JPH05184860A - Method for solidifying byproduct of wet type line-gypsum flue gas desulfurizer - Google Patents

Method for solidifying byproduct of wet type line-gypsum flue gas desulfurizer

Info

Publication number
JPH05184860A
JPH05184860A JP4005401A JP540192A JPH05184860A JP H05184860 A JPH05184860 A JP H05184860A JP 4005401 A JP4005401 A JP 4005401A JP 540192 A JP540192 A JP 540192A JP H05184860 A JPH05184860 A JP H05184860A
Authority
JP
Japan
Prior art keywords
flue gas
gypsum
slurry
fly ash
concentrated
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
JP4005401A
Other languages
Japanese (ja)
Inventor
Masakazu Onizuka
雅和 鬼塚
Atsushi Tatani
淳 多谷
Kenji Inoue
井上  健治
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 Heavy Industries Ltd
Original Assignee
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
Application filed by Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP4005401A priority Critical patent/JPH05184860A/en
Priority to DK92610079T priority patent/DK0543767T3/en
Priority to AT92610079T priority patent/ATE147369T1/en
Priority to EP19920610079 priority patent/EP0543767B1/en
Priority to DE69216564T priority patent/DE69216564T2/en
Priority to US07/978,259 priority patent/US5395561A/en
Publication of JPH05184860A publication Critical patent/JPH05184860A/en
Pending legal-status Critical Current

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Abstract

PURPOSE:To produce a formed solidified body as semifinished products from a concentrated slurry by concentrating absorbent slurry drawn out from a wet type lime-gypsum flue gas desulfurizer, kneading the concentrated slurry, fly ash and quicklime to form a formed body, and drying and solidifying the formed body by heating air unsaturated with moisture produced by recovery heat from flue gas. CONSTITUTION:Absorbent slurry drawn out from a wet type lime-gypsum flue gas desulfurizer is concentrated by a slurry concentrator 13. The concentrated slurry whose main component is gypsum, fly ash 18 and quicklime or slaked lime 19 are kneaded in a kneading tank 20 to form a formed body in a forming tank 21. On the other hand, heating air unsaturated with moisture 31 produced by heat recovered from untreated gas 1 by a heat recovery unit 30 is fed to a curing dryer 22 to dry and solidify the formed body. As a result, formed solidified bodies usable for building materials are produced from the concentrated slurry and gypsum or fly ash which have a tendency to be surplus heretofere depending on market conditions is made utilized effectively.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は湿式石灰石膏法排煙脱硫
装置における吸収後抜き出しスラリの処理方法に関し、
建築資材として活用し得る固化体を副生する方法に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating after-absorption extracted slurry in a wet lime gypsum method flue gas desulfurization apparatus,
The present invention relates to a method for producing a solidified body that can be used as a building material.

【0002】[0002]

【従来の技術】従来の湿式石灰石膏法排煙脱硫装置の一
態様を図2に基づき説明する。図2において、吸収塔1
02に導入された未処理排ガス101はポンプ105で
吸収塔102上部のスプレーパイプ106から散布され
る循環吸収スラリと接触し脱硫され、清浄排ガス107
として排出される。排ガスからSO2 を吸収して循環タ
ンク103に流下した循環吸収スラリには吸収したSO
2 が亜硫酸塩として含まれており、この亜硫酸塩を酸化
して石膏化するために循環タンク103底部には空気1
04が吹き込まれている。一方、循環タンク103には
吸収したSO2 の量論量に見合う石灰石スラリ吸収剤が
配管111から供給されており、この供給量に見合った
量の循環吸収スラリが配管112から抜き出され固液分
離機113で固液分離される。固液分離操作で、主成分
が石膏である固相114と濾液とに分離され、該濾液の
一部は配管110から石灰石スラリ調整用に石灰石スラ
リ貯槽108に送液され、残りは配管115から排水と
して系外の排水処理工程116へ抜き出される。
2. Description of the Related Art One mode of a conventional wet lime gypsum method flue gas desulfurization apparatus will be described with reference to FIG. In FIG. 2, the absorption tower 1
The untreated exhaust gas 101 introduced into 02 is desulfurized by contact with the circulating absorption slurry sprayed from the spray pipe 106 above the absorption tower 102 by the pump 105, and the purified exhaust gas 107
Is discharged as. The SO 2 absorbed from the exhaust gas was absorbed by the circulating absorption slurry flowing down to the circulation tank 103 by absorbing SO 2.
2 is contained as sulfite, and in order to oxidize this sulfite to form gypsum, air 1 is placed at the bottom of the circulation tank 103.
04 is blown. On the other hand, the circulation tank 103 is supplied with the limestone slurry absorbent corresponding to the stoichiometric amount of the absorbed SO 2 through the pipe 111, and the amount of the circulation absorption slurry corresponding to the supplied amount is extracted through the pipe 112 and solid-liquid. Solid-liquid separation is performed by the separator 113. The solid-liquid separation operation separates the solid phase 114 whose main component is gypsum and the filtrate, a part of the filtrate is sent from the pipe 110 to the limestone slurry storage tank 108 for adjusting the limestone slurry, and the rest is sent from the pipe 115. It is extracted as wastewater to the wastewater treatment process 116 outside the system.

