JPH0238172Y2 - - Google Patents
Info
- Publication number
- JPH0238172Y2 JPH0238172Y2 JP10615585U JP10615585U JPH0238172Y2 JP H0238172 Y2 JPH0238172 Y2 JP H0238172Y2 JP 10615585 U JP10615585 U JP 10615585U JP 10615585 U JP10615585 U JP 10615585U JP H0238172 Y2 JPH0238172 Y2 JP H0238172Y2
- Authority
- JP
- Japan
- Prior art keywords
- ash
- exhaust gas
- fluidized bed
- combustion
- furnace
- 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
- 238000002485 combustion reaction Methods 0.000 claims description 42
- 239000007789 gas Substances 0.000 claims description 39
- 238000000926 separation method Methods 0.000 claims description 6
- 239000007787 solid Substances 0.000 claims description 5
- 238000007599 discharging Methods 0.000 claims description 2
- 239000002912 waste gas Substances 0.000 claims 2
- 230000032258 transport Effects 0.000 claims 1
- 239000002956 ash Substances 0.000 description 53
- 239000002245 particle Substances 0.000 description 9
- 239000003245 coal Substances 0.000 description 8
- 239000000446 fuel Substances 0.000 description 8
- 239000000428 dust Substances 0.000 description 5
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 5
- 238000001816 cooling Methods 0.000 description 4
- 238000010586 diagram Methods 0.000 description 3
- 239000003546 flue gas Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- 241000234435 Lilium Species 0.000 description 2
- 235000019738 Limestone Nutrition 0.000 description 2
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 239000012159 carrier gas Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 239000006028 limestone Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 239000002006 petroleum coke Substances 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 229910052717 sulfur Inorganic materials 0.000 description 2
- 239000011593 sulfur Substances 0.000 description 2
- 229910052815 sulfur oxide Inorganic materials 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- RNFJDJUURJAICM-UHFFFAOYSA-N 2,2,4,4,6,6-hexaphenoxy-1,3,5-triaza-2$l^{5},4$l^{5},6$l^{5}-triphosphacyclohexa-1,3,5-triene Chemical compound N=1P(OC=2C=CC=CC=2)(OC=2C=CC=CC=2)=NP(OC=2C=CC=CC=2)(OC=2C=CC=CC=2)=NP=1(OC=1C=CC=CC=1)OC1=CC=CC=C1 RNFJDJUURJAICM-UHFFFAOYSA-N 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000010883 coal ash Substances 0.000 description 1
- 239000011335 coal coke Substances 0.000 description 1
- 239000002826 coolant Substances 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 239000012717 electrostatic precipitator Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003063 flame retardant Substances 0.000 description 1
- 238000005243 fluidization Methods 0.000 description 1
- 239000010881 fly ash Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
Description
【考案の詳細な説明】
(産業上の利用分野)
本考案は流動層燃焼装置、とくに、石炭や石油
コークスなどのように、燃焼後に多量の固形灰分
を出す燃料を用いる流動層燃焼装置に関する。[Detailed Description of the Invention] (Industrial Application Field) The present invention relates to a fluidized bed combustion apparatus, and in particular to a fluidized bed combustion apparatus that uses a fuel that produces a large amount of solid ash after combustion, such as coal or petroleum coke.
