JPS5817648B2 - Exhaust gas purification method for open combustion appliances - Google Patents
Exhaust gas purification method for open combustion appliancesInfo
- Publication number
- JPS5817648B2 JPS5817648B2 JP53061203A JP6120378A JPS5817648B2 JP S5817648 B2 JPS5817648 B2 JP S5817648B2 JP 53061203 A JP53061203 A JP 53061203A JP 6120378 A JP6120378 A JP 6120378A JP S5817648 B2 JPS5817648 B2 JP S5817648B2
- Authority
- JP
- Japan
- Prior art keywords
- combustion
- catalyst
- exhaust gas
- air
- open
- 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 title claims description 47
- 238000000034 method Methods 0.000 title claims description 11
- 238000000746 purification Methods 0.000 title description 2
- 239000003054 catalyst Substances 0.000 claims description 50
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims description 28
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims description 22
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 20
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 claims description 16
- 229910052763 palladium Inorganic materials 0.000 claims description 14
- 239000004568 cement Substances 0.000 claims description 13
- 239000003513 alkali Substances 0.000 claims description 11
- 229910052697 platinum Inorganic materials 0.000 claims description 11
- 239000000463 material Substances 0.000 claims description 10
- 229910000027 potassium carbonate Inorganic materials 0.000 claims description 8
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 5
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 5
- 239000004571 lime Substances 0.000 claims description 5
- 150000004645 aluminates Chemical class 0.000 claims description 4
- 238000004898 kneading Methods 0.000 claims description 2
- 238000000465 moulding Methods 0.000 claims 1
- 230000000694 effects Effects 0.000 description 12
- 239000007789 gas Substances 0.000 description 11
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 9
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 8
- 239000003350 kerosene Substances 0.000 description 8
- 229910000510 noble metal Inorganic materials 0.000 description 8
- 239000004745 nonwoven fabric Substances 0.000 description 5
- 229910002092 carbon dioxide Inorganic materials 0.000 description 4
- 238000010411 cooking Methods 0.000 description 4
- 230000007423 decrease Effects 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 238000010438 heat treatment Methods 0.000 description 4
- 230000003647 oxidation Effects 0.000 description 4
- 238000007254 oxidation reaction Methods 0.000 description 4
- 239000010970 precious metal Substances 0.000 description 4
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 3
- 239000004743 Polypropylene Substances 0.000 description 3
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 3
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 description 3
- 238000003915 air pollution Methods 0.000 description 3
- 229910002091 carbon monoxide Inorganic materials 0.000 description 3
- 229910044991 metal oxide Inorganic materials 0.000 description 3
- 150000004706 metal oxides Chemical class 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 231100000572 poisoning Toxicity 0.000 description 3
- 230000000607 poisoning effect Effects 0.000 description 3
- -1 polypropylene Polymers 0.000 description 3
- 229920001155 polypropylene Polymers 0.000 description 3
- 229910052703 rhodium Inorganic materials 0.000 description 3
- 239000010948 rhodium Substances 0.000 description 3
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 description 3
- 229910052707 ruthenium Inorganic materials 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 2
- 239000013543 active substance Substances 0.000 description 2
- 239000011230 binding agent Substances 0.000 description 2
- 239000001768 carboxy methyl cellulose Substances 0.000 description 2
- 239000010419 fine particle Substances 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N iron oxide Inorganic materials [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- NDLPOXTZKUMGOV-UHFFFAOYSA-N oxo(oxoferriooxy)iron hydrate Chemical compound O.O=[Fe]O[Fe]=O NDLPOXTZKUMGOV-UHFFFAOYSA-N 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000009827 uniform distribution Methods 0.000 description 2
- 229920002134 Carboxymethyl cellulose Polymers 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- 206010019233 Headaches Diseases 0.000 description 1
- 230000010718 Oxidation Activity Effects 0.000 description 1
- 206010033799 Paralysis Diseases 0.000 description 1
- 239000011398 Portland cement Substances 0.000 description 1
- 206010070863 Toxicity to various agents Diseases 0.000 description 1
- 238000005299 abrasion Methods 0.000 description 1
