JPS6327076B2 - - Google Patents

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Publication number
JPS6327076B2
JPS6327076B2 JP55113535A JP11353580A JPS6327076B2 JP S6327076 B2 JPS6327076 B2 JP S6327076B2 JP 55113535 A JP55113535 A JP 55113535A JP 11353580 A JP11353580 A JP 11353580A JP S6327076 B2 JPS6327076 B2 JP S6327076B2
Authority
JP
Japan
Prior art keywords
water
slag tank
pipe
supplied
neutralized
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
Application number
JP55113535A
Other languages
Japanese (ja)
Other versions
JPS5738980A (en
Inventor
Tsugio Nagai
Masayasu Murata
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 JP11353580A priority Critical patent/JPS5738980A/en
Publication of JPS5738980A publication Critical patent/JPS5738980A/en
Publication of JPS6327076B2 publication Critical patent/JPS6327076B2/ja
Granted legal-status Critical Current

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  • Treating Waste Gases (AREA)

Description

【発明の詳細な説明】 この発明は石炭火力発電所のプラントから排出
される粉塵,酸性またはアルカリ性の排出物を公
害を出さぬ状態で処理する方法に係り、特に系内
で生成された中和処理水をプラント内で有効に利
用する方法に関する。
[Detailed Description of the Invention] This invention relates to a method for treating dust, acidic or alkaline waste discharged from a coal-fired power plant in a non-polluting state, and in particular, it relates to a method for treating dust, acidic or alkaline waste discharged from a coal-fired power plant, and in particular, to treat neutralized waste generated within the system. It relates to a method for effectively utilizing treated water within a plant.

火力発電所,特に石炭火力発電所においては微
粉炭,細粒炭の燃焼により生ずるクリンカ,フラ
イアツシユの量が多く、その処理が問題となつて
いる。火炉底部側のスラツグタンク内に堆積する
クリンカの排出搬送には水流ジエツトが好まし
く、またこのスラツグタンクと火炉底部の気密に
は水封用の水を必要とする。一方電気集塵器等の
集塵器で捕集するアツシユはフライアツシユをと
称されるとおり粒径はミクロン級であり、軽く舞
い上つて取り扱いに注意を要し、しかも排出量も
多い。
BACKGROUND OF THE INVENTION In thermal power plants, especially coal-fired power plants, large amounts of clinker and fly ash are generated from the combustion of pulverized coal and fine grain coal, and their disposal has become a problem. A water jet is preferred for discharging and transporting clinker accumulated in the slag tank at the bottom of the furnace, and water for water sealing is required to airtight the slag tank and the bottom of the furnace. On the other hand, the particle size of the debris collected by a dust collector such as an electrostatic precipitator is micron-level, as is called fly debris, and it is easily blown up, requiring careful handling, and the amount of discharge is large.

一例として700MW級の石炭火力発電所用ボイ
ラ一基につきこれらの量を示すと、クリンカは
10T/h,フライアツシユは80T/h,クリンカ
搬送用水は300T/h,フライアツシユ加湿用水
は15〜20T/hに達する。また脱硫装置の冷却塔
から排出される排水はPH1〜2の強酸で排出量は
18T/hであり、排ガス中のSO2,SO3をCaOで
処理する際に生ずるCaSO4(石膏)を濃縮させる
シツクナからの排水はPH9.0〜9.5のアルカリ性液
である。
As an example, if these amounts are shown for one boiler for a 700 MW class coal-fired power plant, the clinker is
10T/h, fly ash 80T/h, clinker transport water 300T/h, fly ash humidification water 15-20T/h. In addition, the waste water discharged from the cooling tower of the desulfurization equipment is a strong acid with a pH of 1 to 2, and the amount discharged is
18T/h, and the wastewater from Shitukuna, which concentrates CaSO 4 (gypsum) produced when SO 2 and SO 3 in exhaust gas are treated with CaO, is an alkaline liquid with a pH of 9.0 to 9.5.

以上の如く石炭火力発電所からは大量のフライ
アツシユやクリンカが排出され、脱硫過程からは
排ガス減温用の噴霧水による高濃度の塩酸,弗酸
を含む硫酸液が、またCaOとの反応によるCaSO4
の排出があり、これらの処理と搬送のため
350T/hの水量を必要とするものである。
As mentioned above, large amounts of fly ash and clinker are discharged from coal-fired power plants, and from the desulfurization process, a sulfuric acid solution containing highly concentrated hydrochloric acid and hydrofluoric acid is produced by the spray water used to cool the exhaust gas, and CaSO is produced by the reaction with CaO. Four
Due to the treatment and transportation of
It requires a water flow of 350T/h.

