JPH0550324B2 - - Google Patents

Info

Publication number
JPH0550324B2
JPH0550324B2 JP59234878A JP23487884A JPH0550324B2 JP H0550324 B2 JPH0550324 B2 JP H0550324B2 JP 59234878 A JP59234878 A JP 59234878A JP 23487884 A JP23487884 A JP 23487884A JP H0550324 B2 JPH0550324 B2 JP H0550324B2
Authority
JP
Japan
Prior art keywords
dust
containing gas
gas
cylinder
partition wall
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 - Lifetime
Application number
JP59234878A
Other languages
Japanese (ja)
Other versions
JPS61114709A (en
Inventor
Noryuki Oda
Haruo Watanabe
Toshihiro Morishita
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.)
AGC Inc
Original Assignee
Asahi Glass Co Ltd
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 Asahi Glass Co Ltd filed Critical Asahi Glass Co Ltd
Priority to JP59234878A priority Critical patent/JPS61114709A/en
Publication of JPS61114709A publication Critical patent/JPS61114709A/en
Publication of JPH0550324B2 publication Critical patent/JPH0550324B2/ja
Granted legal-status Critical Current

Links

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、含塵ガス発生源装置からの含塵ガス
の処理方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to a method for processing dust-containing gas from a dust-containing gas generation source device.

[従来の技術] 第4図に示すような、通気性多孔質筒を用い
る含塵ガスの除塵装置は従来より知られていた
(例えば特開昭58−3620参照)。すなわち第4図に
おいて、複数の通気性多孔質体からなる筒11
は下端を閉じられ、上端を開かれて鉛直に並置さ
れている。筒11の上端はその外側を管板71
により気密に支持されて中部缶体22内に収容さ
れている。中部缶体22の胴部には含塵ガス入口
31が、下部缶体23には粉塵切出し弁51を備
えた粉塵取出し口52が、上部缶体21には清浄
ガス出口41が、それぞれ設けられている。
[Prior Art] A dust removal device for dust-containing gas using a permeable porous cylinder as shown in FIG. 4 has been known for some time (see, for example, Japanese Patent Laid-Open No. 58-3620). That is, in FIG. 4, a cylinder 11 made of a plurality of breathable porous bodies
are vertically juxtaposed, closed at the bottom and open at the top. The upper end of the tube 11 has its outer side connected to the tube plate 71.
It is housed in the middle can body 22 while being airtightly supported. A dust-containing gas inlet 31 is provided in the body of the middle can 22, a dust outlet 52 equipped with a dust cutoff valve 51 is provided in the lower can 23, and a clean gas outlet 41 is provided in the upper can 21. ing.

含塵ガス発生源装置下流からの含塵ガスが含塵
ガス入口31より供給されると、含塵ガスは各
筒11の外部空間に入り、筒11の内外の圧力
差により清浄ガスが筒11の筒壁を通過し、
筒11内に出て、清浄ガス出口41より系外に取
り出される。
When dust-containing gas from downstream of the dust-containing gas generation source device is supplied from the dust-containing gas inlet 31, the dust-containing gas enters the external space of each cylinder 11, and clean gas flows into the cylinder 11 due to the pressure difference between the inside and outside of the cylinder 11. passes through the cylinder wall of
The gas exits into the cylinder 11 and is taken out of the system through the clean gas outlet 41.

一方、筒11の外壁で通過を阻止された粉塵
は、時間の経過とともに筒11の外壁上に堆積
し、ある場合にはその一部が落下して下部缶体2
3に集められるとともに、堆積した粉塵は過層
を形成し、含塵ガスの精密過が行なわれる。
On the other hand, the dust that is blocked from passing by the outer wall of the cylinder 11 accumulates on the outer wall of the cylinder 11 over time, and in some cases, a part of it falls and falls into the lower can body.
3, the accumulated dust forms an overlayer, and precise filtration of the dust-containing gas is performed.

