reference numeral 1 denotes a desulfurizer (not shown).
Raw water tank for temporarily storing wastewater released from
2 is a gas-liquid contact device for bringing waste water and flue gas into direct contact,
Reference numeral 3 denotes a circulation pump that circulates the waste water in the gas-liquid contact device to make it contact the combustion exhaust gas in the gas-liquid contact device.

【0016】脱硫装置からの排水はラインaにより一旦
原水タンク1に貯蔵されたのち、ラインbを介して気液
接触装置2に供給される。気液接触装置2ではラインb
より供給された排水をラインc及び循環ポンプ3により
ラインeより供給される燃焼排ガスに直接接触するため
循環する。この接触の際、燃焼排ガスの有する熱により
排水中の水分が蒸発する。燃焼排ガスは排水中の水分が
蒸発するに要する熱分相当温度が低下するとともに、同
燃焼排ガス中の水分の含有率が増加して、気液接触装置
2によりラインfを介して系外へ排出される。気液接触
装置2より排出される燃焼排ガスは再度脱硫装置にて処
理する前の燃焼排ガスと合流させ、合わせて脱硫装置に
て処理するなどの処理方法が採用される。
The waste water from the desulfurization unit is once stored in a raw water tank 1 by a line a, and then supplied to a gas-liquid contact unit 2 through a line b. Line b in the gas-liquid contact device 2
The wastewater supplied from the line c and the circulation pump 3 are circulated by the circulation pump 3 so as to directly contact the combustion exhaust gas supplied from the line e. At the time of this contact, the water in the waste water evaporates due to the heat of the combustion exhaust gas. The temperature of the flue gas corresponding to the heat component required for evaporating the water in the waste water decreases, and the content of the water in the flue gas increases, and the flue gas is discharged out of the system via the line f by the gas-liquid contact device 2. Is done. A processing method is adopted in which the combustion exhaust gas discharged from the gas-liquid contact device 2 is combined with the combustion exhaust gas before being processed again by the desulfurization device, and then combined and processed by the desulfurization device.

【0017】一方、排水は気液接触装置2内で燃焼排ガ
スと接触するため排水中の水分が蒸発し、排水中に含有
される固形成分,塩成分,金属の酸化物及び燃焼灰等の
非蒸発成分が濃縮され、また、排水容量も減容化され、
こののちラインdを介して気液接触装置2より排出され
る。
On the other hand, the waste water contacts the combustion exhaust gas in the gas-liquid contact device 2, so that the water in the waste water evaporates, and the solid components, salt components, metal oxides and non-burning ash contained in the waste water. Evaporation components are concentrated, and drainage capacity is reduced,
Thereafter, the gas is discharged from the gas-liquid contact device 2 via the line d.

【0018】続いて蒸気その他の加熱媒体を用いる場合
の一実施態様について図2により説明する。図2におい
て1′は脱硫装置(図示なし)から放出される排水を一
旦貯蔵するための原水タンク、2′は排水中の水分を蒸
発するための蒸発缶、3′は蒸発缶2′内の排水の温度
を上昇するための排水加熱器、4′は蒸発缶2′で蒸発
した水分を凝縮・回収するための冷却器、5′は蒸発缶
2′内での排水中水分の蒸発を促進するために蒸発缶
2′内を減圧にするとともに蒸発缶2′内で発生した蒸
気をすみやかに冷却器4′に移動するための真空排気装
置である。
Next, an embodiment in which steam or other heating medium is used will be described with reference to FIG. In FIG. 2, reference numeral 1 'denotes a raw water tank for temporarily storing waste water discharged from a desulfurizer (not shown), 2' an evaporator for evaporating water in the waste water, and 3 'an evaporator in the evaporator 2'. Drain heater for raising the temperature of the waste water, 4 'is a cooler for condensing and recovering the water evaporated in the evaporator 2', 5 'promotes evaporation of the water in the waste water in the evaporator 2' This is a vacuum evacuation device for reducing the pressure inside the evaporator 2 ′ and quickly moving the steam generated in the evaporator 2 ′ to the cooler 4 ′.