これら排出物の一部は有価物として使用するが
排液,フライアツシユ,クリンカとも二次公害を
防止するため中和して排出する必要がある。以上
説明した処理過程にあつては大量の水を必要とす
るがこれを外部から供給するのは不経済であり、
可能な限り系内で使用する水を再利用することが
好ましい。
Although some of these wastes are used as valuable materials, the wastewater, flyash, and clinker all need to be neutralized before being discharged to prevent secondary pollution. The treatment process described above requires a large amount of water, but it is uneconomical to supply this from outside.
It is preferable to reuse the water used within the system as much as possible.

この発明の目的は上述した問題点に鑑み、系内
で生成された水を可能な限り再使用して外部から
の補給水の供給量を減少させる方法を提供するこ
とにある。
SUMMARY OF THE INVENTION In view of the above-mentioned problems, an object of the present invention is to provide a method of reusing the water produced within the system as much as possible to reduce the amount of supplementary water supplied from outside.

要するにこの発明は排水の中和処理により系内
で生成された中性液を脱硫や、スラツグタンクと
ボイラのシール用水として利用することを特徴と
する方法である。
In short, this invention is a method characterized in that the neutral liquid produced in the system by neutralizing wastewater is used for desulfurization and as water for sealing the slag tank and boiler.

以下この発明の実施例を図面を用いて説明す
る。
Embodiments of the present invention will be described below with reference to the drawings.