【0003】[0003]

【発明が解決しようとする課題】以上具体的に従来例を
説明したが、従来例において固液分離により副生した主
成分石膏の固体は石膏ボードやセメントなどの原料とし
て市場に供給されているが、社会情勢の変動或いは立地
環境などの条件によって需給のバランスが取れず、余剰
の副生石膏は埋立投棄せざるを得ないなど安定した市場
の開拓が望まれている。
Although the conventional examples have been concretely described above, the solid of the main component gypsum, which is a by-product of solid-liquid separation in the conventional examples, is supplied to the market as a raw material for gypsum board, cement and the like. However, due to conditions such as changes in social conditions or location environment, supply and demand cannot be balanced, and surplus byproduct gypsum must be dumped in landfills, and stable market development is desired.

【0004】また、石炭焚きの例では燃焼残さとしてフ
ライアッシュが多量生成するが、このフライアッシュも
一部はフライアッシュセメント原料として市場が見込め
るものの、大半は埋立投棄されているのが実情であり、
地域によってはこれら副生石膏及びフライアッシュの埋
立地の確保が問題視されているところもあり、安定した
市場が見込める用途開発が嘱望されている。
Further, in the case of coal burning, a large amount of fly ash is produced as a combustion residue, and although some of this fly ash can be expected as a raw material for fly ash cement in the market, most of it is actually dumped in landfill. ,
In some areas, securing landfill sites for these by-product gypsum and fly ash is regarded as a problem, and there is a strong demand for application development that can expect a stable market.

【0005】本発明は上記技術水準及び上記要望に応じ
うる湿式石灰石膏法排煙脱硫装置からの副生品を建築資
材として活用できる製品にする有用な方法を提供しよう
とするものである。
The present invention is intended to provide a useful method for making a by-product from a wet lime gypsum method flue gas desulfurization apparatus which can meet the above-mentioned state of the art and the above-mentioned demand into a product which can be utilized as a building material.

【0006】[0006]

【課題を解決するための手段】本発明は湿式石灰石膏法
排煙脱硫装置から抜き出される吸収スラリを濃縮し、該
石膏を主成分とする濃縮スラリとフライアッシュ及び生
石灰もしくは消石灰とを混練して成形した成形物を、排
煙からの回収熱によって生成された水分未飽和加熱空気
によって乾燥固化することを特徴とする湿式石灰石膏法
排煙脱硫装置副生品の固化方法である。
According to the present invention, an absorbent slurry extracted from a wet lime gypsum method flue gas desulfurization apparatus is concentrated, and a concentrated slurry containing gypsum as a main component is kneaded with fly ash and quick lime or slaked lime. A method for solidifying a by-product of a wet lime gypsum method flue gas desulfurization apparatus, which comprises drying and solidifying a molded article molded by the above method with heated water unsaturated unsaturated water generated by heat recovered from flue gas.

【0007】本発明において、濃縮スラリ(石膏:乾燥
基準):フライアッシュ:生石灰の混合比は重量比で大
略25〜40:40〜65:6〜20である。
In the present invention, the mixing ratio of concentrated slurry (gypsum: dry basis): fly ash: quick lime is about 25-40: 40-65: 6-20 by weight.