堆積した粉塵の層厚が増すと筒11の内外の
圧力差が大きくなるため、一定の時間間隔毎の逆
洗などにより、これらの粉塵を除去して通気抵抗
を少なくすることが一般的に行なわれている。
As the layer thickness of the accumulated dust increases, the pressure difference between the inside and outside of the cylinder 11 increases, so it is generally done to reduce ventilation resistance by removing this dust by backwashing at regular intervals, etc. It is.

[発明が解決しようとする問題点] しかし、従来から使用されているこのような含
塵ガス処理装置は、大型で工業規模のものとして
はこれまで実用化されていない。この理由として
は以下いのようなことが挙げられる。
[Problems to be Solved by the Invention] However, such conventionally used dust-containing gas treatment apparatuses have not been put to practical use on a large, industrial scale. Reasons for this include the following.

まず、高温のあるいは腐食性の含塵ガスを処理
するためには例えばセラミツク製の筒が望まし
いが、長尺のセラミツク筒は成形も焼成も容易
でなく、かつ重量も大きく吊下げ構造も複雑にな
る。これに代えて短尺のセラミツク筒を長手方
向に積み重ねて用いることも考えられるが、筒
を支持する腕木または支持体を含塵ガス流路内に
設けねばならず、こうした腕木などの上に粉塵が
堆積してその落下を妨げるなどの難点もあつて、
筒を長尺にしがたく、したがつて単位面積あた
りの処理ガス量が小さく、大風量の含塵ガスの処
理に適しない。
First, to treat high-temperature or corrosive dust-containing gases, it is desirable to use ceramic tubes, but long ceramic tubes are not easy to shape or fire, are heavy, and require a complicated hanging structure. Become. Alternatively, short ceramic tubes may be stacked longitudinally and used, but arms or supports for supporting the tubes would have to be provided in the dust-containing gas flow path, and dust would accumulate on these arms. There are also disadvantages such as the accumulation of material that prevents it from falling.
It is difficult to make the cylinder long, so the amount of gas to be processed per unit area is small, and it is not suitable for processing dust-containing gas with a large air volume.

ついで粉塵濃度の大きい含塵ガスの場合、一部
の粗大粉塵を除く他の全ての粉塵が筒11の外
壁に吸いつけられるため、筒11の内外の圧力
差の増大速度が大きく、逆洗を頻繁に行なう必要
があつて逆洗用送風機の動力費がかさむ上に、逆
洗時の処理能力ダウンを考慮して余分の能力を持
つた設備としておく必要がある。
Next, in the case of a dust-containing gas with a high dust concentration, all the dust except for some coarse dust is attracted to the outer wall of the cylinder 11, so the pressure difference between the inside and outside of the cylinder 11 increases at a high rate, making it difficult to backwash. This needs to be done frequently, which increases the cost of powering the backwashing blower, and it is also necessary to provide equipment with extra capacity to take into account the reduction in processing capacity during backwashing.

さらに第4図に示すような装置にあつては通常
操業時は粉塵切出し弁51は閉じられており、粉
塵取出口52の上に粉塵が堆積してくる。ある程
度の量の粉塵が堆積すると、装置の操業を停止
し、粉塵切出し弁51を開いて粉塵をとり出さね
ばならず、装置の操業がバツチ式にならざるを得
ず、その上、とり出された粉塵が大気中に飛散す
る恐れがある。また装置の操業を停止しない場合
でも、堆積粉塵をとり出し時には間欠的に非定常
操業となり、かつ、その際に粉塵と含塵ガスとが
大気中に飛散放出される問題がある。
Furthermore, in the case of the apparatus shown in FIG. 4, the dust extraction valve 51 is closed during normal operation, and dust accumulates on the dust extraction port 52. When a certain amount of dust accumulates, it is necessary to stop the operation of the device and open the dust extraction valve 51 to take out the dust, forcing the operation of the device to be batch-type. Dust may be dispersed into the atmosphere. Further, even when the operation of the apparatus is not stopped, there is a problem that the operation becomes intermittently unsteady when the accumulated dust is taken out, and the dust and dust-containing gas are scattered and released into the atmosphere at that time.

