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JP4507404B2 - Boiler flue gas treatment system - Google Patents

Boiler flue gas treatment system Download PDF

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Publication number
JP4507404B2
JP4507404B2 JP2000398033A JP2000398033A JP4507404B2 JP 4507404 B2 JP4507404 B2 JP 4507404B2 JP 2000398033 A JP2000398033 A JP 2000398033A JP 2000398033 A JP2000398033 A JP 2000398033A JP 4507404 B2 JP4507404 B2 JP 4507404B2
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JP
Japan
Prior art keywords
exhaust gas
gypsum
treatment system
magnesium hydroxide
flue 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 - Fee Related
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JP2000398033A
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Japanese (ja)
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JP2002191936A (en
Inventor
文彦 山口
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IHI Corp
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IHI Corp
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Description

【0001】
【発明の属する技術分野】
本発明は、ボイラから排出される排ガスに含まれる高無水硫酸(SO3 )を除去し、これを水酸化マグネシウム石膏法を用いて回収すると共にSO2 を除去するためのボイラ排煙処理システムに関するものである。
【0002】
【従来の技術】
従来、ボイラ排ガス中のSOx の除去は、SO2 については、吸収塔内で吸収液をスプレーし、排ガスと気液接触させてSO2 を吸収除去することがなされているが、この湿式脱硫や半乾式脱硫装置では、SO3 の吸収除去は不可能であり、これが大気に放出されると硫酸ミストによる紫煙の原因となる。
【0003】
そこで、SO3 については、煙道内にアルカリ剤を噴射してSO3 を吸収除去することがなされている。
【0004】
またSO2 の吸収剤として、Mg(OH)2 を用い、吸収酸化後、CaO又はCa(OH)2 を加えて副製品として石膏を回収するプロセスがある。
【0005】
【発明が解決しようとする課題】
しかしながら、高SO3 含有ガスの中和では、未反応CaO又はCa(OH)2 が、廃棄され、不経済となる問題がある。また水酸化マグネシウム石膏法では、補給剤としてCaO又はCa(OH)2 が別途必要となる問題がある。
【0006】
そこで、本発明の目的は、上記課題を解決し、排ガスからSO3 とSO2 とを除去するにおいて、吸収剤と補給剤を効率よく使用してシステムを簡素化できるボイラ排煙処理システムを提供することにある。
【0007】
【課題を解決するための手段】
上記目的を達成するために、請求項1の発明は、ボイラからの排ガスに粉末状の生石灰又は消石灰からなる吸収剤を添加して排ガス中のSO3 を吸収除去した後、そのボイラ排ガスを吸収剤と共に脱硫装置に導入し、その脱硫装置で水酸化マグネシウムを脱硫剤とするスラリと接触させてSO2 を吸収除去し、その脱硫剤と吸収剤とを熟成槽で置換反応させて石膏と水酸化マグネシウムにし、石膏を回収すると共に水酸化マグネシウムを脱硫剤として再利用するようにしたボイラ排煙処理システムである。
【0008】
請求項2の発明は、脱硫装置内で、SO2 を吸収して亜硫酸マグネシウムとなったスラリにエアを吹き込んで硫酸マグネシウムに酸化する請求項1記載のボイラ排煙処理システムである。
【0009】
請求項3の発明は、排ガス中のS分に対して当モル以上になるよう生石灰又は消石灰を添加し、未反応の生石灰又は消石灰を脱硫装置を介して熟成槽に補給剤として供給して脱硫後の硫酸マグネシウムと置換反応させる請求項1記載のボイラ排煙処理システムである。
【0010】
請求項4の発明は、熟成槽内での置換反応で生成した石膏と水酸化マグネシウムとをハイドロサイクロン等の石膏分離器で粒径分離して石膏と水酸化マグネシウムを分離する請求項2記載のボイラ排煙処理システムである。
【0011】
【発明の実施の形態】
以下、本発明の好適実施の形態を添付図面に基づいて詳述する。
【0012】
図1は、本発明のボイラ排煙処理システムの構成図を示したものである。
【0013】