石炭焚きボイラ1の排ガスは電気集塵器2を経
て管路3,4から脱硫フアン5,熱交換器6を通
り、脱硫装置7の冷却塔7aに入りミストエリミ
ネータ7bを経て吸収塔7cに流入する。この吸
収塔内で排ガスは石灰石粉を含む水を循環ポンプ
7d,管路7g,噴霧ノズル7eよりなる装置か
ら噴霧を受け、含有するSO2,SO3ガスはこれと
反応しCaSO4となつて吸収塔7cの底部に貯溜す
る。水滴を含むガスはデミスタ7fで水滴を除去
されヒータ8で昇温し熱交換器6で更に昇温し管
路9,煙突0を経由して大気中に放出される。ダ
ンパ11a,11b,11cは脱硫装置の運転中
止もしくは点検する場合の排ガス流れの切換え用
に使用される。一方電気集塵器2で捕集されたフ
ライアツシユはブロア12からの圧力空気で管路
13により気流輸送され、サイロ14に供給され
る。その適量は管路50を経てミキサ15に送ら
れ、噴霧ノズル管15aの噴霧水で加湿混練され
た後トラツク16で所定の場所に輸送され、投棄
もしくは有効利用(例えばセメントに添加)され
る。フライアツシユはこの管路50によつて排出
されるのとは別に管路47に流入し、排水処理槽
29から管路30,31および31aを経て抽出
された上澄み液とミキサ47aにおて混練された
後アルカリ性液として前記排水処理槽29に供給
される。冷却塔7a,冷却塔循環タンク20,循
環ポンプ21,管路22の間を循環流動する排ガ
ス冷却用水は冷却過程でPH1〜2程度の強酸性液
となり、その一部は管路23により抽出され排水
処理槽29に供給される。ここにおいて前記アル
カリ性液と混合して中性化される。中和された処
理液(水)は管路30aにより冷却水循環経路に
供給されこの強酸性液を希釈する。また管路44
に流入した処理液はこの管路を経て管路46の補
給水Wと合流する。処理液と合流した補給水(以
下単に「補給水」と称する)Wは先ずスラツグタ
ンク1aとボイラ1のシール用およびスラツグタ
ンク1aに対する給水として利用される。第2図
はスラツグタンクの詳細を示し、補給水Wはスラ
ツグタンク1aに形成した断面略U字形の溝部6
0に流入する。この溝部60のほぼ中央部にはヘ
ツダ1bから吊下した仕切り板1cが配置してあ
り、この仕切板1cおよび溝部60に流入した補
給水Wによりスラツグタンク1aを気密に保持し
ている。溝部60より溢流した補給水は管路46
bに流入し次の使用に供される。一方管路46c
に流入した補給水Wはスラツグタンク1a内に流
入して貯留される。溶融した不燃物はボイラ1を
流下しこの貯留水により急激に冷却されることに
より比較的小径の粒子に崩壊しスラツグタンク1
aの底部にクリンカとして堆積する。なおスラツ
グタンク1a上方空間内は非常に高温であるため
貯留水の蒸発も激しく、このため管路46cによ
り補給水Wを供給し水面が常時一定の高さを保持
するように水流を制御する。次に、溝部60から
溢流した補給水はポンプ45により管路46bを
経て吸収塔7c底部から噴霧ノズル7eに石灰石
を含有する脱硫液を循環供給する管路7gに補給
水として供給する。脱硫剤として使用する石灰石
スラリーは石灰石粉を収容する石灰石サイロ17
から送られる石灰石粉を石灰石スラリータンク1
8内で供給水と混合しポンプ19,管路19aを
経て吸収塔7cへ供給する。
Exhaust gas from the coal-fired boiler 1 passes through an electric precipitator 2, pipes 3 and 4, a desulfurization fan 5, a heat exchanger 6, enters a cooling tower 7a of a desulfurization device 7, passes through a mist eliminator 7b, and flows into an absorption tower 7c. do. In this absorption tower, the exhaust gas is sprayed with water containing limestone powder from a device consisting of a circulation pump 7d, a pipe 7g, and a spray nozzle 7e, and the SO 2 and SO 3 gases it contains react with it and become CaSO 4 . It is stored at the bottom of the absorption tower 7c. The gas containing water droplets is removed by a demister 7f, heated by a heater 8, further heated by a heat exchanger 6, and discharged into the atmosphere via a pipe 9 and a chimney 0. The dampers 11a, 11b, and 11c are used to switch the exhaust gas flow when stopping or inspecting the desulfurization equipment. On the other hand, the fly ash collected by the electrostatic precipitator 2 is pneumatically transported through a pipe line 13 using pressurized air from a blower 12, and is supplied to a silo 14. An appropriate amount of the mixture is sent to the mixer 15 via the pipe 50, humidified and kneaded with water sprayed from the spray nozzle pipe 15a, and then transported to a predetermined location by the truck 16, where it is dumped or put to effective use (for example, added to cement). In addition to being discharged through this pipe 50, the fly ash flows into a pipe 47 and is mixed with the supernatant liquid extracted from the wastewater treatment tank 29 via pipes 30, 31, and 31a in a mixer 47a. After that, it is supplied to the wastewater treatment tank 29 as an alkaline liquid. The exhaust gas cooling water that circulates between the cooling tower 7a, the cooling tower circulation tank 20, the circulation pump 21, and the pipe line 22 becomes a strongly acidic liquid with a pH of about 1 to 2 during the cooling process, and a part of it is extracted through the pipe line 23. The wastewater is supplied to the wastewater treatment tank 29. Here, it is mixed with the alkaline liquid and neutralized. The neutralized treatment liquid (water) is supplied to the cooling water circulation path through the pipe 30a to dilute this strong acidic liquid. Also, the pipe line 44
The processing liquid flowing into the pipe passes through this pipe and joins with the make-up water W in the pipe . The make-up water (hereinafter simply referred to as "make-up water") W that has merged with the processing liquid is first used for sealing the slag tank 1a and the boiler 1 and as water supply to the slag tank 1a. FIG. 2 shows the details of the slag tank, and the make-up water W is supplied to the groove 6, which has a substantially U-shaped cross section, formed in the slag tank 1a.
Flows into 0. A partition plate 1c suspended from the header 1b is disposed approximately at the center of the groove 60, and the partition plate 1c and makeup water W flowing into the groove 60 keep the slag tank 1a airtight. The make-up water overflowing from the groove 60 flows into the pipe 46.
b and is used for the next time. On the other hand, conduit 46c
The make-up water W flowing into the slag tank 1a flows into the slag tank 1a and is stored therein. The molten incombustibles flow down the boiler 1 and are rapidly cooled by this stored water, disintegrating into relatively small particles and flowing into the slag tank 1.
It is deposited as clinker at the bottom of a. Note that the space above the slag tank 1a is at a very high temperature, so that the stored water evaporates rapidly, so make-up water W is supplied through the pipe 46c and the water flow is controlled so that the water surface is always maintained at a constant height. Next, the make-up water overflowing from the groove 60 is supplied as make-up water by the pump 45 through the pipe 46b to the pipe 7g which circulates desulfurization liquid containing limestone from the bottom of the absorption tower 7c to the spray nozzle 7e. Limestone slurry used as a desulfurization agent is stored in limestone silo 17 containing limestone powder.
Limestone powder sent from limestone slurry tank 1
The mixed water is mixed with feed water in the tank 8 and supplied to the absorption tower 7c via a pump 19 and a pipe 19a.

