JP2008006320A - Cleaning regeneration filtering media and method for manufacturing cleaning regeneration filtering media - Google Patents
Cleaning regeneration filtering media and method for manufacturing cleaning regeneration filtering media Download PDFInfo
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本発明は、一般家庭で使用される空気清浄機や24時間換気システム空調機、一般ビル・工場向け空調機、家電機器、車載空調機などの機器搭載用洗浄再生エアフィルターや油水分離機、一般固液分離機などの液体用洗浄再生フィルターユニットに好適に利用できる洗浄再生濾材に関する。 The present invention relates to an air purifier, a 24-hour ventilation system air conditioner used in general households, an air conditioner for general buildings and factories, home appliances, an on-vehicle air conditioner, etc. The present invention relates to a cleaning / regeneration filter medium that can be suitably used for a liquid cleaning / regeneration filter unit such as a solid-liquid separator.
ビルの空調管理に用いられているフィルターユニットは、現在使い捨てが多いが、一部のフィルターユニットでは、洗剤を溶かした洗浄液にフィルターユニットを浸し、その状態で超音波を照射して、洗浄液による溶解作用と超音波による物理的作用を用いて洗浄再生が行われている。しかしながら微細塵を捕集することが目的の空調用フィルターユニットや家庭用空気清浄用フィルターユニットには、捕集されるダストの成分として、ディーゼル排ガスに含まれる0.1μm前後の超微粒子カーボンやタバコの煙、厨房から排出される油煙、一般の大気ダストや繊維くずなど、様々なダスト成分が強く固着しており、洗浄液に漬けて超音波を当てるだけでは十分に落ちないのが実状である。 Many filter units currently used for air conditioning management in buildings are disposable, but in some filter units, the filter unit is immersed in a cleaning solution in which detergent is dissolved, and ultrasonic waves are irradiated in that state to dissolve the cleaning unit. Cleaning and regeneration are performed using the action and the physical action of ultrasonic waves. However, in air conditioning filter units and household air cleaning filter units whose purpose is to collect fine dust, ultrafine carbon particles and tobacco of about 0.1 μm contained in diesel exhaust gas are used as components of collected dust. Various dust components such as smoke, oil discharged from the kitchen, general atmospheric dust and fiber scraps are firmly fixed, and it is actually the case that they are not sufficiently removed just by immersing them in cleaning liquid and applying ultrasonic waves.
このため濾材を予め界面活性剤で処理しておき、この濾材にダストを捕集させることで洗浄再生能力を向上させる技術が特許文献1および特許文献2に開示されている。この方法は繊維の親水性を向上させることでダストの剥離性向上を狙った技術である。しかしながら、濾材の表面に界面活性剤を付与しているだけであるため、1回目の洗浄では多少洗浄性が得られるものの、洗浄後のすすぎ工程で界面活性剤がダストとともに洗い流され、2回目以降の洗浄再生能力は極端に悪くなるという問題があった。また家庭用の空気清浄機フィルターユニット、例えば粒子径0.3μmの粒子を99%捕集するような高捕集フィルターユニットの洗浄においては、家庭内に超音波機などが無く、洗浄液に漬け流水で流す程度ではダストの十分な脱離が望めないため、通気性の十分な回復が十分には望めなかった。さらに、高捕集フィルターユニットを構成する濾材には、通常エレクトレット化処理が施されるが、多用されるポリプロピレン繊維からなる濾材を界面活性剤で処理するとイオンの影響でエレクトレット化が不可能になる。そのため、これまでは、エレクトレットフィルターで洗浄再生能力の高いものは作ることが不可能であった。 For this reason, Patent Document 1 and Patent Document 2 disclose techniques for improving the cleaning and regeneration ability by treating the filter medium with a surfactant in advance and collecting dust on the filter medium. This method is a technique aimed at improving dust releasability by improving the hydrophilicity of the fiber. However, since the surface active agent is only applied to the surface of the filter medium, the first cleaning can provide some cleaning performance, but the surfactant is washed away with dust in the rinsing step after the cleaning, and the second and subsequent times. There has been a problem that the cleaning and regeneration ability of the above becomes extremely worse. Also, when cleaning household air purifier filter units, for example, high-collection filter units that collect 99% of particles with a particle size of 0.3 μm, there is no ultrasonic machine in the home, soak in running water. Since it was not possible to expect sufficient detachment of the dust with a flow rate of 1, the air permeability could not be fully recovered. Further, the filter medium constituting the high collection filter unit is usually subjected to electret treatment. However, if the filter medium made of polypropylene fiber is treated with a surfactant, electret conversion becomes impossible due to the influence of ions. . Therefore, until now, it has been impossible to make an electret filter with high cleaning and regeneration ability.
一方、特許文献3に開示されるように、濾材に撥水性を与えるためにフッ素樹脂を付着させる方法も広く行われている。しかしながら、この方法は、濾材にサイズロール等でフッ素樹脂を塗布するため、繊維間の空隙を目詰まりさせる方向に作用する。そのため、特に繊維径が3〜6μmの極細繊維で構成されたメルトブロー不織布など極細繊維で構成された素材を濾材とする場合には、通気抵抗が大幅に増加する欠点があった。 On the other hand, as disclosed in Patent Document 3, a method of attaching a fluororesin is widely performed in order to impart water repellency to the filter medium. However, since this method applies the fluororesin to the filter medium with a size roll or the like, it acts in the direction of clogging the voids between the fibers. For this reason, in particular, when a material composed of ultrafine fibers such as a melt blown nonwoven fabric composed of ultrafine fibers having a fiber diameter of 3 to 6 μm is used as a filter medium, there is a drawback that the airflow resistance is greatly increased.
この他、濾過材料を親水化する技術は特許文献4にも開示されている。この文献に記載の技術は、親油性の超高分子量ポリエチレン多孔膜をアルゴン等の炭化水素系のガス雰囲気中に入れプラズマ加工を行い親水性にするというものである。この方法によれば、加工直後は濾材を構成する繊維表面に親水性基が付着しているが、親水性基が時間の経過と共に繊維内部に潜り込むためか親水性が低下し、洗浄性が持続しないという問題があった。また、特許文献4には、疎水性膜の親水性を高めるため、膜をフッ素系の界面活性剤などで処理する方法や膜をフッ素ガスに接触させ表面加工を施す方法が存在することも紹介されている。しかしながら、これらはいずれも濾材表面に施されるものであるため、上述したような問題があるものであった。
本発明の目的は、家庭で洗浄しても十分に付着ダストが落ち通気性の回復性が望める洗浄再生濾材および洗浄再生フィルターユニットを提供することを目的とする。 An object of the present invention is to provide a cleaning / regeneration filter medium and a cleaning / regeneration filter unit that can sufficiently reduce attached dust even after cleaning at home, and that can be improved in air permeability.
上記課題を解決するための本発明は、次の(1)〜(5)を特徴とするものである。
(1)濾材を構成する素材の分子構造にフッ素原子とカルボキシル基とを含む洗浄再生濾材。
(2)JIS L1907(2004)に記載のバイレック法に準拠して測定された水吸い上げ高さが5mm以上である、前記(1)に記載の洗浄再生濾材。
(3)少なくともエレクトレット不織布を含む、前記(1)または(2)に記載の洗浄再生濾材。
(4)前記(1)〜(3)のいずれかに記載の洗浄再生濾材を用いた洗浄再生フィルターユニット。
(5)フッ素、酸素、および水分と反応させることによって、濾材を構成する素材の分子構造にフッ素原子とカルボキシル基とを導入することを特徴とする洗浄再生濾材の製造方法。
The present invention for solving the above-described problems is characterized by the following (1) to (5).
(1) A cleaning and regenerating filter medium containing a fluorine atom and a carboxyl group in the molecular structure of the material constituting the filter medium.
(2) The washed and regenerated filter medium according to (1), wherein the water suction height measured in accordance with the birec method described in JIS L1907 (2004) is 5 mm or more.
(3) The cleaning / regenerating filter medium according to (1) or (2), comprising at least an electret nonwoven fabric.
(4) A cleaning / regenerating filter unit using the cleaning / regenerating filter medium according to any one of (1) to (3).
(5) A method for producing a washed and regenerated filter medium, wherein fluorine atoms and carboxyl groups are introduced into the molecular structure of the material constituting the filter medium by reacting with fluorine, oxygen, and moisture.