図1において、10は、重油焚きの小型乃至中型のボイラで、そのボイラ10から排出される排ガスが脱硝装置11に流されて脱硝される。この部分の温度は300〜400℃である。
【0014】
この脱硝装置11と下流のガス−エアヒータ(GAH)12とを結ぶダクト13には、粉末状の生石灰(CaO)又は消石灰(Ca(OH)2 )からなる吸収剤を添加する吸収剤注入ライン14が接続される。
【0015】
ガス−エアヒータ12はダクト15を介してバグフィルタ式或いは電気集塵式の集じん機16に接続され、その集じん機16からの排ガスが煙突18より大気に放出されるようになっている。
【0016】
ガス−エアヒータ12の入口側のダクト13に注入する吸収剤としての生石灰、又は消石灰は、排ガス中の(SO2 +SO3 )量に対しての過剰量を見込んだ量例えばS分に対してCaが当モル以上になるよう添加する。
【0017】
この300〜400℃の温度範囲の排ガス中に生石灰又は消石灰の吸収剤を添加すると、下記中和反応に従って効率よく無水硫酸(SO3 )を吸収除去することができる。
【0018】
CaO + SO3 → CaSO4
又は、
Ca(OH)2 + SO3 → CaSO4 +H2
ガス−エアヒータ12で排ガスは、ボイラ燃焼用空気と熱交換されて温度が下げられて脱硫装置16に供給され、ライン17から供給された脱硫剤としての水酸化マグネシウムのスラリと接触され、排ガス中のSO2 が吸収除去されて煙突18から排気される。
【0019】
この場合、煙突18の排気の白煙化を防止するために、図には示していないが、脱硫装置16の前後にガス−ガスヒータを設置し、前段のガス−ガスヒータで脱硫装置16に流入する排ガスから熱回収し、後段のガス−ガスヒータで、排気する排ガスの飽和水蒸気温度以上に再加熱することで、白煙化を防止できる。すなわち、ガス−エアヒータ12を出た排ガスの温度が170℃とし、この排ガスを前段のガス−ガスヒータで、70〜80℃程度にして熱回収し、脱硫装置16で更に温度が下がり飽和蒸気となるが、これを後段のガス−ガスヒータで再加熱して、その排ガスの飽和水蒸気温度以上に加熱することで、煙突18から排気しても、飽和蒸気温度以下になることがないため白煙化を防止できる。
【0020】
なお、脱硫装置16と煙突18間に電気集塵機を設けてもよい。
【0021】
さて、脱硫装置16には、ライン17から水酸化マグネシウム(Mg(OH)2 を脱硫剤とするスラリが供給されて排ガスと気液接触される。
【0022】
この水酸化マグネシウムの粒径は1〜2μmであり、排ガス中のSO2 と下式のように反応して排ガスを脱硫する。
【0023】
Mg(OH)2 + SO2 → MgSO3 + H2
脱硫で生じた亜硫酸マグネシウムは、脱硫装置16に空気吹き込みライン20からスラリ中に吹き込まれたエアにより下式のように酸化されて硫酸マグネシウムとなる。
【0024】
MgSO3 + 1/2O2 → MgSO4
また、脱硫装置16には、ガスエアヒータ12の前段で排ガス二添加された生石灰又は消石灰からなる未反応の吸収剤とSO3 を吸収した硫酸カルシウムが流入し、これが脱硫剤のスラリと共にスラリライン21を介して熟成槽22に導入される。
【0025】
熟成槽22では、脱硫で生じた硫酸マグネシウムと未反応吸収剤(CaO又はCa(OH)2 )が、下式のような置換反応にて、石膏と水酸化マグネシウムにされる。
【0026】
MgSO4 + CaO + H2 O → CaSO4 + Mg(OH)2
熟成槽22で置換反応されたスラリは、ライン23より、ハイドロサイクロン等からなる石膏分離器24に供給される。
【0027】
石膏分離器24では、ハイドロサイクロン等の簡単な遠心分離操作で、石膏と水酸化マグネシウムに分離できる。
【0028】
分離した石膏25は、副製品として回収し、水酸化マグネシウムは、図には示していないが、固液分離器で排水27と分離し、ライン26から水酸化マグネシウムの脱硫剤として脱硫装置16に戻して再利用する。
【0029】
このように、排ガスに高濃度で含まれ、これが紫煙の原因となる無水硫酸を生石灰又は消石灰で中和し、未反応の生石灰又は消石灰を直接脱硫装置へ投入し、これを水酸化マグネシウム石膏法のカルシウム塩として使用することで、新たな生石灰等を必要とせずに、しかも脱硫剤としての水酸化マグネシウムは繰り返して使用することが可能となる。
【0030】
また、この排煙脱硫システムに湿式電気集塵機、ガス−ガスヒータ等を敷設することで、より厳しい環境対策を実施することが可能となる。
【0031】
【発明の効果】
以上要するに本発明によれば、排ガスに高濃度で含まれ、これが紫煙の原因となる無水硫酸を生石灰又は消石灰で中和し、未反応の生石灰又は消石灰を直接脱硫装置へ投入し、これを水酸化マグネシウム石膏法のカルシウム塩として使用することで、システムの簡素化ができる。
【図面の簡単な説明】
【図1】本発明の一実施の形態を示す図である。
【符号の説明】
10 ボイラ
12 ガス−エアヒータ
14 吸収剤添加ライン
16 脱硫装置
22 熟成槽
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a boiler flue gas treatment system for removing high sulfuric anhydride (SO 3 ) contained in exhaust gas discharged from a boiler, recovering this using a magnesium hydroxide gypsum method, and removing SO 2. Is.