- DPXJVFZANSGRMM-UHFFFAOYSA-N acetic acid;2,3,4,5,6-pentahydroxyhexanal;sodium Chemical compound [Na].CC(O)=O.OCC(O)C(O)C(O)C(O)C=O DPXJVFZANSGRMM-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 239000000440 bentonite Substances 0.000 description 1
- 229910000278 bentonite Inorganic materials 0.000 description 1
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical compound O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 239000008280 blood Substances 0.000 description 1
- 210000004369 blood Anatomy 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 230000007177 brain activity Effects 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002090 carbon oxide Inorganic materials 0.000 description 1
- 235000010948 carboxy methyl cellulose Nutrition 0.000 description 1
- 239000008112 carboxymethyl-cellulose Substances 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000004455 differential thermal analysis Methods 0.000 description 1
- 208000002173 dizziness Diseases 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 231100000869 headache Toxicity 0.000 description 1
- 230000020169 heat generation Effects 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 238000003905 indoor air pollution Methods 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 230000002452 interceptive effect Effects 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000007769 metal material Substances 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 229910000033 sodium borohydride Inorganic materials 0.000 description 1
- 239000012279 sodium borohydride Substances 0.000 description 1
- 229910000029 sodium carbonate Inorganic materials 0.000 description 1
- 235000019812 sodium carboxymethyl cellulose Nutrition 0.000 description 1
- 229920001027 sodium carboxymethylcellulose Polymers 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
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
- Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)
- Incineration Of Waste (AREA)
- Combustion Of Fluid Fuel (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Description
【発明の詳細な説明】
本発明は開放型燃焼器具の排ガス浄化方法に関するもの
である。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for purifying exhaust gas from an open combustion appliance.
近年−酸化炭素による大気汚染が問題となっている。In recent years, air pollution caused by carbon oxide has become a problem.
一酸化炭素(以下COと記す)の発生源は自動車等の移
動発生源と大型ボイラー等の固定発生源である。The sources of carbon monoxide (hereinafter referred to as CO) are mobile sources such as automobiles and stationary sources such as large boilers.
従来から、一酸化炭素の毒性は一般に広く知られている
所であるが、行政的にも大気汚染防止の観点から、自動
車排ガス規制などの形で発生源対策が推進された結果、
一般大気汚染のレベルとしては、その汚染は著しく緩和
されるに至ったが、逆に今日では室内汚染の観点から、
その1部の実態が公表されたりして、室内汚染の問題物
質として注目されている。The toxicity of carbon monoxide has long been widely known, but from the perspective of preventing air pollution, government efforts have been made to take measures against the source of carbon monoxide in the form of automobile exhaust gas regulations.
Although the level of general air pollution has been significantly reduced, on the contrary, from the perspective of indoor pollution,
The actual situation of some of them has been made public, and they are attracting attention as a problematic substance for indoor pollution.
COは血液中のへモグ遁ピンと結合しやすく、これの吸
入により記憶学習のような頭脳活動に影響が現われさら
に大量に吸うと頭痛、目まい、手足のマヒなどの中毒症
状となり最終的には死に到る。CO easily binds to hemoguton pins in the blood, and when inhaled, it affects brain activities such as memory and learning, and when inhaled in large quantities, it causes toxic symptoms such as headaches, dizziness, and paralysis of the limbs, eventually leading to death. Arrive.
しかし開放型の燃焼装置に於いては抑制燃焼技術のみか
らの対処には限界があり、特に家庭用ガス、石油暖房器
具ではCOが0.3〜0.51/ h r発生しその結
果室内の濃度は環境基準のioppmをはるかに上まわ
る。However, in open-type combustion equipment, there are limits to what can be done only by suppressed combustion technology; in particular, household gas and oil heating equipment generates CO of 0.3 to 0.51/hr, resulting in indoor The concentration far exceeds the environmental standard of ioppm.
それ故燃焼中は時々窓をあけて空気を入れ換える必要が
あるが、冬場では暖まった空気を戸外に排気する事は暖
房能率上好ましくなく、室内を良好な空気環境に維持す
るためには、発生したCOを室内で浄化する技術との併
用が望ましい。Therefore, during combustion, it is necessary to open the window from time to time to exchange the air, but in winter, exhausting warm air outside is not desirable in terms of heating efficiency, and in order to maintain a good indoor air environment, it is necessary to It is desirable to use this method in combination with technology that purifies the CO indoors.
また給湯や調理用の燃焼器具においても室内汚染防止の
観点から浄化技術の確立が望まれている。Furthermore, it is desired to establish purification technology for combustion appliances for hot water supply and cooking from the viewpoint of preventing indoor pollution.