本発明の洗浄再生濾材は、濾材を構成する素材の分子構造にカルボキシル基が導入されているので、当該素材が極細繊維のポリプロピレン繊維からなるメルトブロー不織布やポリエステル繊維不織布、微多孔PTFE膜、微多孔PE膜のような撥水性の高いものであっても高い親水性を発揮することができ、高い洗浄再生性を発揮することができる。また、濾材を構成する素材の分子構造に、カルボキシル基と共にフッ素原子を導入することで、極性基のCOOH基が水に溶出することを効果的に防ぐことができる。その結果、親水性効果を長時間にわたって発揮することができる。 Since the carboxyl group is introduced into the molecular structure of the material constituting the filter medium, the washing and regenerating filter medium of the present invention has a melt blown nonwoven fabric, polyester fiber nonwoven fabric, microporous PTFE membrane, microporous material composed of polypropylene fibers of ultrafine fibers. Even a highly water-repellent material such as a PE film can exhibit high hydrophilicity and can exhibit high cleaning reproducibility. Moreover, by introducing a fluorine atom together with a carboxyl group into the molecular structure of the material constituting the filter medium, it is possible to effectively prevent the polar COOH group from eluting into water. As a result, the hydrophilic effect can be exhibited for a long time.
また、本発明の濾材は、洗浄再生性が高く、超音波洗浄機を使用したり薬剤を使用したりしなくても高い洗浄再生性を発揮できるので、超音波洗浄機がない家庭や薬剤汚染が問題となる液体の精密濾過などに好適に使用することも可能である。 Moreover, the filter medium of the present invention has high cleaning regenerative properties, and can exhibit high cleaning regenerative properties without using an ultrasonic cleaner or chemicals. It is also possible to use it suitably for the microfiltration of the liquid which becomes a problem.
本発明の洗浄再生濾材および洗浄再生フィルターユニットについて、エアフィルター用途のものを例に説明を行う。エアフィルター用途のフィルターユニットは、たとえば、捕集性能を発揮する極細繊維不織布からなる濾材とそれを補強するための不織布濾材とが積層されて一体化されてなる。フィルターユニット毎に定められ定格風量条件での捕集性能は、粒子径0.3〜0.5μm範囲の粒子に対し10%以上であることが、好ましくは15%以上、99.99%以下であることが好ましい。そのような高性能のフィルターユニットに用いられる濾材において、本技術は特に好適である。具体的には、家庭用空気清浄機やビル空調用、産業用などのフィルターユニットで用いられる濾材に好適である。 The cleaning / regenerating filter medium and the cleaning / regenerating filter unit of the present invention will be described taking an air filter as an example. A filter unit for use in an air filter is formed by, for example, stacking and integrating a filter medium made of an ultrafine fiber nonwoven fabric that exhibits collection performance and a nonwoven filter medium for reinforcing the filter medium. The collection performance under the rated air flow conditions determined for each filter unit is preferably 10% or more, preferably 15% or more and 99.99% or less for particles having a particle diameter of 0.3 to 0.5 μm. Preferably there is. The present technology is particularly suitable for a filter medium used in such a high-performance filter unit. Specifically, it is suitable for filter media used in filter units for home air purifiers, building air conditioners, and industrial use.
フィルターユニットを構成する濾材の素材としては、特に限定されるものではなく、ポリプロピレン、ポリエステル、ポリ乳酸、ポリエチレン、フッ素系樹脂、ビニロン、ナイロン、レーヨンなどの合成繊維を用いた織編物や不織布、網状物あるいは有機高分子からなる微多孔膜など幅広く使用できる。 The material of the filter medium constituting the filter unit is not particularly limited, and woven or knitted fabric or nonwoven fabric using a synthetic fiber such as polypropylene, polyester, polylactic acid, polyethylene, fluororesin, vinylon, nylon, rayon, or net-like. It can be used widely, such as a microporous film made of a product or an organic polymer.
上述したようにフィルターユニットを複数の濾材で構成する場合は、捕集性能を発揮する濾材の素材としてポリプロピレン繊維からなる不織布を用いることが好ましい。ポリプロピレン繊維不織布はエレクトレット化して捕集効率を高めること可能である。また、捕集性能を発揮する濾材の補強材としては、洗浄時の洗浄液(水系)に浸しても寸法変化率が小さくヤング率が大きいポリエステル繊維やビニロン繊維からなる不織布を使用することが好ましい。さらに、撥水性、耐薬品性に関して共に優れた性能を示すフッ素樹脂のPTFE、3フッ化ビニデンなどの織編物、不織布、微多孔膜は、本発明を適用することで親水性となり通液性を向上させることが可能となるので、高捕集性、高耐薬品性を併せもつという点で好適素材である。 As described above, when the filter unit is composed of a plurality of filter media, it is preferable to use a non-woven fabric made of polypropylene fibers as a material for the filter media exhibiting the collection performance. Polypropylene fiber nonwoven fabric can be electretized to increase the collection efficiency. Moreover, it is preferable to use the nonwoven fabric which consists of a polyester fiber and a vinylon fiber with a small dimensional change rate and a large Young's modulus even if immersed in the washing | cleaning liquid (aqueous system) at the time of washing | cleaning as a reinforcing material of the filter medium which exhibits collection performance. Furthermore, PTFE, a fluororesin that exhibits excellent performance in terms of water repellency and chemical resistance, woven and knitted fabrics such as vinylidene fluoride, non-woven fabrics, and microporous membranes become hydrophilic and liquid-permeable by applying the present invention. Since it can be improved, it is a suitable material in that it has both high collection and chemical resistance.
捕集性能を発揮する濾材の素材として織編物や不織布を用いる場合、粒子径0.3〜0.5μm範囲の粒子に対し10%〜70%程度の捕集性能を得るためには、平均繊維径が0.5〜10μm、目付が10〜100g/m2の素材を用いることが好ましい。繊維径は細い方が低目付で高い捕集性能が得られるが捕捉した固体粒子の物理的な脱離性が悪くなり易い。そのため、平均繊維径は太い方が良く2μm以上が特に好適である。一方、平均繊維径が大きくなり過ぎると同じ捕集性能を得るために目付を増やす必要が生じ経済的でない。このため、平均繊維径は7μm以下が特に好ましい。なおCOOH基とフッ素原子の導入に際して繊維径や目付で加工制限を受けないため、必要とする捕集性能、通気抵抗およびダスト脱離性から素材を決めれば良い。 When woven or knitted fabric or nonwoven fabric is used as the material of the filter medium that exhibits the collection performance, in order to obtain the collection performance of about 10% to 70% with respect to the particles having a particle diameter of 0.3 to 0.5 μm, the average fiber It is preferable to use a material having a diameter of 0.5 to 10 μm and a basis weight of 10 to 100 g / m 2 . A finer fiber diameter has a lower basis weight and higher collection performance, but the physical detachability of the captured solid particles tends to deteriorate. For this reason, the average fiber diameter should be thick, and 2 μm or more is particularly preferable. On the other hand, if the average fiber diameter becomes too large, it is necessary to increase the basis weight in order to obtain the same collection performance, which is not economical. For this reason, the average fiber diameter is particularly preferably 7 μm or less. Since introduction of COOH groups and fluorine atoms is not subject to processing restrictions due to fiber diameter or basis weight, the material may be determined from the required collection performance, ventilation resistance, and dust detachability.
また補強材としてポリエステル繊維、ビニロン繊維あるいはレーヨンなどからなる不織布を用いる場合には、乾式法や湿式法で製造された不織布を広く使用でき、これもCOOH基とフッ素原子の導入に関わる制限事項がないため、寿命に関わるダスト保持量や補強材としての剛性の面から繊維の太さや目付、堅さを選定すれば良い。 In addition, when using a nonwoven fabric made of polyester fiber, vinylon fiber, rayon or the like as a reinforcing material, a nonwoven fabric produced by a dry method or a wet method can be widely used, and this also has restrictions related to the introduction of COOH groups and fluorine atoms. Therefore, it is only necessary to select the thickness, basis weight, and stiffness of the fiber from the viewpoint of the dust retention amount related to the life and the rigidity as the reinforcing material.
本発明においては、濾材を構成する素材の分子構造にフッ素原子とカルボキシル基とが含まれるが、次に、上記のような素材にフッ素原子およびカルボキシル基を導入する方法(以後、F加工と記述する)について、ポリプロピレン極細繊維不織布を例にとって説明する。 In the present invention, the molecular structure of the material constituting the filter medium includes fluorine atoms and carboxyl groups. Next, a method of introducing fluorine atoms and carboxyl groups into the above materials (hereinafter referred to as F processing). ) Will be described using a polypropylene ultrafine fiber nonwoven fabric as an example.