[0002]
[Prior art]
Traditionally, the removal of SOx in the boiler flue gas, for SO 2 is to spray the absorption liquid in the absorption column, but by contacting the exhaust gas with a gas-liquid be absorbed removing SO 2 have been made, Ya this wet desulfurization The semi-dry type desulfurization apparatus cannot absorb and remove SO 3 , and if it is released to the atmosphere, it causes purple smoke due to sulfuric acid mist.
[0003]
Such being the case, the SO 3, it has been made for absorbing and removing SO 3 by injecting an alkaline agent to the flue.
[0004]
As absorber SO 2, with Mg (OH) 2, after absorption oxidation, there is a process for recovering gypsum as a by-product by adding CaO or Ca (OH) 2.
[0005]
[Problems to be solved by the invention]
However, neutralization of a high SO 3 content gas has a problem that unreacted CaO or Ca (OH) 2 is discarded and becomes uneconomical. Further, the magnesium hydroxide gypsum method has a problem that CaO or Ca (OH) 2 is separately required as a replenisher.
[0006]
SUMMARY OF THE INVENTION Accordingly, an object of the present invention is to provide a boiler flue gas treatment system that can solve the above problems and simplify the system by efficiently using an absorbent and a replenisher in removing SO 3 and SO 2 from exhaust gas. There is to do.
[0007]
[Means for Solving the Problems]
In order to achieve the above-mentioned object, the invention of claim 1 is to absorb the boiler exhaust gas after adding SO 3 in the exhaust gas by adding an absorbent composed of powdered quicklime or slaked lime to the exhaust gas from the boiler. It is introduced into a desulfurization unit together with an agent, and is contacted with a slurry using magnesium hydroxide as a desulfurization agent in the desulfurization unit, so that SO 2 is absorbed and removed. This is a boiler flue gas treatment system that uses magnesium oxide to recover gypsum and reuse magnesium hydroxide as a desulfurization agent.
[0008]
The invention according to claim 2 is the boiler flue gas treatment system according to claim 1, wherein in the desulfurization apparatus, air is blown into the slurry which has become SO 2 by absorbing SO 2 and is oxidized to magnesium sulfate.
[0009]
In the invention of claim 3, quick lime or slaked lime is added so as to be equimolar or more with respect to S content in the exhaust gas, and unreacted quick lime or slaked lime is supplied as a replenisher to the aging tank via a desulfurization apparatus to desulfurize The boiler flue gas treatment system according to claim 1, wherein a substitution reaction is performed with magnesium sulfate afterwards.
[0010]
According to a fourth aspect of the present invention, the gypsum and magnesium hydroxide produced by the substitution reaction in the aging tank are separated in particle size by a gypsum separator such as a hydrocyclone to separate the gypsum and the magnesium hydroxide. It is a boiler flue gas treatment system.
[0011]
DETAILED DESCRIPTION OF THE INVENTION
Preferred embodiments of the present invention will be described below in detail with reference to the accompanying drawings.
[0012]
FIG. 1 shows a block diagram of a boiler flue gas treatment system of the present invention.
