JP3096989B2 - Adsorbent and gas purification method containing ketone organic solvent - Google Patents
Adsorbent and gas purification method containing ketone organic solventInfo
- Publication number
- JP3096989B2 JP3096989B2 JP02410097A JP41009790A JP3096989B2 JP 3096989 B2 JP3096989 B2 JP 3096989B2 JP 02410097 A JP02410097 A JP 02410097A JP 41009790 A JP41009790 A JP 41009790A JP 3096989 B2 JP3096989 B2 JP 3096989B2
- Authority
- JP
- Japan
- Prior art keywords
- adsorbent
- zeolite
- organic solvent
- ketone
- based organic
- 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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Landscapes
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Silicates, Zeolites, And Molecular Sieves (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、ケトン系有機溶剤を含
むガスの浄化に有用な吸着剤およびその使用法に関する
ものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an adsorbent useful for purifying a gas containing a ketone organic solvent and a method for using the same.
【0002】[0002]
【従来の技術】従来、溶剤を含むガスの浄化には吸着剤
として活性炭が広範に使用されてきた。しかし、ガス中
にケトン系有機溶剤が含まれる場合には、活性炭の触媒
作用によりしばしば微量の分解生成物の生成が確認され
る。これらの分解生成物のうち、脱着され易いものは回
収溶剤の純度低下、脱着されにくいものは活性炭を汚染
して吸着障害の原因となる。また、分解生成物は酸であ
る場合が多く、これが装置材料の腐食などの悪影響をお
よぼす。2. Description of the Related Art Conventionally, activated carbon has been widely used as an adsorbent for purifying gas containing a solvent. However, when a ketone-based organic solvent is contained in the gas, the formation of trace amounts of decomposition products is often confirmed by the catalytic action of activated carbon. Of these decomposition products, those that are easily desorbed will lower the purity of the recovered solvent, and those that are hardly desorbed will contaminate the activated carbon and cause adsorption failure. The decomposition products are often acids, which have an adverse effect such as corrosion of equipment materials.
【0003】ケトン類は、吸着剤表面における酸化作用
によってエノール型中間体を経てカルボン酸を生成す
る。この反応は発熱を伴うため、急激に進行し、かつ発
生した反応熱が蓄積し、十分な酸素の供給がある場合に
は反応は連鎖的に進み、ついには活性炭層自体が発火す
ることもある。新鮮な活性炭の着火温度は、400〜5
00℃程度であるが、高沸物が多量に蓄積したものでは
200℃以下になることもある。[0003] Ketones generate a carboxylic acid via an enol-type intermediate by an oxidizing action on the surface of the adsorbent. Since this reaction is exothermic, it progresses rapidly, and the generated reaction heat accumulates.If there is sufficient oxygen supply, the reaction proceeds in a chain, and eventually the activated carbon layer itself may ignite. . The ignition temperature of fresh activated carbon is 400-5
The temperature is about 00 ° C., but it may be 200 ° C. or less when a large amount of high-boiling substances is accumulated.
【0004】この様にケトン系有機溶剤を含むガスの浄
化に活性炭を使用する場合には、様々な問題がある。こ
のため、触媒活性の低い活性炭を使用したり、吸着想の
上流部に過湿装置を設置し、吸着熱、反応熱などによる
層の温度上昇を防止するなどの工夫がなされていた。し
かし、吸着剤として活性炭を使用する以上、ケトン系有
機溶剤に対する例えば多少の触媒作用は避けられない。
過湿装置を取り付けた場合には、触媒作用の抑制は可能
となるが、相対湿度が高くなると活性炭の有機溶剤に対
する吸着量が低下する。このため、吸着装置の運転管理
には細心の注意が必要であった。As described above, there are various problems when using activated carbon for purifying a gas containing a ketone-based organic solvent. For this reason, various measures have been taken, such as using activated carbon having low catalytic activity or installing a dehumidifier upstream of the adsorption device to prevent the temperature of the bed from rising due to heat of adsorption, heat of reaction, or the like. However, as long as activated carbon is used as the adsorbent, for example, some catalytic action on the ketone organic solvent cannot be avoided.
When a humidifier is installed, the catalytic action can be suppressed, but when the relative humidity increases, the amount of activated carbon adsorbed on the organic solvent decreases. For this reason, extreme care was required in the operation management of the adsorption device.
【0005】また、近年活性炭にかわる新しい吸着剤と
して疎水性を高めたゼオライトも有機化合物の吸着に使
用され始めている(特公表60−501495号公報お
よび特開昭64−85113号公報)。Further, in recent years, zeolite having enhanced hydrophobicity as a new adsorbent replacing activated carbon has begun to be used for adsorption of organic compounds (Japanese Patent Publication No. 60-501495 and Japanese Patent Application Laid-Open No. 64-85113).