また含塵ガスが高温、高圧、大気圧より低い圧
力、有毒性、あるいは可燃性などであり、または
粉塵が有毒性、可燃性、発火性、あるいは大気と
反応して変質しやすいなどである場合にはきわめ
て複雑な粉塵とり出し機構を必要としていた。
In addition, if the dust-containing gas is high temperature, high pressure, pressure lower than atmospheric pressure, toxic, or flammable, or if the dust is toxic, flammable, flammable, or easily deteriorates by reacting with the atmosphere, etc. This required an extremely complex dust removal mechanism.

本発明は従来技術の上述のような問題点を解決
する含塵ガスの処理方法を提供するにある。
The present invention provides a method for treating dust-containing gas that solves the above-mentioned problems of the prior art.

[問題点を解決するための手段と作用] 本発明は、含塵ガス発生源装置下流からの含塵
ガスを、概ね鉛直に配設された通気性多孔質の隔
壁で区画された空間の上部より送入し、清浄ガス
を該隔壁を通過させて取り出すとともに、高含塵
ガスを該隔壁を通過させることなく該空間の下部
より取り出し、取り出した該高含塵ガスを前記含
塵ガス発生源装置上流に還流せしめることを特徴
とする含塵ガスの処理方法である。
[Means and effects for solving the problems] The present invention directs dust-containing gas from downstream of a dust-containing gas generation source device to the upper part of a space partitioned by a permeable porous partition wall disposed approximately vertically. The clean gas is passed through the partition wall and taken out, and the high dust-containing gas is taken out from the lower part of the space without passing through the partition wall, and the high dust-containing gas is sent to the dust-containing gas generation source. This is a method for treating dust-containing gas, which is characterized by refluxing the dust-containing gas upstream of the device.

以下、本発明を図面を参照しながら詳細に説明
する。
Hereinafter, the present invention will be explained in detail with reference to the drawings.

第1図および第2図からわかるように、複数の
中空円筒状かつ上下端とも開放されている筒1
0がおおむね鉛直に並置され、各筒10の上下
端をそれぞれ管板70,75で気密に支持されて
中部缶体25内に収容されている。各筒10は
例えばコージエライト質セラミツク製の通気性多
孔質焼結体からなる。
As can be seen from FIGS. 1 and 2, a plurality of hollow cylindrical tubes 1 with open upper and lower ends
0 are arranged approximately vertically side by side, and the upper and lower ends of each cylinder 10 are airtightly supported by tube plates 70 and 75, respectively, and housed in the middle can body 25. Each tube 10 is made of an air-permeable porous sintered body made of cordierite ceramic, for example.

上部缶体26の頂部には含塵ガス入口30が、
下部缶体27の底部には分離された粉塵および高
含塵ガスを取り出す高含塵ガス出口50が、中部
缶体25の胴部には清浄ガス出口40が、それぞ
れ設けてあり、これら全体として集塵装置60を
構成する。
A dust-containing gas inlet 30 is provided at the top of the upper can body 26.
A high dust content gas outlet 50 is provided at the bottom of the lower can body 27 to take out separated dust and high dust content gas, and a clean gas outlet 40 is provided at the body of the middle can body 25. A dust collector 60 is configured.

含塵ガス発生源装置である高炉65の下流であ
る炉頂からの高温高圧(例えば約120℃、ゲージ
圧1〜3気圧)の、かつ有毒な一酸化炭素を多含
する含塵ガスは配管を通じて含塵ガス入口30に
供給される。含塵ガスは各筒10内に高速で流
入し、筒10内外の圧力差により、清浄ガス
筒10の管壁を通過して筒10外に出て、清浄
ガス出口40に取り出される。
The dust-containing gas, which is high temperature and high pressure (e.g., approximately 120°C, gauge pressure 1 to 3 atm) and contains a lot of toxic carbon monoxide, is discharged from the top of the blast furnace downstream of the blast furnace 65, which is the dust-containing gas generation source device. The dust-containing gas is supplied to the inlet 30 through the dust-containing gas inlet 30. The dust-containing gas flows into each cylinder 10 at high speed, and due to the pressure difference between the inside and outside of the cylinder 10, it passes through the pipe wall of the clean gas cylinder 10, exits the cylinder 10, and is taken out to the clean gas outlet 40.