【0019】図2において脱硫装置からの排水はライン
a′により一旦原水タンク1′に貯蔵されたのち、ライ
ンb′を介して蒸発缶2′に供給される。蒸発缶2′内
の排水はラインc′を介して排水加熱器3′に供給され
る。排水加熱器3′には蒸気その他の加熱媒体がライン
e′により供給され、蒸発缶2′より供給される排水を
昇温した後ラインf′により系外へ排出される。排水加
熱器3′にて昇温された排水はラインd′を介して再び
蒸発缶2′に戻る。蒸発缶2′内は真空排気装置5′に
よりその圧力が負圧に維持され、かつ前述の如く排水加
熱器3′にて排水温度が上昇しているため、蒸発缶2′
内の排水中水分は蒸発することとなり、同蒸発により生
じる蒸気はラインg′を介して蒸発缶2′より抜き出さ
れ、冷却器4′に送られる。冷却器4′内に送られた蒸
気はラインh′により冷却器4′に供給される冷却媒体
と熱交換を行い、凝縮して水分(液体)となりライン
j′により冷却器4′より抜き出され、系外へ排出され
る。ラインh′より冷却器4′に供給された冷却媒体は
ラインi′より抜き出される。冷却器4′にて気体中の
蒸気分を水分(液体)として回収したのちの非凝縮性気
体はラインk′を介して真空排気装置5′に送られたの
ち、更にラインl′を介して系外へ排出される。
In FIG. 2, the waste water from the desulfurization unit is once stored in a raw water tank 1 'by a line a' and then supplied to an evaporator 2 'through a line b'. The wastewater in the evaporator 2 'is supplied to a wastewater heater 3' via a line c '. Steam and other heating media are supplied to the drain heater 3 'through a line e', and the waste water supplied from the evaporator 2 'is heated and discharged out of the system through a line f'. The wastewater whose temperature has been raised by the wastewater heater 3 'returns to the evaporator 2' again via the line d '. Since the pressure inside the evaporator 2 'is maintained at a negative pressure by the evacuation unit 5' and the temperature of the waste water is raised by the waste water heater 3 'as described above, the evaporator 2'
The water contained in the waste water evaporates, and the vapor generated by the evaporation is extracted from the evaporator 2 ′ through the line g ′ and sent to the cooler 4 ′. The steam sent into the cooler 4 'exchanges heat with the cooling medium supplied to the cooler 4' through a line h ', and condenses into moisture (liquid) to be extracted from the cooler 4' through a line j '. And is discharged out of the system. The cooling medium supplied from line h 'to cooler 4' is extracted from line i '. The non-condensable gas after recovering the vapor content in the gas as water (liquid) in the cooler 4 'is sent to the evacuation unit 5' through the line k ', and further through the line l'. It is discharged out of the system.

【0020】一方、蒸発缶2′にて排水中水分を蒸気と
して分離された後の濃縮排水はラインm′を介して蒸発
缶2′より抜き出され系外へ排出される。
On the other hand, the concentrated wastewater separated from the wastewater as steam in the evaporator 2 'is extracted from the evaporator 2' via a line m 'and discharged to the outside of the system.

【0021】図には、蒸気その他の加熱媒体を用いた場
合の本発明の一実施態様を示したが、蒸発缶2′及び排
水加熱器3′は蒸気その他の加熱媒体の熱効率の上昇を
目的として複数としてもよい。
FIG. 1 shows an embodiment of the present invention in which steam or another heating medium is used. The purpose of the evaporator 2 'and the drain heater 3' is to increase the thermal efficiency of the steam or other heating medium. May be plural.

【0022】[0022]

【発明の効果】本発明は処理対象の排水を濃縮すること
により、公共水域へ放流できない成分を濃縮・減容化で
きるため、従来の排水処理設備の如く煩雑な装置構成、
複雑な運転制御が不必要となるばかりか、本発明では装
置構成が簡素となるため設備費の低減並びに敷地面積の
縮少にもつながる。
According to the present invention, since the components which cannot be discharged to public waters can be concentrated and reduced in volume by concentrating the wastewater to be treated, a complicated apparatus configuration as in the conventional wastewater treatment equipment,
Not only does complicated operation control become unnecessary, but the present invention also simplifies the device configuration, which leads to a reduction in equipment costs and a reduction in the area of the site.

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

【図1】本発明による排水処理装置の一実施態様を示す
説明図
FIG. 1 is an explanatory view showing one embodiment of a wastewater treatment apparatus according to the present invention.

【図2】本発明による排水処理装置の他の実施態様を示
す説明図
FIG. 2 is an explanatory view showing another embodiment of the wastewater treatment device according to the present invention.