【0006】[0006]
【発明が解決しようとする課題】しかし、本発明者らが
この疎水性ゼオライトによる、ケトン系有機溶剤の吸着
を試みたところ、活性炭と同様触媒活性を示すことを見
出だした。すなわち、活性炭や疎水性ゼオライトなどに
よるケトン系有機溶剤を含む排ガスの浄化においてケト
ン系有機溶剤の吸着操作は可能であるが、吸着剤の加熱
再生等の過程においてケトン系有機溶剤が吸着剤上でそ
の触媒作用により分解または重合反応を起こす。その結
果、濃縮したまたは回収した有機溶剤中のケトン系有機
溶剤の純度は低く、再利用することができなかった。ま
た、吸脱着操作を繰り返すうちに吸着剤自体の吸着性能
も低下し、安定した排ガス浄化が出来ないだけでなく、
発火や装置腐食など安全や保守上の問題もあった。However, when the present inventors tried to adsorb a ketone organic solvent with this hydrophobic zeolite, they found that they exhibited catalytic activity similar to activated carbon. In other words, in the purification of exhaust gas containing a ketone-based organic solvent using activated carbon or hydrophobic zeolite, etc., the adsorption operation of the ketone-based organic solvent is possible, but in the process of heating and regeneration of the adsorbent, the ketone-based organic solvent is deposited on the adsorbent. A decomposition or polymerization reaction is caused by the catalytic action. As a result, the purity of the ketone-based organic solvent in the concentrated or recovered organic solvent was low and could not be reused. In addition, as the adsorption / desorption operation is repeated, the adsorption performance of the adsorbent itself decreases, and not only cannot stable exhaust gas purification be performed,
There were also safety and maintenance issues such as ignition and equipment corrosion.
【0007】発明者らは、特に吸着剤のケトン系有機溶
剤に対する触媒活性に注目し、特別な操作を行うことな
く排ガスから高純度のケトン系有機を回収でき、さらに
は発火や吸着性能低下の恐れがない、ケトン系有機溶剤
に対して触媒性を示さない吸着剤を提供すべく鋭意検討
を重ねた。The inventors have paid particular attention to the catalytic activity of the adsorbent for ketone-based organic solvents, and have been able to recover high-purity ketone-based organics from exhaust gas without performing any special operation. The present inventors have conducted intensive studies to provide an adsorbent that does not show a catalytic property with respect to a ketone organic solvent without fear.
【0008】[0008]
【課題を解決するための手段】本発明は、ケトン系有機
溶剤を含む排ガスの浄化に好適な、水熱焼成を行った疎
水性ゼオライトからなる吸着剤およびその使用法を提供
するものである。SUMMARY OF THE INVENTION The present invention provides an adsorbent comprising hydrothermally calcined hydrophobic zeolite which is suitable for purifying exhaust gas containing a ketone-based organic solvent, and a method of using the same.
【0009】以下、本発明の詳細について説明する。Hereinafter, the present invention will be described in detail.
【0010】ゼオライト結晶の基本構造はSiO4およ
びその置換体のAlO4のそれぞれの四面体であり、そ
れらが互いに頂点の酸素原子を共有し、3次元方向に発
達した結晶構造を形成している。その結果、ゼオライト
結晶は他の鉱物にみられないような非常に大きな空洞や
孔路を有している。これらの細孔の入口径はゼオライト
によって異なるが、通常3〜9オングストロームであり
種々の分子を細孔内部に捕捉することができる。また、
結晶内部にはAlO4の負電荷を補うために陽イオンが
存在している。この陽イオンによって形成された静電場
の影響により極性分子や分極性分子を選択的に吸着す
る。汎用の吸着剤として一般的に使用されているA型ゼ
オライト、X型ゼオライト、Y型ゼオライト等のSiO
2/Al2O3モル比は2〜5と低く、これらのゼオラ
イトは有機化合物よりも水を選択的に吸着する。したが
って、有機溶剤を含む排ガスの浄化用吸着剤としては適
当ではない。The basic structure of a zeolite crystal is a tetrahedron of SiO 4 and its substituted AlO 4 , which share the apex oxygen atom with each other to form a crystal structure developed in a three-dimensional direction. . As a result, zeolite crystals have very large cavities and pores that are not found in other minerals. Although the entrance diameter of these pores differs depending on the zeolite, it is usually 3 to 9 Å, and various molecules can be trapped inside the pores. Also,
A cation exists inside the crystal to supplement the negative charge of AlO 4 . Polar molecules and polarizable molecules are selectively adsorbed under the influence of the electrostatic field formed by the cations. SiO such as A-type zeolite, X-type zeolite and Y-type zeolite which are generally used as general-purpose adsorbents
The 2 / Al 2 O 3 molar ratio is as low as 2 to 5, and these zeolites adsorb water selectively over organic compounds. Therefore, it is not suitable as an adsorbent for purifying exhaust gas containing an organic solvent.