(従来の技術)
埋蔵量の少ない石油から、資源量の多い石炭に
エネルギー源を転換することが急がれている。石
炭は石油に比し硫黄含有量が多く、灰分を多く含
むことから燃料としての取り扱いには工夫を要す
る。石炭からエネルギーを取り出す燃焼炉として
注目されているのが流動層燃焼炉である。流動層
燃焼炉は、炉の底部に設けた空気室の天井部を構
成する空気分散板を介して、その上部にある流動
層に、流動化兼燃焼用空気を供給し、流動層を構
成する流動媒体(砂、セメントクリンカーなどの
耐熱性粒子で構成され、場合によつては、石灰石
などの脱硫剤粒子を含むことがある)を、あたか
も水の沸騰するように流動化させ、層中に供給さ
れた石炭粒子などのような燃料を燃焼させるもの
である。流動層の高さは50〜100cm程度であり、
700〜1000℃に加熱された高温の流動媒体の有す
る大きな熱容量のため、石炭に限らず、含水率の
高い汚泥、難燃性のEP灰や石油コークスなども
容易に燃焼させることができる。(Conventional technology) There is an urgent need to switch energy sources from oil, which has limited reserves, to coal, which has abundant resources. Coal has a higher sulfur content than petroleum and contains more ash, so it requires special care when handling it as a fuel. A fluidized bed combustion furnace is attracting attention as a combustion furnace for extracting energy from coal. In a fluidized bed combustion furnace, air for fluidization and combustion is supplied to the fluidized bed above it through an air distribution plate that forms the ceiling of an air chamber installed at the bottom of the furnace, forming a fluidized bed. The fluidized medium (composed of heat-resistant particles such as sand, cement clinker, etc., and in some cases may contain desulphurizing agent particles such as limestone) is fluidized as if it were boiling water, and It burns a supplied fuel such as coal particles. The height of the fluidized bed is about 50 to 100 cm,
Due to the large heat capacity of the high-temperature fluidized medium heated to 700-1000°C, it is possible to easily burn not only coal but also sludge with a high moisture content, flame-retardant EP ash, petroleum coke, etc.
燃料を1000℃以上の高温で燃焼させると、燃焼
用空気に含まれている窒素と酸素が結合して酸化
窒素(NOx)を生成し、これが燃焼排ガス中に
高濃度に含有されると、環境汚染という公害問題
を生ずる。 When fuel is burned at a high temperature of 1000℃ or higher, the nitrogen and oxygen contained in the combustion air combine to produce nitrogen oxides (NOx). This creates a pollution problem.
また、硫黄分を多く含む燃料を燃焼させる場
合、流動媒体に石灰石粉末を混合して、燃焼によ
つて生成する硫黄酸化物(SOx)を除去すること
が行われているが、この脱硫反応を効果的に行わ
せるには、流動層の温度を850〜1000℃に維持す
ることが必要である。 Additionally, when burning fuel with a high sulfur content, limestone powder is mixed into the fluidized medium to remove sulfur oxides (SOx) produced during combustion, but this desulfurization reaction is To be effective, it is necessary to maintain the temperature of the fluidized bed between 850 and 1000°C.
以上のような理由から、流動層温度を800〜
1000℃に保つて、石炭などの燃料を燃焼させるこ
とが一般に行われている。一方、流動層で石炭粒
子やEP灰などを燃焼させる場合、粒子径の小さ
い燃料は流動化空気などのガスによつて、流動層
からその上部空塔部に飛散し、十分に燃焼しない
ままで燃焼排ガスによつて煙道に運ばれる。ま
た、比較的大きい粒子の燃焼も、流動層中での流
動燃焼によつて小粒子に粉砕されるが、800〜
1000℃の批較的低い流動層温度では、その粒子中
心部まで完全に燃焼することなく、空塔部を経
て、燃焼排ガスによつて煙道に運ばれる。 For the above reasons, the fluidized bed temperature is set to 800~
It is common practice to maintain the temperature at 1000℃ and burn fuel such as coal. On the other hand, when burning coal particles, EP ash, etc. in a fluidized bed, fuel with small particle size is scattered from the fluidized bed to the upper part of the tower by gases such as fluidized air, and remains unburned. Carried into the flue by flue gases. In addition, the combustion of relatively large particles is also pulverized into small particles by fluidized combustion in a fluidized bed.
At a relatively low fluidized bed temperature of 1000°C, the particles are carried to the flue by flue gas through the empty column without being completely combusted.