まず、密閉されたタンク内にポリプロピレン極細繊維不織布を入れ、タンク内の空気を抜いた後、該タンクに外部から、フッ化水素を電気分解して作成したフッ素ガスとともに酸素ガスを導入する。その結果、ポリマー表面のC−H結合やC−CH3にC−F結合の導入が起こり、下記式の反応が進む。 First, a polypropylene ultrafine fiber nonwoven fabric is put in a sealed tank, the air in the tank is evacuated, and oxygen gas is introduced into the tank from the outside together with fluorine gas prepared by electrolyzing hydrogen fluoride. As a result, C—H bonds on the polymer surface and C—F bonds are introduced into C—CH 3 , and the reaction of the following formula proceeds.
(CH2CHCH3)n+F2+O2→(CF2CFCOF)n→(CF2CFCOOH)n
ポリプロピレン側鎖のメチル基はCF3になるものと−COFに変化するものとに分かれるが、−COFは不安定であるため、すぐに気中の水分や基材が持つ水分と反応して−COOHに変化する。その結果、濾材を構成する素材はポリマー表面が極性化され、分子構造レベルでみれば撥水性と親水性の部分が混在するものの、全体としてみれば、分子構造的に外側に位置するカルボキシル基が支配的に効果を発揮するためか、親水性を帯びるのである。
(CH 2 CHCH 3 ) n + F 2 + O 2 → (CF 2 CFCOF) n → (CF 2 CFCOOH) n
The methyl group of the polypropylene side chain is divided into those that become CF 3 and those that change to —COF, but because —COF is unstable, it immediately reacts with moisture in the air and the moisture of the substrate— Change to COOH. As a result, the material constituting the filter medium is polarized on the polymer surface, and water repellent and hydrophilic parts are mixed at the molecular structure level, but on the whole, there are carboxyl groups located on the outside in terms of molecular structure. This is because it exerts a dominant effect or is hydrophilic.
このとき、カルボキシル基に置換する割合を調整することで撥水性と親水性のバランスを調整することも可能であり、これは酸素ガスの混合濃度で調整することができる。 At this time, it is also possible to adjust the balance between water repellency and hydrophilicity by adjusting the ratio of substitution with carboxyl groups, which can be adjusted by the mixed concentration of oxygen gas.
続いて、上記のような親水性付与によって濾材の洗浄再生能力が向上する原理について説明する。 Subsequently, the principle of improving the cleaning and regeneration ability of the filter medium by imparting hydrophilicity as described above will be described.
フィルターユニットが捕集対象とする粒子には、通常固体粒子と液状粒子があり、これらの粒子は油性成分や水溶性成分で構成されていると考えられている。家庭やビル関係で使用される空気清浄機フィルターでは、一般大気に含まれる塵埃に加えて使用環境特有の砂塵、繊維屑、タバコ煙、微細塵などが捕集対象粒子となる。たとえば、道路に面した所で使用されたフィルターユニットでは、ディーゼル排ガス由来と推定される微小カーボン粒子や油分も捕集対象粒子となる。繊維に捕集されたこれら粒子の様子を実際に顕微鏡で観察すると、付着前の粒子の形状を留めているのは固体粒子のみで、親水性の高い液状粒子は拡がって付着している。また、拡がって付着した液状粒子は、固体粒子間の隙間を埋め、結果的に固体粒子の接着剤として作用すると考えられる。この様子は特にタバコ煙を主な捕集対象とする家庭用空気清浄機フィルターユニットで顕著に観察することができる。すなわち、タバコ煙は豊富に水を含んだ粒子であり濾材表面に拡がって付着、乾燥し固着していると推定される。 The particles to be collected by the filter unit are usually solid particles and liquid particles, and these particles are considered to be composed of oily components and water-soluble components. In the air purifier filter used in homes and buildings, in addition to dust contained in the general atmosphere, sand dust, fiber scraps, tobacco smoke, fine dust and the like specific to the use environment are collected particles. For example, in a filter unit used in a place facing a road, fine carbon particles and oil components estimated to be derived from diesel exhaust gas are also collected particles. When the state of these particles collected in the fiber is actually observed with a microscope, only the solid particles retain the shape of the particles before adhesion, and the liquid particles having high hydrophilicity are spread and adhered. Further, it is considered that the liquid particles spread and adhered fill the gaps between the solid particles, and as a result, act as an adhesive for the solid particles. This situation can be particularly observed with a domestic air purifier filter unit that mainly collects tobacco smoke. In other words, it is presumed that tobacco smoke is abundantly water-containing particles, spreads on the filter medium surface, adheres, dries and adheres.
このような状態の濾材から捕集粒子を洗い落とすためには、粒子捕集部に洗浄液の浸透が十分行われる必要がある。特に粒子が付着した濾材表面と粒子との界面部分に洗浄液が浸透して、洗浄液に可溶な成分を溶かしだし、粒子を落ちやすくする必要がある。 In order to wash off the collected particles from the filter medium in such a state, it is necessary that the cleaning liquid is sufficiently infiltrated into the particle collecting portion. In particular, it is necessary that the cleaning liquid penetrates into the interface portion between the surface of the filter medium to which the particles adhere and the particles, so that components soluble in the cleaning liquid are dissolved and the particles are easily dropped.
しかしながら、濾材を構成する素材が従来のポリプロピレン極細繊維不織布からなる場合、当該濾材は撥水性が高いため、家庭洗濯用合成洗剤、例えばP&G(株)のアリエール、ライオン(株)のトップ、花王(株)のアタックなどを溶解した洗浄液に浸しても、洗浄液が殆ど浸透しない。そのため、濾材表面に固着している粒子には洗浄液が浸透したとしても、濾材内部の繊維間に形成された空間に捕捉された粒子には洗浄液が浸透しにくく、短時間で粒子を十分に洗い落とすことが困難である。 However, when the material constituting the filter medium is made of a conventional polypropylene ultrafine fiber nonwoven fabric, the filter medium has high water repellency. Therefore, synthetic detergent for home laundry, for example, P & G Co., Ltd. Arière, Lion Co., Ltd. top, Kao ( Even if it is dipped in a cleaning solution in which an attack of Co., Ltd. is dissolved, the cleaning solution hardly penetrates. Therefore, even if the cleaning liquid permeates the particles fixed on the surface of the filter medium, the cleaning liquid does not easily permeate the particles trapped in the spaces formed between the fibers inside the filter medium, and the particles are sufficiently washed out in a short time. Is difficult.
一方、本発明の洗浄再生濾材は、濾材を構成する素材がポリプロピレン極細繊維不織布であっても、極性基であるカルボキシル基とフッ素原子とを繊維構成分子に含有させて親水化したものであるので、濾材を洗浄液に浸せば、洗浄液が濾材表面の粒子とともに濾材内部、さらにはその内部に捕捉された粒子にも速やか浸透し、粒子が膨潤するとともに洗浄液に可溶な成分が粒子から溶けだす。その結果、濾材に固着していた粒子の足場が失わることになり、粒子を速やかに洗い落とせるのである。 On the other hand, even if the material constituting the filter medium is a polypropylene ultrafine fiber non-woven fabric, the washed and regenerated filter medium of the present invention is made hydrophilic by incorporating a polar carboxyl group and a fluorine atom into a fiber constituent molecule. If the filter medium is immersed in the cleaning liquid, the cleaning liquid quickly penetrates into the inside of the filter medium together with the particles on the surface of the filter medium, and further to the particles trapped in the filter medium, and the particles swell and dissolve components soluble in the cleaning liquid from the particles. As a result, the scaffold for the particles adhering to the filter medium is lost, and the particles can be washed off quickly.