【0011】ゼオライトはSiO2/Al2O3モル比
20以上で親水性失い、次第に疎水性を示すようにな
る。このように疎水性を示すゼオライトは、有機溶剤を
含む排ガスの浄化に対して、活性炭と同様に疎水性吸着
剤として有用である。しかし、疎水性ゼオライトは同時
に触媒作用も備えている。従って、ケトン系有機溶剤等
のように反応性の高い有機化合物と接触させた場合、加
熱再生の過程で吸着されたケトン系有機溶剤はゼオライ
トの触媒作用により分解または重合反応をおこす。さら
に、長期間吸着剤として使用しているうちに残留してい
るケトン系有機溶剤は低重合物あるいは分解物となり、
発火、吸着能低下、装置腐食等の原因となる。この様な
触媒反応は再生を加熱によって行う場合の脱着操作では
特に激しくおこり、低温で行うPSA操作でもわずかで
はあるが進行する。さらに、ケトン系有機溶剤の分解反
応が発熱反応であるために、熱再生を伴わないPSA法
の場合でも反応熱が吸着剤層に蓄積し、吸着剤温度が急
激に上昇する場合がある。Zeolite loses hydrophilicity at a SiO 2 / Al 2 O 3 molar ratio of 20 or more and gradually becomes hydrophobic. The zeolite exhibiting such hydrophobicity is useful as a hydrophobic adsorbent, similarly to activated carbon, for purifying exhaust gas containing an organic solvent. However, hydrophobic zeolites also have a catalytic effect. Therefore, when it is brought into contact with a highly reactive organic compound such as a ketone-based organic solvent, the ketone-based organic solvent adsorbed in the process of heating and regeneration causes a decomposition or polymerization reaction by the catalytic action of zeolite. Furthermore, the ketone-based organic solvent remaining during use as an adsorbent for a long time becomes a low polymer or a decomposed product,
It may cause ignition, decrease in adsorption capacity, and corrosion of equipment. Such a catalytic reaction occurs particularly violently in the desorption operation in the case where the regeneration is performed by heating, and progresses to a small extent even in the PSA operation performed at a low temperature. Furthermore, since the decomposition reaction of the ketone-based organic solvent is an exothermic reaction, even in the case of the PSA method without heat regeneration, the heat of reaction accumulates in the adsorbent layer and the adsorbent temperature may rise rapidly.
【0012】この触媒反応の活性点は疎水性ゼオライト
結晶中の酸点または塩基点と考えられる。したがって、
SiO2/Al2O3モル比が無限大のゼオライトは触
媒作用がないと考えられる。しかしながら、実際に入手
または調整の可能なゼオライトのSiO2/Al2O3
モル比は、500程度が限界である。これは、ゼオライ
トの原料として使用可能な珪素源中に微量ではあるが珪
素以外の金属酸化物が含まれていることによる。例え
ば、直接合成法の場合には、珪素源中の微量のアルミニ
ウム等の金属原子が結晶化の過程で選択的にゼオライト
結晶骨格に取り込まれる。また、鉱酸等による酸抽出法
の場合でもゼオライト中の微量の金属原子を完全に除去
することは実際上不可能である。The active site of this catalytic reaction is considered to be an acid site or a base site in the hydrophobic zeolite crystal. Therefore,
A zeolite having an infinite SiO 2 / Al 2 O 3 molar ratio is considered to have no catalytic action. However, the zeolite SiO 2 / Al 2 O 3 that is actually available or tunable
The limit of the molar ratio is about 500. This is because a small amount of a metal oxide other than silicon is contained in a silicon source usable as a raw material of zeolite. For example, in the case of the direct synthesis method, a trace amount of metal atoms such as aluminum in a silicon source are selectively incorporated into the zeolite crystal skeleton during the crystallization process. Further, even in the case of an acid extraction method using a mineral acid or the like, it is practically impossible to completely remove a trace amount of metal atoms in zeolite.
【0013】この様な理由から、疎水性を示すゼオライ
トは、反応性の高いケトン系有機溶剤を含む排ガスに対
してその触媒作用により、従来吸着剤としての使用が困
難であった。For these reasons, zeolite exhibiting hydrophobicity has been conventionally difficult to use as an adsorbent due to its catalytic action on exhaust gas containing highly reactive ketone-based organic solvents.
