JP5221872B2 - Deodorizing material - Google Patents
Deodorizing material Download PDFInfo
- Publication number
- JP5221872B2 JP5221872B2 JP2006349349A JP2006349349A JP5221872B2 JP 5221872 B2 JP5221872 B2 JP 5221872B2 JP 2006349349 A JP2006349349 A JP 2006349349A JP 2006349349 A JP2006349349 A JP 2006349349A JP 5221872 B2 JP5221872 B2 JP 5221872B2
- Authority
- JP
- Japan
- Prior art keywords
- test
- deodorizing material
- weight
- parts
- carbodihydrazide
- 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.)
- Active
Links
Images
Landscapes
- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
本発明は、特にホルムアルデヒドやアセトアルデヒドなどのアルデヒド類の臭い成分の除去性能に優れた脱臭材に関するものである。 The present invention relates to a deodorizing material excellent in removal performance of odorous components of aldehydes such as formaldehyde and acetaldehyde.
一般に、商業施設や工場、レストランなどで用いられる業務用の換気装置では、排気流路に脱臭材を配設して脱臭することが行われている。 In general, in a commercial ventilation apparatus used in commercial facilities, factories, restaurants, etc., deodorizing material is disposed in an exhaust passage to deodorize it.
従来より、この脱臭に用いる脱臭材としては、含水珪酸マグネシウム粘土鉱物を主成分とするハニカム通気孔の連続多孔構造体のものが知られている。(例えば、特許文献1参照)。
しかし、上記従来の脱臭材は、ガス状の有機化合物に対しては脱臭性能を有しているが、シックハウス症候群やタバコの刺激臭の原因となっているホルムアルデヒドやアセトアルデヒドその他のアルデヒド類の脱臭性能は、十分に発揮することができないといった不都合を生じていた。 However, the above-mentioned conventional deodorizing materials have deodorizing performance against gaseous organic compounds, but deodorizing performance of formaldehyde, acetaldehyde and other aldehydes that cause the irritating odor of sick house syndrome and tobacco. Caused the inconvenience that it could not be fully demonstrated.
本発明は係る実情に鑑みてなされたものであって、アルデヒド類への高い除去効率を発現し、かつ、長期間使用することができる脱臭材を提供することを目的としている。 The present invention was made in view of the circumstances of, aims at a high removal efficiency to aldehydes and outgoing current, and provides a deodorizing material can be used for a long time.
本発明者等は、アルデヒド類の臭気成分の除去について鋭意研究を重ねたところ、含水珪酸マグネシウム組成物にカルボジヒドラジドを添着したものが優れた脱臭効果を発揮することを知見し、本発明に至ったものである。 As a result of intensive studies on the removal of odorous components from aldehydes, the present inventors have found that a hydrated magnesium silicate composition with carbodihydrazide exerts an excellent deodorizing effect, leading to the present invention. It is a thing.
すなわち、本発明は、含水珪酸マグネシウム組成物から得られるペレット状物にカルボジヒドラジドが添着されたことを特徴とする脱臭材である。 That is, the present invention is a deodorizing material characterized in that carbodihydrazide is attached to pellets obtained from a hydrous magnesium silicate composition.
