JPH0133644Y2 - - Google Patents
Info
- Publication number
- JPH0133644Y2 JPH0133644Y2 JP11455380U JP11455380U JPH0133644Y2 JP H0133644 Y2 JPH0133644 Y2 JP H0133644Y2 JP 11455380 U JP11455380 U JP 11455380U JP 11455380 U JP11455380 U JP 11455380U JP H0133644 Y2 JPH0133644 Y2 JP H0133644Y2
- Authority
- JP
- Japan
- Prior art keywords
- water
- exhaust gas
- cooling water
- wastewater treatment
- treatment tank
- 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
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 32
- 239000007788 liquid Substances 0.000 claims description 21
- 239000000498 cooling water Substances 0.000 claims description 13
- 238000001816 cooling Methods 0.000 claims description 12
- 238000004065 wastewater treatment Methods 0.000 claims description 10
- 230000002378 acidificating effect Effects 0.000 claims description 9
- 239000010881 fly ash Substances 0.000 claims description 8
- 239000010802 sludge Substances 0.000 claims description 8
- 238000006477 desulfuration reaction Methods 0.000 claims description 6
- 230000023556 desulfurization Effects 0.000 claims description 6
- 238000010790 dilution Methods 0.000 claims 1
- 239000012895 dilution Substances 0.000 claims 1
- 238000000034 method Methods 0.000 description 6
- 230000007935 neutral effect Effects 0.000 description 5
- 239000002253 acid Substances 0.000 description 4
- 239000002893 slag Substances 0.000 description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 3
- 239000000428 dust Substances 0.000 description 3
- 239000012717 electrostatic precipitator Substances 0.000 description 3
- 239000007921 spray Substances 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 238000005260 corrosion Methods 0.000 description 2
- 230000007797 corrosion Effects 0.000 description 2
- 238000007865 diluting Methods 0.000 description 2
- 238000007789 sealing Methods 0.000 description 2
- 150000007513 acids Chemical class 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 239000008213 purified water Substances 0.000 description 1
- 230000001568 sexual effect Effects 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Preventing Corrosion Or Incrustation Of Metals (AREA)
Description
【考案の詳細な説明】
この考案は石炭火力発電所等のプラントから排
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装置に係り、特に系
内で生成される強酸性液の希釈を良好に行うこと
のできる装置に関する。[Detailed description of the invention] This invention relates to a device that processes dust, acidic or alkaline waste discharged from plants such as coal-fired power plants without causing pollution, and in particular strong acids generated within the system. The present invention relates to a device that can effectively dilute sexual fluid.
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 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 that accumulates 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 particle size of the debris collected by a dust collector such as an electrostatic precipitator is micron-sized, as is called fly debris, and it is easily blown up, requiring careful handling, and the amount of debris being emitted 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, 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 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。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。特に前記
した強酸性液は排ガス冷却用として循環して使用
する間に増々酸性度が高くなり配管の腐食等の問
題を生じるので、PH値をほぼ一定に保持し、あま
り酸性度が高くならないよう配慮する必要があ
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. 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. In particular, as the strongly acidic liquid mentioned above is circulated and used for cooling exhaust gas, its acidity increases and causes problems such as corrosion of pipes, so the PH value should be kept almost constant and the acidity should not become too high. It is necessary to take this into account.
この考案の目的は以上の問題点に鑑み、排ガス
冷却用水の酸性度を一定値以下に保持し、かつこ
のために系外から特別に水の補給を行う必要のな
い装置を提供することにある。 In view of the above problems, the purpose of this invention is to provide a device that maintains the acidity of exhaust gas cooling water below a certain value and does not require special water supply from outside the system. .
要するにこの考案は排ガス冷却用水の循環系路
に排水処理装置から抽出した中和水、スラツジや
クリンカ運搬用に使用した水等を供給する管路を
接続し、排ガス冷却用水に対しほぼ中性の水を加
えることにより循環する排ガス冷却用水の酸性度
をほぼ定常値に保持するよう構成したものであ
る。 In short, this idea connects a pipe line that supplies neutralized water extracted from wastewater treatment equipment, water used for transporting sludge and clinker, etc. to the circulation system of exhaust gas cooling water, and provides an almost neutral solution to the exhaust gas cooling water. By adding water, the acidity of the circulating exhaust gas cooling water is maintained at a substantially constant value.