【0014】しかしながら、ゼオライトの結晶骨格はS
iO4やAlO4等の無機酸化物で形成されており、不
燃性である。このため、有機溶剤等の可燃性物質を含む
排ガスの浄化に対して吸着剤自体が着火する事がなく、
安全上極めて魅力的な吸着剤である。However, the crystal skeleton of zeolite is S
It is made of an inorganic oxide such as iO 4 or AlO 4 and is nonflammable. For this reason, the adsorbent itself does not ignite for purification of exhaust gas containing flammable substances such as organic solvents,
It is a very attractive adsorbent for safety.
【0015】本発明者らは、各種ゼオライトを直接合成
法または合成ゼオライトに修飾処理を施す方法によって
調製し、ケトン系有機溶剤に対して触媒活性のないゼオ
ライト系吸着剤を得るべく鋭意検討を重ねた。その結
果、水熱焼成を行った疎水性ゼオライトはケトン系有機
溶剤に対して、触媒活性を示さず、発火等の危険性のな
い優れた吸着剤であることを見いだした。The present inventors have prepared various zeolites by a direct synthesis method or a method of modifying the synthetic zeolites, and have intensively studied to obtain a zeolite adsorbent having no catalytic activity for a ketone organic solvent. Was. As a result, it has been found that the hydrothermally calcined hydrophobic zeolite does not exhibit catalytic activity with respect to the ketone-based organic solvent and is an excellent adsorbent having no danger of ignition.
【0016】疎水性ゼオライトのSiO2/Al2O3
モル比が50未満の場合は、水熱焼成処理を行ってもケ
トン系有機溶剤に対する活性点を完全に消滅させること
が困難であり、よりよく活性点を消滅させるうえで、疎
水性ゼオライトとしてはSiO2/Al2O3モル比5
0以上のものが好適である。水熱焼成処理の条件は、疎
水性ゼオライトの構造やSiO2/Al2O3モル比に
よって異なるが、水熱焼成処理の条件を工夫することに
よってケトン系有機溶剤に対して触媒活性を示さない吸
着剤を得ることが可能である。The hydrophobic zeolite SiO 2 / Al 2 O 3
When the molar ratio is less than 50, it is difficult to completely extinguish the active sites for the ketone-based organic solvent even when the hydrothermal calcination treatment is performed, and in order to extinguish the active sites better, as a hydrophobic zeolite, SiO 2 / Al 2 O 3 molar ratio 5
Those having 0 or more are preferable. The conditions of the hydrothermal calcination treatment vary depending on the structure of the hydrophobic zeolite and the SiO 2 / Al 2 O 3 molar ratio, but by devising the conditions of the hydrothermal calcination treatment, no catalytic activity is exhibited for the ketone-based organic solvent. It is possible to obtain an adsorbent.
【0017】疎水性ゼオライトの調製方法としては、天
然ゼオライト或は合成ゼオライトを出発原料として鉱酸
などを用いた脱アルミニウム処理等によって調製する方
法或はシリカ源、アルミナ源、アルカリ源及び有機鉱化
剤を混合し結晶化する直接合成法がある。The hydrophobic zeolite may be prepared by a method of preparing a natural zeolite or a synthetic zeolite as a starting material by dealumination using a mineral acid or the like, or a silica source, an alumina source, an alkali source and an organic mineralizer. There is a direct synthesis method in which an agent is mixed and crystallized.
【0018】脱アルミニウム処理等によって調製された
疎水性ゼオライトとしては、脱アルミニウムモルデナイ
ト((N.Y.Chen,J.Phy.Chem.,8
0,(1),60−64(1976))、超疎水性Y型
ゼオライト(特開昭54−122700号公報、Stu
dies in Surface Science a
nd Catalysis,Volume 5,203
−210(1980)、疎水性L型ゼオライト(特開昭
63−50312号公報)などが知られている。Examples of the hydrophobic zeolite prepared by dealumination or the like include dealuminated mordenite ((NY Chen, J. Phy. Chem., 8).
0, (1), 60-64 (1976)), superhydrophobic Y-type zeolite (JP-A-54-122700, Stu)
dies in Surface Science a
nd Catalyst, Volume 5,203
-210 (1980), hydrophobic L-type zeolite (JP-A-63-50312) and the like.
【0019】直接合成法によって調製された疎水性ゼオ
ライトとしては、ZSM−5(特公昭46−10064
号公報)、ZSM−11(特公昭53−23280号公
報)、ZSM−12(特公昭52−16079号公
報)、ZSM−22(特開昭59−111912号公
報)、ZSM−23(特開昭51−149900号公
報)、ZSM−48(特開昭56−22622号公
報)、シリカライト(特開昭54−72795号公報)
等が知られている。The hydrophobic zeolite prepared by the direct synthesis method includes ZSM-5 (JP-B-46-10064).