一方、筒10の内壁で通過を阻止された粉塵
は、含塵ガスの下方に向かう流れの粘性と高速の
ガス流によつて増速され、慣性により下方に高速
で沈降する主に粗粒粉塵の壁面への衝突による削
り落し効果により落下せしめられ、また粉塵相互
が衝突して凝集し、粉塵自身の慣性と重力により
落下して、下部缶体27内に入る。この間、粉塵
の一部は筒10の内壁近傍に凝集付着して粉塵
過層を形成するとともに、粉塵の大部分は落下
して連続的に含塵ガスの集塵が進められる。
On the other hand, the dust that is blocked from passing by the inner wall of the cylinder 10 is accelerated by the viscosity of the downward flow of the dust-containing gas and the high-speed gas flow, and is mainly coarse-grained dust that settles downward at high speed due to inertia. The particles fall due to the scraping effect caused by the collision with the wall surface, and the particles collide with each other and aggregate, and fall due to the inertia and gravity of the particles themselves and enter the lower can body 27. During this time, a part of the dust coagulates and adheres to the vicinity of the inner wall of the cylinder 10 to form a dust overlayer, and most of the dust falls, and the dust-containing gas is continuously collected.

高含塵ガス出口50が閉じられていると、高含
塵ガス出口50周辺には粉塵が堆積してくるが、
同時に下部缶体27内のガスは流れず、したがつ
て筒10の下端周辺におけるガスの流速もゼロ
となり、この部位の筒10内には粉塵のよる削
り落し効果などが充分に作用せず、したがつて
筒10内壁に粉塵層が厚く付着して含塵ガスの
過処理能力が低下する。
If the high dust content gas outlet 50 is closed, dust will accumulate around the high dust content gas outlet 50.
At the same time, the gas inside the lower can body 27 does not flow, and therefore the gas flow velocity around the lower end of the cylinder 10 also becomes zero, and the scraping effect of dust does not work sufficiently in the cylinder 10 at this part. Therefore, a thick layer of dust adheres to the inner wall of the cylinder 10, reducing the ability to over-process dust-containing gas.

したがつて本発明においては高含塵ガス出口5
0を開いて、連続的に下部缶体27内のガスを取
り出すようにされる。このガスは含塵ガス入口3
0から送入される含塵ガスに比べて粉塵濃度が相
対的に高められた高含塵ガスとなつている。この
高含塵ガスが前述の筒10内を落下してきた粉
塵を含有していることはいうまでもない。
Therefore, in the present invention, the high dust-containing gas outlet 5
0 is opened, and the gas in the lower can body 27 is continuously taken out. This gas is dust-containing gas inlet 3
This is a high dust-containing gas with a relatively high dust concentration compared to the dust-containing gas fed in from zero. It goes without saying that this highly dust-containing gas contains the dust that has fallen inside the cylinder 10 mentioned above.

ついで高含塵ガス出口50から取り出された高
含塵ガスは配管を通り、送風機66を経て、高炉
65の原料投入口に還流せしめられる。一方、送
入された含塵ガスの大部分はほとんど温度、圧力
を低下せしめられることなく清浄ガスとなつて清
浄ガス出口40から取り出され、配管を経て動力
回収タービン67に導かれ、ここで動力回収され
るとともにほぼ大気圧まで減圧され、図示せぬガ
スホルダに至る。
Next, the highly dusty gas taken out from the highly dusty gas outlet 50 passes through the pipe, passes through the blower 66, and is refluxed to the raw material input port of the blast furnace 65. On the other hand, most of the introduced dust-containing gas becomes clean gas with almost no drop in temperature or pressure and is taken out from the clean gas outlet 40, guided through piping to the power recovery turbine 67, where the power is While being collected, the pressure is reduced to approximately atmospheric pressure, and the gas reaches a gas holder (not shown).