【図3】従来の排水処理設備の一態様を示す説明図FIG. 3 is an explanatory view showing one embodiment of a conventional wastewater treatment facility.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 吉田 弘 名古屋市緑区大高町字北関山20番地の1 中部電力株式会社 技術開発本部 電 力技術研究所内 (72)発明者 鳥屋尾 守 名古屋市緑区大高町字北関山20番地の1 中部電力株式会社 技術開発本部 電 力技術研究所内 (72)発明者 筒井 浩養 千代田区丸の内二丁目5番1号 三菱重 工業株式会 社 本社内 (72)発明者 小竹 進一郎 千代田区丸の内二丁目5番1号 三菱重 工業株式会 社 本社内 (72)発明者 鵜川 直彦 広島市西区観音新町四丁目6番22号 三 菱重工業株式会社 広島研究所内 (72)発明者 沖野 進 広島市西区観音新町四丁目6番22号 三 菱重工業株式会社 広島研究所内 (72)発明者 中村 積 広島市西区観音新町四丁目6番22号 三 菱重工業株式会社 広島研究所内 (56)参考文献 特開 平2−152518(JP,A) 特開 平1−94920(JP,A) 特開 平3−8411(JP,A) 特開 昭63−141601(JP,A) 特開 昭63−224701(JP,A) 実開 昭61−204633(JP,U) (58)調査した分野(Int.Cl.7,DB名) B01D 53/50 B01D 53/34 B01D 53/77 C02F 1/04 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Hiroshi Yoshida, 1-20, Kitakanyama, Odaka-cho, Midori-ku, Nagoya-shi Within Chubu Electric Power Co., Inc. Technology Development Headquarters Power Technology Research Institute (72) Inventor Mamoru Toriyao Midori, Nagoya-shi 1 at 20 Kita-Sanzan, Otaka-cho, Chubu Electric Power Research Institute, Chubu Electric Power Co., Inc. (72) Inventor Hiroyo Tsutsui 2-5-1 Marunouchi, Chiyoda-ku Mitsubishi Heavy Industries, Ltd. Inventor Shinichiro Kotake 2-5-1 Marunouchi, Chiyoda-ku Mitsubishi Heavy Industries, Ltd. ) Inventor: Susumu Okino, 6-22, Kannonshinmachi, Nishi-ku, Hiroshima-shi, Hiroshima Research Laboratory, Mitsubishi Heavy Industries, Ltd. (72) Inventor: Shigeru Nakamura West, Hiroshima-shi 4-6-22 Kannon Shinmachi Hiroshi Laboratory, Mitsubishi Heavy Industries, Ltd. (56) References JP-A-2-152518 (JP, A) JP-A-1-94920 (JP, A) JP-A-3-8411 ( JP, A) JP-A-63-141601 (JP, A) JP-A-63-224701 (JP, A) JP-A-61-204633 (JP, U) (58) Fields investigated (Int. Cl. 7 , (DB name) B01D 53/50 B01D 53/34 B01D 53/77 C02F 1/04

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 燃焼排ガス中の二酸化硫黄ガスをアルカ
リ剤により吸収分離する脱硫装置より放出される排水の
濃縮処理装置であって、前記脱硫装置より放出される排
水を貯蔵する原水タンクと、該原水タンクからの排水と
前記脱硫装置に通ずる前の前記燃焼排ガスの一部を導入
して接触させ、前記排水を濃縮して濃縮排水を取得する
気液接触装置とを備え、該気液接触装置は底部に溜めた
排水を上部の空間部に循環させ、該空間部において前記
燃焼排ガスと直接接触させて水分を蒸発させて濃縮し、
循環液の一部を濃縮排水として排出するように構成され
なることを特徴とする脱硫装置より放出される排水の
濃縮処理装置
1. A wastewater discharged from a desulfurization device that absorbs and separates sulfur dioxide gas in combustion exhaust gas with an alkali agent .
A concentration treatment device, wherein the waste gas is discharged from the desulfurization device.
A raw water tank for storing water and drainage from the raw water tank;
Part of the flue gas before passing through the desulfurization unit is introduced
To contact and concentrate the wastewater to obtain concentrated wastewater
A gas-liquid contact device, which is stored at the bottom
The wastewater is circulated to the upper space, and the
Direct contact with combustion exhaust gas to evaporate water and concentrate,
It is configured to discharge part of the circulating fluid as concentrated wastewater.
It is Te effluent concentration treatment device to be released from the desulfurization apparatus according to claim.
【請求項2】 燃焼排ガス中の二酸化硫黄ガスをアルカ
リ剤により吸収分離する脱硫装置より放出される排水の
濃縮処理装置であって、前記脱硫装置より放出される排
水を貯蔵する原水タンクと、該原水タンクからの排水を
供給して減圧下に水分を蒸発させる蒸発缶、該蒸発缶内
の排水を循環通過させて加熱媒体により温度を上昇させ
る排水加熱器、前記蒸発缶から蒸発する水蒸気を凝縮分
離する冷却器、該冷却器の後流に設けられた真空排気装
とを備え、前記排水を減圧下に維持された前記蒸発缶
内で水分を蒸発させて濃縮し、濃縮排水として排出する
ように構成されてなることを特徴とする脱硫装置より放
出される排水の濃縮処理装置
2. The wastewater discharged from a desulfurization unit that absorbs and separates sulfur dioxide gas in flue gas with an alkaline agent .
A concentration treatment device, wherein the waste gas is discharged from the desulfurization device.
A raw water tank for storing water and drainage from the raw water tank
An evaporator for supplying and evaporating water under reduced pressure, inside the evaporator
Circulates through the wastewater and raises the temperature with a heating medium.
A water heater, a condenser for condensing and separating water vapor evaporating from the evaporator, and a vacuum exhaust device provided downstream of the cooler, wherein the evaporator can maintain the wastewater under reduced pressure.
Concentrate by evaporating the water inside and discharge as concentrated wastewater
Wastewater concentration treatment device to be released from the desulfurization apparatus characterized by comprising configured to.
JP3156460A 1991-06-27 1991-06-27 Concentration treatment equipment for wastewater discharged from desulfurization equipment Expired - Fee Related JP3021094B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3156460A JP3021094B2 (en) 1991-06-27 1991-06-27 Concentration treatment equipment for wastewater discharged from desulfurization equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3156460A JP3021094B2 (en) 1991-06-27 1991-06-27 Concentration treatment equipment for wastewater discharged from desulfurization equipment