したがつて、流動層燃焼装置から燃焼排ガスに
は未燃分の多い灰が置く含まれので、サイクロン
式集じん器で灰分を分離し、これを1100℃程度の
高温に維持した流動層式再燃焼炉に投入して未燃
分を完全に燃焼させ、フライアツシユとして利用
できる燃焼灰とすることが行われている。 Therefore, since the flue gas from the fluidized bed combustion equipment contains a large amount of unburned ash, the ash is separated using a cyclone type dust collector and this is maintained at a high temperature of about 1100°C. It is put into a combustion furnace to completely burn off the unburned matter, and it is turned into combustion ash that can be used as fly ash.
(考案が解決しようとする問題点)
従来は、サイクロン式集じん器で排ガスから分
離した石炭灰を、一度冷却して貯灰タンクに貯
め、ここから再燃焼炉に供給している。これは、
灰中の未燃炭素分が30〜40%であるので、温度が
高いまま搬送したり貯灰すると燃焼する危険があ
るためである。ところが、灰を冷却したのち再燃
焼炉で燃焼するのは、冷却による熱損失が大きい
こと、冷却剤として水が一般に使われるが、この
ユーテイリテイが大きいこと、また、冷却器や冷
却後の灰を運搬するコンベヤなどの設備費が大き
いなどの問題があつた。(Problems that the invention aims to solve) Conventionally, coal ash is separated from exhaust gas using a cyclone dust collector, is cooled and stored in an ash storage tank, and is then supplied to a reburning furnace. this is,
This is because the unburned carbon content in the ash is 30 to 40%, so there is a risk of combustion if the ash is transported or stored at a high temperature. However, burning the ash in a reburning furnace after cooling it is difficult because there is a large heat loss due to cooling, water is generally used as a coolant, but this utility is large, and it is difficult to use a cooler or to burn the ash after cooling. There were problems such as the high cost of equipment such as conveyors for transportation.
(問題点を解決するための手段)
本考案は上記従来技術の問題点を解決するた
め、サイクロン式集じん器で捕集された燃焼灰
を、その燃焼灰より低温の燃焼排ガスで、貯灰タ
ンクに搬送しながら冷却することにより、灰のも
つている顕熱を搬送ガスに回収し、この搬送ガス
により回収した熱エネルギーを、空気予熱器など
により有効に利用しようとするものである。(Means for Solving the Problems) In order to solve the above-mentioned problems of the prior art, the present invention aims to store combustion ash collected by a cyclone dust collector using combustion exhaust gas that is lower temperature than the combustion ash. By cooling the ash while transporting it to a tank, the sensible heat of the ash is recovered into a carrier gas, and the thermal energy recovered by this carrier gas is used effectively in an air preheater or the like.
すなわち、本考案は、流動層燃焼炉と、該炉か
ら排出された燃焼排ガスより固形灰分を分離する
分離装置と、固形灰分を分離された排ガスを通過
させてその熱エネルギーを回収する空気予熱器
と、この熱回収された排ガスを外気に排出する排
出装置よりなる流動層燃焼装置において、前記分
離装置の後流の排ガス通路部から、排ガスの一部
をバイパスさせるバイパス管路を分岐し、該バイ
パス管路には排ガス昇圧通風機と、昇圧後の排ガ
スを前記分離装置の灰取出し装置に導く管路と、
前記灰取出し装置から取り出された灰を前記排ガ
スで搬送して、灰タンクに送る管路とを設け、か
つ該灰タンクにおいて灰と分離された排ガスを前
記空気予熱器に供給する管路を設けたことを特徴
とする。 That is, the present invention includes a fluidized bed combustion furnace, a separator that separates solid ash from the combustion exhaust gas discharged from the furnace, and an air preheater that passes the exhaust gas from which the solid ash has been separated and recovers its thermal energy. In a fluidized bed combustion apparatus comprising an exhaust device for discharging the heat-recovered exhaust gas to the outside air, a bypass pipe is branched from the exhaust gas passage downstream of the separation device to bypass a part of the exhaust gas, and the exhaust gas is bypassed. The bypass pipe line includes an exhaust gas pressurization fan, and a pipe line that leads the pressurized exhaust gas to the ash removal device of the separation device.