JP), ZSM-11 (JP-B No. 53-23280), ZSM-12 (JP-B No. 52-16079), ZSM-22 (JP-A No. 59-111912), and ZSM-23 (JP-A No. 59-111912). JP-A-51-149900), ZSM-48 (JP-A-56-22622), silicalite (JP-A-54-72795).
Etc. are known.
【0020】これらいずれをも本発明の疎水性ゼオライ
トとして好適に使用することができる。Any of these can be suitably used as the hydrophobic zeolite of the present invention.
【0021】また、ゼオライトは分子ふるい効果を示す
ため、吸着可能な分子の種類はゼオライト種類によって
決まる。ケトン系有機溶剤を排ガス中から回収する場合
は、ゼオライトの細孔入口径が吸着される分子径よりも
大きければよい。通常は、細孔入口が酵素8、10また
は12員環のゼオライトであればよく、チャバサイト、
オフレタイト、モルデナイト、フォージャサイト、L、
Ω、ZSM−5、ZSM−11型などの結晶構造のもの
が適している。Since zeolite exhibits a molecular sieving effect, the types of molecules that can be adsorbed are determined by the type of zeolite. When the ketone-based organic solvent is recovered from the exhaust gas, it is sufficient that the pore entrance diameter of the zeolite is larger than the molecular diameter to be adsorbed. Normally, the pore entrance may be a zeolite having an 8, 10 or 12-membered enzyme ring, such as chabazite,
Offretite, mordenite, faujasite, L,
Crystal structures such as Ω, ZSM-5 and ZSM-11 are suitable.
【0022】疎水性ゼオライトに対する水熱焼成処理の
水蒸気濃度は2vol%以上がよく、5vol%以上の
水蒸気濃度が実用的な実施条件である。水蒸気濃度が高
い場合は焼成温度が比較的穏やかな条件下でも本発明の
吸着剤を得ることが可能である。しかし、500℃未満
の温度での水熱焼成では、吸着剤のケトン系有機溶剤に
対する触媒活性は完全に消滅させることは困難である。
また、1200℃をこえると、疎水性ゼオライトの結晶
構造自体が崩壊しがちである。すなわち、水熱焼成を実
施するのに好適な温度範囲は、500〜1200℃であ
り、望ましくは600〜1000℃である。水熱焼成処
理の時間は水蒸気濃度及び焼成温度によって異なるが、
上記温度範囲において30分以上行う必要がある。The water vapor concentration in the hydrothermal calcination treatment on the hydrophobic zeolite is preferably 2 vol% or more, and a water vapor concentration of 5 vol% or more is a practical condition for practical use. When the water vapor concentration is high, the adsorbent of the present invention can be obtained even under the condition that the calcination temperature is relatively mild. However, in the case of hydrothermal calcination at a temperature lower than 500 ° C., it is difficult to completely eliminate the catalytic activity of the adsorbent for the ketone-based organic solvent.
When the temperature exceeds 1200 ° C., the crystal structure itself of the hydrophobic zeolite tends to collapse. That is, the temperature range suitable for performing hydrothermal calcination is 500 to 1200 ° C, preferably 600 to 1000 ° C. The time of hydrothermal firing varies depending on the water vapor concentration and firing temperature,
It is necessary to carry out for 30 minutes or more in the above temperature range.
【0023】吸着剤は通常、円柱状、球状またはハニカ
ム状の形態で使用される。ゼオライト粉末をこれらの形
状のものとするには、疎水性ゼオライト結晶自体に結晶
性がないので、担体とゼオライト結晶またはゼオライト
結晶相互の結合性を高めるためシリカゾル、シリカゲ
ル、粘土鉱物等の無機系バインダー成分を添加し、成形
やハニカム化等の2次加工を行う。バインダー成分とし
ては不活性なものが望ましく、アルミナゾルやアルミナ
ゲルのようにケトン系有機溶剤に対して反応活性を示す
ものは不適当である。また、成形やハニカム化の後、こ
れら2次加工品の形状を維持させるために焼成処理が必
要である。このとき、水熱条件下で焼成操作をおこなえ
ば、疎水性ゼオライト粉末を予じめ水熱焼成しておく必
要はない。すなわち、本発明の吸着剤を製造する合理的
な実施方法として、まず疎水性ゼオライト粉末の2次加
工を行い、引続き水熱焼成を行う方法が可能である。も
ちろん、水熱焼成を行った疎水性ゼオライト粉末を2次
加工し、穏やかな条件下で焼成しても本発明の吸着剤を
得ることができる。The adsorbent is usually used in the form of a column, a sphere or a honeycomb. In order to make the zeolite powder of these shapes, since the hydrophobic zeolite crystal itself has no crystallinity, an inorganic binder such as silica sol, silica gel, clay mineral or the like is used to enhance the binding between the carrier and the zeolite crystal or zeolite crystal. The components are added and secondary processing such as molding and honeycomb formation is performed. As the binder component, an inactive one is desirable, and one that shows a reaction activity with respect to a ketone-based organic solvent such as alumina sol or alumina gel is inappropriate. Further, after forming or honeycomb formation, a baking treatment is required to maintain the shape of these secondary processed products. At this time, if the calcination operation is performed under hydrothermal conditions, it is not necessary to previously hydrophobize the hydrophobic zeolite powder. That is, as a rational method for producing the adsorbent of the present invention, a method in which the hydrophobic zeolite powder is firstly subjected to secondary processing and then hydrothermal firing is possible. Needless to say, the adsorbent of the present invention can be obtained by subjecting the hydrophobic zeolite powder subjected to hydrothermal firing to secondary processing and firing under mild conditions.