また、親水性の高い液状粒子は、親水性の高い繊維表面に接触した場合、親水性の低い液状粒子の場合に比較して濾材の表面により拡がって付着する。たとえばタバコの煙粒子の付着実験では、大気中に含まれる塵などの固体粒子も繊維に付着するが、水を豊富に含んだタバコの煙粒子が濾材に接触するとともに拡がって付着する様子を顕微鏡観察で見ることができる。このとき本発明の洗浄再生濾材は、局所的にみると濾材を構成する素材が撥水性の部分と親水性の部分とを併せもつためか、液状粒子がさらに横に拡がりやすい。その結果、拡がって付着した液状粒子による固体粒子の接着強化も弱まり、洗浄液によってさらに洗い流しやすくなる。 Further, when the liquid particles having high hydrophilicity are brought into contact with the fiber surface having high hydrophilicity, the liquid particles spread and adhere to the surface of the filter medium as compared with the liquid particles having low hydrophilicity. For example, in a cigarette smoke particle adhesion experiment, solid particles such as dust contained in the atmosphere also adhere to the fiber, but the tobacco smoke particles rich in water contact the filter medium and spread to adhere to the microscope. Can be seen by observation. At this time, the washing regenerated filter medium of the present invention is likely to spread the liquid particles further laterally because the material constituting the filter medium has both a water-repellent part and a hydrophilic part when viewed locally. As a result, the adhesion enhancement of the solid particles due to the liquid particles spreading and weakened is weakened, and it becomes easier to wash away with the cleaning liquid.
さらに、従来から表面改質技術としてコロナ放電処理、プラズマ処理によって水酸基やカルボキシル基を導入する技術は知られていたが、これらの技術では親水性効果が十分に持続しなかったのに対して、本発明の濾材は、上記親水性効果が長期間にわたって維持される。その理由は明らかではないが、カルボキシル基とともにフッ素原子を共存させることで、カルボキシル基の繊維内部への潜り込みが生じにくくなっているからと考えられる。 Furthermore, techniques for introducing hydroxyl groups and carboxyl groups by corona discharge treatment and plasma treatment as surface modification techniques have been known, but the hydrophilic effect was not sustained sufficiently with these techniques, In the filter medium of the present invention, the hydrophilic effect is maintained over a long period of time. The reason is not clear, but it is thought that the presence of the fluorine atom together with the carboxyl group makes it difficult for the carboxyl group to enter the fiber.
F加工は、フィルターユニットを複数の濾材で構成する場合、一部の濾材だけに施すことも可能ではある。しかしながら、洗浄再生性を高めるためには全濾材に施すことが好ましい。 The F processing can be applied only to a part of the filter media when the filter unit is constituted by a plurality of filter media. However, it is preferable to apply to all the filter media in order to improve the washing reproducibility.
また、上記F加工は、従来の界面活性剤による表面処理と違って水を使用しないドライプロセスのため、余分な水を除くためのディップマングル加工を必要とせず、濾材の潰れもおこらない。このため、かさ高な状態の親水性濾材をことができ、より洗浄液の浸透がよくなり捕集粒子の離脱性がさらによくなる。 Further, unlike the conventional surface treatment with a surfactant, the F processing is a dry process that does not use water, and therefore does not require dip mangle processing for removing excess water, and the filter medium is not crushed. For this reason, a bulky hydrophilic filter medium can be obtained, the penetration of the cleaning liquid becomes better, and the detachability of the collected particles is further improved.
そして、本発明においては、濾材を構成する素材の分子構造にフッ素原子とカルボキシル基とを含ませるにあたって、フッ素、酸素の濃度や処理時間などを制御して、JIS L1907(2004)に記載のバイレック法に準拠して測定される水吸い上げ高さが5mm以上となるようにすることが好ましい。この値を5mm以上になるようにすることで、家庭でも行える洗浄方法、すなわち、一般衣料用洗剤や台所洗剤を溶かした水に漬けて、後は流水で流す程度の洗浄方法でも捕集粒子の脱落が効果的に良くなり、フィルター通気性(圧損)の回復率が急激によくなる。フィルターの圧損回復率で表現すると、この値が4mm以下では85%程度であるが、5mm以上にすると95%程度となる。この圧損回復率の概念については、例えば空調用洗浄再生フィルターに関して業界が再生能力の業界基準を90%以上に設定しようとしていることからして、極めて高いものであるといえる。なお、より好ましい範囲は10mm以上であり、一方、上限は200mmが好ましく、より好適には20〜150mm範囲である
さらに、本発明においては、フィルターユニットを構成する濾材に少なくともエレクトレット不織布を含むことが好ましい。エレクトレット加工は公知の方法で行えばよく、たとえばポリプロピレンの織編物、不織布、繊維やフッ素樹脂の微多孔膜などに対して行うことが出来る。なお、エレクトレット加工と上記F加工とを同一の濾材構成素材に行う場合、その順番に気を付ける必要がある。たとえば、エレクトレット加工を特開平1−287914号公報に示されるコロナ放電法で行う場合はF加工の前後どちらでおこなっても捕集性能で殆ど差のないものが得られるが、特表平9―501604号公報に示されるハイドロチャージ法で行う場合は、F加工を先に行い、その後にエレクトレット加工を行うことが好ましい。F加工を先に行うことでポリプロピレンの親水性が高くなり不織布内部の繊維交絡の隅々にまで水が浸透し、濡れ面積が増える。その結果、高い電荷量を加工物に与えることができ、高捕集性能のエレクトレット濾材を得ることができる。
In the present invention, when the fluorine atom and the carboxyl group are included in the molecular structure of the material constituting the filter medium, the concentration and treatment time of fluorine and oxygen are controlled, and the birec described in JIS L1907 (2004). It is preferable that the water suction height measured in accordance with the law is 5 mm or more. By setting this value to 5 mm or more, the cleaning method that can be performed at home, that is, by immersing it in water in which general laundry detergent or kitchen detergent is dissolved, and then washing it with running water, the collected particles The dropout is effectively improved and the recovery rate of the filter air permeability (pressure loss) is drastically improved. Expressed by the pressure loss recovery rate of the filter, this value is about 85% when it is 4 mm or less, but it is about 95% when it is 5 mm or more. The concept of the pressure loss recovery rate can be said to be extremely high because, for example, the industry is trying to set the industry standard of regeneration capacity to 90% or more for air-conditioning cleaning regeneration filters. The more preferable range is 10 mm or more, while the upper limit is preferably 200 mm, and more preferably 20 to 150 mm. Furthermore, in the present invention, the filter medium constituting the filter unit may include at least an electret nonwoven fabric. preferable. The electret processing may be performed by a known method, and can be performed on, for example, polypropylene woven or knitted fabric, non-woven fabric, fiber or fluororesin microporous film. In addition, when performing an electret process and the said F process to the same filter-medium constituent material, it is necessary to pay attention to the order. For example, when electret processing is performed by the corona discharge method disclosed in Japanese Patent Application Laid-Open No. 1-287914, there is almost no difference in collection performance regardless of whether it is performed before or after F processing. In the case of performing the hydrocharge method disclosed in Japanese Patent No. 501604, it is preferable to perform F processing first and then perform electret processing. By performing the F processing first, the hydrophilicity of the polypropylene is increased, and water penetrates into every corner of the fiber entanglement inside the nonwoven fabric, increasing the wetted area. As a result, a high charge amount can be given to the workpiece, and an electret filter medium with high collection performance can be obtained.
なお、F加工の検証はESCA分析で行うことができる。 The F processing can be verified by ESCA analysis.
以下、本発明の洗浄再生濾材および洗浄再生フィルターユニットについて、実施例を用いて具体的に説明するが、記載内容に限定されるものではない。 Hereinafter, although the washing | cleaning reproduction | regeneration filter material and washing | cleaning reproduction | regeneration filter unit of this invention are demonstrated concretely using an Example, it is not limited to description content.
なお、実施例で行っている濾材の水の吸い上げ高さは、繊維製品の吸水性試験方法JIS L1907(2004)に記載のバイレック法(吸水時間10分間)で行った。 In addition, the water suction height of the filter medium performed in the Examples was measured by the birec method (water absorption time 10 minutes) described in the water absorption test method JIS L1907 (2004) for textiles.
濾材の圧損測定、捕集効率測定はJIS B9908(1991)に記載の換気用エアフィルターユニット形式1に準じて実施した。 The pressure loss measurement and the collection efficiency measurement of the filter medium were carried out according to the air filter unit type 1 for ventilation described in JIS B9908 (1991).
フィルターユニットの圧損測定はJIS B9908(1991)に記載の換気用エアフィルターユニット形式3に準じて実施した。 The pressure loss measurement of the filter unit was performed according to the air filter unit type 3 for ventilation described in JIS B9908 (1991).
ダスト負荷は、JIS Z8901(1974)に記載のJIS15種のダスト(日本粉体工業協会販売の試験用ダスト)を用いて、JIS B9908(1991)に記載の換気用エアフィルターユニット形式3に準じ、ダストの濾材貫通風速が6.5m/分でダスト負荷前圧損の3倍になるまで実施した。 The dust load is based on the air filter unit type 3 for ventilation described in JIS B9908 (1991) using JIS15 type dust described in JIS Z8901 (1974) (test dust sold by Japan Powder Industry Association) It was carried out until the speed of dust passing through the filter medium was 6.5 m / min and tripled the pressure loss before dust load.