A pipe line is provided for conveying the ash taken out from the ash extraction device using the exhaust gas and sending it to an ash tank, and a pipe line is provided for supplying the exhaust gas separated from the ash in the ash tank to the air preheater. It is characterized by:
(考案の実施例)
第1図は本考案の一実施例を示す流動層燃焼装
置の系統図である。流動層式主燃焼炉1におい
て、空気室1aの上部に設けた空気分散板1bよ
り供給された空気により、その上方の流動媒体が
流動層1cを形成する。流動層に供給された石炭
粒子12は層中で燃焼しながら、空塔部1d、煙
道3aを経て燃焼排ガスに同伴され、未燃分を含
んだ灰としてサイクロン式集じん器3で捕集され
る。(Embodiment of the invention) FIG. 1 is a system diagram of a fluidized bed combustion apparatus showing an embodiment of the invention. In the fluidized bed main combustion furnace 1, the air supplied from the air distribution plate 1b provided at the upper part of the air chamber 1a causes the fluidized medium above the air to form a fluidized bed 1c. The coal particles 12 supplied to the fluidized bed are burned in the bed and are entrained in the combustion exhaust gas through the empty column 1d and the flue 3a, and are collected by the cyclone dust collector 3 as ash containing unburned components. be done.
灰分を分離された燃焼排ガスは煙道3bを通つ
て空気予熱器4に入る。ここで排ガスの熱エネル
ギーは、主燃焼炉1や再燃焼炉2に供給される燃
焼用空気を加熱するのに用いられる。燃焼排ガス
は、その後、電気集じん器5に入り微細な灰分を
捕集除去されたのち、誘引通風機6を経て煙突1
3から大気に放出される。 The combustion exhaust gas from which the ash content has been separated enters the air preheater 4 through the flue 3b. Here, the thermal energy of the exhaust gas is used to heat combustion air supplied to the main combustion furnace 1 and the reburning furnace 2. The combustion exhaust gas then enters an electrostatic precipitator 5 to collect and remove fine ash, and then passes through an induced draft fan 6 to the chimney 1.
3 is released into the atmosphere.
第1図の実施例では、誘引通風機6を出た排ガ
スの一部はバイパス7aより分岐し、昇圧通風機
7で昇圧され、バイパス7b、弁7cを経てベン
チユリ式灰取出装置7dに到り、サイクロン式集
じん器3のホツパーに貯められた灰を取り出しつ
つ管路8aを経てサイクロン分離器8まで灰を搬
送される。 In the embodiment shown in FIG. 1, a part of the exhaust gas exiting the induced draft fan 6 is branched from the bypass 7a, is boosted in pressure by the boost draft fan 7, and reaches the bench lily type ash removal device 7d via the bypass 7b and the valve 7c. While taking out the ash stored in the hopper of the cyclone type dust collector 3, the ash is transported to the cyclone separator 8 via the pipe 8a.
サイクロン分離器8で、灰分を分離したのちの
排ガスは、管路8bに合流する。サイクロン分離
器8で分離された灰は灰タンク9に貯灰される。 After the ash is separated in the cyclone separator 8, the exhaust gas flows into the pipe line 8b. The ash separated by the cyclone separator 8 is stored in an ash tank 9.
昇圧通風機を出た燃焼排ガスは酸素含有率が低
いので、灰取出し装置7から管路8aを経て灰を
搬送する場合、灰が燃焼する恐れがなく、灰タン
ク9も空気と遮断されるため、同タンク内で灰が
燃焼する恐れもない。 Since the combustion exhaust gas leaving the booster ventilator has a low oxygen content, when the ash is transported from the ash removal device 7 through the pipe 8a, there is no risk of the ash being burned, and the ash tank 9 is also isolated from the air. , there is no risk of ash burning in the same tank.