[0013]
In FIG. 1, reference numeral 10 denotes a heavy oil-fired small to medium-sized boiler, and exhaust gas discharged from the boiler 10 is passed through a denitration device 11 for denitration. The temperature of this part is 300-400 degreeC.
[0014]
An absorbent injection line 14 for adding an absorbent made of powdered quicklime (CaO) or slaked lime (Ca (OH) 2 ) to the duct 13 connecting the denitration device 11 and the downstream gas-air heater (GAH) 12. Is connected.
[0015]
The gas-air heater 12 is connected to a bag filter type or electric dust collection type dust collector 16 through a duct 15, and exhaust gas from the dust collector 16 is discharged from the chimney 18 to the atmosphere.
[0016]
Quick lime or slaked lime as an absorbent to be injected into the duct 13 on the inlet side of the gas-air heater 12 is an amount that is expected to be excessive with respect to the amount of (SO 2 + SO 3 ) in the exhaust gas, for example, Ca for S content. Is added so as to be at least equimolar.
[0017]
When an absorbent of quicklime or slaked lime is added to the exhaust gas in the temperature range of 300 to 400 ° C., sulfuric anhydride (SO 3 ) can be efficiently removed according to the following neutralization reaction.
[0018]
CaO + SO 3 → CaSO 4
Or
Ca (OH) 2 + SO 3 → CaSO 4 + H 2 O
The exhaust gas is heat-exchanged with boiler combustion air by the gas-air heater 12, the temperature is lowered and supplied to the desulfurization device 16, and contacted with the slurry of magnesium hydroxide as the desulfurization agent supplied from the line 17. The SO 2 is absorbed and removed and exhausted from the chimney 18.
[0019]
In this case, in order to prevent white smoke in the exhaust of the chimney 18, a gas-gas heater is installed before and after the desulfurization device 16, and flows into the desulfurization device 16 with the preceding gas-gas heater. By recovering heat from the exhaust gas and reheating it to a temperature equal to or higher than the saturated water vapor temperature of the exhaust gas to be exhausted by a subsequent gas-gas heater, white smoke can be prevented. That is, the temperature of the exhaust gas exiting the gas-air heater 12 is set to 170 ° C., and the exhaust gas is recovered by heat at about 70 to 80 ° C. with the preceding gas-gas heater, and the temperature is further lowered by the desulfurization device 16 to become saturated steam. However, by reheating this with a gas-gas heater at the latter stage and heating it above the saturated water vapor temperature of the exhaust gas, even if exhausted from the chimney 18, it will not become below the saturated vapor temperature. Can be prevented.
[0020]
An electric dust collector may be provided between the desulfurization device 16 and the chimney 18.
[0021]
Now, a slurry using magnesium hydroxide (Mg (OH) 2 as a desulfurizing agent is supplied from the line 17 to the desulfurization device 16 and brought into gas-liquid contact with the exhaust gas.
[0022]
This magnesium hydroxide has a particle size of 1 to 2 μm and reacts with SO 2 in the exhaust gas as shown in the following formula to desulfurize the exhaust gas.
[0023]
Mg (OH) 2 + SO 2 → MgSO 3 + H 2 O
Magnesium sulfite produced by desulfurization is oxidized into magnesium sulfate by the air blown into the slurry from the air blowing line 20 into the desulfurization apparatus 16 as shown in the following formula.
[0024]
MgSO 3 + 1 / 2O 2 → MgSO 4
Further, unreacted absorbent made of quick lime or slaked lime added with exhaust gas before the gas air heater 12 and calcium sulfate absorbed SO 3 flow into the desulfurization apparatus 16, and this is a slurry line 21 together with the slurry of the desulfurization agent. Is introduced into the aging tank 22.
[0025]
In the aging tank 22, magnesium sulfate and unreacted absorbent (CaO or Ca (OH) 2 ) generated by desulfurization are converted into gypsum and magnesium hydroxide by a substitution reaction as shown in the following formula.
[0026]
MgSO 4 + CaO + H 2 O → CaSO 4 + Mg (OH) 2
The slurry subjected to the substitution reaction in the aging tank 22 is supplied from a line 23 to a gypsum separator 24 made of hydrocyclone or the like.
[0027]
The gypsum separator 24 can be separated into gypsum and magnesium hydroxide by a simple centrifugal separation operation such as a hydrocyclone.