第3図は本発明を重質油接触分解装置の再生塔
に適用した例を示す。再生塔からは例えばシリカ
アルミナ触媒などの飛散触媒を含む排ガス(例え
ば約650℃、ゲージ圧約2気圧)が発生する。従
来、この再生塔排ガスは再生塔内の第1段サイク
ロン、第2段サイクロンを経た後、再生塔外に設
けられた第3段サイクロンで10ミクロン程度以上
の粉塵をほとんど除去され、動力回収タービンに
導かれて動力回収し、ほぼ大気圧まで減圧された
上で、さらに電気集塵機に通されるのが一般的で
あつた。
FIG. 3 shows an example in which the present invention is applied to a regeneration tower of a heavy oil catalytic cracker. The regeneration tower generates exhaust gas (eg, about 650° C., gauge pressure of about 2 atmospheres) containing a scattered catalyst such as a silica-alumina catalyst. Conventionally, this regeneration tower exhaust gas passes through the first stage cyclone and second stage cyclone inside the regeneration tower, and then the third stage cyclone installed outside the regeneration tower, where most of the dust of about 10 microns or more is removed, and then the power recovery turbine It was common for the gas to be guided into the air, recover the power, reduce the pressure to almost atmospheric pressure, and then pass through an electrostatic precipitator.

本発明の方法を適用すると、再生塔68内には
第1段サイクロン、第2段サイクロンともなくさ
れて、再生塔排ガスは直接に集塵装置60(第1
図、第2図で示したと同様の装置なので第3図で
は略示する)に導かれる。得られる清浄ガスは動
力回収タービン67に導かれて動力回収されたの
ち、電気集塵機などによる追加の集塵を必要とす
ることなく、図示せぬ煙突から排出される。一
方、集塵装置60底部からの高含塵ガスは配管を
通り、送風機66を経て、再生塔68の再生塔排
ガス出口よりは上流にあたる再生塔流動層内に還
流される。なお直接に再生塔68に還流するかわ
りに、これと配管で連接されている図示せぬ反応
塔系に還流してもよく、これも本発明に包含され
る。
When the method of the present invention is applied, the first stage cyclone and the second stage cyclone are eliminated in the regeneration tower 68, and the regeneration tower exhaust gas is directly supplied to the dust collector 60 (the first stage cyclone).
Since the device is similar to that shown in FIG. 2, it is omitted in FIG. 3). The resulting clean gas is guided to a power recovery turbine 67 for power recovery, and is then discharged from a chimney (not shown) without the need for additional dust collection using an electrostatic precipitator or the like. On the other hand, the highly dust-containing gas from the bottom of the dust collector 60 passes through the pipe, passes through the blower 66, and is refluxed into the regeneration tower fluidized bed located upstream of the regeneration tower exhaust gas outlet of the regeneration tower 68. Note that instead of being directly refluxed to the regeneration column 68, it may be refluxed to a reaction column system (not shown) connected to this via piping, and this is also included in the present invention.

上記説明においては通気性多孔質の隔壁の形状
が中空円筒状の例を示した。かかる形状は製作が
比較的容易であり、かつ、強度も大きく、隔壁両
側の圧力差に耐えやすい利点があるが、例えば隔
壁を中空角筒状としたり、平板状としてもよい。
また第1図においては上端から下端まで一体物と
なつた筒を示したが、長手方向に適宜結合した
ものであつてもよいし、必要に応じて上下端のみ
ならず、長手方向の中央部に管板を増設してもよ
い。
In the above description, an example is shown in which the shape of the air-permeable porous partition wall is a hollow cylinder. Such a shape is relatively easy to manufacture, has high strength, and has the advantage of being able to easily withstand the pressure difference on both sides of the partition wall, but the partition wall may be formed into a hollow rectangular tube shape or a flat plate shape, for example.
In addition, although FIG. 1 shows a cylinder that is integrated from the upper end to the lower end, it may be joined as appropriate in the longitudinal direction. A tube plate may be added to the

隔壁の材質としては焼結金属なども採用できる
が、高温あるいは腐食性の含塵ガスから有効に清
浄ガスを回収し、あるいは有効にエネルギ回収を
図るためにはセラミツク製であることが望まし
く、なかでもコージエライト、ムライト、溶融シ
リカ、アルミナ、シヤモツト、チタン酸アルミニ
ウム、炭化ケイ素、窒化ケイ素などのセラミツク
製であると耐熱性、耐食性、低熱膨張性、耐熱衝
撃性などの点で好ましい。
Although sintered metal can be used as the material for the partition wall, ceramic is preferable in order to effectively recover clean gas from high-temperature or corrosive dust-containing gas, or to effectively recover energy. However, it is preferable to use ceramics such as cordierite, mullite, fused silica, alumina, siyamoto, aluminum titanate, silicon carbide, and silicon nitride in terms of heat resistance, corrosion resistance, low thermal expansion, and thermal shock resistance.

