JPH07178317A - Removing method of nitrogen dioxide - Google Patents
Removing method of nitrogen dioxideInfo
- Publication number
- JPH07178317A JPH07178317A JP5355338A JP35533893A JPH07178317A JP H07178317 A JPH07178317 A JP H07178317A JP 5355338 A JP5355338 A JP 5355338A JP 35533893 A JP35533893 A JP 35533893A JP H07178317 A JPH07178317 A JP H07178317A
- Authority
- JP
- Japan
- Prior art keywords
- activated carbon
- exhaust gas
- nitrogen dioxide
- contact chamber
- contact
- 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.)
- Pending
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Treating Waste Gases (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、オフィスや住宅の空気
清浄器、あるいは燃焼装置の排気ダクトや自動車のマフ
ラ−等に設けられる二酸化窒素除去装置に関するもので
ある。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a nitrogen dioxide removing device provided in an air cleaner of an office or a house, an exhaust duct of a combustion device, a muffler of an automobile or the like.
【0002】[0002]
【従来技術】燃焼排ガス中の二酸化窒素は人体に有害で
あるため、従来よりこれを除去するために種々の方式が
開発されているが、再循環法や水噴射法等いずれも除去
効率が悪かったり装置が大形化するなどの欠点があり、
また自動車等の排気ガス処理用として貴金属触媒を用い
てNO2 を還元するものもあるが、高価である上に、排
気中のS0x等による腐食のために触媒の寿命が短いと
いう欠点があった。また一般に活性炭を充填材として用
いる吸着装置は、小形且つ安価に製造でき、しかもすぐ
れた吸着能力をもっているが、吸着能力の持続時間がき
わめて短いために、自動車や燃焼装置等の排気ガス処理
用としては実用化が困難であった。2. Description of the Related Art Since nitrogen dioxide in combustion exhaust gas is harmful to the human body, various methods have been developed to remove it, but neither the recirculation method nor the water injection method has a poor removal efficiency. There is a drawback that the device becomes large,
Further, there is a catalyst for reducing NO2 using a noble metal catalyst for treating exhaust gas of automobiles, etc., but it has a drawback that it is expensive and the catalyst has a short life due to corrosion due to S0x in exhaust gas. In general, an adsorption device that uses activated carbon as a filler can be manufactured in a small size and at a low cost, and has an excellent adsorption capacity, but since the duration of the adsorption capacity is extremely short, it is used for exhaust gas treatment of automobiles, combustion devices, etc. Was difficult to put into practical use.
【0003】[0003]
【発明が解決しようとする課題】本発明は上記の点に鑑
み、高い吸着能力を有する活性炭を用いて、その効力を
長時間持続させることができる手段を見出すことによ
り、高価な貴金属触媒や高温を使用することなく、高い
除去率と短い滞留時間で、自動車や燃焼装置から出る排
気ガス中のNO2 を除去することができる二酸化窒素除
去装置をきわめて簡単且つ安価な構成で提供することを
目的とするものである。In view of the above points, the present invention uses an activated carbon having a high adsorption capacity and finds a means capable of maintaining its effect for a long time. It is an object of the present invention to provide a nitrogen dioxide removing device with a very simple and inexpensive structure that can remove NO2 in exhaust gas emitted from an automobile or a combustion device with a high removal rate and a short residence time without using To do.
【0004】[0004]
【課題を解決するための手段】本発明による二酸化窒素
除去装置は、図2に示すように、活性炭成形物又は活性
炭繊維を強アルカリ水溶液に浸漬し乾燥させてなる充填
材1を、要すれば適当な粒度に粉砕したのち、排気ガス
の供給口2及び排出口3を有し内部に金網又は多孔板4
で仕切られた接触室5を有する装置本体6の該接触室5
内に充填して、排気ガスを上記充填材1に接触させるよ
うにしたものであり、活性炭を直接吸着材として使用す
るのではなく、NO2 を吸着するための強アルカリの担
体として利用した点に特徴を有するものである。The nitrogen dioxide removing apparatus according to the present invention, as shown in FIG. 2, includes a filler 1 obtained by immersing an activated carbon molding or activated carbon fiber in a strong alkaline aqueous solution and drying it. After crushing to an appropriate particle size, it has an exhaust gas supply port 2 and an exhaust gas outlet 3 and has a wire mesh or perforated plate 4 inside.