′本発明は開放型燃焼器具より発生するCOを除去
する為に燃焼部の上に対流が不十分の場合には送風機を
設け、その空気流路に室温でもCOを酸化する触媒層を
設けて排ガス空気を浄化する方法であり、本発明の採用
により室内に放出されるCOは大幅に減少する。'In order to remove CO generated from open combustion equipment, the present invention installs a blower above the combustion section when convection is insufficient, and provides a catalyst layer in the air flow path that oxidizes CO even at room temperature. This is a method of purifying exhaust gas air, and by adopting the present invention, CO released into the room can be significantly reduced.
燃焼装置は点火直後の立上り時に多量のCOを発生する
。A combustion device generates a large amount of CO during startup immediately after ignition.
これは立上り時の不完全燃焼によって発生するものであ
り安定燃焼になると低減する。This occurs due to incomplete combustion at startup, and decreases when combustion becomes stable.
その為開放型燃焼装置では発生したCOはそのまま室内
へ放出され室内はCOによって汚染されていた。For this reason, in open combustion devices, the generated CO is directly released into the room, and the room is contaminated with CO.
室内の空気汚染を防ぐ為、石油、ガスの暖房機器では室
外の空気を使って燃焼をおこない燃焼排ガスは室外へ排
気する強制給排気方式が近年発達したが、開放型のスト
ーブは安価である理由より依然として人気があり発生す
るCOの除去が望まれていた。In order to prevent indoor air pollution, forced air supply and exhaust systems have been developed in recent years for oil and gas heating equipment that use outdoor air to perform combustion and exhaust the combustion exhaust gas outdoors, but this is why open stoves are cheaper. Removal of the still popular and emitted CO was desired.
また給湯用小型湯沸機や調理器具用バーナーに於てもそ
の使い易さ、性能、技術的困難さより開放型であり発生
するCOの除去が強く望まれていた。Furthermore, in view of ease of use, performance, and technical difficulty, there has been a strong desire for small water heaters for water supply and burners for cooking utensils to be open-type and to remove the generated CO.
室内で発生するCOを除去するには触媒によって無害な
CO2に変化させる方法しかない。The only way to remove CO generated indoors is to convert it into harmless CO2 using a catalyst.
C0酸化触媒としてはホブカライドなどの金属酸化物と
白金、パラジウムなどの貴金属があるが、金属酸化物触
媒は室温でも充分に活性を発揮するが水蒸気の存在です
ぐに劣下する欠点を有する。C0 oxidation catalysts include metal oxides such as fobucalide and noble metals such as platinum and palladium. Metal oxide catalysts exhibit sufficient activity even at room temperature, but have the disadvantage that they deteriorate quickly in the presence of water vapor.
貴金属触媒は貴金属をアルミナ、シリカ、活性炭などの
高比表面積を持つ担体に担持させたものであり、貴金属
としては白金のパラジウムが用いられるが100℃以上
の高温でないと活性を発揮しなかった。A noble metal catalyst is a precious metal supported on a carrier with a high specific surface area such as alumina, silica, or activated carbon.The noble metal used is palladium, which is platinum, but it does not exhibit activity unless it is heated to a high temperature of 100°C or higher.
それ故燃焼器具より発生するCoは水分を含むので金属
酸化物触媒を使用する際には除湿器等によって水分を除
去する必要がある。Therefore, since Co generated from combustion equipment contains water, it is necessary to remove water using a dehumidifier or the like when using a metal oxide catalyst.
また貴金属触媒を使用する際には100℃以上に加熱す
る必要があり、その為燃焼部の近くに触媒を置く、他の
昇温設備を必要とするの方法があるが前記の方法は触媒
を置く事により燃焼に影響を与えるので技術的な困難さ
があるなど実用上の制約が多かった。In addition, when using a precious metal catalyst, it is necessary to heat it to over 100°C.Therefore, there are methods such as placing the catalyst near the combustion section or requiring other temperature raising equipment, but the above method does not require heating the catalyst. There were many practical limitations, such as technical difficulties as placing the fuel in the tank would affect combustion.
しかし燃焼によって発生する熱、特に70℃付近の低温
度を利用して多量に発生するCOを除去する技術の開発
は強く望まれていて本発明はその方法を提供するもので
ある。However, there is a strong desire to develop a technology that utilizes the heat generated by combustion, particularly at low temperatures around 70° C., to remove large amounts of CO, and the present invention provides a method for this purpose.