以下この考案の実施例を添付図面を用いて説明
する。 Embodiments of this invention will be described below with reference to the accompanying drawings.
第1図において、石炭焚きボイラ1の排ガスは
電気集塵器2を経由し管路3,4から脱硫フアン
5、熱交換器6を通り脱硫装置の冷却塔7におい
て冷却された後吸収塔(図示せず)で脱硫され
る。脱硫された排ガスは前記熱交換器6において
未処理ガスにより所定の温度まで昇温し、管路9
および3を経て外部に放出される。冷却塔7内で
の未処理ガスの冷却は冷却塔スロート部において
冷却用水を噴霧することにより行うが、冷却水は
これに加えてSO2,SO3やほかの粉塵、さらには
HCl,HF等を捕捉する機能も果す。冷却用水は
循環ポンプ21により冷却塔7、冷却塔循環タン
ク20管路22を循環流動しているが、この冷却
過程でPH1〜2の強酸性液となり、かつスラツジ
も増加するので管路23によりその一部を常時抽
出し排水処理槽29に供給するよう構成してあ
る。 In FIG. 1, exhaust gas from a coal-fired boiler 1 passes through an electrostatic precipitator 2, pipes 3 and 4, a desulfurization fan 5, a heat exchanger 6, and is cooled in a cooling tower 7 of the desulfurization equipment. (not shown). The desulfurized exhaust gas is heated to a predetermined temperature by the untreated gas in the heat exchanger 6, and then passed through the pipe line 9.
and 3 before being released to the outside. The untreated gas in the cooling tower 7 is cooled by spraying cooling water at the throat of the cooling tower, but in addition to this, the cooling water also contains SO 2 , SO 3 and other dust, as well as
It also functions to capture HCl, HF, etc. Cooling water is circulated through the cooling tower 7, the cooling tower circulation tank 20, and the pipe line 22 by the circulation pump 21. During this cooling process, it becomes a strongly acidic liquid with a pH of 1 to 2, and sludge increases, so the water is circulated through the pipe line 23. It is configured so that a part of it is constantly extracted and supplied to the wastewater treatment tank 29.
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1
6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3
0,31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。ここの
排水処理槽29において、前記強酸性液はアルカ
リ性液と混合され中性化される。この場合脱硫過
程で生じたCaSO4を含有するアルカリ性液W1を
加えてもよい。この中性化過程で生じた中性液
(水)は管路30および30aにより強酸性液の
循環経路、例えば冷却塔循環タンク20に供給さ
れ、強酸性液の希釈用に利用する。さらにこの中
性液の一部は管路44によりスラツグタンク1a
とボイラ1の炉底部のシール用水兼プラントの補
給用水として給水することができる。排水処理槽
29底部に堆積したスラツジは管路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搬送され脱水機3
8に流入する。ボイラ底部に形成したスラツグタ
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。一方輸送用に使用した水は沈降槽39に入り
ここにおいて懸濁物の沈降が行われる。凝集した
懸濁物は外部に排出されると共に浄化された水
(ほぼ中性)は循環タンク40に至り、ポンプ4
1を経て一部は管路24により強酸性液の循環経
路に至り、前記管路30,30aにより供給され
る中性化液と共に強酸性液希釈用に利用される。
またその他の水は管路42によりポンプ33の上
流側に導かれ、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。 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. An appropriate amount of the liquid is sent to the mixer 15 through the pipe 50, humidified and kneaded with spray water from the spray nozzle pipe 15a, and then transferred to the track 1.
6, it is transported to a predetermined location and either dumped or put to good use (for example, added to cement). In addition to being discharged through this pipe 50, the fly ash flows into the pipe 47 and flows from the wastewater treatment tank 29 to the pipe 3.
After being kneaded with the supernatant liquid extracted through Steps 0, 31 and 32 in a mixer 47a, it is supplied to the wastewater treatment tank 29 as an alkaline liquid. In the wastewater treatment tank 29 here, the strong acidic liquid is mixed with an alkaline liquid and neutralized. In this case, an alkaline liquid W 1 containing CaSO 4 produced during the desulfurization process may be added. The neutral liquid (water) generated in this neutralization process is supplied to a strong acidic liquid circulation path, for example, the cooling tower circulation tank 20, through pipes 30 and 30a, and is used for diluting the strong acidic liquid. Further, a part of this neutral liquid is transferred to the slag tank 1a through a pipe line 44.