またタバコの煙10本分(銘柄マイルドセブン10mg)の負荷は、上記JIS15種のダスト負荷で用いた評価装置の風洞にエアーとともに燃焼させたタバコの煙を導入し、評価濾材の補強材側を風上側として供給して負荷した。この時のタバコの煙が濾材を通過する風速は0.5m/minとした。 Also, the load of 10 cigarette smoke (brand mild seven 10 mg) was introduced by introducing tobacco smoke burned with air into the wind tunnel of the evaluation device used in the JIS 15 class dust load, and the reinforcing material side of the evaluation filter medium Loaded as the upper side. At this time, the wind speed at which the tobacco smoke passed through the filter medium was 0.5 m / min.
平均繊維径は、濾材をキーエンス(株)販売の機種VE7800型SEMを使用して倍率200倍で撮影し、得られた画像から、当該SEMに標準搭載されていた繊維径分析ソフトを用いてランダムに抽出した繊維500本の繊維幅から求めた
目付は寸法50センチ角の重量を測定し、この数値を4倍して求めた。
The average fiber diameter was obtained by photographing the filter medium at a magnification of 200 times using a model VE7800 type SEM sold by Keyence Corporation, and randomly using the fiber diameter analysis software standardly installed in the SEM from the obtained image. The basis weight obtained from the fiber width of 500 fibers extracted in (1) was obtained by measuring the weight of a 50 cm square and multiplying this value by four.
捕集効率は、JIS B9908(1991)に記載の形式1に準じた試験機を用い、大気エアーに含まれる粒子径0.3〜0.5μm範囲の大気塵について、濾材上流側の粒子数(Ci)と濾材下流側の粒子数(Co)をパーティクルカウンター(リオン社製 商品名KC01D)を用いて評価し下記式から捕集効率を求めた。 The collection efficiency is the number of particles on the upstream side of the filter medium for atmospheric dust with a particle diameter of 0.3 to 0.5 μm contained in atmospheric air using a test machine according to type 1 described in JIS B9908 (1991). Ci) and the number of particles on the downstream side of the filter medium (Co) were evaluated using a particle counter (trade name KC01D manufactured by Rion Co., Ltd.), and the collection efficiency was determined from the following formula.
捕集効率(%)=(1−Co/Ci)×100%
また、F加工は、東洋炭素株式会社と高松帝酸株式会社とが共同で英国BNFL社の協力のもと開発したオン・サイトフッ素発生システム(F技術支援センター所有)の実験設備を用いて実施した。
Collection efficiency (%) = (1-Co / Ci) × 100%
In addition, F processing was carried out using the on-site fluorine generation system (owned by F Technical Support Center), which was jointly developed by Toyo Tanso Co., Ltd. and Takamatsu Tei Co., Ltd. with the cooperation of BNFL. did.
(実施例1)
メルトブロー紡糸法で製造したポリプロピレン極細繊維不織布(平均繊維径2.4μm、目付20g/m2)を用意し、該不織布にF加工を次の条件で行った。すなわち、電解液KF・2HFを電気分解して発生させたフッ素ガスと酸素ガスからなる混合ガス(フッ素ガス濃度2%、温度80℃)を満たしたタンク内でポリプロピレン極細繊維不織布を5分間晒した後、該ポリプロピレン極細繊維不織布を取り出し25℃75%RHの空気中に1時間放置してF加工を完了させた。
(Example 1)
A polypropylene ultrafine fiber nonwoven fabric (average fiber diameter 2.4 μm, basis weight 20 g / m 2 ) produced by the melt blow spinning method was prepared, and F processing was performed on the nonwoven fabric under the following conditions. That is, the polypropylene ultrafine fiber nonwoven fabric was exposed for 5 minutes in a tank filled with a mixed gas (fluorine gas concentration 2%, temperature 80 ° C.) composed of fluorine gas and oxygen gas generated by electrolysis of the electrolytic solution KF · 2HF. Thereafter, the polypropylene ultrafine fiber nonwoven fabric was taken out and left in air at 25 ° C. and 75% RH for 1 hour to complete the F processing.
F加工前後の水吸い上げ高さは、処理前は0mmであったがF加工後は40mmとなり明らかに水の浸透性が改善されていることが確認できた。 The water sucking height before and after the F processing was 0 mm before the processing, but 40 mm after the F processing, and it was confirmed that the water permeability was clearly improved.
(実施例2)
短繊維樹脂加工不織布(ポリエステル短繊維(7dtx)とビニロン短繊維(15dtx)を4対6で配合したウエッブをアクリル酸エステル樹脂で固め目付50g/m2としたもの)にF加工を次の条件で行った。すなわち、電解液KF・2HFを電気分解して発生させたフッ素ガスと酸素ガスからなる混合ガス(フッ素ガス濃度2%、温度80℃)を満たしたタンク内で該短繊維樹脂加工不織布を5分間晒した後、タンクから取り出し25℃75%RHの空気中に1時間放置してF加工を完了させた。
(Example 2)
Short fiber resin processed non-woven fabric (web consisting of polyester short fiber (7 dtx) and vinylon short fiber (15 dtx) in a ratio of 4 to 6 is solidified with acrylate resin to a basis weight of 50 g / m 2 ) I went there. That is, the non-woven fabric processed with short fibers for 5 minutes in a tank filled with a mixed gas (fluorine gas concentration 2%, temperature 80 ° C.) composed of fluorine gas and oxygen gas generated by electrolysis of the electrolytic solution KF · 2HF. After the exposure, it was removed from the tank and left in air at 25 ° C. and 75% RH for 1 hour to complete the F processing.
F加工前後の水吸い上げ高さは、処理前は1mmであったがF加工後は24mmとなり明らかに水の浸透性が改善されていることが確認できた。 The water sucking height before and after the F processing was 1 mm before the processing, but after the F processing, it was 24 mm, and it was confirmed that the water permeability was clearly improved.
(実施例3および比較例1)
捕集性能を発揮する濾材構成素材として、メルトブロー紡糸法で製造したポリプロピレン極細繊維不織布(平均繊維径2.4μm、目付20g/m2)を2枚用意し、該不織布のうち1枚にF加工を次の条件で行った。すなわち、電解液KF・2HFを電気分解して発生させたフッ素ガスと酸素ガスからなる混合ガス(フッ素ガス濃度2%、温度80℃)を満たしたタンク内でポリプロピレン極細繊維不織布を5分間晒した後、該ポリプロピレン極細繊維不織布を取り出し25℃75%RHの空気中に1時間放置してF加工を完了させた。
(Example 3 and Comparative Example 1)
Two polypropylene ultrafine fiber nonwoven fabrics (average fiber diameter 2.4 μm, basis weight 20 g / m 2 ) produced by the melt blow spinning method are prepared as filter material constituent materials that exhibit the collection performance, and F processing is performed on one of the nonwoven fabrics. Was performed under the following conditions. That is, the polypropylene ultrafine fiber nonwoven fabric was exposed for 5 minutes in a tank filled with a mixed gas (fluorine gas concentration 2%, temperature 80 ° C.) composed of fluorine gas and oxygen gas generated by electrolysis of the electrolytic solution KF · 2HF. Thereafter, the polypropylene ultrafine fiber nonwoven fabric was taken out and left in air at 25 ° C. and 75% RH for 1 hour to complete the F processing.
続いて、補強材として、ポリエステルスパンボンド不織布(ルトラビル社製:品番LDH7270W、目付70g/m2)を2枚用意し、F加工を施したポリプロピレン極細繊維不織布とF加工を施さなかったポリプロピレン極細繊維不織布を、それぞれポリエステルスパンボンド不織布と積層して2種類の濾材を作成した。 Subsequently, two polyester spunbond nonwoven fabrics (manufactured by Lutraville: product number LDH7270W, weight per unit area: 70 g / m 2 ) were prepared as reinforcing materials. The polypropylene ultrafine fiber nonwoven fabric subjected to F processing and the polypropylene ultrafine fiber not subjected to F processing. Two types of filter media were prepared by laminating the nonwoven fabric with a polyester spunbond nonwoven fabric.