開放型燃焼器具より発生した熱とCOは燃焼部の上部に
上昇したのち、空気中で拡散して室内に分布される。The heat and CO generated by the open combustion appliance rise to the top of the combustion section, then diffuse in the air and are distributed throughout the room.
その為燃焼部の上部の40〜100℃付近の温度をなす
場所に必要により送風機とCO酸化触媒層を設けること
によって、発生したCOを除去できるわけであり、燃焼
に影響を与えず、実際の使用に際しても小型、コンパク
トな構成となり燃焼部よりも相描離れた位置に設置して
も充分に効果を発揮する。Therefore, by installing a blower and a CO oxidation catalyst layer as necessary in the upper part of the combustion section where the temperature is around 40 to 100 degrees Celsius, the generated CO can be removed, without affecting combustion, and in actual When used, it has a small and compact structure and is fully effective even when installed at a position far away from the combustion section.
第1図は開放型燃焼器具として石油ストーブへの本発明
の応用例である。FIG. 1 shows an example of application of the present invention to a kerosene stove as an open combustion appliance.
石油ストーブ1(開放型燃焼器具)の燃焼部2より発生
した熱は前面よりと後面に設置した反射板3に反射して
室内空気を温める。Heat generated from a combustion part 2 of a kerosene stove 1 (open type combustion appliance) is reflected on reflectors 3 installed at the front and rear surfaces to warm indoor air.
一方発生したCOは天板4を通過して室内に拡散される
ので送風機5によって集められたCOは触媒層6を通過
して浄化され吹出しロアより室内へ放出される。On the other hand, the generated CO passes through the top plate 4 and is diffused into the room, so the CO collected by the blower 5 passes through the catalyst layer 6, is purified, and is discharged into the room from the blowout lower.
触媒は室温から100℃で効果を発揮するので触媒層7
温度がその温度になる様に送風機5と触媒層7を内部に
持つ機器8を燃焼部より離して設置する。Since the catalyst is effective from room temperature to 100°C, the catalyst layer 7
A device 8 having an air blower 5 and a catalyst layer 7 inside is installed away from the combustion part so that the temperature reaches the temperature.
送風機5はシロッコファンが最適であり、その風量は触
媒層6を熱風が通過する程度とし送風によって燃焼に影
響がない構成とする。The blower 5 is optimally a sirocco fan, and its air volume is set to such an extent that hot air passes through the catalyst layer 6, so that the blowing air does not affect combustion.
触媒層6は触媒を2枚の不織布の間にはさんだ物やハニ
カム型が好ましく、特にハニカム型は圧力損失が小さく
、高活性であるので最適である。The catalyst layer 6 is preferably one in which the catalyst is sandwiched between two sheets of non-woven fabric or a honeycomb type. In particular, the honeycomb type is optimal because it has low pressure loss and high activity.
機器8は石油ストーブ1の上に直接設置するか、壁に取
付けるタイプとする。The device 8 is of a type that is installed directly on top of the kerosene stove 1 or is attached to a wall.
第2図は開放型燃焼器具として調理器具用バーナーへの
応用例である。FIG. 2 shows an example of application to a burner for cooking utensils as an open type combustion appliance.
調理器具バーナー9の燃焼部10より発生したCOはダ
クト(空気流路)11の内部に設けられた送風機12に
よってダクト11に吸い込まれ触媒層13によって無害
なCO2に変化して室内に排気される。CO generated from the combustion part 10 of the cooking utensil burner 9 is sucked into the duct 11 by a blower 12 provided inside the duct (air flow path) 11, converted into harmless CO2 by the catalyst layer 13, and exhausted into the room. .
ダクト11は燃焼部10によって加熱される鍋、釜等が
出入れの際に邪魔にならぬ様に設置されるが、燃焼によ
って発生するCOを含んだ空気が充分に吸い込まれる構
成とする。The duct 11 is installed so that it does not get in the way when pots, pots, etc. heated by the combustion part 10 are taken in and out, but it is configured to sufficiently suck in air containing CO generated by combustion.
送風機12はクロスファンが適当と思われる。It seems appropriate for the blower 12 to be a cross fan.
触媒層13は触媒を2枚の不織布の間にはさんだ物やハ
ニカム型を用いる。For the catalyst layer 13, a layer in which a catalyst is sandwiched between two sheets of nonwoven fabric or a honeycomb layer is used.