The water can be supplied as sealing water to the bottom of the boiler 1 and as make-up water for the plant. The sludge accumulated at the bottom of the wastewater treatment tank 29 reaches the water jet conveyor 37 through the pipe 52, where it is conveyed by the water flow from the pump 33 into the pipe 35, and is transferred to the dehydrator 3.
8. The clinker in the slag tank 1a formed at the bottom of the boiler is transferred to a water jet conveyor 36.
The sludge is then supplied to the dehydrator 38 by the water flow in the 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 enters the settling tank 39, where the suspended matter is settled. The aggregated suspended matter is discharged to the outside, and the purified water (nearly neutral) reaches the circulation tank 40 and is pumped to the pump 4.
1, a part of the liquid reaches the strong acid liquid circulation route through a pipe 24, and is used for diluting the strong acid liquid together with the neutralized liquid supplied through the pipes 30 and 30a.
Further, other water is led to the upstream side of the pump 33 through a pipe line 42, and is used without waste as a replenishment of water for clinker and sludge transportation.
この考案を実施することにより排ガスの冷却過
程で生ずる強酸性液を系内で発生した中性水によ
り希釈するので強酸性液循環経路の腐食を安価に
防止することが可能となる。 By implementing this idea, the strong acidic liquid generated during the exhaust gas cooling process is diluted with neutral water generated within the system, making it possible to inexpensively prevent corrosion of the strong acidic liquid circulation path.
第1図はこの考案に係る装置を有する石炭火力
発電プラントの系統図である。
7……冷却塔、24……再利用水導入用管路、
29……排水処理槽、30,30a……中性化液
導入用管路。
FIG. 1 is a system diagram of a coal-fired power plant equipped with a device according to this invention. 7... Cooling tower, 24... Reused water introduction pipe,
29... Waste water treatment tank, 30, 30a... Pipe line for introducing neutralized liquid.
Claims (1)
り排ガスを冷却し、冷却水の一部を排水処理槽に
おいてフライアツシユ含有水により中性化処理
し、さらにクリンカおよび排水処理槽のスラツジ
を水流輸送しかつ水流輸送に用いた水を懸濁物を
除去した後再利用するものにおいて、排ガス冷却
用水循環経路に対し、排水処理槽の中性化液を供
給する管路、および懸濁物除去後の再利用水を供
給する管路を各々接続して排ガス冷却用水の抜取
り量に対応する量を補給し循環する酸性冷却水の
希釈をする排ガス冷却用水希釈装置。 During desulfurization of exhaust gas, the exhaust gas is cooled by circulating cooling water, a portion of the cooling water is neutralized with flyash-containing water in a wastewater treatment tank, and clinker and sludge from the wastewater treatment tank are transported by water. In systems where the water used for water is reused after removing suspended matter, the water circulation path for exhaust gas cooling is connected to the pipe line that supplies the neutralized liquid to the wastewater treatment tank, and the reused water after removing the suspended matter. An exhaust gas cooling water dilution device that connects the pipes that supply the exhaust gas cooling water and replenishes the amount corresponding to the amount of exhaust gas cooling water extracted to dilute the circulating acidic cooling water.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11455380U JPH0133644Y2 (en) | 1980-08-14 | 1980-08-14 |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11455380U JPH0133644Y2 (en) | 1980-08-14 | 1980-08-14 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5739969U JPS5739969U (en) | 1982-03-03 |
| JPH0133644Y2 true JPH0133644Y2 (en) | 1989-10-12 |
Family
ID=29475534
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP11455380U Expired JPH0133644Y2 (en) | 1980-08-14 | 1980-08-14 |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0133644Y2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP5866948B2 (en) * | 2011-10-07 | 2016-02-24 | Jfeスチール株式会社 | Sintered exhaust gas cooling method for sintered exhaust gas desulfurization equipment |
-
1980
- 1980-08-14 JP JP11455380U patent/JPH0133644Y2/ja not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5739969U (en) | 1982-03-03 |
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