また、搬送に用いたバイパス7b中の燃焼排ガ
スの温度は100〜130℃であるが、高温の燃焼灰を
搬送中に約200℃に昇温され、煙道3bにおいて、
サイクロン分離器3から流れてきた排ガスと合流
する。この混合ガスは空気予熱器にて燃焼用空気
を加熱する。これにより熱回収が行われる。 In addition, the temperature of the combustion exhaust gas in the bypass 7b used for conveyance is 100 to 130°C, but the temperature is increased to about 200°C while conveying the high-temperature combustion ash, and in the flue 3b,
It merges with the exhaust gas flowing from the cyclone separator 3. This mixed gas heats the combustion air in the air preheater. This performs heat recovery.
なお、前記実施例では誘引通風機6を出たあと
排ガスをバイパスさせたが、第1図の点線で示す
ように空気予熱器4の前から燃焼排ガスの一部を
分岐し、バイパス7a′より昇圧通風機7にバイパ
スさせることも可能である。その後の動作は前記
実施例と同様である。この場合は、誘引通風機6
を通過する排ガス量が減少するので、同通風機を
小型の設備とすることができる。 In the above embodiment, the exhaust gas was bypassed after exiting the induced draft fan 6, but as shown by the dotted line in FIG. It is also possible to bypass the boost fan 7. The subsequent operation is similar to that of the previous embodiment. In this case, induced draft fan 6
Since the amount of exhaust gas passing through the ventilator is reduced, the ventilator can be made into a small-sized equipment.
第1図の実施例において、灰タンク9に貯めら
れた灰を再燃焼炉2に供給するには、排ガスをバ
イパス7bから分岐した管路11、弁11aを経
で灰取出し装置11bに供給し、灰タンク9中の
灰を管路10を通して再燃焼炉2に供給する。 In the embodiment shown in FIG. 1, in order to supply the ash stored in the ash tank 9 to the reburning furnace 2, the exhaust gas is supplied to the ash removal device 11b via a pipe line 11 branched from the bypass 7b and a valve 11a. , the ash in the ash tank 9 is fed to the reburning furnace 2 through a line 10.
第2図は主燃焼炉1および再燃焼炉2に流動媒
体を補充する構成を示したものである。誘引通風
機6を出た排ガスの一部をバイパスさせ、昇圧通
風機7′で昇圧したのち管路11′、弁11a′を経
てベンチユリ式流動媒体取出し装置11b′に供給
し、ここで常温の流動媒体を煙突入口の排ガスで
管路10′,10a′,10b′を経て主燃焼炉1お
よび再燃焼炉2に搬送することにより、搬送中に
流動媒体が加熱される。したがつて、その分だけ
煙突から排出する排ガスの熱エネルギーを回収す
ることになり、第1図に示した実施例と併せて実
施すれば熱回収効果をさらに促進することができ
る。 FIG. 2 shows a configuration for replenishing the main combustion furnace 1 and the reburning furnace 2 with a fluidized medium. A part of the exhaust gas exiting the induced draft fan 6 is bypassed, and the pressure is increased by the pressure boost draft fan 7', and then supplied to the bench lily type fluidized medium extraction device 11b' through the pipe 11' and the valve 11a', where it is heated to room temperature. By conveying the fluidized medium with the exhaust gas from the smoke inlet via the pipes 10', 10a', 10b' to the main combustion furnace 1 and the reburning furnace 2, the fluidized medium is heated during the conveyance. Therefore, the thermal energy of the exhaust gas discharged from the chimney will be recovered accordingly, and if implemented in conjunction with the embodiment shown in FIG. 1, the heat recovery effect can be further promoted.
(考案の効果)
本考案を実施することにより、流動層燃焼装置
から排出される灰分を適切に冷却しつつその熱エ
ネルギーを回収するとともに、灰タンク内での灰
の燃焼を防止することができる。(Effects of the invention) By implementing the invention, it is possible to appropriately cool the ash discharged from the fluidized bed combustion equipment and recover its thermal energy, and to prevent the ash from being burned in the ash tank. .