これら2種の濾材について、水の吸い上げ高さを評価したところ、F加工を施さなかったポリプロピレン極細繊維不織布とポリエステルスパンボンド不織布とを積層した濾材(A)が0mmであったのに対して、F加工を施したポリプロピレン極細繊維不織布とポリエステルスパンボンド不織布とを積層した濾材(B)は25mmとなり、明らかに水の浸透性が改善されていることが確認できた。 For these two types of filter media, when the water suction height was evaluated, the filter media (A) in which the polypropylene ultrafine fiber nonwoven fabric and the polyester spunbond nonwoven fabric that had not been subjected to F processing were 0 mm, The filter medium (B) obtained by laminating the F-processed polypropylene ultrafine fiber nonwoven fabric and the polyester spunbond nonwoven fabric was 25 mm, and it was confirmed that the water permeability was clearly improved.
次に、2種類の濾材(A)、(B)から濾材有効面積100cm2の試料を3枚ずつ採取し、以下の手順で、各濾材の洗浄再生性を評価した。 Next, three samples each having a filter medium effective area of 100 cm 2 were collected from the two types of filter media (A) and (B), and the cleaning and reproducibility of each filter media was evaluated by the following procedure.
(1)2種類の濾材(A)、(B)それぞれについて、3枚の試験片の圧損平均値を求め、(A)の濾材の圧損Δp1および(B)の濾材の圧損Δp2を得た。 (1) For each of the two types of filter media (A) and (B), the average pressure loss of the three test pieces was determined, and the pressure loss Δp1 of the filter media of (A) and the pressure loss Δp2 of the filter media of (B) were obtained.
(2)次に、2種類の濾材(A)、(B)の各試験片にタバコの煙10本分を補強材側を風上側として負荷した。 (2) Next, 10 pieces of tobacco smoke were loaded on the test pieces of the two types of filter media (A) and (B) with the reinforcing material side as the windward side.
(3)ついで、JIS15種のダストを2種類の濾材(A)、(B)の各試験片に負荷し、圧力損失がΔp1、Δp2それぞれの3倍になるまで付着させた。 (3) Next, JIS 15 type dust was loaded on each of the two types of filter media (A) and (B), and adhered until the pressure loss was three times greater than Δp1 and Δp2, respectively.
(4)その後、JIS15種ダストが付着した濾材を、水道水2Lを入れた超音波洗浄機(本田電子(株)製商品形式W113)に、補強材側を下向きにして浮かべ、28メガヘルツ、45メガヘルツ、100メガヘルツの超音波を1分間づつこの順番で作用させた後、取り出し100℃で5時間の乾燥を行った。 (4) After that, the filter medium on which JIS15 type dust adhered is floated with an ultrasonic cleaner (product type W113 manufactured by Honda Electronics Co., Ltd.) with tap water 2L, with the reinforcing material side facing downward, 28 MHz, 45 Megahertz and 100 megahertz ultrasonic waves were allowed to act in this order for 1 minute, then removed and dried at 100 ° C. for 5 hours.
(5)最後に、2種類の濾材(A)、(B)それぞれについて、3枚の試験片の圧損平均値を求めて(A)の濾材の圧損Δp3および(B)の濾材の圧損Δp4とし、その値から下記式に基づき圧損変化率を求めた。 (5) Finally, for each of the two types of filter media (A) and (B), the pressure loss average value of the three test pieces is obtained, and the pressure loss Δp3 of the filter media in (A) and the pressure loss Δp4 of the filter media in (B) are obtained. The pressure loss change rate was determined from the value based on the following formula.
濾材(A)の圧損変化率 (WP)=(Δp3/Δp1−1)×100%
濾材(B)の圧損変化率 (UP)=(Δp4/Δp2−1)×100%
この結果、WP=20%、UP=4%であった。明らかにF加工の効果によりダストの脱離性が良くなることが確認できた。
Rate of change in pressure loss of filter medium (A) (W P ) = (Δp3 / Δp1-1) × 100%
Pressure drop change rate of the filter medium (B) (U P) = (Δp4 / Δp2-1) × 100%
As a result, W P = 20% and U P = 4%. Apparently, it was confirmed that the dust removability was improved by the effect of F processing.
(実施例4、5)
メルトブロー紡糸法で製造したポリプロピレン極細繊維不織布(平均繊維径2.4μm、目付20g/m2)に、実施例1より加工時間が短い2条件でF加工処理を行い、それらをポリエステルスパンボンド不織布(ルトラビル社製:品番LDH7270W、目付70g/m2)と積層して、2種の濾材を得た。すなわち、混合ガスに晒す時間を30秒間、40秒間とした以外は実施例1と同様にして、水吸上げ高さ4mmのポリプロピレン極細繊維不織布と水吸上げ高さ5mmのポリプロピレン極細繊維不織布とを用意し、それぞれをポリエステルスパンボンド不織布(ルトラビル社製:品番LDH7270W、目付70g/m2)と積層し2種の濾材(C)、(D)を得た。
(Examples 4 and 5)
Polypropylene ultrafine fiber nonwoven fabric (average fiber diameter 2.4 μm, basis weight 20 g / m 2 ) produced by the melt blow spinning method is subjected to F processing under two conditions shorter than Example 1, and these are processed into polyester spunbond nonwoven fabric ( Two types of filter media were obtained by laminating with Lutraville Corporation: product number LDH7270W, basis weight 70 g / m 2 ). That is, a polypropylene ultrafine fiber nonwoven fabric with a water suction height of 4 mm and a polypropylene ultrafine fiber nonwoven fabric with a water suction height of 5 mm were prepared in the same manner as in Example 1 except that the time for exposure to the mixed gas was 30 seconds and 40 seconds. Each was prepared and laminated with a polyester spunbonded nonwoven fabric (manufactured by Lutraville: product number LDH7270W, basis weight 70 g / m 2 ) to obtain two types of filter media (C) and (D).
続いて、実施例3と同じ条件、手順で、各濾材の洗浄再生性を評価した。その結果、UPは、濾材(C)が7%、濾材(D)が5%であった。 Subsequently, the washing reproducibility of each filter medium was evaluated under the same conditions and procedures as in Example 3. As a result, U P is the filter medium (C) is 7%, the filter medium (D) was 5%.
次にこれら試料にもう一度先程と同じ方法でダスト負荷を行い各濾材の洗浄再生性を評価したところ、UPは、濾材(C)が12%、濾材(D)が6%に変化し、耐久性でF加工時間の長かった濾材(D)の方が優れていることが確認された。 Then was evaluated for cleaning regeneration of each filter media performs dust load again just the same way to these samples, U P is the filter medium (C) is 12%, the filter medium (D) is changed to 6%, durability It was confirmed that the filter medium (D) having a long F processing time was superior.
(実施例6)
メルトブロー紡糸法で製造したポリプロピレン極細繊維不織布(平均繊維径2.4μm、目付20g/m2)にポリエステルスパンボンド不織布(ルトラビル社製:品番LDH7270W、目付70g/m2)を積層し濾材とした後、実施例1の条件でF加工を行った。この濾材の水吸い上げ高さは、処理前が0mmであったがF加工直後は28mmであった。さらに、この濾材を室内に半年間放置して水吸い上げ高さを評価したところ27mmで殆ど低下せず、親水性効果の持続性が高いことがわかった。
(Example 6)
After laminating a polypropylene spunbond nonwoven fabric (Lutraville, product number LDH7270W, weight per unit area 70 g / m 2 ) on a polypropylene ultrafine fiber nonwoven fabric (average fiber diameter 2.4 μm, basis weight 20 g / m 2 ) manufactured by the melt blow spinning method to obtain a filter medium F processing was performed under the conditions of Example 1. The water suction height of this filter medium was 0 mm before treatment, but was 28 mm immediately after F processing. Furthermore, when this filter medium was left in the room for half a year and the water suction height was evaluated, it was found that there was almost no decrease at 27 mm, and the sustainability of the hydrophilic effect was high.
次に、実施例3と全く同じ条件、手順で濾材の洗浄再生性を評価した。その結果、UPが2.5%となり、実施例3より良くなることがわかった。濾材全体が親水化されダスト脱離性がさらに良く成るため好結果が得られたと考えられる。 Next, the cleaning reproducibility of the filter medium was evaluated under exactly the same conditions and procedures as in Example 3. As a result, UP was 2.5%, which was found to be better than Example 3. It is thought that good results were obtained because the entire filter medium was made hydrophilic and the dust detachability was further improved.