隔壁で区画された空間の上端部における含塵ガ
スの下向き流速は一般に大きいことが粗粒粉塵な
どによる削り落し効果の上で好ましく、2m/s
以上、特には5m/s以上が望まれる。しかし余
り高速であると、隔壁自体までも削られてしまう
上、動力損も増大するので、100m/s以下、特
には50m/s以下が望まれる。
It is generally preferable that the downward flow velocity of the dust-containing gas at the upper end of the space partitioned by the partition wall be high in terms of the scraping effect of coarse dust, and is 2 m/s.
In particular, a speed of 5 m/s or more is desired. However, if the speed is too high, the partition wall itself will be scraped and power loss will also increase, so a speed of 100 m/s or less, particularly 50 m/s or less is desired.

隔壁で区画された空間の下端部における含塵ガ
スの下向き流速が余りに小さすぎると削り落し効
果が充分でなくなるので、好ましくはこれは0.3
m/s以上とされる。
If the downward flow velocity of the dust-containing gas at the lower end of the space partitioned by the partition wall is too low, the scraping effect will not be sufficient, so it is preferably 0.3
m/s or more.

本発明において高含塵ガス、含塵ガス、清浄ガ
スとは粉塵濃度に関して相対的な概念であつて、
上記した順に粉塵濃度が低下しているものを指
し、絶対的な特定の粉塵濃度を規定するものでは
ない。
In the present invention, high dust-containing gas, dust-containing gas, and clean gas are relative concepts with respect to dust concentration.
This refers to those in which the dust concentration decreases in the order listed above, and does not specify an absolute specific dust concentration.

また含塵ガス発生源装置とは高炉、重質油接触
分解装置再生塔に限定されるものではない。また
含塵ガス発生源装置下流とは同装置含塵ガスが排
出される部位を示し、これに対して同装置上流と
は上述した同装置下流より上流に位置する部位で
あつて、好ましくは粉体状もしくは流体状の原材
料が同装置に供給される部位である。
Further, the dust-containing gas generation source device is not limited to a blast furnace or a heavy oil catalytic cracker regeneration tower. Furthermore, the term "downstream of the dust-containing gas generation source device" refers to the part from which the dust-containing gas is discharged, whereas the term "upstream of the apparatus" refers to the part located upstream of the above-mentioned downstream part of the apparatus, and is preferably a part located upstream from the downstream part of the apparatus. This is the part where raw materials in physical or fluid form are supplied to the device.

[効果] このような本発明の処理方法においては、管板
75などの隔壁支持手段を含塵ガス流路側でな
く、清浄ガス流路側に容易に設けられるので、か
かる支持手段に粉塵が堆積しない。また粉塵およ
び高速ガス流による削り落し効果が隔壁の上から
下まで全域にわたつて有効に機能するようになる
ので隔壁面上に粉塵層が厚く形成されることがほ
とんどなくなり、したがつて従来技術に比べて逆
洗頻度をきわめて小さくできる。
[Effects] In the treatment method of the present invention, the partition support means such as the tube plate 75 can be easily provided on the clean gas flow path side instead of on the dust-containing gas flow path side, so that dust does not accumulate on the support means. . In addition, since the scraping effect of dust and high-speed gas flows effectively over the entire area from the top to the bottom of the partition wall, it is almost impossible for a thick dust layer to form on the partition wall surface. The frequency of backwashing can be significantly reduced compared to