【0008】また、排煙からの回収熱によって生成され
る水分未飽和加熱空気に種々の方法が考えられるが、排
煙からの回収熱で水と空気を加熱して加熱水と加熱空気
を生成させ、これらを接触させて先ず水分飽和加熱空気
を生成し、該水分飽和加熱空気に前記加熱空気を混合し
て水分未飽和加熱空気を生成させる方法があげられる。
Various methods can be considered for the moisture-unsaturated heated air generated by the heat recovered from the flue gas. The recovered heat from the flue gas heats water and air to generate heated water and heated air. Then, these are brought into contact with each other to first generate moisture-saturated heated air, and the heated air is mixed with the moisture-saturated heated air to generate moisture-unsaturated heated air.

【0009】[0009]

【作用】本発明によれば、上記したとおり、副生された
循環吸収スラリの濃縮スラリとフライアッシュと生石灰
あるいは消石灰とを混練成形した後、排煙からの回収熱
を利用して水分飽和加熱空気に加熱空気を製造し、これ
らを混合して若干水分未飽和な加熱空気となし、これを
乾燥媒体として上記混練成形品を緩やかな速度で乾燥し
半製品としての成形固化体を最終的に副生できるもので
ある。
According to the present invention, as described above, after the concentrated slurry of the circulating absorption slurry produced as a by-product, fly ash and quick lime or slaked lime are kneaded and molded, the saturated heat of moisture is utilized by utilizing the heat recovered from the flue gas. Heated air is produced into air, and these are mixed to form heated air with a slightly unsaturated water content, and this is used as a drying medium to dry the above kneaded molded product at a moderate speed to finally obtain a molded solidified product as a semi-finished product. It is a by-product.

【0010】[0010]

【実施例】本発明の一実施態様を図1によって具体的に
説明する。図1において、吸収塔2に導入された未処理
排ガス1はポンプ5で吸収塔2上部のスプレーパイプ6
から散布される循環吸収スラリと接触し脱硫され、清浄
排ガス7として排出される。排ガスからSO2 を吸収し
て循環タンク3に流下した循環吸収スラリには吸収した
SO2 が亜硫酸塩として含まれており、この亜硫酸塩を
酸化して石膏化するために循環タンク3底部には空気4
が吹き込まれている。
EXAMPLE One embodiment of the present invention will be specifically described with reference to FIG. In FIG. 1, the untreated exhaust gas 1 introduced into the absorption tower 2 is pumped by a spray pipe 6 above the absorption tower 2 by a pump 5.
It is desulfurized by coming into contact with the circulating absorption slurry sprayed from and is discharged as clean exhaust gas 7. The circulating absorption slurry that absorbed SO 2 from the exhaust gas and flowed down to the circulation tank 3 contained the absorbed SO 2 as sulfite, and the bottom of the circulation tank 3 is located at the bottom of the circulation tank 3 in order to oxidize this sulfite to form gypsum. Air 4
Is blown in.

【0011】一方、循環タンク3には吸収したSO2
量論量に見合う石灰石スラリ吸収剤が配管11から供給
されており、この供給量に見合った量の循環吸収スラリ
が配管12から抜き出され、スラリ濃縮器13で濃縮さ
れ、濃縮スラリは配管17より混練槽20に送られ、一
方、希薄スラリの大部分は配管10を経て石灰石スラリ
貯槽8に戻され、残りが不純物の濃縮を避けるため排水
として配管15から排水処理工程16へと抜き出され
る。前記混練槽20へは濃縮スラリの他フライアッシュ
18と生石灰あるいは消石灰19が供給され、これらは
該混練槽20で十分混合練り上げされた後、成形機21
に送られ成形される。成形された前記混練物は、次いで
養生乾燥器22に送られる。
On the other hand, the circulation tank 3 is supplied with a limestone slurry absorbent corresponding to the stoichiometric amount of absorbed SO 2 from the pipe 11, and the amount of the circulation absorption slurry corresponding to the supplied amount is extracted from the pipe 12. The concentrated slurry is sent to the kneading tank 20 through the pipe 17, while most of the diluted slurry is returned to the limestone slurry storage tank 8 through the pipe 10 and the remainder is concentrated to avoid impurities. Therefore, the waste water is extracted from the pipe 15 to the waste water treatment process 16. In addition to the concentrated slurry, fly ash 18 and quick lime or slaked lime 19 are supplied to the kneading tank 20, which are sufficiently mixed and kneaded in the kneading tank 20 and then a molding machine 21.
Sent to and molded. The formed kneaded product is then sent to the curing dryer 22.