次に排水処理槽29内のスラツジは管路52に
より水流ジエツト搬送器37に至り、ポンプ33
から管路35に流入した水により水流輸送され脱
水機38に流入する。またスラツグタンク1a内
のクリンカは水流ジエツト搬送器36に至り、管
路34の水流によつて前記スラツジと同様に脱水
機38に供給される。脱水機38に供給されたク
リンカおよびスラツジは脱水した後排出されトラ
ツク16aにより所定の場所に輸送される。一方
輸送用に使用した水は沈降槽39に送られ、ここ
において懸濁物の沈降が行われる。懸濁物の除去
が完了し浄化した水は循環タンク40,およびポ
ンプ41に至り、一部は管路24によつて排ガス
冷却用水の希釈用に、また残りは管路42により
スラツジ,クリンカの水流輸送用水の補充用に利
用される。
Next, the sludge in the wastewater treatment tank 29 reaches a water jet conveyor 37 via a pipe 52, and a pump 33
The water flowing into the pipe line 35 is transported by water flow and flows into the dehydrator 38 . Further, the clinker in the slag tank 1a reaches a water jet conveyor 36, and is supplied to a dehydrator 38 by the water flow in a pipe 34 in the same way as the sludge. The clinker and sludge supplied to the dehydrator 38 are dehydrated and then discharged and transported to a predetermined location by the truck 16a. On the other hand, the water used for transportation is sent to a settling tank 39, where the suspended matter is settled. The purified water after the removal of suspended matter is completed reaches a circulation tank 40 and a pump 41, a part of which is used for diluting exhaust gas cooling water through a pipe 24, and the rest is used for sludge and clinker through a pipe 42. Used for replenishing water for water transport.

この発明を実施することにより中和された処理
水をボイラ火炉とスラツグタンクとの接続部のシ
ール用,脱硫過程の補充用水,スラツグタンクの
貯留水補充用等に利用ででき、系内で生成された
処理水を無駄なく利用できる。
By implementing this invention, the neutralized treated water can be used for sealing the connection between the boiler furnace and the slag tank, replenishing water for the desulfurization process, replenishing the stored water in the slag tank, etc. Treated water can be used without waste.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図はこの発明に係る方法を実施するための
排出物処理プラントの系統図、第2図はボイラと
スラツグタンク接続部の詳細図である。 1……石炭焚きボイラ、1a……スラツグタン
ク、7……脱硫装置、7a……冷却塔、7g……
脱硫剤含有液循環管路、29……排水処理槽、4
4……中性化液供給用管路、46,46b……補
給水供給用管路。
FIG. 1 is a system diagram of an effluent treatment plant for carrying out the method according to the invention, and FIG. 2 is a detailed diagram of the connection between the boiler and the slag tank. 1...Coal-fired boiler, 1a...Slag tank, 7...Desulfurizer, 7a...Cooling tower, 7g...
Desulfurizing agent-containing liquid circulation pipe, 29... wastewater treatment tank, 4
4... Pipe line for supplying neutralized liquid, 46, 46b... Pipe line for supplying makeup water.

Claims (1)

【特許請求の範囲】 1 石炭焚きボイラから排出される排ガス中のフ
ライアツシユを捕集し、排ガス自体は脱硫処理す
るものにおいて、脱硫過程で排ガス冷却用に使用
した強酸性液を、フライアツシユを含有するアル
カリ性液で中性化処理し、中性化処理した水をボ
イラとスラツグタンクのシール用に利用し、かつ
このシール部での溢流水を脱硫剤含有水の循環過
程に補給水として供給することを特徴とする中和
処理水の再利用方法。 2 スラツグタンクのシール部に供給する水の一
部を分岐する管路によりスラツグタンクにスラツ
グタンク貯留水として供給することを特微とする
特許請求の範囲第1項記載の中和処理水の再利用
方法。
[Scope of Claims] 1. In a device that collects fly ash in exhaust gas discharged from a coal-fired boiler and desulfurizes the exhaust gas itself, the strongly acidic liquid used for cooling the exhaust gas in the desulfurization process contains fly ash. The water is neutralized with an alkaline liquid, and the neutralized water is used for sealing the boiler and slag tank, and the overflow water from this seal is supplied as make-up water to the circulation process of desulfurizing agent-containing water. A distinctive method for reusing neutralized water. 2. The method for reusing neutralized water according to claim 1, characterized in that a part of the water supplied to the seal portion of the slag tank is supplied to the slag tank as slag tank stored water through a branching pipe.
JP11353580A 1980-08-20 1980-08-20 Method for reusing of neutralization treated water Granted JPS5738980A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11353580A JPS5738980A (en) 1980-08-20 1980-08-20 Method for reusing of neutralization treated water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11353580A JPS5738980A (en) 1980-08-20 1980-08-20 Method for reusing of neutralization treated water

Publications (2)

Publication Number Publication Date
JPS5738980A JPS5738980A (en) 1982-03-03
JPS6327076B2 true JPS6327076B2 (en) 1988-06-01

Family

ID=14614778

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11353580A Granted JPS5738980A (en) 1980-08-20 1980-08-20 Method for reusing of neutralization treated water

Country Status (1)

Country Link
JP (1) JPS5738980A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109745813A (en) * 2018-03-29 2019-05-14 王雅珍 Nitre dehydration integrated tower and its application method drop in YZ type vortex mixed desulfurization and dedusting

Also Published As

Publication number Publication date
JPS5738980A (en) 1982-03-03

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