JPH0155910B2 - - Google Patents

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Publication number
JPH0155910B2
JPH0155910B2 JP55106800A JP10680080A JPH0155910B2 JP H0155910 B2 JPH0155910 B2 JP H0155910B2 JP 55106800 A JP55106800 A JP 55106800A JP 10680080 A JP10680080 A JP 10680080A JP H0155910 B2 JPH0155910 B2 JP H0155910B2
Authority
JP
Japan
Prior art keywords
tank
liquid
water
coal
wastewater treatment
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
JP55106800A
Other languages
Japanese (ja)
Other versions
JPS5732704A (en
Inventor
Masayasu Murata
Tsugio Nagai
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 JP10680080A priority Critical patent/JPS5732704A/en
Publication of JPS5732704A publication Critical patent/JPS5732704A/en
Publication of JPH0155910B2 publication Critical patent/JPH0155910B2/ja
Granted legal-status Critical Current

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  • Processing Of Solid Wastes (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (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、特に焼却
灰の除去、脱硫等の過程で生ずる排水中の懸濁物
質の除去を良好に行える方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating dust, acidic or alkaline waste discharged from a coal-fired power plant in a non-polluting manner, and in particular for the removal of incinerated ash, desulfurization, etc. This invention relates to a method for effectively removing suspended solids from wastewater generated during the process.

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推積するク
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と称され
るとおりミクロン級であり、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 ART In thermal power plants, especially coal-fired power plants, large amounts of clinker and fly ash are produced by combustion of pulverized coal and fine grained 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.
In addition, sealing water is required to seal the slag tank and the bottom of the furnace. On the other hand, the debris collected by dust collectors such as electrostatic precipitators is micron-sized, as is called fly debris, and is easily blown up, requiring careful handling, and the amount of emissions is large.

一例として700MW級の石炭火力発電所用ボイ
ラー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搭
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, showing these amounts for a boiler unit for a 700MW class coal-fired power plant, clinker is
10T/h, fly ash 80T/h, clinker transport water 300T/h, fly ash humidification water 15-20T/h. In addition, the wastewater 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
18 T/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。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
るため中性化して排出する必要がある。排水の中
性化の際にスラツジが生ずるが、このスラツジお
よび前記クリンカ除去のために使用した水に含有
するこれらスラツジおよびクリンカを除去するた
めには広大な沈降用の池が必要となり、反対に小
型の沈降槽等を利用する場合には高価な凝集剤を
大量に使用せねばならない。
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. Some of these wastes are used as valuable materials, but some wastewater and
Both fly ash and clinker must be neutralized before being discharged to prevent secondary pollution. Sludge is generated during the neutralization of wastewater, but in order to remove the sludge and clinker contained in the water used for removing the sludge and clinker, a vast settling pond is required. If a small settling tank or the like is used, a large amount of expensive flocculant must be used.

この発明の目的はスラツジ、クリンカ等を排出
処理する際に使用した水が含有する懸濁物質を良
好かつ安価に除去でき、この水の再使用を効果的
に行う装置を提供することにある。
An object of the present invention is to provide an apparatus that can effectively and inexpensively remove suspended solids contained in water used in discharging sludge, clinker, etc., and can effectively reuse this water.