第1図は本考案の一実施例を説明するための図
面、第2図は流動媒体を燃焼排ガスを使つて主燃
焼炉および再燃焼炉で搬送する実施説明図であ
る。
1……流動層式主燃焼炉、2……再燃焼炉、3
……分離装置、4……空気予熱器、6……誘引通
風機、7a,7a′,7b……排ガスバイパス管
路、7……昇圧通風機、7d……分離装置の灰取
出し装置、8……灰ホツパーの灰分離装置、8a
……灰の搬送管路、8b……排ガス管路、9……
灰タンク、10……灰の搬送管路、12……燃料
供給装置、13……煙突。
FIG. 1 is a diagram for explaining one embodiment of the present invention, and FIG. 2 is an explanatory diagram of an implementation in which a fluidized medium is conveyed through a main combustion furnace and a reburning furnace using combustion exhaust gas. 1...Fluidized bed main combustion furnace, 2...Reburning furnace, 3
... Separation device, 4 ... Air preheater, 6 ... Induced draft fan, 7a, 7a', 7b ... Exhaust gas bypass pipe, 7 ... Boosting draft fan, 7d ... Ash removal device of separation device, 8 ...Ash hopper ash separation device, 8a
...Ash conveyance pipe, 8b...Exhaust gas pipe, 9...
Ash tank, 10...Ash conveyance pipe, 12...Fuel supply device, 13...Chimney.
Claims (1)
スより固形灰分を分離する分離装置と、固形灰分
を分離された排ガスを通過させてその熱エネルギ
ーを回収する空気予熱器と、この熱回収された排
ガスを外気に排出する排出装置よりなる流動層燃
焼装置において、前記分離装置の後流の排ガス通
路部から、排ガスの一部をバイパスさせるバイパ
ス管路を分岐し、該バイパス管路には排ガス昇圧
通風機と、昇圧後の排ガスを前記分離装置の灰取
出し装置に導く管路と、前記灰取出し装置から取
り出された灰を前記排ガスで搬送して、灰タンク
に送る管路とを設け、かつ該灰タンクにおいて灰
と分離された排ガスを前記空気予熱器に供給する
管路を設けたことを特徴とする流動層燃焼装置。 A fluidized bed combustion furnace, a separator that separates solid ash from the combustion exhaust gas discharged from the furnace, an air preheater that passes the exhaust gas from which the solid ash has been separated and recovers its thermal energy, and an air preheater that recovers the heat energy. In a fluidized bed combustion apparatus comprising an exhaust device for discharging waste gas to the outside air, a bypass pipe for bypassing a part of the exhaust gas is branched from an exhaust gas passage downstream of the separator, and the bypass pipe is provided with a bypass pipe for bypassing a part of the waste gas. A booster ventilator, a pipe line that leads the pressurized exhaust gas to the ash removal device of the separation device, and a pipe line that transports the ash taken out from the ash removal device with the exhaust gas and sends it to the ash tank, A fluidized bed combustion apparatus, further comprising a pipe line for supplying exhaust gas separated from ash in the ash tank to the air preheater.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP10615585U JPH0238172Y2 (en) | 1985-07-11 | 1985-07-11 |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP10615585U JPH0238172Y2 (en) | 1985-07-11 | 1985-07-11 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6218512U JPS6218512U (en) | 1987-02-04 |
| JPH0238172Y2 true JPH0238172Y2 (en) | 1990-10-16 |
Family
ID=30981256
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP10615585U Expired JPH0238172Y2 (en) | 1985-07-11 | 1985-07-11 |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0238172Y2 (en) |
-
1985
- 1985-07-11 JP JP10615585U patent/JPH0238172Y2/ja not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6218512U (en) | 1987-02-04 |
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