【0024】ところで、バインダーを使用しないで製造
されたゼオライト成形体が特開昭62−70225号や
特開昭62−138320号などの公報に示されてい
る。この様な、バインダー成分を含まないゼオライト成
形体を脱アルミニウム処理し、疎水性ゼオライトとした
ものを水熱焼成したものは、吸着量が大きく本発明の吸
着剤としてさらに好適である。Incidentally, zeolite molded bodies produced without using a binder are disclosed in Japanese Patent Application Laid-Open Nos. 62-70225 and 62-138320. Such a zeolite molded body that does not contain a binder component is subjected to dealumination treatment to obtain a hydrophobic zeolite, which is then subjected to hydrothermal calcination, which has a large adsorption amount and is more suitable as the adsorbent of the present invention.
【0025】本発明の吸着剤は、メチルエチルケトン、
メチルイソブチルケトン、シクロヘキサノンなどのケト
ン系有機溶剤を含む排ガスの浄化用吸着剤として特に有
用であり、固定層吸着装置、流動層吸着装置、移動層吸
着装置、ハニカムローター濃縮装置などいずれの装置に
おいても好適に使用できる。また、吸脱着操作の方法と
してPSA法、PTSA法、TSA法などがあるがいず
れの方式にも適用することができる。The adsorbent of the present invention comprises methyl ethyl ketone,
It is particularly useful as an adsorbent for purifying exhaust gas containing ketone-based organic solvents such as methyl isobutyl ketone and cyclohexanone, and can be used in any device such as a fixed-bed adsorption device, a fluidized-bed adsorption device, a moving-bed adsorption device, and a honeycomb rotor concentration device. It can be suitably used. In addition, there are a PSA method, a PTSA method, a TSA method, and the like as a method of the adsorption / desorption operation, but any method can be applied.
【0026】[0026]
【発明の効果】この発明は、以上述べたように、水熱焼
成を行った疎水性ゼオライトをケトン系有機溶剤を含む
排ガス浄化用吸着剤として提供するものである。これに
より、従来困難であったケトン系有機溶剤排ガスの濃縮
や溶剤回収などの吸着操作が、吸着装置に特別な工夫を
施すことなく可能となった。また、本発明の吸着剤が触
媒性をまったく示さないため、従来問題となっていた吸
着装置の腐食や吸着剤層の発火等の危険性がなくなっ
た。As described above, the present invention provides a hydrothermally calcined hydrophobic zeolite as an adsorbent for purifying exhaust gas containing a ketone-based organic solvent. As a result, adsorption operations such as concentration of exhaust gas of a ketone-based organic solvent and solvent recovery, which have been difficult in the past, can be performed without special measures for the adsorption device. In addition, since the adsorbent of the present invention does not show any catalytic property, the danger of corrosion of the adsorber and ignition of the adsorbent layer, which have been problems in the related art, are eliminated.
【0027】[0027]
【実施例】以下に、本発明の実施例を説明する。 実施例1,比較例1(実施例1) SiO2/Al2O3モル比14、格子定数24.33
オングストロームのY型ゼオライトを50℃の1.5N
の塩酸水溶液により脱アルミニウム処理し、SiO2/
Al2O3モル比500の疎水性Y型ゼオライトを得
た。この疎水性ゼオライト100重量部に対してバイン
ダーとして25重量部の粘土を加え、直径3mmの円柱
状成形体を得た。この成形体を水蒸気濃度20vol%
の空気流通下、800℃で2時間焼成し、吸着剤をえ
た。Embodiments of the present invention will be described below. Example 1, Comparative Example 1 (Example 1) SiO 2 / Al 2 O 3 molar ratio 14, lattice constant 24.33
Angstrom Y-type zeolite with 1.5N at 50 ° C
Dealumination with a hydrochloric acid aqueous solution of SiO 2 /
A hydrophobic Y-type zeolite having an Al 2 O 3 molar ratio of 500 was obtained. 25 parts by weight of clay was added as a binder to 100 parts by weight of this hydrophobic zeolite to obtain a columnar molded body having a diameter of 3 mm. This molded body is subjected to a water vapor concentration of 20 vol%.