含水珪酸マグネシウム組成物は、例えば、含水珪酸マグネシウム粘土鉱物を主成分とする粉末材料を結合材とともに湿式混練した後、ロッド状、ペレット状、マカロニ状などの任意の形状に押し出し成形し、乾燥後に焼成して含水珪酸マグネシウムペレット状物として形成することができる。ここで用いる含水珪酸マグネシウム粘土鉱物としては、ホルマイト、ゼオライト、セピオライト、シロタイル、ラフリナイト、およびアタパルジャイト等が挙げられる。結合材はPVA樹脂、PTFE(ポリテトラフルオロエチレン)、PVDF(ポリフッ化ビニリデン)、PVC(ポリ塩化ビニル)、ポリアクリル酸エステル、エポキシ樹脂、フェノール樹脂、ポリエチレン、ポリプロピレン、ABS樹脂、ポリエステルなどのポリマー、シリカゾル、アルミナゾル、ベントナイト、カオリナイト等の粘土鉱物が挙げられる。 The hydrous magnesium silicate composition is, for example, wet kneaded together with a binder with a powder material mainly composed of hydrous magnesium silicate clay mineral, then extruded into any shape such as rod, pellet, macaroni, etc., and after drying It can be fired to form hydrous magnesium silicate pellets. Examples of the hydrous magnesium silicate clay mineral used here include holmite, zeolite, sepiolite, sirotile, rafrinite, and attapulgite. The binder is a polymer such as PVA resin, PTFE (polytetrafluoroethylene), PVDF (polyvinylidene fluoride), PVC (polyvinyl chloride), polyacrylate, epoxy resin, phenol resin, polyethylene, polypropylene, ABS resin, polyester, etc. And clay minerals such as silica sol, alumina sol, bentonite and kaolinite.
含水珪酸マグネシウムペレット状物は、このペレット状物を多数充填することにより形成された多数の空隙が連続して通気可能な通気孔を形成するように連続多孔構造となされたものであれば、特に限定されるものではなく、例えば、粒状の含水珪酸マグネシウムペレット状物を積み重ね、隣接するペレット状物同士の間隙から通気させるようにしたものであってもよいし、中空ロッド状やマカロニ状の形状を有する含水珪酸マグネシウムペレット状物として成形し、これらを通気性を有する容器内に充填したものであってもよい。なお、通気時の含水珪酸マグネシウムペレット状物と通気ガスとの接触を多くしようとして粒子を細かくしたり充填密度を上げた場合、通気抵抗が増すこととなり、通気抵抗を低くした場合、含水珪酸マグネシウムペレット状物と通気ガスとを充分に接触させることができなくなる。したがって、これら含水珪酸マグネシウムペレット状物の大きさ、通気抵抗などは、用いる場所や許容される通気圧力損失などに応じたものを適宜選択できる。 The hydrous magnesium silicate pellet is particularly suitable if it has a continuous porous structure so that a large number of voids formed by filling a large number of the pellets can be continuously vented. It is not limited, and for example, granular hydrous magnesium silicate pellets may be stacked and aerated from the gap between adjacent pellets, or may be hollow rod or macaroni It may be formed as a hydrous magnesium silicate pellet having the above and filled with a breathable container. If the particles are made finer or the packing density is increased in order to increase the contact between the hydrous magnesium silicate pellets and the aeration gas during ventilation, the ventilation resistance will increase, and if the ventilation resistance is lowered, the hydrous magnesium silicate will increase. It becomes impossible to sufficiently contact the pellet and the aeration gas. Accordingly, the size, ventilation resistance, etc. of these hydrous magnesium silicate pellets can be appropriately selected according to the place of use and the allowable ventilation pressure loss.
カルボジヒドラジドは、化学式NH 2 NH−CO- NHNH 2 で表される。このカルボジヒドラジドは、含水珪酸マグネシウムペレット状物100重量部に対して1重量部以上15重量部以下、好ましくは5重量部以上10重量部以下となるように、上記含水珪酸マグネシウムペレット状物に添着される。 Carbodihydrazide is represented by the chemical formula NH 2 NH—CO—NHNH 2 . The carbodihydrazide is attached to the hydrous magnesium silicate pellet so that it is 1 to 15 parts by weight, preferably 5 to 10 parts by weight, per 100 parts by weight of the hydrous magnesium silicate pellets. Is done.