要するにこの発明は、石炭焚ボイラの排ガスよ
り捕集したフライアツシユの一部と脱硫前段の排
ガス冷却後の酸性冷却水W1と脱硫過程で生じた
アルカリ性液W2との供給を受ける排水処理槽2
9の上澄み液と捕集したフライアツシユを混合す
るミキサ15を有するフライアツシユ処理系と、
ボイラ底部のスラツグタンク1a内水中に落下し
た塊状高温石炭灰の破砕粒子たるスラツグと循環
する処理水との混合物と、排水処理槽29のスラ
ツジと弁60付きの管路59より上澄み液の供給
を受ける脱水器38をもつ粉粒体含有液の処理系
と、脱水器38の上澄み液と貯炭場53の粉状石
炭を含む排水と排水処理槽29上澄み液の供給を
受ける沈降槽39を有する処理水回収系と、排水
処理槽29の上澄み液の供給を受けスラツグタン
ク上端をシールするシール系と、沈降槽39の液
が供給される循環タンク40の液をポンプ41を
経由し処理水を循環使用するポンプ33に供給す
る処理水循環系と、よりなりボイラより排出する
粉粒体を処理水から分離し、分離した処理水を循
環使用する石炭火力発電所の排液排出物処理方法
であることを特徴とする。
In short, this invention provides a wastewater treatment tank 2 that receives a portion of fly ash collected from the exhaust gas of a coal-fired boiler, acidic cooling water W 1 after cooling the exhaust gas in the pre-desulfurization stage, and alkaline liquid W 2 generated during the desulfurization process.
a fly ash processing system having a mixer 15 for mixing the supernatant liquid of 9 and the collected fly ash;
A mixture of slag, which is crushed particles of lumpy high-temperature coal ash that has fallen into the water in the slag tank 1a at the bottom of the boiler, and circulating treated water, sludge from the wastewater treatment tank 29, and supernatant liquid are supplied from a pipe 59 with a valve 60. Treated water has a treatment system for a powder-containing liquid having a dehydrator 38, a sedimentation tank 39 that receives the supernatant liquid from the dehydrator 38, wastewater containing powdered coal from a coal storage yard 53, and the supernatant liquid from a wastewater treatment tank 29. A recovery system, a sealing system that receives the supernatant liquid from the wastewater treatment tank 29 and seals the upper end of the slag tank, and a circulation tank 40 that receives the liquid from the sedimentation tank 39 and circulates and uses the treated water via a pump 41. The method is characterized by a treated water circulation system that supplies the pump 33 and a method for treating effluent from a coal-fired power plant, which separates powder and granules discharged from the boiler from the treated water, and circulates and uses the separated treated water. shall be.

以下この発明の一実施例を図面を用いて説明す
る。
An embodiment of the present invention will be described below with reference to the drawings.