The mixture was calcined at 800 ° C. for 2 hours under an air flow to obtain an adsorbent.
【0028】(比較例1) 一方、塩酸水溶液による脱アルミニウム処理を行ってい
ないSiO2/Al2O3モル比14のY型ゼオライト
100重量部に対してバインダーとして25重量部の粘
土を加え、直径3mmの円柱状成形体を得た。この成形
体を水蒸気濃度20vol%の空気流通下、800℃で
2時間焼成し、吸着剤をえた。[0028] (Comparative Example 1) On the other hand, 25 parts by weight of the clay added as a binder with respect to Y-type zeolite 100 parts by weight of SiO 2 / Al 2 O 3 molar ratio 14 not subjected to dealumination by aqueous hydrochloric acid, A cylindrical molded body having a diameter of 3 mm was obtained. The molded body was fired at 800 ° C. for 2 hours under an air flow having a water vapor concentration of 20 vol% to obtain an adsorbent.
【0029】メチルエチルケトンに対するこれら吸着剤
の吸脱着試験を以下の方法によって行った。The adsorption / desorption test of these adsorbents with respect to methyl ethyl ketone was performed by the following method.
【0030】<吸脱着試験方法> 吸脱着試験用カラムはガラス製の内径6cm、長さ45
cmのものを使用した。このカラムに吸着剤を層高35
cmとなるように充填し、吸脱着試験を行った。吸着試
験は、25℃でおこなった。メチルエチルケトン濃度3
000ppmの空気(水分濃度10000ppm)を流
速0.2m/秒で吸着剤層に流し、出口部のメチルエチ
ルケトン濃度が150ppmとなった時間を破過時間
(分)とした。さらに、出口部のメチルエチルケトン濃
度が3000ppmになるまで吸着試験を行い、吸着試
験終了後のカラム重量(Wa)を測定した。<Adsorption / desorption test method> The adsorption / desorption test column was made of glass and had an inner diameter of 6 cm and a length of 45 cm.
cm. This column is filled with adsorbent at bed height 35.
cm, and an adsorption / desorption test was performed. The adsorption test was performed at 25 ° C. Methyl ethyl ketone concentration 3
000 ppm air (moisture concentration 10,000 ppm) was flowed through the adsorbent layer at a flow rate of 0.2 m / sec, and the time when the methyl ethyl ketone concentration at the outlet became 150 ppm was defined as breakthrough time (minutes). Further, the adsorption test was performed until the methyl ethyl ketone concentration at the outlet became 3000 ppm, and the column weight (Wa) after the completion of the adsorption test was measured.
【0031】脱離試験は、メチルエチルケトンを吸着し
た吸着剤層に0.075m/秒で乾燥空気を流しながら
カラムをリボンヒーターで150℃まで加熱し、メチル
エチルケトンの出口濃度が10ppm以下となるまで行
い、カラムを冷却し、脱離試験終了後のカラム重量(W
d)を測定した。また、脱離ガス中のメチルエチルケト
ン濃度を図積分し、メチルエチルケトン回収量(Wr)
をもとめた。In the desorption test, the column was heated to 150 ° C. with a ribbon heater while flowing dry air at 0.075 m / sec through the adsorbent layer adsorbing methyl ethyl ketone, until the outlet concentration of methyl ethyl ketone became 10 ppm or less. After cooling the column, the column weight (W
d) was measured. In addition, the methyl ethyl ketone concentration in the desorbed gas is integrated, and the recovered methyl ethyl ketone (Wr)
I sought.
【0032】メチルエチルケトン回収率(%)は、次式
により求めた。結果を表1に示す。The methyl ethyl ketone recovery rate (%) was determined by the following equation. Table 1 shows the results.
【0033】 メチルエチルケトン回収率(%)=Wr×100/(W
a−Wd) 吸着層の入口および出口のメチルエチルケトン濃度は、
ガスクロマトグラフィー(検出計:FID)で測定し
た。 実施例2,比較例2(実施例2) 合成モルデナイト型ゼオライトを脱アルミニウム処理
し、SiO2/Al2O3モル比200の疎水性モルデ
ナイト型ゼオライトを得た。この疎水性モルデナイト型
ゼオライト100重量部に対してバインダーとして25
重量部のシリカゾルを加え、直径3mmの円柱状成形体
を得た。この成形体を水蒸気濃度20vol%の空気流
通下、700℃で10時間焼成し、吸着剤をえた。Methyl ethyl ketone recovery rate (%) = Wr × 100 / (W
a-Wd) The methyl ethyl ketone concentrations at the inlet and outlet of the adsorption layer are
It was measured by gas chromatography (detector: FID). Example 2, Comparative Example 2 (Example 2) Synthesis mordenite zeolite dealuminated, hydrophobic-mordenite type zeolite of SiO 2 / Al 2 O 3 molar ratio of 200. 100 parts by weight of this hydrophobic mordenite type zeolite is used as a binder as 25
The silica sol in parts by weight was added to obtain a cylindrical molded body having a diameter of 3 mm. This molded body was fired at 700 ° C. for 10 hours under an air flow having a water vapor concentration of 20 vol% to obtain an adsorbent.