触媒はアルカリ、粉末活性炭、セメント材の混練成型物
に白金、ロジウム、ルテニウムより選んだ1種以上とパ
ラジウムを同時に、もしくはパラジウム単独を担持した
ものであり、特にアルカリとして炭酸カリウム、セメン
ト材としてアルミン酸石灰を用いたもの、白金とパラジ
ウムを同時に担持させたものは高活性であった。The catalyst is a kneaded molded product of alkali, powdered activated carbon, and cement material, which supports one or more selected from platinum, rhodium, and ruthenium and palladium at the same time, or palladium alone.In particular, potassium carbonate is used as the alkali, and aluminum is used as the cement material. Those using acid lime and those supporting platinum and palladium at the same time were highly active.
それゆえ炭酸カリウム、アルミン酸石灰、粉末活性炭の
混練成型物に白金、パラジウムを同時に担持させたもの
を使用する。Therefore, a kneaded and molded product of potassium carbonate, lime aluminate, and powdered activated carbon that simultaneously supports platinum and palladium is used.
本発明は他の開放型燃焼器具にも適用できる。The invention is also applicable to other open combustion appliances.
実施例としては低温CO酸化触媒としてアルカリ、粉末
活性炭、セメント材の混練成型物に白金、ロジウム、ル
テニウムの群より選択した一種以上とパラジウムを同時
に、もしくはパラジウム単独で担持させたものを使用し
た。As an example, as a low-temperature CO oxidation catalyst, one or more selected from the group of platinum, rhodium, and ruthenium and palladium were simultaneously supported on a kneaded molded product of alkali, powdered activated carbon, and cement material, or palladium alone was supported.
触媒の担体は担持物質を純粋に、粒径を細かく、広範囲
に均一分布で担持させるとともに担体の比表面積が大き
く高強度であることが必要である。The catalyst carrier must support the supported substance in a pure manner with fine particle size and uniform distribution over a wide range, and must also have a large specific surface area and high strength.
アルカリは担体に貴金属を担持させる場合に貴金属塩化
物を溶解した含浸液のPI−(をアルカリへ変化させ貴
金属が担体に粒径細かく均一に分散した状態で吸着され
る様に手順の最適化を計った。When a precious metal is supported on a carrier, the alkali is used to change the impregnating liquid PI- (in which noble metal chloride is dissolved) into an alkali, and the procedure must be optimized so that the noble metal is adsorbed onto the carrier in a fine and uniformly dispersed state. I measured it.
粉末活性炭は担体の比表面積を大きくするなどの担体の
細孔物性に寄与しているものと考えられる。It is thought that the powdered activated carbon contributes to the pore physical properties of the carrier, such as increasing the specific surface area of the carrier.
セメント材は担体の強度を大きくするとともにその耐熱
性、耐摩耗性を向上させる寄与を果たしていると考えら
れる。It is believed that the cement material contributes to increasing the strength of the carrier and improving its heat resistance and abrasion resistance.
アルカリとしては炭酸カリウム、水酸化カリウム、水酸
化カルシウム、炭酸ナトIJウム等があげられるが、使
い易さと性能面より炭酸カリウムが最適であった。Examples of the alkali include potassium carbonate, potassium hydroxide, calcium hydroxide, sodium carbonate, etc., but potassium carbonate was the most suitable in terms of ease of use and performance.
セメント材はポルトランドセメント、焼石膏、ベントナ
イト、アルミン酸石灰を主成分とするアルミナセメント
等があげられるが性能面よりアルミナセメントが最適で
あった。Cement materials include portland cement, calcined gypsum, bentonite, and alumina cement whose main component is lime aluminate, but alumina cement was the most suitable in terms of performance.
その理由はアルミナセメントに含有する酸化第二鉄と酸
化カルシウムの助触媒的な効果の影響であると思われる
。The reason for this is thought to be the cocatalytic effect of ferric oxide and calcium oxide contained in alumina cement.
また結合剤としてアルミナが安定な担体を構成する役割
を果していると推定される。It is also presumed that alumina as a binder plays a role in forming a stable carrier.
担持物質として白金、ロジウム、ルテニウム、パラジウ
ム等の貴金属を使用した。Noble metals such as platinum, rhodium, ruthenium, and palladium were used as supporting materials.