この添着は、上記含水珪酸マグネシウムペレット状物を、カルボジヒドラジドの薬剤中に含浸させて含水珪酸マグネシウムペレット状物にカルボジヒドラジドを添着することによって行うことができる。このカルボジヒドラジドは、含水珪酸マグネシウムペレット状物100重量部に対して1重量部未満の場合、アルデヒド類に対して十分な脱臭能力を得ることができず、一方、15重量部を超えると、アルデヒド類に対する脱臭能力が飽和するとともに、カルボジヒドラジド自体に含まれるアミノ基によって脱臭材自体から放散するアミン臭が強くなり使用する用途によっては好ましくない。 This attachment can be carried out by impregnating the hydrated magnesium silicate pellets in a carbodihydrazide agent and attaching carbodihydrazide to the hydrated magnesium silicate pellets. When this carbodihydrazide is less than 1 part by weight relative to 100 parts by weight of the hydrous magnesium silicate pellets, sufficient deodorizing ability cannot be obtained with respect to aldehydes. The deodorizing ability with respect to the odor is saturated, and the amine group contained in the carbodihydrazide itself increases the amine odor emitted from the deodorizing material itself.
なお、この添着は、含浸添着に限定されるものではなく、上記含水珪酸マグネシウム粒状ペレット状物にカルボジヒドラジドの薬剤をスプレーによって噴霧することで添着するものであってもよいし、刷毛などで塗布することによって添着するものであってもよい。 Note that this attachment is not limited to impregnation attachment, and the hydrated magnesium silicate pellets may be attached by spraying a carbodihydrazide drug by spraying, or applied with a brush or the like. It may be attached by doing.
このようにして構成される脱臭材は、含水珪酸マグネシウムペレット状物に添着させたカルボジヒドラジドがアミノ基を有するため、脱臭材自体の臭気が発生することとなる。したがって、脱臭材自体のアミン臭を低減させる目的で、含水珪酸マグネシウムペレット状物100重量部に対して5重量部以上となるようにリン酸を添着してもよい。この場合、リン酸の添着は、含水珪酸マグネシウムペレット状物にカルボジヒドラジドを添着した後、同じ要領でリン酸を添着するものであってもよいし、含水珪酸マグネシウムペレット状物にリン酸を添着した後、同じ要領でカルボジヒドラジドを添着するものであってもよいし、含水珪酸マグネシウムペレット状物にカルボジヒドラジドとリン酸とを同時に添着するものであってもよい。このリン酸の添着量が、含水珪酸マグネシウムペレット状物100重量部に対して5重量部未満の場合には、このアミン臭低減効果が低く脱臭材自体の臭気を十分に除去することができない。また、5重量部以上では、アミン臭の除去効果が認められる。しかしながらリン酸添加量の増加に伴い、アセトアルデヒドの除去率が低下する現象があるため、したがって、含水珪酸マグネシウムペレット状物に添着させるリン酸の量としては、含水珪酸マグネシウムペレット状物100重量部に対して5重量部以上10重量部以下の範囲で、脱臭材に要求される脱臭能力に応じて適宜調整できる。このリン酸の添着についても、上記カルボジヒドラジドの添着と同様に含浸添着に限定されるものではなく、スプレーによる噴霧で添着するものであってもよいし、刷毛などによる塗布によって添着するものであってもよい。 In the deodorizing material thus configured, the odor of the deodorizing material itself is generated because the carbodihydrazide added to the hydrous magnesium silicate pellets has an amino group. Therefore, phosphoric acid may be added so as to be 5 parts by weight or more with respect to 100 parts by weight of the hydrous magnesium silicate pellets for the purpose of reducing the amine odor of the deodorizing material itself. In this case, phosphoric acid may be added by adding carbodihydrazide to the hydrous magnesium silicate pellet and then adding phosphoric acid in the same manner, or adding phosphoric acid to the hydrous magnesium silicate pellet. Then, carbodihydrazide may be attached in the same manner, or carbodihydrazide and phosphoric acid may be attached simultaneously to the hydrous magnesium silicate pellet. When the amount of phosphoric acid added is less than 5 parts by weight with respect to 100 parts by weight of the hydrous magnesium silicate pellets, the amine odor reducing effect is low and the odor of the deodorizing material itself cannot be sufficiently removed. Moreover, the removal effect of an amine odor is recognized by 5 weight part or more. However, as the amount of phosphoric acid added increases, there is a phenomenon that the removal rate of acetaldehyde decreases. Therefore, the amount of phosphoric acid added to the hydrous magnesium silicate pellets is 100 parts by weight of hydrous magnesium silicate pellets. On the other hand, in the range of 5 parts by weight or more and 10 parts by weight or less, it can be appropriately adjusted according to the deodorizing ability required for the deodorizing material. The addition of phosphoric acid is not limited to impregnation as in the case of carbodihydrazide, but may be applied by spraying with a spray, or by application with a brush or the like. May be.
