JPS5855302Y2 - Coal ash processing equipment - Google Patents
Coal ash processing equipmentInfo
- Publication number
- JPS5855302Y2 JPS5855302Y2 JP11199980U JP11199980U JPS5855302Y2 JP S5855302 Y2 JPS5855302 Y2 JP S5855302Y2 JP 11199980 U JP11199980 U JP 11199980U JP 11199980 U JP11199980 U JP 11199980U JP S5855302 Y2 JPS5855302 Y2 JP S5855302Y2
- Authority
- JP
- Japan
- Prior art keywords
- ash
- coal
- ammonia
- gas
- exhaust gas
- 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
Landscapes
- Processing Of Solid Wastes (AREA)
- Incineration Of Waste (AREA)
- Treating Waste Gases (AREA)
Description
【考案の詳細な説明】
本考案は石炭焚ボイラーにおける高ダスト脱硝方式で捕
集されるアンモニア成分を含む灰の処理装置に関する。[Detailed Description of the Invention] The present invention relates to an apparatus for treating ash containing an ammonia component collected in a high dust denitrification method in a coal-fired boiler.
発電用等のボイラーに用いられる燃料は最近、重油から
石炭に移行しつつあるが、石炭を用いる場合には排ガス
中の窒素酸化物、ダスト等が重油に比べて多く、排ガス
を無公害化して大気中に放出するのには脱硝、集じん等
の処理をしなければならない。The fuel used in boilers for power generation and other purposes has recently been shifting from heavy oil to coal, but when coal is used, the exhaust gas contains more nitrogen oxides, dust, etc. than heavy oil, so it is difficult to make the exhaust gas pollution-free. Before it can be released into the atmosphere, it must undergo denitrification, dust collection, and other treatments.
脱硝装置としてはアンモニアによる接触還元法が実用化
されている。A catalytic reduction method using ammonia has been put into practical use as a denitrification device.
この場合脱硝装置。集塵器の組合せ方について種々研究
開発が進められている。In this case, a denitrification device. Various research and development efforts are underway on how to combine dust collectors.
現在、石炭焚排ガス処理方式として実用化が考えられて
いるものには、排ガスを脱硝装置に通した後に集塵器に
通す高ダスト脱硝方式と、排ガスを集塵器に通した後に
脱硝装置に通す低ダスト脱硝方式とがあるが、一般に低
ダスト脱硝方式は脱硝装置の下流にある空気予熱器が閉
塞を起し易い欠点があるため高ダスト脱硝方式が有利で
あると考えられている。Currently, there are two types of coal-fired exhaust gas treatment methods that are being considered for practical use: a high-dust denitrification method in which exhaust gas is passed through a denitrification device and then passed through a dust collector; There is a low-dust denitrification method that allows the denitrification device to pass through the air, but the low-dust denitrification method generally has the disadvantage that the air preheater downstream of the denitrification device is easily clogged, so the high-dust denitrification method is considered to be advantageous.
しかしながら、高ダスト脱硝方式では、注入したアンモ
ニアの一部の未反応分がガス中のSO3と反応し生成し
たアンモニア化合物を付着した灰が集塵器で捕集される
こととなる。However, in the high dust denitrification method, a part of the unreacted portion of the injected ammonia reacts with SO3 in the gas, and the ash adhering to the generated ammonia compound is collected by the dust collector.
捕集された灰は上述の如くアンモニア化合物を吸着して
おり、そのまま埋立てや工業用材料に利用すると、臭気
の問題や排水中に窒素分が入る等二次公害につながる場
合がある。The collected ash adsorbs ammonia compounds as mentioned above, and if it is used as a landfill or as an industrial material, it may lead to secondary pollution such as odor problems and nitrogen content entering the wastewater.
そのため、従来と同様灰の有効利用を図ろうとする場合
には、捕集した灰に含有するアンモニア分を除去しなけ
ればならない。Therefore, in order to utilize the ash effectively as in the past, the ammonia content contained in the collected ash must be removed.