The contact chamber 5 of the apparatus main body 6 having the contact chamber 5 partitioned by
It is filled inside and the exhaust gas is brought into contact with the above-mentioned filling material 1. The activated carbon is not used as an adsorbent directly but is used as a strong alkali carrier for adsorbing NO2. It has characteristics.
【0005】[0005]
【作用】活性炭を燃焼排ガス中の二酸化窒素の吸着材と
して使用する場合、活性炭は二酸化窒素ばかりでなく排
ガス中に多量に含まれている種々の炭化水素をも吸着す
る。これらの炭化水素はいずれも親油性であって、親水
性の二酸化窒素と馴染まない性質を有し、そのために従
来の活性炭フィルタにおいては、活性炭がある程度炭化
水素を吸着した後は、二酸化窒素に対する吸着能力が急
激に低下するという性質があった。そこで本発明は、活
性炭自体の吸着能を、二酸化窒素のみと化学反応して炭
化水素と反応しない強アルカリの吸着に使い尽くすこと
によって、活性炭のもつ大きな比表面積を強アルカリに
よる二酸化窒素の吸着のみに利用するようにしたもので
あり、それによって排ガス中の二酸化窒素のみを選択的
に吸着させ、その吸着効率を長時間持続せしめたもので
ある。本方式によれば、NaOH,NaHCO3 ,Na
CO3 等の強アルカリを活性炭繊維を担体とした固体状
の物質として固定層方式で排気ガスと接触させることが
でき、しかも反応温度は常温でよく、また接触時間は特
に制約はないが例えば0.1秒でも十分であるから、装
置の小型化が可能である。なお活性炭を強アルカリ水溶
液に浸漬する際に、粉末でなく活性炭成形物又は活性炭
繊維を使用したのは、液状の強アルカリに浸漬処理する
際に、粉末状の活性炭では自由に浮遊して自己保形性が
なく、また攪拌するとペースト状になって多孔質性が損
なわれ、吸着性能が低下するからである。When the activated carbon is used as an adsorbent for nitrogen dioxide in the combustion exhaust gas, the activated carbon adsorbs not only nitrogen dioxide but also various hydrocarbons contained in a large amount in the exhaust gas. All of these hydrocarbons are lipophilic and have a property that they are not compatible with hydrophilic nitrogen dioxide. Therefore, in a conventional activated carbon filter, after the activated carbon has adsorbed hydrocarbons to some extent, it is adsorbed on nitrogen dioxide. There was a property that the ability dropped sharply. Therefore, the present invention exhausts the adsorption capacity of activated carbon itself to the adsorption of strong alkali that does not react with hydrocarbons by chemically reacting only with nitrogen dioxide, so that the large specific surface area of activated carbon can be absorbed only by strong alkali. In this way, only nitrogen dioxide in the exhaust gas is selectively adsorbed, and the adsorption efficiency is maintained for a long time. According to this method, NaOH, NaHCO3, Na
A strong alkali such as CO3 can be brought into contact with exhaust gas in a fixed bed system as a solid substance using activated carbon fibers as a carrier, and the reaction temperature may be room temperature, and the contact time is not particularly limited, but is, for example, 0. Since one second is sufficient, the device can be downsized. When immersing the activated carbon in a strong alkaline aqueous solution, activated carbon moldings or activated carbon fibers were used instead of powder because the activated carbon in powder form floats freely and self-protects when immersed in a liquid strong alkaline. This is because it has no form, and when it is stirred, it becomes a paste and the porosity is impaired, and the adsorption performance decreases.