このようにして構成される脱臭材は、アルデヒド類の臭気を高い除去効率で除去し、かつ、長期にわたって脱臭効果を維持することができるだけでなく、今までの含水珪酸マグネシウムペレット状物が有していた他の臭い成分の除去性能についてもそのまま維持することができる。したがって、他の臭い成分の中にアルデヒド類を含んだ複合臭気に対しても、この脱臭材一つで除去することが可能となる。 The deodorizing material constituted in this way not only removes the odor of aldehydes with high removal efficiency and maintains the deodorizing effect over a long period of time, but also the conventional hydrous magnesium silicate pellets have The removal performance of other odorous components that have been present can also be maintained. Therefore, it is possible to remove even a complex odor containing aldehydes in other odor components with this single deodorizing material.
以上述べたように、本発明の脱臭材によると、アルデヒド類の臭気を高い除去効率で除去し、かつ、長期にわたって脱臭効果を維持することができる。 As described above, according to the deodorizing material of the present invention, the odor of aldehydes can be removed with high removal efficiency, and the deodorizing effect can be maintained over a long period of time.
また、リン酸を添着することにより、脱臭材自体の臭気も抑えることができるので、広い用途に適用可能となる。 Further, by impregnating the-phosphate, it can be suppressed even odor deodorizing material itself, and can be applied in a wide range of applications.
以下、本発明の実施例を挙げて具体的に説明する。
アセトアルデヒド1パス除去特性試験1
含水珪酸マグネシウム成形体のペレット状物を、6〜8メッシュの篩にかけ、整粒したペレット状物約12〜14g(容積20〜24cc)を用意した。
Examples of the present invention will be specifically described below.
Acetaldehyde 1-pass removal characteristic test 1
About 12-14 g (volume 20-24 cc) of the pellet-shaped material which adjusted the pellet-form thing of the hydrous magnesium silicate molded object through the sieve of 6-8 mesh, and prepared the particle size.
このペレット状物に、カルボジヒドラジド、アジピン酸ジヒドラジド、コハク酸ジヒドラジドをそれぞれ含浸添着して表1に示すように、参考例1〜参考例3、比較例1〜3の各試験脱臭材を用意した。 This pelletized product, carbodihydrazide, adipic acid dihydrazide, and each impregnating and adding succinic acid dihydrazide, as shown in Table 1, Reference Example 1 to Reference Example 3, were prepared each test deodorizing material of Comparative Example 1-3 .
各試験脱臭材を25mmφの円筒状容器に充填し、入口側から10ppmに調整したアセトアルデヒドガスを1.0m/sの線速度で供給し、各試験脱臭材を通過した後の出口側でアセトアルデヒドガスの濃度測定を行った。測定は、ガステック社製のガス検知管を使用してガス通過1分後、60分後、120分後のそれぞれについて行った。出口濃度から各試験脱臭材によって除去されたアセトアルデヒドガスの除去率を求めた。結果を表1に示す。 Each test deodorizing material is filled in a cylindrical container of 25 mmφ, acetaldehyde gas adjusted to 10 ppm is supplied from the inlet side at a linear velocity of 1.0 m / s, and acetaldehyde gas is passed on the outlet side after passing through each test deodorizing material. The concentration was measured. The measurement was performed using a gas detection tube manufactured by Gastec Co., Ltd., after 1 minute, 60 minutes, and 120 minutes after gas passage. The removal rate of the acetaldehyde gas removed by each test deodorizing material was determined from the outlet concentration. The results are shown in Table 1.