【0034】(比較例2) 焼成を乾燥空気中で行った以外は実施例2と同様に行
い、吸着剤をえた。Comparative Example 2 An adsorbent was obtained in the same manner as in Example 2 except that calcination was performed in dry air.
【0035】これらの吸着剤についても、実施例1と同
様の方法で吸脱着試験を行い、メチルエチルケトン回収
率を求めた。For these adsorbents, an adsorption / desorption test was performed in the same manner as in Example 1, and the methyl ethyl ketone recovery rate was determined.
【0036】 表 1 破過時間(分) メチルエチルケトン回収率(%) 実施例1 260 99.9 比較例1 260 94.8 実施例2 151 99.2 比較例2 155 84.7Table 1 Breakthrough time (min) Methyl ethyl ketone recovery rate (%) Example 1 260 99.9 Comparative Example 1 260 94.8 Example 2 151 99.2 Comparative Example 2 155 84.7
Claims (3)
3モル比が50以上であることを特徴とするケトン系有
機溶剤を吸着する疎水性ゼオライトからなる吸着剤1. A hydrothermal sintering treatment is performed to obtain SiO 2 / Al 2 O
An adsorbent comprising a hydrophobic zeolite for adsorbing a ketone-based organic solvent, wherein the molar ratio is 3 or more.
上,焼成温度500〜1200℃および焼成時間30分
以上の条件で行われたものである、請求項1記載の吸着
剤。2. The adsorbent according to claim 1, wherein the hydrothermal calcination treatment is performed under the conditions of a steam concentration of 2 vol% or more, a calcination temperature of 500 to 1200 ° C., and a calcination time of 30 minutes or more.
1,または2に記載の吸着剤と接触させることを特徴と
する、ケトン系有機溶剤含有ガスの浄化方法。3. A method for purifying a gas containing a ketone-based organic solvent, comprising bringing a gas containing a ketone-based organic solvent into contact with the adsorbent according to claim 1 or 2.
Priority Applications (5)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP02410097A JP3096989B2 (en) | 1990-12-13 | 1990-12-13 | Adsorbent and gas purification method containing ketone organic solvent |
| DE1991600534 DE69100534T3 (en) | 1990-12-13 | 1991-10-04 | Purification method of exhaust gases containing organic ketone solvents |
| EP19910116924 EP0490037B2 (en) | 1990-12-13 | 1991-10-04 | Method of cleaning waste gas containing ketonic organic solvents |
| CA 2054254 CA2054254C (en) | 1990-12-13 | 1991-10-25 | Adsorbent and cleaning method of waste gas containing ketonic organic solvents |
| US07/987,538 US5256385A (en) | 1990-12-13 | 1992-12-07 | Adsorbent and cleaning method of waste gas containing ketonic organic solvents |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP02410097A JP3096989B2 (en) | 1990-12-13 | 1990-12-13 | Adsorbent and gas purification method containing ketone organic solvent |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH04210235A JPH04210235A (en) | 1992-07-31 |
| JP3096989B2 true JP3096989B2 (en) | 2000-10-10 |
Family
ID=18519323
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP02410097A Expired - Fee Related JP3096989B2 (en) | 1990-12-13 | 1990-12-13 | Adsorbent and gas purification method containing ketone organic solvent |
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| Country | Link |
|---|---|
| JP (1) | JP3096989B2 (en) |
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| JP2017114755A (en) * | 2015-12-25 | 2017-06-29 | ユニオン昭和株式会社 | Zeolite and manufacturing method therefor |
| KR102151420B1 (en) * | 2018-11-27 | 2020-09-03 | 주식회사 에코프로 | Chemical filter |
| JP2021080132A (en) * | 2019-11-19 | 2021-05-27 | 東ソー株式会社 | Hydrophobic zeolite and method for producing the same |
| JP7540167B2 (en) * | 2020-03-10 | 2024-08-27 | 東ソー株式会社 | Hydrophobic MFI zeolite, its production method, and its uses |
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|---|---|
| JPH04210235A (en) | 1992-07-31 |
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