石炭焚ボイラ1の排ガスは集塵装置(電気集塵
器)2を経由し、管路3を経て脱硫装置(図示せ
ず)に至り脱硫された後系外に排出される。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5
0を経てミキサ15に送られ、噴霧ノズル管15
aの噴露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31およ
び32を経て抽出された上澄み液とミキサ47a
におい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。脱硫前段の排ガス減
温過程で循環使用されている冷却水(PH1〜2程
度の強酸液)の一部は抽出され、被処理液W1
して排水処理槽29に供給され、前記フライアツ
シユのアルカリ性液と混合して中性化される。こ
の場合脱硫過程で生じたCaSO4を含有するアルカ
リ性液W2を加えてもよい。この中性化過程にお
いて排水処理装置内に堆積したスラツジは液の含
有量多くそのまゝ廃棄できないので管路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。なお排水処理槽29の水位制
御運転において高水位のときは弁60付きの脱水
機38に送るほか、クリンカホツパ1aのシール
用水、管路30よりの排ガス冷却用にも送られ
る。ボイラ底部に形成したスラツグタンク1a内
に保有されている水中には水炉内より通常クリン
カと称する高温の塊状の石炭灰が落下し急冷によ
る衝撃で数mm寸法の粒に破砕されてスラツグと称
する黒色硝子状のクリンカ粒となる。このクリン
カ粒(以下単にスラツグと称す)は水流ジエツト
搬送器36に至り、管路34の水流により前記ス
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。脱水機38内の上澄み液は沈降槽
39に送られ、ここにおいて懸濁物質の沈降が行
われる。一方貯炭場53においては石炭の自然発
火を防止するため水W3を散布し、微粉炭等の石
炭の細粒(以下微粉炭で総称する)を含有する水
は側溝54に流入し管路55により排出される。
この微粉炭を含有する水の一部は管路55から分
岐する管路56に流入し、この管路を経て前記沈
降槽39に流入する。この場合、管路56にミキ
サ57を配置し、管路31から分岐した管路58
により排水処理装置29内の上澄み液を導入し、
ミキサ57において前記微粉炭を含有する水に上
澄み液を添加して微細粒炭の沈降防止をするよう
にしてもよい。沈降槽39に流入した微粉炭は凝
集剤として作用し、脱水機38から供給された排
水中の懸濁物を凝集沈降させる。凝集した懸濁物
は外部に排出され、浄化された水は循環タンク4
0に至り、ポンプ41を経て一部は管路24に至
り、管路30内の排水処理装置29の上澄み液と
共に排ガス冷却用水の補充用水として利用され残
りは管路42によりポンプ33の上流側に導かれ
管路36のプラント外からの補給水に加えられク
リンカおよびスラツジ輸送用水の補充用として無
駄なく利用される。排水処理槽29の上澄み液の
一部は管路62によりクリンカホツパシール水の
管路61へシール水の一部として加えられる。
Exhaust gas from the coal-fired boiler 1 passes through a dust collector (electrostatic precipitator) 2 and a conduit 3 to a desulfurization device (not shown) where it is desulfurized and then discharged to the outside of the system. On the other hand, fly ash collected by the electrostatic precipitator 2 is pneumatically transported through a pipe line 13 using pressurized air from a blower 12 and supplied to a silo 14. The appropriate amount is pipe 5
0 to the mixer 15, and the spray nozzle pipe 15
After being humidified and kneaded with the spray water of step a, the mixture is transported by truck 16 to a predetermined location and is either dumped or used effectively (for example, added to cement). In addition to being discharged through this pipe 50, the fly ash flows into a pipe 47 and mixes it with the supernatant liquid extracted from the wastewater treatment tank 29 via pipes 31 and 32.
After being kneaded in , the alkaline liquid is supplied to the wastewater treatment tank 29 as an alkaline liquid. A part of the cooling water (strong acid liquid with a pH of about 1 to 2) that is circulated and used in the exhaust gas temperature reduction process before desulfurization is extracted and supplied to the wastewater treatment tank 29 as the liquid to be treated W1 , where it is used as the alkaline liquid in the fly ash. It is neutralized by mixing with In this case, an alkaline liquid W 2 containing CaSO 4 produced during the desulfurization process may be added. The sludge accumulated in the wastewater treatment equipment during this neutralization process has a high liquid content and cannot be disposed of as it is, so it reaches the water jet conveyor 37 via the pipe 52, and the water flowing from the pump 33 into the pipe 35 causes the water to flow. The water is transported and flows into the dehydrator 38. In the water level control operation of the wastewater treatment tank 29, when the water level is high, the water is sent to the dehydrator 38 equipped with the valve 60, as well as water for sealing the clinker hopper 1a and cooling the exhaust gas from the pipe line 30. Into the water held in the slag tank 1a formed at the bottom of the boiler, high-temperature lumpy coal ash, usually called clinker, falls from the water reactor and is crushed into particles several millimeters in size by the impact of rapid cooling, resulting in black particles called slag. It becomes glassy clinker grains. This clinker grain (hereinafter simply referred to as slag) 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. The supernatant liquid in the dehydrator 38 is sent to a sedimentation tank 39, where suspended solids are sedimented. On the other hand, in the coal storage yard 53, water W3 is sprayed to prevent spontaneous combustion of the coal, and water containing fine particles of coal such as pulverized coal (hereinafter collectively referred to as pulverized coal) flows into the side ditch 54 and flows into the pipe 55. is discharged by
A part of the water containing this pulverized coal flows into a pipe 56 branching from the pipe 55, and flows into the settling tank 39 via this pipe. In this case, a mixer 57 is arranged in the conduit 56, and a conduit 58 branched from the conduit 31
The supernatant liquid in the wastewater treatment device 29 is introduced by
A supernatant liquid may be added to the water containing the pulverized coal in the mixer 57 to prevent the pulverized coal from settling. The pulverized coal that has flowed into the sedimentation tank 39 acts as a coagulant and causes suspended matter in the waste water supplied from the dehydrator 38 to coagulate and settle. The aggregated suspended matter is discharged to the outside, and the purified water is sent to the circulation tank 4.
0, part of it passes through the pump 41 and reaches the pipe line 24, where it is used together with the supernatant liquid of the wastewater treatment device 29 in the pipe line 30 as replenishment water for exhaust gas cooling, and the rest is sent through the pipe line 42 to the upstream side of the pump 33. The water is introduced into the pipe 36 and added to the make-up water from outside the plant, and is used without waste as a replenishment water for clinker and sludge transportation. A portion of the supernatant liquid in the wastewater treatment tank 29 is added to the clinker hop seal water conduit 61 via a conduit 62 as part of the seal water.