更に同じ条件で2回目のダスト負荷を行い濾材の洗浄再生性を評価したところ、UPが3%と脱離性は殆ど低下せず効果が持続することも確認できた。 Further Evaluation of the washing regeneration of the filter medium a second time dust load in the same conditions, 3% and leaving the U P was also confirmed that the effect lasts not decrease little.
(実施例7、8)
メルトブロー紡糸法で製造した繊維径の異なる2種類のポリプロピレン極細繊維不織布e、f(e:平均繊維径2.4μm、目付40g/m2、f:平均繊維径4.1μm、目付40g/m2)を用意した。次に、それらポリプロピレン極細繊維不織布e、fそれぞれを、短繊維樹脂加工不織布(ポリエステル短繊維(7dtx)とビニロン短繊維(15dtx)を4対6で配合したウエッブをアクリル酸エステル樹脂で固め目付50g/m2としたもの)と積層し、その積層体について実施例1の条件でF加工を行い、ポリプロピレン極細繊維不織布eを用いた濾材(E)とポリプロピレン極細繊維不織布fを用いた濾材(F)を得た。これら濾材の水吸い上げ高さは、濾材(E)が23mm、濾材(F)が24mmと殆ど差が無いものであった。
(Examples 7 and 8)
Two types of polypropylene ultrafine fiber nonwoven fabrics e and f (e: average fiber diameter 2.4 μm, basis weight 40 g / m 2 , f: average fiber diameter 4.1 μm, basis weight 40 g / m 2 manufactured by the melt blow spinning method and having different fiber diameters ) Was prepared. Next, each of these polypropylene ultrafine fiber nonwoven fabrics e and f is made of a short fiber resin processed nonwoven fabric (polyester short fiber (7 dtx) and vinylon short fiber (15 dtx) in a ratio of 4 to 6, and a basis weight of 50 g is set with an acrylic ester resin. / M 2 ), and the laminate is subjected to F processing under the conditions of Example 1 to obtain a filter medium (E) using the polypropylene ultrafine fiber nonwoven fabric e and a filter medium using the polypropylene ultrafine fiber nonwoven fabric f (F ) The water suction height of these filter media was almost the same as 23 mm for the filter media (E) and 24 mm for the filter media (F).
次に、実施例3と全く同じ条件、手順で濾材の洗浄再生性を評価した。その結果、濾材(E)のUPが2.5%、濾材(F)のUPが1.8%であった。平均繊維径が大きいポリプロピレン極細繊維不織布を用いた濾材(F)の方がダスト脱離性が良いことを確認できた。 Next, the cleaning reproducibility of the filter medium was evaluated under exactly the same conditions and procedures as in Example 3. As a result, U P is 2.5% of the filter medium (E), U P of the filter medium (F) was 1.8%. It was confirmed that the filter medium (F) using the polypropylene ultrafine fiber nonwoven fabric having a large average fiber diameter had better dust detachability.
(実施例9および比較例2)
PTFE膜(平均細孔径0.2μm、厚み0.05mm)に補強材のポリエステルスパンボンド不織布(東レ(株)製:品番H30601、目付60g/m2)を積層し濾材としたものを2枚用意し、そのうちの1枚に実施例1の方法でF加工を行った。この2種類の濾材について水の吸い上げ高さを評価したところ、F加工を施していない濾材(G)の水吸い上げ高さは0mmで、F加工を施した濾材(H)の水吸い上げ高さは10mmであった。
(Example 9 and Comparative Example 2)
Two sheets of PTFE membrane (average pore size 0.2 μm, thickness 0.05 mm) are laminated as a reinforcing material polyester spunbond nonwoven fabric (Toray Industries, Inc .: product number H30601, basis weight 60 g / m 2 ) to prepare two filter media One of them was subjected to F processing by the method of Example 1. When the water suction height of these two types of filter media was evaluated, the water suction height of the filter material (G) not subjected to F processing was 0 mm, and the water suction height of the filter material (H) subjected to F processing was It was 10 mm.
次に、実施例3と全く同じ条件、手順で各濾材の洗浄再生性を評価した。その結果、F加工を施していない濾材(G)の圧損変化率WPが56%であるのに対して、F加工を施した濾材(H)の圧損変化率UPが18%であり、PTFE膜を用いた場合であってもF加工により脱離性を大幅に改善出来ることが分かった。 Next, the cleaning reproducibility of each filter medium was evaluated under exactly the same conditions and procedures as in Example 3. As a result, while the pressure drop change rate W P of the filter medium not subjected to F processing (G) is 56%, the pressure loss change rate U P of the filter medium which has been subjected to F machining (H) is 18%, It was found that the detachability can be greatly improved by F processing even when a PTFE membrane is used.
(実施例10、11)
平均繊維径の異なる2種類のメルトブロー不織布を用意した。すなわち、平均繊維径2.4μmのポリプロピレン極細繊維不織布(目付20g/m2、捕集効率30%)と平均繊維径4.0μmのポリプロピレン極細繊維不織布(目付50g/m2、捕集効率30%)とを用意し、それぞれに補強材としてポリエステルスパンボンド不織布(ルトラビル社製:品番LDH7270W、目付70g/m2)を積層し濾材とした後、実施例1の方法でF加工を行った。F加工後の水吸い上げ高さは、平均繊維径2.4μmのポリプロピレン極細繊維不織布とポリエステルスパンボンド不織布との積層濾材(I)が25mm、平均繊維径4.0μmのポリプロピレン極細繊維不織布とポリエステルスパンボンド不織布との積層濾材(J)が23mmであった。
(Examples 10 and 11)
Two types of melt blown nonwoven fabrics having different average fiber diameters were prepared. That is, a polypropylene ultrafine fiber nonwoven fabric having an average fiber diameter of 2.4 μm (weight per unit 20 g / m 2 , collection efficiency 30%) and a polypropylene ultrafine fiber nonwoven fabric having an average fiber diameter of 4.0 μm (weight per unit 50 g / m 2 , collection efficiency 30%). And a polyester spunbonded non-woven fabric (manufactured by Lutraville: product number LDH7270W, basis weight 70 g / m 2 ) as a reinforcing material and laminated to obtain a filter medium, followed by F processing by the method of Example 1. The water pick-up height after F processing is 25 mm for the laminated filter medium (I) of polypropylene fine fiber nonwoven fabric having an average fiber diameter of 2.4 μm and a polyester spunbond nonwoven fabric, and polypropylene fine fiber nonwoven fabric having an average fiber diameter of 4.0 μm and polyester span. The laminated filter medium (J) with the bond nonwoven fabric was 23 mm.
次に、純水をそれぞれの濾材に吹きつけエレクトレット加工を行った。加工後の捕集効率は濾材(I)が93%、濾材(J)が75%であった。 Next, the electret process was performed by spraying pure water on each filter medium. The collection efficiency after processing was 93% for the filter medium (I) and 75% for the filter medium (J).
その後、実施例3と全く同じ条件、手順で各濾材の洗浄再生性を評価した。その結果、UPは濾材(I)が4%、濾材(J)が2.5%であった。親水性の高いポリプロピレン不織布であってもエレクトレット加工が可能であり、また洗浄再生性も得られることが確認できた。 Thereafter, the cleaning reproducibility of each filter medium was evaluated under exactly the same conditions and procedures as in Example 3. As a result, U P is the filter medium (I) is 4%, the filter media (J) was 2.5%. It was confirmed that electret processing is possible even with a highly hydrophilic polypropylene non-woven fabric, and that cleanability can be obtained.
(実施例12、比較例3)
メルトブロー紡糸法で製造したポリプロピレン極細繊維不織布(平均繊維径4.1μm、目付40g/m2)に短繊維樹脂加工不織布(ポリエステル短繊維(1.5dtx)とビニロン短繊維(15dtx)を6対4で配合したウエッブをアクリル酸エステル樹脂で固め目付40g/m2としたもの)を両面に積層した濾材を2枚作成し、そのうちの1枚に、実施例1の方法でF加工を行った。水吸い上げ高さは、F加工を行った濾材(K)が24mmで無加工の濾材(L)は3mmであった。
(Example 12, Comparative Example 3)
Polypropylene ultrafine fiber nonwoven fabric (average fiber diameter 4.1 μm, basis weight 40 g / m 2 ) produced by the melt blow spinning method and short fiber resin processed nonwoven fabric (polyester short fiber (1.5 dtx) and vinylon short fiber (15 dtx) 6 to 4 Two filter media were prepared by laminating the web blended in (1) with an acrylate resin and having a basis weight of 40 g / m 2 ), and F processing was performed on one of them by the method of Example 1. The water suction height was 24 mm for the filter medium (K) subjected to F processing and 3 mm for the unprocessed filter medium (L).