さらに第1図の高炉を含塵ガス発生源装置とし
た場合にあつては、従来のバツチ式処理方法で
は、粉塵取出し時に危険な高温高圧の一酸化炭素
多含ガスも漏出して危険であり、あるいはこれを
防ぐために複雑なパージシステムを必要とした
が、本発明によれば、取扱いしにくい粉塵として
ではなく粉塵のほとんどを移送しやすい高含塵ガ
スとして扱える。さらにこれを系外に放出するこ
となく、高炉に還流するので高温高圧の一酸化炭
素多含ガスが漏出する危険もなくなる。
Furthermore, when the blast furnace shown in Figure 1 is used as a dust-containing gas generation source, the conventional batch treatment method is dangerous because dangerous high-temperature, high-pressure carbon monoxide-rich gas leaks out when dust is removed. However, according to the present invention, most of the dust can be treated as a highly dust-containing gas that is easy to transport, rather than as dust that is difficult to handle. Furthermore, since this gas is returned to the blast furnace without being released outside the system, there is no risk of leakage of high temperature, high pressure carbon monoxide-rich gas.

また第3図の重質油接触分解装置を含塵ガス発
生源装置とした場合にあつては、従来のバツチ式
処理方法では、かなりの量の飛散触媒が粉塵とし
て回収されながら、一つには取出し時に大気と接
触して触媒活性が変化し、再利用しがたいなどの
理由により廃棄されていたものが多かつたが、本
発明によれば、こうした触媒粉塵を容易に再使用
できる。
In addition, when the heavy oil catalytic cracking equipment shown in Figure 3 is used as a dust-containing gas generation source, in the conventional batch treatment method, a considerable amount of the scattered catalyst is recovered as dust, but it is However, according to the present invention, such catalyst dust can be easily reused.However, according to the present invention, such catalyst dust can be easily reused.

このように本発明によれば、含塵ガスを構成す
るガスまたは粉塵が人体への危険や高い化学的作
用(例えば可燃性とか発火性)あるいは高い物理
的作用(例えば高温とか高圧)を有する場合であ
つても格別の粉塵取出し機構を要することなく処
理できる上に、有用な粉塵を積極的に再利用する
こともできる。
As described above, according to the present invention, if the gas or dust constituting the dust-containing gas is dangerous to the human body, has a high chemical effect (for example, flammability or ignition), or has a high physical effect (for example, high temperature or high pressure), Even if it is, it can be treated without requiring a special dust removal mechanism, and useful dust can be actively reused.

さらにセラミツク製の隔壁を用いることによ
り、高温高圧のまま操業できるので、ベンチユリ
スクラバ、サイクロン、電気集塵機などからなる
複合集塵システムが不要となりうる上に、動力な
どのエネルギを有効に回収できる。
Furthermore, by using ceramic bulkheads, the system can be operated at high temperatures and pressures, making it possible to eliminate the need for a composite dust collection system consisting of a bench scrubber, cyclone, electrostatic precipitator, etc., and to effectively recover power and other energy.

そのうえ、従来のバツチ式処理方法では、粉塵
取出し時に粉塵のブリツジングがしばしば起きて
操業が不安定になつたり、粉塵切出し弁に粉塵が
かみ込んだり、ブリツジング防止のために下部缶
体のホツパ部の水平となす角度を大きくとる必要
があるなどの問題点があつた。しかるに本発明に
よれば、粉塵とガスとを同時にとりだすので、か
かるブリツジングやかみ込みがほとんど発生せ
ず、さらにホツパ部に前記角度も小さくでき、し
たがつて下部缶体の高さを小さく抑えることもで
きる。
Furthermore, in the conventional batch processing method, dust bridging often occurs during dust extraction, making operations unstable, dust gets stuck in the dust removal valve, and the hopper section of the lower can body is closed to prevent bridging. There were problems such as the need to make a large angle with the horizontal. However, according to the present invention, since dust and gas are taken out at the same time, such bridging and jamming hardly occur, and the angle at the hopper part can also be made small, so that the height of the lower can body can be kept small. You can also do it.