比較的安価なパラジウムは単独か、もしくは他の貴金属
物質との組合せで高活性な触媒となり、特に白金、パラ
ジウムの組合せは相乗効果を発揮して著しい酸化活性が
得られた。Palladium, which is relatively inexpensive, becomes a highly active catalyst when used alone or in combination with other noble metal materials, and in particular, the combination of platinum and palladium exhibited a synergistic effect and achieved remarkable oxidation activity.
次に触媒の調整方法について記す。Next, the method for preparing the catalyst will be described.
アルカリとして炭酸カリウム、セメント材としてアルミ
ナセメントを用い、炭酸カリウムは100メツシユ全通
、粉末活性炭は300メツシユ全通の粒度のもの、アル
ミナセメントはその組成がアルミナが45%以上、酸化
第二鉄が10%以下のものを使った。Potassium carbonate is used as the alkali, and alumina cement is used as the cement material. Potassium carbonate has a particle size of 100 mesh, powdered activated carbon has a particle size of 300 mesh, and alumina cement has a composition of at least 45% alumina and ferric oxide. I used less than 10%.
担体は重量比で炭酸カリウム10部、粉末活性炭30部
、アルミン酸石灰60部にバインダーとしてカルボキシ
メチルセルロースナトリウム(CMC)0.5部を添加
して水とともに混練成型した。The carrier was prepared by adding 0.5 part of sodium carboxymethyl cellulose (CMC) as a binder to 10 parts of potassium carbonate, 30 parts of powdered activated carbon, and 60 parts of lime aluminate in weight ratio, and kneading the mixture with water.
混練物は充分に乾燥した後8〜20メツシユに分級して
担体とした。The kneaded material was thoroughly dried and then classified into 8 to 20 meshes to form a carrier.
上記担体を充分に乾燥した後パラジウムと白金を溶かし
た溶液に浸漬して吸着をおこなわせた。After the carrier was sufficiently dried, it was immersed in a solution containing palladium and platinum to effect adsorption.
パラジウムと白金は担体に対して各0.3wt%吸着さ
れる様にその量を調整した。The amounts of palladium and platinum were adjusted so that 0.3 wt% of each was adsorbed on the carrier.
吸着された担体は水素化ホウ素ナトリウムで還元した後
充分に乾燥し300℃で1時間熱処理して触媒とした。The adsorbed carrier was reduced with sodium borohydride, thoroughly dried, and heat-treated at 300° C. for 1 hour to obtain a catalyst.
なお調整した触媒は2枚のポリプロピレンの不織布の間
にはさみこみ触媒層とした。The prepared catalyst was sandwiched between two polypropylene nonwoven fabrics to form a catalyst layer.
本発明の効果の判定として自然換気する6畳の部屋(容
積29.6771”)で開放型石油ストーブを燃焼させ
室内CO濃度を測定した。To determine the effectiveness of the present invention, an open kerosene stove was burned in a naturally ventilated 6-tatami room (volume: 29.6771''), and the indoor CO concentration was measured.
第3図は、本発明なしの場合Iと本発明を採用した場合
■の室内CO濃度であり、ここで使用したCO酸化触媒
は、上記「触媒の調整方法」で説明したものを用いた。FIG. 3 shows the indoor CO concentration in case I without the present invention and in case II with the present invention, and the CO oxidation catalyst used here was the one explained in the above "Catalyst adjustment method".
開放型石油ストーブは発熱量2200〜2300k c
a L/h r の状態で燃焼させ室内濃度は部屋の
中央部の空気を吸引し非分散形赤外方式のCO分析計で
分析した。Open type kerosene stove has a calorific value of 2200 to 2300 kc
The mixture was combusted at a L/hr, and the indoor concentration was analyzed using a non-dispersive infrared CO analyzer after sucking air from the center of the room.
■は開放型石油ストーブの天板に第1図の構成からなる
機器を設置した場合である。(2) shows the case where the equipment having the configuration shown in Figure 1 is installed on the top plate of an open kerosene stove.
触媒層は300X100mmの大きさの2枚のポリプロ
ピレン不織布の間に100gの触媒を5朋の層高で均一
分布に充填したものであり、その温度は70〜80℃で
あった。The catalyst layer was made by filling 100 g of catalyst in a uniform distribution between two sheets of polypropylene nonwoven fabric with a size of 300 x 100 mm at a layer height of 5 mm, and the temperature was 70 to 80°C.