Publications (2)

Publication Number Publication Date
JPH054024A JPH054024A (en) 1993-01-14
JP3021094B2 true JP3021094B2 (en) 2000-03-15

Family

ID=15628236

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3156460A Expired - Fee Related JP3021094B2 (en) 1991-06-27 1991-06-27 Concentration treatment equipment for wastewater discharged from desulfurization equipment

Country Status (1)

Country Link
JP (1) JP3021094B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102322796B (en) * 2011-07-20 2013-07-03 唐大春 Laser detection device and method for gear parameters
SG11201903136TA (en) * 2017-03-24 2019-05-30 Mitsubishi Shipbuilding Co Ltd Drainage system for marine desulfurization device

Also Published As

Publication number Publication date
JPH054024A (en) 1993-01-14

Similar Documents

Publication Publication Date Title
US8052763B2 (en) Method for removing dissolved solids from aqueous waste streams
US3638708A (en) Methods of multiple stage evaporation from heat sources other than steam
JP4688842B2 (en) Wastewater treatment method
CN109836020B (en) Treatment system and method for zero discharge of old landfill leachate
WO1998054096A1 (en) System for recovering and treating waste water
JP2520317B2 (en) Ultrapure water production apparatus and method
CN111439882A (en) Desulfurization wastewater zero discharge system utilizing flue gas waste heat of power plant
JP3021094B2 (en) Concentration treatment equipment for wastewater discharged from desulfurization equipment
CN208440312U (en) A kind of processing system of desulfurization wastewater
CN113105052B (en) High-salinity wastewater concentration and crystallization system and method
JPH11207146A (en) Method for recovering gypsum from flue gas desulfurization wastewater
JP2740533B2 (en) Wet exhaust gas desulfurization method
JP2955067B2 (en) Operation control method for waste water treatment equipment discharged from desulfurization unit
JP3366258B2 (en) Method and apparatus for evaporating and concentrating sulfuric acid-containing wastewater
JP2805497B2 (en) Treatment of wet flue gas desulfurization wastewater
JPS5815039B2 (en) Waste incineration plant wastewater treatment method
JP3861268B2 (en) Thermal power plant wastewater treatment method
JPH1176750A (en) Flue gas treating device
JPH10263558A (en) Treatment of fluorine-containing desulfurized waste water
JP3702511B2 (en) Wastewater treatment method in wet flue gas desulfurization system
JP3217402B2 (en) Wastewater desulfurization equipment wastewater treatment equipment
JP2002233731A (en) Method and apparatus for treating waste gas
JPH0815529B2 (en) Vapor regeneration method for solvent recovery equipment
JP3169419B2 (en) Waste liquid combustion method using absorption refrigerator
JP2005098551A (en) Method and facility for recovering energy generated in sewage treatment plant

Legal Events

Date Code Title Description
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 19991214

LAPS Cancellation because of no payment of annual fees