【0006】[0006]
【実施例】図1は本発明を自動車の排気ガス除去装置と
して実施する場合の例を示したもので、エンジンからの
排気は排気筒7により、途中NO−NO2 変換器8を通
って二酸化窒素除去装置6に供給される。二酸化窒素除
去装置6は、図2に示すように、金属板よりなる筒状の
装置本体6内に金網又は多孔板4で前後を仕切られた接
触室5を設けると共に、前端及び後端にそれぞれ排気ガ
スの供給口2及び排出口3を設け、接触室5内には活性
炭繊維を強アルカリ水溶液に浸漬し乾燥させてなる充填
材1を充填したものである。なおNO−NO2 変換器8
としては、放電でオゾンを発生させてNOを酸化する方
法が有効であり、貴金属触媒を用いる方法に比し、製造
コスト、耐久性等の点で遥かに有利である。なおこのN
O−NO2 変換器は、自動車用としては付設するのが望
ましいが、オフィス用あるいは家庭用の場合は、NOが
NO2 へ変わる速度が非常に遅いことを考慮すれば、必
ずしも付設する必要はない。また活性炭繊維の代わりに
活性炭成形物を使用する場合は、アルカリ溶液を含浸さ
せ乾燥させたのち、成形物を適当な粒度(例えば0.3
mm径)に粉砕する。なおアルカリの種類としては、N
aOH,NA2 CO3 ,NaHCO3 等が安価に使用で
きるが、種類によるNO2 吸収率の差異は認められなか
った。また高温排気ガスに対する充填材の耐熱性につい
ては、活性炭繊維の重量減少率が100℃で約2%、4
00℃で約10%であるが、化学的性質については殆ど
影響されない。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 shows an example in which the present invention is embodied as an exhaust gas removing device for an automobile. Exhaust gas from an engine is exhausted by an exhaust stack 7 through a NO--NO2 converter 8 on the way to nitrogen dioxide. It is supplied to the removing device 6. As shown in FIG. 2, the nitrogen dioxide removing device 6 is provided with a contact chamber 5 partitioned by a wire net or a perforated plate 4 in a tubular device body 6 made of a metal plate, and has front and rear ends respectively. An exhaust gas supply port 2 and an exhaust gas exhaust port 3 are provided, and the contact chamber 5 is filled with a filler 1 obtained by immersing activated carbon fiber in a strong alkaline aqueous solution and drying it. The NO-NO2 converter 8
For this, a method of generating ozone by discharge to oxidize NO is effective, and is far more advantageous in terms of manufacturing cost, durability and the like than a method of using a noble metal catalyst. This N
The O-NO2 converter is preferably attached for an automobile, but is not necessarily attached for an office or a home, considering that the rate at which NO changes to NO2 is very slow. When an activated carbon molded product is used instead of the activated carbon fiber, the molded product is impregnated with an alkaline solution and dried, and then the molded product has an appropriate particle size (for example, 0.3).
(mm diameter). The type of alkali is N
Although aOH, NA2 CO3, NaHCO3, etc. can be used at low cost, no difference in NO2 absorption rate depending on the type was observed. Regarding the heat resistance of the filler against high temperature exhaust gas, the weight loss rate of the activated carbon fiber was about 2% at 100 ° C, 4
Approximately 10% at 00 ° C, but little effect on chemistry.
【0007】実例1:本テストは主として、アルカリ処
理活性炭繊維のNOとNO2 に対する吸着性能の差、及
び滞留時間に対する吸収率の変化を、未処理の活性炭と
比較して測定したもので、試験管中で13%NAOH水
溶液11.0gに、1.75gの活性炭繊維を浸漬し、
約10分経過後に活性炭繊維を取り出して直径17mm
の反応管に入れ、充填材とした。このときの充填部分の
体積すなわち接触室の容積は3.4mlである。これに
NO2 の濃度80〜90ppb、NOの濃度160〜2
00ppb、RH30〜40%の排気ガスを、流量20
00ml/分、温度25℃で、176時間流した。図3
は、このテスト結果を示したもので、これによればアル
カリ処理活性炭が、特にNO2 に対して極めて優れた吸
着性能を有することが分かる。横軸の滞留因子W/F
は、順次ガス流量を変えて反応管内での滞留時間の影響
を測定するための係数で、W(g)は充填材のグラム
数、F(リットル/分)は排気ガスの流量を示してい
る。Example 1: This test was conducted mainly by measuring the difference in the adsorption performance of the alkali-treated activated carbon fiber for NO and NO2 and the change in the absorption rate with respect to the residence time in comparison with the untreated activated carbon. Soak 1.75 g of activated carbon fiber in 11.0 g of 13% NaOH aqueous solution,
Activated carbon fiber is taken out after about 10 minutes and the diameter is 17 mm.