送風機はシロッコファンを用い触媒層を0.3m/sの
流速で通過する様にその送風量を調節した。A sirocco fan was used as the blower, and the amount of air blown was adjusted so that the air passed through the catalyst layer at a flow rate of 0.3 m/s.
送風量と触媒の充填密度、層高はそれらの値が大きいほ
ど触媒の活性が向上するが、送風量が多いと燃焼に影響
を与えて不安定な燃焼状態になり、触媒の充填密度、層
高が大きくなると圧力損失が大きくなるので風量が減少
し活性度が低下する等の問題点がある。The larger the airflow rate, catalyst packing density, and bed height, the higher the catalyst activity. As the height increases, the pressure loss increases, resulting in problems such as a decrease in air volume and a decrease in activity.
それらの要因について数多く試験した結果、上記の条件
が最適であった。As a result of numerous tests regarding these factors, the above conditions were found to be optimal.
触媒層の温度は不織布としてのポリプロピレンの使用限
界温度が110〜130℃であり、また触媒の使用温度
も100℃以下で使う事が望ましいので100°C以下
望ましくは70〜80℃になる様に触媒層の位置を工夫
する必要がある。The temperature of the catalyst layer should be 100°C or less, preferably 70-80°C, since the limit temperature for use of polypropylene as a nonwoven fabric is 110 to 130°C, and it is desirable to use the catalyst at a temperature of 100°C or less. It is necessary to consider the position of the catalyst layer.
本発明を採用すると開放型燃焼器具より室内へ発生する
有害ガス、特にCOを高性能に除去する。When the present invention is adopted, harmful gases, especially CO, generated indoors from open combustion appliances can be efficiently removed.
これは触媒の担体が多孔質であり高活性物質である貴金
属を粒径細かく高範囲に均一状態で担持しているからで
あり、低温に於てCOを高活性に酸化するとともに水蒸
気の存在が活性を向上させる働きをもつので燃焼排ガス
浄化用触媒としては最適である。This is because the catalyst carrier is porous and supports the precious metal, which is a highly active substance, in a fine particle size and uniformly over a wide range, and it oxidizes CO with high activity at low temperatures and also eliminates the presence of water vapor. Since it works to improve activity, it is ideal as a catalyst for purifying combustion exhaust gas.
耐久性の面でも示差熱分析によれば385℃で発熱を伴
って分解するがそれ以下の温度範囲では安定であり、発
明者等は触媒を高温度の雰囲気中に長時間放置したとこ
ろ300℃で1ケ月連続、200°Cで3ケ月連続放置
しても活性が低下しない事を確認した。In terms of durability, differential thermal analysis shows that the catalyst decomposes with heat generation at 385°C, but is stable below that temperature range, and the inventors found that when the catalyst was left in a high-temperature atmosphere for a long time, it reached 300°C. It was confirmed that the activity did not decrease even after being left at 200°C for 1 month or 3 months at 200°C.
しかし実用上その様な条件下に触媒が置かれる事は絶対
になく70〜80℃の温度雰囲気中で使用するので熱的
にも充分に安定である事がわかる。However, in practice, the catalyst is never placed under such conditions and is used in an atmosphere at a temperature of 70 to 80°C, so it is understood that it is sufficiently thermally stable.
一方被毒の影響であるが、燃焼排ガス中にはNOxやH
Cなどがか含まれている。On the other hand, regarding the effects of poisoning, NOx and H
Contains C etc.
点火直後などの不完全燃焼時にはCOが多量に発生する
がNOxはほとんど発生しない。During incomplete combustion, such as immediately after ignition, a large amount of CO is generated, but almost no NOx is generated.
反面完全燃焼時にはCOの発生はあまりないがNOxは
比較的多い。On the other hand, during complete combustion, not much CO is produced, but NOx is relatively large.
しかし燃焼におけるNOxは大部分がNOであり、NO
2は考えなくてもよい。However, most of the NOx in combustion is NO;
You don't have to think about 2.
その為NOxの被毒は安定燃焼時におけるN。のみを考
えればよいわけであり、本触媒は貴金属を活性物質とし
て利用しているのでNOを弱く吸着するがCOとの反応
が最も起こり易いのですぐに脱離し触媒作用を低下させ
ない。Therefore, NOx poisoning occurs during stable combustion. Since this catalyst uses a noble metal as an active substance, it weakly adsorbs NO, but since it most easily reacts with CO, it is quickly desorbed and does not reduce the catalytic action.