【0012】一方、未処理排ガス1から熱回収器30で
回収した熱を熱媒循環配管25を介して空気加熱器29
及び水分飽和空気発生器26へと供給し、これら供給さ
れた熱は空気加熱器29では空気28と、水分飽和加熱
空気発生器26では水27及び加熱空気24とそれぞれ
熱交換され、次いで、空気加熱器29で作られた加熱空
気24と水分飽和加熱空気発生器26で作られた水分飽
和加熱空気23とを混合し、水分が若干未飽和な空気3
1となし前記養生乾燥器22へ供給する。養生乾燥器2
2では成形品の大きさに応じて所定時間前記水分未飽和
加熱空気31が供給され、養生乾燥が行われ所定時間経
過した後、副生品としての成形固化体33が製品として
回収される。
On the other hand, the heat recovered from the untreated exhaust gas 1 by the heat recovery device 30 is passed through the heat medium circulation pipe 25 to the air heater 29.
And the moisture-saturated air generator 26, and the supplied heat is exchanged with the air 28 in the air heater 29 and with the water 27 and the heated air 24 in the moisture-saturated heated air generator 26, respectively, and then the air The air 3 having a slightly unsaturated water content is obtained by mixing the heated air 24 produced by the heater 29 with the moisture saturated heated air 23 produced by the water saturated air generator 26.
1 and None Supply to the curing dryer 22. Curing dryer 2
In No. 2, the water-unsaturated heated air 31 is supplied for a predetermined time according to the size of the molded product, and after curing and drying for a predetermined time, the molded solidified body 33 as a by-product is recovered as a product.

【0013】以上本発明を具体的に説明したが、養生乾
燥器22からの排気32の一部分もしくは大部分を水分
飽和加熱空気発生器26へ循環してもよい。
Although the present invention has been described in detail above, a part or most of the exhaust 32 from the curing dryer 22 may be circulated to the moisture saturated heated air generator 26.

【0014】本発明を図1の態様をなす具体的実施例を
用いてさらに具体的に説明する。
The present invention will be described in more detail with reference to a specific embodiment having the form shown in FIG.

【0015】(実施例)温度が180℃、SO2 が14
50ppm の未処理排ガス1を毎時8000m3 N処理す
る湿式石灰石膏法排煙脱硫装置において、熱回収器30
で回収した熱を利用して毎時500m3 Nの空気28を
60℃に加熱し、さらに、その80%を水分飽和加熱空
気発生器26に供給し60℃の水分飽和加熱空気23と
なし、前記加熱空気24の残りと混合して養生乾燥器2
2に供給した。
(Example) Temperature is 180 ° C., SO 2 is 14
In the wet limestone gypsum method flue gas desulfurization apparatus for treating 50 ppm of untreated exhaust gas 1 at 8000 m 3 N per hour, a heat recovery unit 30
The air 28 of 500 m 3 N per hour is heated to 60 ° C. by utilizing the heat recovered in step 1, and 80% of the air 28 is supplied to the moisture saturated heating air generator 26 to form the moisture saturated heating air 23 of 60 ° C. Curing dryer 2 mixed with the rest of heated air 24
Feed to 2.

【0016】一方、スラリ濃縮機13からは固形分濃度
約40%の濃縮スラリを毎時25kg(乾燥固形分基準)
だけ混練機20に供給し、混練機20へはさらに、フラ
イアッシュ18を50kgと生石灰19を8kg供給した。
混練機20で混練されたものを成形機21で4×4×1
6cmサイズに成形し養生乾燥器22へ供給した。この養
生乾燥器22でおよそ3日間養生乾燥してから成形固化
体を取り出した。また、養生乾燥器22から取り出した
成形固化体を4cm立方体に切り出し圧縮強度を測定した
結果、130kgf/cm2 以上であった。この値はレンガ等
の建築資材に相当する強度をもつものであり建築資材と
して使用可能であると判断される。
On the other hand, from the slurry concentrator 13, 25 kg / h of concentrated slurry having a solid content of about 40% (based on dry solid content)
Then, 50 kg of fly ash 18 and 8 kg of quicklime 19 were further supplied to the kneading machine 20.
What is kneaded by the kneading machine 20 is 4 × 4 × 1 by the molding machine 21.
It was molded into a 6 cm size and supplied to the curing dryer 22. The molded and solidified body was taken out after being cured and dried by the curing and drying device 22 for about 3 days. The molded solidified product taken out from the curing dryer 22 was cut into a 4 cm cube and the compression strength was measured. As a result, it was 130 kgf / cm 2 or more. This value has a strength equivalent to that of building materials such as bricks, and it is judged that it can be used as a building material.