それぞれの濾材を用いて幅250mm、長さ320mm、厚み30mmのフィルターユニットを1個ずつ作成し、洗浄再生性を評価供した。なお、ユニット作成条件は、濾材の山高さ28mm、濾材収納面積1.26/個とした。 One filter unit having a width of 250 mm, a length of 320 mm, and a thickness of 30 mm was prepared for each filter medium, and the cleaning and reproducibility was evaluated. The unit creation conditions were a filter medium peak height of 28 mm and a filter medium storage area of 1.26 / piece.
続いて、得られたフィルターユニットについて洗浄再生性を次のように評価した。 Subsequently, the cleaning reproducibility of the obtained filter unit was evaluated as follows.
(1)2個のフィルターユニットそれぞれについて、風量3.1m2/分で風を流し、圧力損失を測定した。その結果、いずれのフィルターユニットも圧損は23Paであった。 (1) With respect to each of the two filter units, air was flowed at an air volume of 3.1 m 2 / min, and pressure loss was measured. As a result, the pressure loss of any filter unit was 23 Pa.
(2)次いで、JIS15種ダストをJIS B9908(1991)に記載の形式3に準じて圧損が初期圧損の2倍になるまで付着させた。 (2) Next, JIS 15 type dust was adhered until the pressure loss doubled the initial pressure loss in accordance with type 3 described in JIS B 9908 (1991).
(3)その後、JIS15種ダストが付着したフィルターユニットを、P&G社の家庭用洗剤アリエールを2%濃度で溶かした40Lの洗浄液に1時間漬け置きした後、そのフィルターユニットに水圧0.2MPaの水道水を吹き掛けダストの脱離作業を行い、その後、天日で3日間の乾燥を行った。 (3) After that, the filter unit with JIS 15 type dust adhered was immersed in a 40 L cleaning solution in which P & G's household detergent Arière was dissolved at a concentration of 2% for 1 hour, and then the water pressure of 0.2 MPa was applied to the filter unit. The dust was detached by spraying water, and then dried for 3 days in the sun.
(5)乾燥後のフィルターユニットについて、上記(1)と同様にして再度圧損を測定し、圧損変化率を求めた。 (5) For the filter unit after drying, the pressure loss was measured again in the same manner as in (1) above, and the rate of change in pressure loss was determined.
その結果、F加工を行っていない濾材(L)を用いたフィルターユニットの圧損変化率WPが25%であるのに対して、F加工を行った濾材(K)を用いたフィルターユニットの圧損変化率UPが5%であり、フィルターユニットとしてみてもF加工の効果が明らかに高いことが確認できた。 Pressure loss resulting filter unit pressure drop change rate W P of the filter unit using the filter medium that has not been F machining (L) Whereas 25%, was used filter medium (K) subjected to F machining The change rate UP was 5%, and it was confirmed that the F processing effect was clearly high even when viewed as a filter unit.
(比較例4)
メルトブロー紡糸法で製造したポリプロピレン極細繊維不織布(平均繊維径2.4μm、目付20g/m2)に補強材のポリエステルスパンボンド不織布(ルトラビル社製:品番LDH7270W、目付70g/m2)を積層し、界面活性剤としてオクチルジメチルアンモニウムクロリド(三洋化成(株)、商品名カチオンDDC−50)を不織布重量の5%付着した濾材を作成した。界面活性剤加工後の水吸い上げ高さは27mmであった。
(Comparative Example 4)
Meltblown spinning polypropylene microfibrous non-woven fabric prepared in (average fiber diameter 2.4 [mu] m, basis weight 20 g / m 2) polyester spunbonded nonwoven reinforcing material (Rutorabiru Co., Ltd. No. LDH7270W, basis weight 70 g / m 2) was laminated, A filter medium was prepared in which octyldimethylammonium chloride (Sanyo Kasei Co., Ltd., trade name Cation DDC-50) as a surfactant was attached to 5% of the weight of the nonwoven fabric. The water suction height after processing the surfactant was 27 mm.
ついで実施例3と同じ方法で洗浄再生性を評価したところ、UPが4%であった。続いて、同じ条件で2回目のダスト負荷を行い洗浄再生性を評価したところ、UPは7%と脱離性が悪化し洗浄再生能力が低下したことが分かった。界面活性剤が消失することが原因と考えられた。 Subsequently, when the cleaning reproducibility was evaluated in the same manner as in Example 3, the UP was 4%. Subsequently, when the second dust load was applied under the same conditions and the cleaning and regenerating property was evaluated, it was found that UP was 7%, the desorbing property was deteriorated and the cleaning and regenerating capability was lowered. The cause was thought to be the disappearance of the surfactant.
(比較例5)
メルトブロー紡糸法で製造したポリプロピレン極細繊維不織布(平均繊維径2.4μm、目付20g/m2)に補強材のポリエステルスパンボンド不織布(ルトラビル社製:品番LDH7270W、目付70g/m2)を積層した濾材に、フッ素樹脂(旭硝子製パラジェッPRニュー)を濾材重量の3%付着(乾燥後有効成分)させた。フッ素樹脂加工後の水吸い上げ高さは0mmであった。
(Comparative Example 5)
A filter medium obtained by laminating a polyester spunbond nonwoven fabric (manufactured by Lutraville, product number: LDH7270W, weight per unit area: 70 g / m 2 ) on a polypropylene ultrafine fiber non-woven fabric (average fiber diameter: 2.4 μm, basis weight: 20 g / m 2 ) manufactured by the melt blow spinning method. Next, 3% of the weight of the filter medium was attached (active ingredient after drying) with a fluororesin (Araji Glass Parajep PR New). The water suction height after processing the fluororesin was 0 mm.
フッ素樹脂加工前後の濾材圧損を測定したところ加工前55Paであったが、加工後は67Paとなり目詰まりが促進されていた。 When the filter media pressure loss before and after the fluororesin processing was measured, it was 55 Pa before processing, but it was 67 Pa after processing, and clogging was promoted.
(比較例6)
メルトブロー紡糸法で製造したポリプロピレン極細繊維不織布(平均繊維径2.4μm、目付20g/m2)に補強材のポリエステルスパンボンド不織布(ルトラビル社製:品番LDH7270W、目付70g/m2)を積層した濾材に、下記条件でプラズマ処理を行った。
(Comparative Example 6)
A filter medium obtained by laminating a polyester spunbond nonwoven fabric (manufactured by Lutraville, product number: LDH7270W, weight per unit area: 70 g / m 2 ) on a polypropylene ultrafine fiber non-woven fabric (average fiber diameter: 2.4 μm, basis weight: 20 g / m 2 ) manufactured by the melt blow spinning method. In addition, plasma treatment was performed under the following conditions.
周波数 5KHz
印可時間 30秒
雰囲気ガス アセトン含有アルゴン
大気圧 0.12MPa
加工直後の水吸い上げ高さは13mmであったが、室内に放置して半年後に水吸い上げ高さを評価したところ7mmまで低下していた。
Frequency 5KHz
Application time 30 seconds Atmospheric gas Acetone-containing argon Atmospheric pressure 0.12 MPa
The water suction height immediately after processing was 13 mm. However, when the water suction height was evaluated after being left in the room for six months, it was reduced to 7 mm.
ついで実施例3と同じ方法で洗浄再生性を評価したところ、UPが8%であった。続いて、同じ条件で2回目のダスト負荷を行い洗浄再生性を評価したところ、UPは12%と脱離性が悪化し洗浄再生能力が低下したことが分かった。 Then, when the cleaning reproducibility was evaluated in the same manner as in Example 3, the UP was 8%. Subsequently, when the second dust load was applied under the same conditions and the cleaning and regenerating property was evaluated, it was found that UP was 12%, the detaching property was deteriorated and the cleaning and regenerating capability was lowered.
本発明の洗浄再生濾材および洗浄再生フィルターユニットは、一般空調用からクリーンルーム用高性能フィルターユニット、空気清浄機用フィルター、車載用フィルター(液体、空気)として使用できるものである。 The cleaning / regenerating filter medium and cleaning / regenerating filter unit of the present invention can be used as a general-purpose air-conditioning to clean room high-performance filter unit, an air purifier filter, and an in-vehicle filter (liquid, air).
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| JP7011401B2 (en) | 2017-04-24 | 2022-01-26 | 日本無機株式会社 | Air purifier and air purifying method |
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