また担体はアルカリと活性炭を含有しているがアルカリ
とNOとは反応しない、粉末活性炭はNOは吸着しない
、水分の存在下でNO2をNoへ還元する、NO□の吸
着容量は小さく脱着するの理由よりNOxによる被毒は
ほとんどない。In addition, although the carrier contains alkali and activated carbon, alkali and NO do not react with each other, powdered activated carbon does not adsorb NO, reduces NO2 to No in the presence of moisture, and has a small adsorption capacity for NO□, which can be desorbed. For some reason, there is almost no poisoning caused by NOx.
また燃焼装置の改良によってもNOxは大幅に低減でき
る。NOx can also be significantly reduced by improving combustion equipment.
SO2は燃料成分中のS分や空気中のH2Sの存在があ
まり考えられないので排ガス中にはほとんど存在しない
。SO2 hardly exists in the exhaust gas because the presence of S in the fuel component and H2S in the air is unlikely.
CO2は触媒の活性にあまり影響しない。CO2 does not significantly affect the activity of the catalyst.
H2Oは触媒の活性を助ける。炭火水素は触媒により酸
化される。H2O helps activate the catalyst. Hydrocarbons are oxidized by a catalyst.
以上の利用より本触媒は排ガス中の他成分ガスの影響を
受ける事なく高性能にCOを酸化する。Through the use described above, this catalyst oxidizes CO with high performance without being affected by other component gases in exhaust gas.
本発明は他の開放型燃焼器具、例えば調理器具用バーナ
ー等にも同様に適用できる。The invention is equally applicable to other open combustion appliances, such as cooker burners.
本発明は燃焼部を改良する事なく燃焼により発生するC
Oを燃焼部の上部に触媒層を設置して除去するので、燃
焼に影響を与えない。The present invention eliminates carbon dioxide generated by combustion without improving the combustion part.
Since O is removed by installing a catalyst layer above the combustion section, it does not affect combustion.
大規模な装置を必要としない。Does not require large-scale equipment.
燃焼部の上部に載せる鍋、釜の設置の妨げにならない等
の利点を有するばかりでなく学内循環するので発生する
COやNOxの量を減少させるので効果をひじように期
待できる。Not only does it have the advantage of not interfering with the installation of pots and kettles placed on top of the combustion section, but it also circulates within the campus, reducing the amount of CO and NOx generated, so it can be expected to be extremely effective.
第1図は石油ストーブへの応用例を示す正面図、第2図
は調理器具用バーナーへの応用例を示す側面図、第3図
は石油ストーブへ応用した場合のCO濃度の推移を示す
図である。Figure 1 is a front view showing an example of application to a kerosene stove, Figure 2 is a side view showing an example of application to a cookware burner, and Figure 3 is a diagram showing changes in CO concentration when applied to a kerosene stove. It is.
Claims (1)
担体に、白金とパラジウムを担持した触媒層を空気流路
に設けるとともに、上記アルカリとして炭酸カリウム、
セメント材としてアルミン酸石灰を用いた開放型燃焼器
具の排ガス浄化方法。1 A catalyst layer supporting platinum and palladium is provided in the air flow path on a carrier obtained by kneading and molding alkali, powdered activated carbon, and cement material, and as the alkali, potassium carbonate,
A method for purifying exhaust gas from open combustion appliances using lime aluminate as a cement material.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53061203A JPS5817648B2 (en) | 1978-05-22 | 1978-05-22 | Exhaust gas purification method for open combustion appliances |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53061203A JPS5817648B2 (en) | 1978-05-22 | 1978-05-22 | Exhaust gas purification method for open combustion appliances |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS54151561A JPS54151561A (en) | 1979-11-28 |
| JPS5817648B2 true JPS5817648B2 (en) | 1983-04-08 |
Family
ID=13164385
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP53061203A Expired JPS5817648B2 (en) | 1978-05-22 | 1978-05-22 | Exhaust gas purification method for open combustion appliances |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5817648B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5697868A (en) * | 1980-01-08 | 1981-08-06 | Matsushita Electric Ind Co Ltd | Analyzing method of carbon monoxide |
| CN103528106B (en) * | 2013-10-25 | 2016-03-30 | 罗依依 | A kind of smoke exhaust ventilator and method with gas cleaning and oil recovery function |
-
1978
- 1978-05-22 JP JP53061203A patent/JPS5817648B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS54151561A (en) | 1979-11-28 |
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