【0017】[0017]

【発明の効果】本発明によれば、上記したとおり、湿式
石灰石膏法排煙脱硫装置から副生される石膏を主成分と
したスラリから建築資材として使用可能な成形固化体を
製造することができ、従来、市場の情勢に左右されて余
剰気味になったりすることのあった石膏あるいはフライ
アッシュの有効活用が可能となった。
As described above, according to the present invention, a molded solidified body usable as a building material can be produced from a slurry containing gypsum as a main component, which is a by-product of a wet lime gypsum method flue gas desulfurization apparatus. It is now possible to effectively use plaster or fly ash, which in the past may have been a little surplus depending on the market situation.

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

【図1】本発明の実施例に係る態様例の説明図。FIG. 1 is an explanatory diagram of a mode example according to an embodiment of the present invention.

【図2】従来例における湿式石灰石膏法排煙脱硫装置の
一態様の説明図。
FIG. 2 is an explanatory view of one mode of a wet limestone gypsum method flue gas desulfurization apparatus in a conventional example.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 湿式石灰石膏法排煙脱硫装置から抜き出
される吸収スラリを濃縮し、該石膏を主成分とする濃縮
スラリとフライアッシュ及び生石灰もしくは消石灰とを
混練して成形した成形物を、排煙からの回収熱によって
生成された水分末飽和加熱空気によって乾燥固化するこ
とを特徴とする湿式石灰石膏法排煙脱硫装置副生品の固
化方法。
1. A molded product obtained by concentrating an absorbing slurry extracted from a wet lime gypsum method flue gas desulfurization device, kneading the concentrated slurry containing the gypsum as a main component, fly ash, and quick lime or slaked lime, and molding the mixture. A method for solidifying a by-product of a wet limestone gypsum method flue gas desulfurization apparatus, characterized by drying and solidifying by heated moisture powder saturated heat generated by heat recovered from flue gas.
JP4005401A 1991-11-20 1992-01-16 Method for solidifying byproduct of wet type line-gypsum flue gas desulfurizer Pending JPH05184860A (en)

Priority Applications (6)

Application Number Priority Date Filing Date Title
JP4005401A JPH05184860A (en) 1992-01-16 1992-01-16 Method for solidifying byproduct of wet type line-gypsum flue gas desulfurizer
DK92610079T DK0543767T3 (en) 1991-11-20 1992-11-19 Process for the preparation of solid castings of a by-product of wet lime-plaster desulfurization of flue gas
AT92610079T ATE147369T1 (en) 1991-11-20 1992-11-19 METHOD FOR PRODUCING SOLID SHAPED BODIES FROM BY-PRODUCTS OF THE LIME-GYPSUM WET DESULFURIZATION OF EXHAUST GASES
EP19920610079 EP0543767B1 (en) 1991-11-20 1992-11-19 Method of producing solid moldings from a by-product of wet limestone-gypsum desulfurization of flue gas
DE69216564T DE69216564T2 (en) 1991-11-20 1992-11-19 Process for the production of solid moldings from by-products of lime-gypsum wet desulfurization of exhaust gases
US07/978,259 US5395561A (en) 1991-11-20 1992-11-20 Method of producing solid moldings from a by-product of wet limestone-gypsum desulfurization of flue gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4005401A JPH05184860A (en) 1992-01-16 1992-01-16 Method for solidifying byproduct of wet type line-gypsum flue gas desulfurizer

Publications (1)

Publication Number Publication Date
JPH05184860A true JPH05184860A (en) 1993-07-27

Family

ID=11610127

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4005401A Pending JPH05184860A (en) 1991-11-20 1992-01-16 Method for solidifying byproduct of wet type line-gypsum flue gas desulfurizer

Country Status (1)

Country Link
JP (1) JPH05184860A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2021193974A1 (en) * 2020-03-27 2021-09-30 三菱パワー株式会社 Absorption liquid treatment system for smoke exhaust desulfurization device

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2021193974A1 (en) * 2020-03-27 2021-09-30 三菱パワー株式会社 Absorption liquid treatment system for smoke exhaust desulfurization device

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