このような不都合を解決する手段として、集塵器で捕集
した灰を加熱し灰の温度を高くしてアンモニア化合物(
例えば、硫安)を灰から分離し、分離されたガス(アン
モニア、SO3等)を脱硝装置の流入端を戻すことが容
易に考えられるが、このような処理を施行するとSO3
が再循環し脱硝装置やその下流に設置されている空気予
熱器を通過するガス中のSO3濃度が高くなってしまう
という問題がある。As a means to solve these inconveniences, the ash collected in the dust collector is heated to raise the temperature of the ash, and the ammonia compound (
For example, it is easy to think of separating ammonium sulfate) from the ash and returning the separated gas (ammonia, SO3, etc.) to the inlet end of the denitration equipment, but if such treatment is carried out, SO3
There is a problem in that the SO3 concentration in the gas that is recirculated and passes through the denitrification device and the air preheater installed downstream thereof increases.
本考案は上述のような従来方法の有する欠点を解決すべ
く考案されたもので、その目的は高ダスト脱硝方式にお
いて集塵器に捕集された灰を石炭焚ボイラから抽出され
た高温燃焼ガスで加熱してアンモニア化合物を分解して
灰から分離し発生したガスを更に石炭焚ボイラの火炉燃
焼部へ送気して該ガス中のSO3を高温燃焼部でSO2
に分解して灰中から生ずる有害成分を無害化し得る石炭
灰の処理装置を提供することにある。The present invention was devised to solve the drawbacks of the conventional methods as described above, and its purpose is to convert the ash collected in the dust collector in the high-dust denitrification method into high-temperature combustion gas extracted from a coal-fired boiler. The ammonia compound is decomposed and separated from the ash, and the generated gas is further sent to the furnace combustion section of the coal-fired boiler to convert SO3 in the gas into SO2 in the high-temperature combustion section.
An object of the present invention is to provide a coal ash processing device capable of decomposing harmful components generated from the ash into harmless substances.
以下、添付図面を参照して本考案の実施例を説明する。Hereinafter, embodiments of the present invention will be described with reference to the accompanying drawings.
添付図面において、1は石炭灰処理装置である。In the accompanying drawings, 1 is a coal ash processing device.
2は燃焼部を有する火炉3を備え、高温燃焼ガス抽出部
4が設けられた石灰臭ボイラである。2 is a lime-smelling boiler equipped with a furnace 3 having a combustion section and a high-temperature combustion gas extraction section 4.
ボイラ2の排ガス排出口2aは排ガス煙道5へ連通され
ている。An exhaust gas outlet 2a of the boiler 2 is communicated with an exhaust gas flue 5.
排ガス煙道5には、脱硝装置6、空気予熱器7および集
塵器8がこの順に介設されている。A denitrification device 6, an air preheater 7, and a dust collector 8 are installed in the exhaust gas flue 5 in this order.
脱硝装置6はその上流側の煙道5にアンモニア注入管9
が接続されて構成されている。The denitrification device 6 has an ammonia injection pipe 9 in the flue 5 on the upstream side.
are connected and configured.
集塵器8の灰排出部8aは灰輸送装置10を経て灰処理
装置11へ接続されている。The ash discharge section 8a of the dust collector 8 is connected to an ash processing device 11 via an ash transport device 10.
灰処理装置11には、また、高温燃焼ガス抽出部からの
高温燃焼ガスを送気する高温燃焼ガス送気路12が接続
され、高温燃焼ガスで灰を加熱し、分解されて生ずるア
ンモニア、SO3を含む加熱ガスを火炉3の燃焼部へ送
気するガス送気路13が接続されている。The ash processing device 11 is also connected to a high-temperature combustion gas air passage 12 for supplying high-temperature combustion gas from the high-temperature combustion gas extraction section, which heats the ash with the high-temperature combustion gas and decomposes it to generate ammonia and SO3. A gas air passage 13 is connected thereto for feeding heating gas containing gas to the combustion section of the furnace 3.
14は処理灰排出口である。14 is a treated ash outlet.
次に、本考案装置の動作を説明する。Next, the operation of the device of the present invention will be explained.
石炭焚ボイラ2で発生した排ガスは排ガス煙道5を経て
大気中へ放出される前に、排ガス中の窒素酸化物は脱硝
装置で排出基準以下に抑制される。Before the exhaust gas generated in the coal-fired boiler 2 is released into the atmosphere through the exhaust gas flue 5, nitrogen oxides in the exhaust gas are suppressed to below emission standards by a denitrification device.