It was put in the reaction tube of No. 2 and used as a filler. At this time, the volume of the filled portion, that is, the volume of the contact chamber is 3.4 ml. The concentration of NO2 is 80 to 90 ppb and the concentration of NO is 160 to 2
Exhaust gas of 00ppb, RH 30-40%, flow rate 20
Flowed at 00 ml / min at a temperature of 25 ° C. for 176 hours. Figure 3
Shows the results of this test, which shows that the alkali-treated activated carbon has an extremely excellent adsorption performance especially for NO2. Retention factor W / F on the horizontal axis
Is a coefficient for measuring the influence of residence time in the reaction tube by sequentially changing the gas flow rate, W (g) is the number of grams of the filler, and F (liter / min) is the flow rate of the exhaust gas. .
【0008】実例2:本テストは主として吸着性能の持
続時間を測定したもので、1.06gのNa2 CO3
(和光、99.7%)を8.62gの水に入れて、固体
Na2CO3 が完全に溶けてから、1.15gの活性炭
繊維を上記Na2 CO3 水溶液に入れる。こうして処理
した活性炭繊維のうち0.29gを直径6mmの反応管
に入れた。このときの充填部分の体積は0.6mlであ
る。これにNO2 の濃度80〜90ppb、NOの濃度
160〜200ppb、RH30〜35%の排気ガス
を、流量1160〜1230ml/分で、0〜340時
間流した。図4はこの測定結果を示したもので、数百時
間連続使用しても吸着性能は殆ど劣化しないことが示さ
れている。Example 2: This test mainly measures the duration of the adsorption performance, 1.06 g of Na2 CO3
(Wako, 99.7%) was added to 8.62 g of water to completely dissolve the solid Na2 CO3, and then 1.15 g of activated carbon fiber was added to the Na2 CO3 aqueous solution. 0.29 g of the activated carbon fiber thus treated was put into a reaction tube having a diameter of 6 mm. The volume of the filled portion at this time is 0.6 ml. Exhaust gas having a NO2 concentration of 80 to 90 ppb, an NO concentration of 160 to 200 ppb, and an RH of 30 to 35% was flown therein at a flow rate of 1160 to 1230 ml / min for 0 to 340 hours. FIG. 4 shows the result of this measurement, and it is shown that the adsorption performance hardly deteriorates even after continuous use for several hundred hours.
【0009】実例3:本テストは主として、排ガス中の
NOxの濃度とNO2 の吸収率の関係を調べたもので、
3.64gのNaHCO3 (和光、99.8〜100
%)を47.1gの水に入れて、NaHCO3 の飽和水
溶液を作り、1.81gの活性炭繊維を上記NaHCO
3 水溶液に入れる。こうして処理した活性炭繊維のうち
0.32gを直径6mmの反応管に入れる。充填部分の
体積は0.81mlである。これにNO2 の濃度80〜
85ppb、NOの濃度0〜210ppb、RH50%
の排気ガスを、流量2230ml/分で、0〜25時間
流した。図5はこの測定結果を示したもので、NO2 の
濃度が増大しても、吸収率には殆ど影響を与えないこと
が示されている。Example 3: This test mainly examines the relationship between the concentration of NOx in the exhaust gas and the absorption rate of NO2.
3.64 g of NaHCO3 (Wako, 99.8-100)
%) In 47.1 g of water to make a saturated aqueous solution of NaHCO3, and 1.81 g of activated carbon fiber is added to the above NaHCO3.
3 Put in an aqueous solution. 0.32 g of the activated carbon fiber thus treated is put into a reaction tube having a diameter of 6 mm. The volume of the filling part is 0.81 ml. NO2 concentration of 80 ~
85 ppb, NO concentration 0-210 ppb, RH 50%
Exhaust gas was flowed at a flow rate of 2230 ml / min for 0 to 25 hours. FIG. 5 shows the result of this measurement, and it is shown that even if the concentration of NO2 is increased, it has little effect on the absorption rate.