アセトアルデヒド1パス除去特性試験2
含水珪酸マグネシウム成形体のペレット状物を、6〜8メッシュの篩にかけ、整粒したペレット状物服12〜14g(容積20〜24cc)と、同じく6〜8メッシュの篩にかけて整粒した活性炭のペレット状物とを用意した。
Acetaldehyde 1-pass
The pellets of the hydrous magnesium silicate compact were passed through a 6-8 mesh sieve, and the size of the pelletized clothes 12-14 g (volume 20-24 cc), and the activated carbon which was also granulated through a 6-8 mesh sieve. A pellet was prepared.
これらのペレット状物に、カルボジヒドラジドをそれぞれ含浸添着し、ペレット状物100重量部に対して10重量部となるようにカルボジヒドラジドを含浸添着した含水珪酸マグネシウムのペレット状物からなる参考例4の試験脱臭材と、ペレット状物100重量部に対して5重量部となるようにカルボジヒドラジドを含浸添着した活性炭のペレット状物からなる比較例4の試験脱臭材と、ペレット状物100重量部に対して10重量部となるようにカルボジヒドラジドを含浸添着した活性炭のペレット状物からなる比較例5の試験脱臭材をそれぞれ用意した。 These pellets was carbodihydrazide were respectively impregnated impregnation, consisting of pellets of hydrous magnesium silicate impregnated impregnated with carbodihydrazide so as to be 10 parts by weight relative to pellets was 100 parts by weight of Referential Example 4 The test deodorizing material, the test deodorizing material of Comparative Example 4 consisting of activated carbon pellets impregnated with carbodihydrazide so as to be 5 parts by weight with respect to 100 parts by weight of the pellets, and 100 parts by weight of the pellets On the other hand, the test deodorizing material of Comparative Example 5 made of activated carbon pellets impregnated with carbodihydrazide so as to be 10 parts by weight was prepared.
各試験脱臭材を25mmφの円筒状容器に充填し、各試験脱臭材の入口側から10ppmに調整したアセトアルデヒドガスを1.0m/sの線速度で供給し、各試験脱臭材を通過した後の出口側でアセトアルデヒドガスの濃度測定を行った。測定は、ガステック社製のガス検知管を使用してガス通過 2時間毎に行った。出口濃度から各試験脱臭材によって除去されたアセトアルデヒドガスの除去率を求めた。結果を図1のグラフに示す。 Each test deodorizing material is filled in a cylindrical container of 25 mmφ, and acetaldehyde gas adjusted to 10 ppm is supplied from the inlet side of each test deodorizing material at a linear velocity of 1.0 m / s, and after passing through each test deodorizing material. The concentration of acetaldehyde gas was measured on the outlet side. The measurement was performed every 2 hours through the gas passage using a gas detector manufactured by Gastec. The removal rate of the acetaldehyde gas removed by each test deodorizing material was determined from the outlet concentration. The results are shown in the graph of FIG.
図1の結果から、カルボジヒドラジドを活性炭のハニカム構造体に含浸添着しても十分な除去率を得ることができないが、カルボジヒドラジドを含水珪酸マグネシウムのペレット状物に含浸添着した場合には、除去率が飛躍的に向上することが確認できた。
アルデヒド平衡吸着量評価試験
参考例3の試験脱臭材と、参考例3のカルボジヒドラジドをアジピン酸ジヒドラジドに変更し、それ以外は参考例3と同様に構成した比較例6の試験脱臭材と、参考例3のカルボジヒドラジドをコハク酸ジヒドラジドに変更し、それ以外は参考例3と同様に構成した比較例7の試験脱臭材とをそれぞれ用意した。また、他社製品として、比較例8に係るアニリン系添着剤の試験脱臭材、比較例9に係る過マンガン酸カリ系添着剤の試験脱臭材、比較例10に係るモルフォリン系添着剤の試験脱臭材をそれぞれ用意した。
From the results of FIG. 1, it is not possible to obtain a sufficient removal rate even if carbodihydrazide is impregnated and impregnated into the honeycomb structure of activated carbon. However, when carbodihydrazide is impregnated and impregnated into a pellet of hydrous magnesium silicate, it is removed. It was confirmed that the rate improved dramatically.