これを更に詳しく説明すると、煙道5中を流れる排ガス
とアンモニア注入管9からのアンモニアと混合され、排
ガス中の窒素酸化物とアンモニアとが脱硝装置で反応し
排ガスから窒素酸化物が除去されるように処理工程が進
行するのであるが、その際に注入されたアンモニアがす
べて反応に供されず、一部の未反応分は排ガス中のSO
3と化合したアンモニア化合物として排ガス中に浮遊さ
れ、これらの各成分は排ガスが集塵器8を通過する際に
灰と共に集塵器に捕集される。To explain this in more detail, the exhaust gas flowing through the flue 5 is mixed with ammonia from the ammonia injection pipe 9, and the nitrogen oxides and ammonia in the exhaust gas react with each other in the denitrification device to remove nitrogen oxides from the exhaust gas. The treatment process progresses as shown, but not all of the ammonia injected at that time is subjected to the reaction, and some of the unreacted content becomes SO in the exhaust gas.
When the exhaust gas passes through the dust collector 8, these components are collected together with the ash in the dust collector.
集塵器8で排ガス中の灰の大部分を捕集されて比較的に
清浄となった排ガスは煙道5を経て大気中に放出される
のに対して、捕集された灰は灰輸送装置10により灰処
理装置11へ送られる。Most of the ash in the exhaust gas is collected by the dust collector 8, and the relatively clean exhaust gas is released into the atmosphere through the flue 5, while the collected ash is transported through ash transport. The ash is sent by the device 10 to the ash processing device 11 .
灰処理装置11の中で、灰は高温燃焼ガス抽出部4から
抽出され、送気路12を経て送られて来た高温(350
℃以上)の燃焼ガス中でこれと直接に混合されつつ加熱
される。In the ash processing device 11, ash is extracted from the high-temperature combustion gas extraction section 4, and the high-temperature gas (350
It is heated while being mixed directly with the combustion gas (at temperatures above 30°F (°C) or above).
その際灰中の上記アンモニア化合物は350℃以上にあ
る高温排ガスにより分解してガス状のアンモニアおよび
SO3が灰から分離される。At this time, the ammonia compounds in the ash are decomposed by the high-temperature exhaust gas at a temperature of 350° C. or higher, and gaseous ammonia and SO3 are separated from the ash.
従って、この装置での処理後の灰はアンモニア取分を含
むことはないから、その灰を埋立てや工業用材料として
使用しても、臭気等二次公害を惹起せしめることはなく
、灰を有効に利用し得る。Therefore, the ash treated with this device does not contain ammonia fraction, so even if the ash is used in landfill or as an industrial material, it will not cause secondary pollution such as odor, and the ash will not cause secondary pollution such as odor. It can be used effectively.
また、灰処理装置11で分離されたアンモニアおよびS
O3は火炉へ送り込まれ、そこにおいてアンモニア成分
は窒素や窒素酸化物になるが、この窒素酸化物によるボ
イラー2から排出される排ガス中の窒素酸化物濃度を上
昇させる度合は無視し得る程度である。In addition, ammonia and S separated in the ash processing device 11
O3 is sent to the furnace, where the ammonia component is converted to nitrogen and nitrogen oxides, but the degree to which this nitrogen oxide increases the concentration of nitrogen oxides in the exhaust gas discharged from the boiler 2 is negligible. .
従って、上述のように分離されたアンモニアを火炉2へ
再循環させても窒素酸化物が濃縮されて新らたな処理を
しなければならないという問題は生じない。Therefore, even if the separated ammonia is recycled to the furnace 2 as described above, the problem that nitrogen oxides are concentrated and new treatment is required does not occur.
また、火炉2中に入ったSO3は燃焼ガス高温部におい
て殆んどSO2に分解するから、SO3の濃縮の問題も
惹起しない。Furthermore, since most of the SO3 that has entered the furnace 2 is decomposed into SO2 in the combustion gas high temperature section, the problem of concentration of SO3 does not occur.
以上の説明から明らかなように、本考案によれば、
■ 集塵器で捕集される灰中に含有するアンモニア成分
およびSO3を高温燃焼ガスにより灰から分離できるか
ら灰は埋立てや工業用材料に有効に利用し得る。As is clear from the above explanation, according to the present invention, the ammonia component and SO3 contained in the ash collected by the dust collector can be separated from the ash using high-temperature combustion gas, so the ash can be stored in landfills or used for industrial purposes. It can be effectively used as a material.