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

第1図は本発明の一実施例を、本発明に用いら
れる集塵装置の一例の縦断面図とともに示す説明
図、第2図は第1図における−線横断面図、
第3図は本発明の別の実施例を示す説明図、第4
図は従来例の集塵装置の縦断面図である。
FIG. 1 is an explanatory diagram showing an embodiment of the present invention together with a vertical cross-sectional view of an example of a dust collector used in the present invention, and FIG. 2 is a cross-sectional view taken along the - line in FIG.
FIG. 3 is an explanatory diagram showing another embodiment of the present invention, and FIG.
The figure is a longitudinal sectional view of a conventional dust collector.

Claims (1)

【特許請求の範囲】[Claims] 1 含塵ガス発生源装置下流からの含塵ガスを、
概ね鉛直に配設された通気性多孔質の隔壁で区画
された空間の上部より送入し、清浄ガスを該隔壁
を通過させて取り出すとともに、高含塵ガスを該
隔壁を通過させることなく該空間の下部より取り
出し、取り出した該高含塵ガスを前記含塵ガス発
生源装置上流に還流せしめることを特徴とする含
塵ガスの処理方法。
1 Dust-containing gas from downstream of the dust-containing gas generation source device,
The gas is introduced from the upper part of a space divided by a permeable porous partition wall arranged approximately vertically, and the clean gas is taken out by passing through the partition wall, and the highly dust-containing gas is removed without passing through the partition wall. A method for processing dust-containing gas, which comprises taking out the highly dust-containing gas from a lower part of the space and causing the extracted highly dust-containing gas to flow back upstream of the dust-containing gas generation source device.
JP59234878A 1984-11-09 1984-11-09 Treatment of dust-containing gas Granted JPS61114709A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59234878A JPS61114709A (en) 1984-11-09 1984-11-09 Treatment of dust-containing gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59234878A JPS61114709A (en) 1984-11-09 1984-11-09 Treatment of dust-containing gas

Publications (2)

Publication Number Publication Date
JPS61114709A JPS61114709A (en) 1986-06-02
JPH0550324B2 true JPH0550324B2 (en) 1993-07-28

Family

ID=16977736

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59234878A Granted JPS61114709A (en) 1984-11-09 1984-11-09 Treatment of dust-containing gas

Country Status (1)

Country Link
JP (1) JPS61114709A (en)

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5371375A (en) * 1976-12-08 1978-06-24 Schumacher Nihon Kk Filter for high pressure gas

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5371375A (en) * 1976-12-08 1978-06-24 Schumacher Nihon Kk Filter for high pressure gas

Also Published As

Publication number Publication date
JPS61114709A (en) 1986-06-02

Similar Documents

Publication Publication Date Title
EP0124863B1 (en) Method of treating dust-containing gas and apparatus thereof
US4973458A (en) Fluidized bed system for removing particulate contaminants from a gaseous stream
US4735635A (en) Apparatus and process for filtering high temperature gas streams
US4812149A (en) Hot inert gas purging for filter blowback process
WO1995032787A1 (en) Eliminating ash bridging in ceramic filters
US5282877A (en) Filtration device
EP0944422B1 (en) Hot gas filter and system assembly
ES2024814A6 (en) Vertically tiered particle filtering apparatus.
CN206198879U (en) A kind of fume dust remover
JPH0550324B2 (en)
EP2937130B1 (en) Device for removing entrained catalyst particulates from a gas
JPS59225721A (en) Dust collecting apparatus
JPH0352612A (en) Apparatus and method for separating solid substance from gas
JPH0679651B2 (en) Dust collector
JPS62168524A (en) Apparatus and method for filtering high temperature gas stream
JPH05345109A (en) High temperature gas filtering apparatus
JPS61268332A (en) Dust removal purifying apparatus
JPH0679650B2 (en) Dust collector
JP3971578B2 (en) Exhaust gas treatment equipment
JPH0746339Y2 (en) Dedusting / desulfurization equipment
JP3186639B2 (en) Ceramic ball for combustion gas purification
SU952296A1 (en) Filter for cleaning hot gases
JPH0356086B2 (en)
JPH0670817U (en) Dust removal equipment
SU590001A1 (en) Gas-purifying apparatus