この発明を実施することにより系内で不要物と
して排出される石炭発火防止過程で生じた排水中
の微粉炭を凝集剤として利用するので懸濁物を安
価かつ良好に除去することができ、また処理水は
循環使用でき発電所の水の費用を著るしく低減で
きるという効果を奏する。
By carrying out this invention, the pulverized coal in the waste water produced during the process of preventing coal ignition, which is discharged as an unnecessary substance within the system, is used as a flocculant, so suspended matter can be removed inexpensively and effectively. The treated water can be recycled and used, which has the effect of significantly reducing the cost of water at power plants.

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

第1図はこ発明に係る方法を実施するための廃
棄物処理系統図である。 1……石炭焚ボイラ、1a……スラツグタン
ク、29………排水処理装置、39……沈降槽、
56……微粉炭含有排水導入用管路、58……上
澄み液導入用管路。
FIG. 1 is a waste treatment system diagram for carrying out the method according to the present invention. 1... Coal-fired boiler, 1a... Slug tank, 29... Wastewater treatment equipment, 39... Sedimentation tank,
56... Pipe line for introducing waste water containing pulverized coal, 58... Pipe line for introducing supernatant liquid.

Claims (1)

【特許請求の範囲】 1 石炭焚ボイラの排ガスより捕集したフライア
ツシユの一部と脱硫前段の排ガス冷却後の酸性冷
却水W1と脱硫過程で生じたアルカリ性液W2との
供給を受ける排水処理槽29の上澄み液と捕集し
たフライアツシユを混合するミキサ15を有する
フライアツシユ処理系と、 ボイラ底部のスラツグタンク1a内水中に落下
した塊状高温石炭灰の破砕粒子たるスラツグと循
環する液との混合物と、排水処理槽29のスラツ
ジと弁60付きの管路59より上澄み液の供給を
受ける脱水器38をもつ粉粒体含有液の処理系
と、 脱水器38の上澄み液と貯炭場53の粉状石炭
を含む排水と排水処理槽29の上澄み液の供給を
受ける沈降槽39を有する処理水回収系と、 排水処理槽29の上澄み液の供給を受けスラツ
グタンク上端をシールするシール系と、沈降槽3
9の液が供給される循環タンク40の液をポンプ
41を経由し処理水を循環使用するポンプ33に
供給する処理水循環系と、 よりなりボイラより排出する粉粒体を処理水から
分離し、分離した処理水を循環使用することを特
徴とする石炭火力発電所の排液排出物処理方法。
[Scope of Claims] 1. Wastewater treatment that receives a portion of fly ash collected from the exhaust gas of a coal-fired boiler, acidic cooling water W 1 after cooling the exhaust gas in the pre-desulfurization stage, and alkaline liquid W 2 generated during the desulfurization process. A fly ash processing system having a mixer 15 that mixes the supernatant liquid of the tank 29 and the collected fly ash; a mixture of slag, which is crushed particles of lumpy high-temperature coal ash that has fallen into the water in the slag tank 1a at the bottom of the boiler, and circulating liquid; A treatment system for a powder-containing liquid having a dehydrator 38 that receives sludge from a wastewater treatment tank 29 and a supernatant liquid from a pipe 59 with a valve 60; a treated water recovery system having a sedimentation tank 39 that receives the supply of wastewater containing wastewater and the supernatant liquid of the wastewater treatment tank 29; a seal system that receives the supply of the supernatant liquid of the wastewater treatment tank 29 and seals the upper end of the slag tank;
A treated water circulation system that supplies the liquid in the circulation tank 40 to which the liquid of No. 9 is supplied via the pump 41 to the pump 33 that circulates and uses the treated water; A method for treating effluent from a coal-fired power plant, characterized by recycling separated treated water.
JP10680080A 1980-08-05 1980-08-05 Method for removing suspended solid in settling tank Granted JPS5732704A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10680080A JPS5732704A (en) 1980-08-05 1980-08-05 Method for removing suspended solid in settling tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10680080A JPS5732704A (en) 1980-08-05 1980-08-05 Method for removing suspended solid in settling tank

Publications (2)

Publication Number Publication Date
JPS5732704A JPS5732704A (en) 1982-02-22
JPH0155910B2 true JPH0155910B2 (en) 1989-11-28

Family

ID=14442943

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10680080A Granted JPS5732704A (en) 1980-08-05 1980-08-05 Method for removing suspended solid in settling tank

Country Status (1)

Country Link
JP (1) JPS5732704A (en)

Also Published As

Publication number Publication date
JPS5732704A (en) 1982-02-22

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