■ ■の分離に用いられる高温ガスはボイラ排ガスであ
るので、別途の熱源を要しない。(2) The high temperature gas used for separation in (2) is boiler exhaust gas, so no separate heat source is required.
■ 分離されたアンモニア取分は火炉で窒素や窒素酸化
物になるが、その窒素酸化物によるボイラ排ガス中の窒
素酸化物濃度の上昇は無視し得る程度であり新らたな処
理の問題は生じない。■ The separated ammonia fraction is converted into nitrogen and nitrogen oxides in the furnace, but the increase in nitrogen oxide concentration in the boiler exhaust gas due to nitrogen oxides is negligible and new processing problems arise. do not have.
■ 分離されたSO3は火炉で殆んどSO2に分離され
るから、循環によるSO3の濃縮の問題は生じない等の
優れた効果が得られる。(2) Since most of the separated SO3 is separated into SO2 in the furnace, excellent effects such as no problem of concentration of SO3 due to circulation can be obtained.
添付図面は本考案装置の実施例を示す図である。
図中、1は石炭灰処理装置、2は石炭焚ボイラ、3は火
炉、4は高温燃焼ガス抽出部、6は脱硝装置、9はアン
モニア注入管、8は集塵器、11は灰処理装置である。The accompanying drawings show an embodiment of the device of the present invention. In the figure, 1 is a coal ash processing device, 2 is a coal-fired boiler, 3 is a furnace, 4 is a high-temperature combustion gas extraction section, 6 is a denitrification device, 9 is an ammonia injection pipe, 8 is a dust collector, and 11 is an ash processing device It is.
Claims (1)
られた石炭焚ボイラと、該石炭焚ボイラの排ガス排出口
に接続された脱硝装置と、該脱硝装置の排出口へ接続さ
れた集塵器と、該集塵器ならびに前記高温燃焼ガス抽出
部および前記燃焼部に接続された灰処理装置とを備え、
前記集塵器で捕集された灰を前記灰処理装置内で前記高
温燃焼ガス抽出部から抽出された高温燃焼ガスで加熱し
、更に発生される加熱ガスを前記燃焼部へ送気させて該
加熱ガス中の有害成分を分解するように構成したことを
特徴とする石炭灰処理装置。A coal-fired boiler equipped with a furnace having a combustion section and provided with a high-temperature combustion gas extraction section, a denitrification device connected to an exhaust gas outlet of the coal-fired boiler, and a dust collector connected to the discharge port of the denitrification device. an ash processing device connected to the dust collector, the high temperature combustion gas extraction section and the combustion section,
The ash collected by the dust collector is heated in the ash processing device with high-temperature combustion gas extracted from the high-temperature combustion gas extraction section, and the generated heated gas is sent to the combustion section to A coal ash processing device characterized by being configured to decompose harmful components in heated gas.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP11199980U JPS5855302Y2 (en) | 1980-08-07 | 1980-08-07 | Coal ash processing equipment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP11199980U JPS5855302Y2 (en) | 1980-08-07 | 1980-08-07 | Coal ash processing equipment |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS5736420U JPS5736420U (en) | 1982-02-26 |
JPS5855302Y2 true JPS5855302Y2 (en) | 1983-12-17 |
Family
ID=29473078
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP11199980U Expired JPS5855302Y2 (en) | 1980-08-07 | 1980-08-07 | Coal ash processing equipment |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5855302Y2 (en) |
Families Citing this family (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS602819A (en) * | 1983-06-18 | 1985-01-09 | Babcock Hitachi Kk | Ash content retreating device |
JPS6416327U (en) * | 1987-07-17 | 1989-01-26 | ||
DE3815632A1 (en) * | 1988-05-07 | 1989-11-16 | Kernforschungsz Karlsruhe | Process for melting ash and other ceramic materials having harmful constituents |
JPH072325B2 (en) * | 1990-10-02 | 1995-01-18 | 株式会社スルガ | Method of manufacturing decorative material using veneer |
JP2570012B2 (en) * | 1991-08-02 | 1997-01-08 | 日本鋼管株式会社 | Ash treatment method |
JP2886827B2 (en) * | 1996-07-26 | 1999-04-26 | 大進工業株式会社 | Manufacturing method of seat for seat |
-
1980
- 1980-08-07 JP JP11199980U patent/JPS5855302Y2/en not_active Expired
Also Published As
Publication number | Publication date |
---|---|
JPS5736420U (en) | 1982-02-26 |
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