[0028]
The separated gypsum 25 is recovered as a by-product, and magnesium hydroxide is not shown in the figure, but is separated from the waste water 27 by a solid-liquid separator, and is passed from the line 26 to the desulfurizer 16 as a magnesium hydroxide desulfurizing agent. Return and reuse.
[0029]
In this way, the sulfuric acid that is contained in the exhaust gas at a high concentration, which causes purple smoke, is neutralized with quick lime or slaked lime, and unreacted quick lime or slaked lime is directly fed into the desulfurization apparatus, and this is treated with the magnesium hydroxide gypsum method By using it as a calcium salt, magnesium hydroxide as a desulfurizing agent can be used repeatedly without the need for fresh quicklime or the like.
[0030]
In addition, by installing a wet electric dust collector, a gas-gas heater or the like in this flue gas desulfurization system, it is possible to implement more severe environmental measures.
[0031]
【The invention's effect】
In short, according to the present invention, the sulfuric acid that is contained in the exhaust gas at a high concentration and causes purple smoke is neutralized with quick lime or slaked lime, and unreacted quick lime or slaked lime is directly fed to the desulfurization apparatus, By using it as a calcium salt in the magnesium oxide gypsum method, the system can be simplified.
[Brief description of the drawings]
FIG. 1 is a diagram showing an embodiment of the present invention.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 10 Boiler 12 Gas-air heater 14 Absorbent addition line 16 Desulfurization apparatus 22 Aging tank

Claims (4)

ボイラからの排ガスに粉末状の生石灰又は消石灰からなる吸収剤を添加して排ガス中のSO3 を吸収除去した後、そのボイラ排ガスを吸収剤と共に脱硫装置に導入し、その脱硫装置で水酸化マグネシウムを脱硫剤とするスラリと接触させてSO2 を吸収除去し、その脱硫剤と吸収剤とを熟成槽で置換反応させて石膏と水酸化マグネシウムにし、石膏を回収すると共に水酸化マグネシウムを脱硫剤として再利用することを特徴とするボイラ排煙処理システム。After adding an absorbent made of quick lime powder or slaked lime to the exhaust gas from the boiler to absorb and remove SO 3 in the exhaust gas, the boiler exhaust gas is introduced into the desulfurization apparatus together with the absorbent, and magnesium hydroxide is used in the desulfurization apparatus. is contacted with the slurry to desulfurizing agent SO 2 removed by absorption, desulfurizing agent of magnesium hydroxide together with the desulfurizing agent and the absorbent is a substitution reaction with aging tank to gypsum and magnesium hydroxide, to recover the gypsum Boiler flue gas treatment system characterized by being reused as 脱硫装置内で、SO2 を吸収して亜硫酸マグネシウムとなったスラリにエアを吹き込んで硫酸マグネシウムに酸化する請求項1記載のボイラ排煙処理システム。The boiler flue gas treatment system according to claim 1, wherein air is blown into a slurry that has become SO 2 absorbed into magnesium sulfite in a desulfurization apparatus and oxidized to magnesium sulfate. 排ガス中のS分に対して当モル以上になるよう生石灰又は消石灰を添加し、未反応の生石灰又は消石灰を脱硫装置を介して熟成槽に補給剤として供給して脱硫後の硫酸マグネシウムと置換反応させる請求項1記載のボイラ排煙処理システム。Add quick lime or slaked lime so as to be equimolar or more with respect to the S content in the exhaust gas, supply unreacted quick lime or slaked lime as a replenisher to the aging tank via a desulfurization device, and replace with magnesium sulfate after desulfurization The boiler flue gas treatment system according to claim 1. 熟成槽内での置換反応で生成した石膏と水酸化マグネシウムとをハイドロサイクロン等の石膏分離器で粒径分離して石膏と水酸化マグネシウムを分離する請求項2記載のボイラ排煙処理システム。The boiler flue gas treatment system according to claim 2, wherein gypsum and magnesium hydroxide produced by a substitution reaction in an aging tank are separated in particle size by a gypsum separator such as a hydrocyclone to separate gypsum and magnesium hydroxide.
JP2000398033A 2000-12-27 2000-12-27 Boiler flue gas treatment system Expired - Fee Related JP4507404B2 (en)

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JP4507404B2 true JP4507404B2 (en) 2010-07-21

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