【0010】[0010]
【発明の効果】本発明による二酸化窒素除去装置は上述
のように、活性炭の高い比表面積を利用して、これに予
め強アルカリを吸着させておくものであり、強アルカリ
は自動車や燃焼装置の排気ガス中から親水性のNO2 の
みと選択的に化学反応して、親油性の炭化水素類とは殆
ど反応しないものであるから、従来の活性炭フィルタに
比し吸着能の持続時間を飛躍的に伸長し得たものであ
り、高価な貴金属触媒を必要とせず、しかも反応温度は
常温でよいのでヒータ等を必要とせず、接触時間は極め
て短時間でよいので装置を小型化することができ、燃焼
装置や自動車のマフラ用ばかりでなくオフィスや住宅の
空気清浄器にも好適なNOx除去装置を安価に提供し得
るという利点がある。As described above, the nitrogen dioxide removing apparatus according to the present invention utilizes the high specific surface area of activated carbon to adsorb a strong alkali in advance thereon. Since it selectively chemically reacts only with hydrophilic NO2 from the exhaust gas and hardly reacts with lipophilic hydrocarbons, it has a dramatically longer adsorption time than conventional activated carbon filters. It can be extended, does not require an expensive noble metal catalyst, and does not require a heater or the like because the reaction temperature can be room temperature, and the contact time can be extremely short, so the device can be downsized, There is an advantage that a NOx removal device suitable for not only combustion devices and mufflers for automobiles but also air purifiers for offices and homes can be provided at low cost.
【図1】本発明の一実施例を示す系統図。FIG. 1 is a system diagram showing an embodiment of the present invention.
【図2】同上の要部断面図。FIG. 2 is a sectional view of a main part of the above.
【図3】同上の管内滞留時間に対するNOx減少率の変
化を示すグラフ。FIG. 3 is a graph showing changes in the NOx reduction rate with respect to the residence time in the tube.
【図4】同上のテスト継続時間に対するNO2 減少率の
変化を示すグラフ。FIG. 4 is a graph showing changes in the NO2 reduction rate with respect to the test duration described above.
【図5】同上の反応管入口におけるNOx濃度に対する
NO2 吸収率の変化を示すグラフ。FIG. 5 is a graph showing changes in the NO2 absorption rate with respect to the NOx concentration at the reaction tube inlet of the above.
1 充填材 2 ガス供給口 3 ガス排出口 4 多孔板 5 接触室 6 装置本体あるいは二酸化窒素除去装置 7 排気筒 8 NO−NO2 除去装置 1 Filling Material 2 Gas Supply Port 3 Gas Discharge Port 4 Perforated Plate 5 Contact Chamber 6 Device Main Body or Nitrogen Dioxide Removal Device 7 Exhaust Cylinder 8 NO-NO2 Removal Device
Claims (1)
リ水溶液に浸漬し乾燥させてなる充填材を、要すれば適
当な粒度に粉砕したのち、排気ガスの供給口及び排出口
を有し内部に金網又は多孔板で仕切られた接触室を有す
る装置本体の該接触室内に充填して、排気ガスを上記充
填材に接触させるようにしたことを特徴とする二酸化窒
素除去装置。1. A filler obtained by immersing an activated carbon molded product or activated carbon fiber in a strong alkaline aqueous solution and drying the pulverized product, if necessary, after crushing to an appropriate particle size, and then having an exhaust gas supply port and an exhaust port inside A nitrogen dioxide removing device, characterized in that an exhaust gas is brought into contact with the above-mentioned filling material by filling the contact chamber of a device main body having a contact chamber partitioned by a wire net or a perforated plate.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5355338A JPH07178317A (en) | 1993-12-22 | 1993-12-22 | Removing method of nitrogen dioxide |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5355338A JPH07178317A (en) | 1993-12-22 | 1993-12-22 | Removing method of nitrogen dioxide |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH07178317A true JPH07178317A (en) | 1995-07-18 |
Family
ID=18443363
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP5355338A Pending JPH07178317A (en) | 1993-12-22 | 1993-12-22 | Removing method of nitrogen dioxide |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH07178317A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2012030199A (en) * | 2010-08-03 | 2012-02-16 | Japan Pionics Co Ltd | Method for treating gas containing nitrogen oxide |
CN114367178A (en) * | 2020-12-18 | 2022-04-19 | 南京诺令生物科技有限公司 | Realization of NO2Converted filter element material, preparation method thereof and filter element device comprising same |
-
1993
- 1993-12-22 JP JP5355338A patent/JPH07178317A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2012030199A (en) * | 2010-08-03 | 2012-02-16 | Japan Pionics Co Ltd | Method for treating gas containing nitrogen oxide |
CN114367178A (en) * | 2020-12-18 | 2022-04-19 | 南京诺令生物科技有限公司 | Realization of NO2Converted filter element material, preparation method thereof and filter element device comprising same |
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