Aldehyde equilibrium adsorption amount evaluation test
The test deodorant of Example 3, a carbodihydrazide of Reference Example 3 was changed to adipic acid dihydrazide, otherwise the test deodorizing material of Comparative Example 6 were constituted in the same manner as in Reference Example 3, a carbodihydrazide of Reference Example 3 The test deodorizing material of Comparative Example 7 was prepared in the same manner as Reference Example 3 except that the succinic acid dihydrazide was used. Further, as other company's products, the test deodorizing material of the aniline-based additive according to Comparative Example 8, the test deodorizing material of the potassium permanganate-based additive according to Comparative Example 9, and the test deodorizing of the morpholine-based additive according to Comparative Example 10 Each material was prepared.
各試験脱臭材を22リットル容量の密閉循環式平衡吸着量評価装置に1.0g投入し、5リットル/分の循環風量で、50ppmのアセトアルデヒドと50ppmのホルムアルデヒドとの混合ガスを循環させた。ガステック社製のガス検知管を使用して混合ガスの濃度測定を行い、濃度変化が無く平衡するまで循環させた後、最終測定濃度から各試験脱臭材の平衡吸着量を評価した。結果を表2、図2、図3に示す。 1.0 g of each test deodorizing material was put into a 22 liter capacity closed circulation type equilibrium adsorption amount evaluation apparatus, and a mixed gas of 50 ppm acetaldehyde and 50 ppm formaldehyde was circulated at a circulation air volume of 5 liters / minute. The concentration of the mixed gas was measured using a gas detection tube manufactured by Gastec Co., Ltd., and the mixture was circulated until equilibration without any change in concentration. Then, the equilibrium adsorption amount of each test deodorizing material was evaluated from the final measured concentration. The results are shown in Table 2, FIG. 2 and FIG.
また、この試験で使用したカルボジヒドラジド、アジピン酸ジヒドラジド、コハク酸ジヒドラジド、モルフォリンのそれぞれの添着剤5gを、3リットルの密閉バックに封入し、各添着剤の臭気の強弱を3人のパネラーで官能評価した。 In addition, 5 g of each additive of carbodihydrazide, adipic acid dihydrazide, succinic acid dihydrazide, and morpholine used in this test was sealed in a 3-liter sealed bag, and the odor intensity of each additive was controlled by three panelists. Sensory evaluation was performed.
その結果、モルフォリン>アジピン酸ジヒドラジド>コハク酸ジヒドラジド>カルボジヒドラジドの順で、アミン臭気が低下することが確認できた。
アセトアルデヒド1パス除去特性試験3
参考例3の試験脱臭材に、リン酸を含浸添着して表3および図4に示すように、参考例3、参考例5、実施例1,2の各試験脱臭材を用意した。
As a result, it was confirmed that the amine odor decreased in the order of morpholine> adipic acid dihydrazide> succinic acid dihydrazide> carbodihydrazide.
Acetaldehyde 1-pass removal characteristic test 3
The test deodorizing material of Reference Example 3 was impregnated with phosphoric acid, and the test deodorizing materials of Reference Example 3, Reference Example 5, and Examples 1 and 2 were prepared as shown in Table 3 and FIG.
各試験脱臭材12〜14gのアミン臭気の有無を3人のパネラーで官能評価した。その結果、ペレット状物100重量部に対して5重量部以上となるようにリン酸を含浸添着した場合、アミン臭気が気にならないといった結果が得られた。 The presence or absence of amine odor of 12 to 14 g of each test deodorizing material was sensory-evaluated by three panelists. As a result, when the phosphoric acid was impregnated and impregnated so as to be 5 parts by weight or more with respect to 100 parts by weight of the pellet-like material, a result that the amine odor was not a concern was obtained.
次に、このようにしてリン酸を含浸添着した各試験脱臭材12〜14gを、25mmφの円筒状容器に充填し、各試験脱臭材の入口側から10ppmに調整したアセトアルデヒドガスを1.0m/sの線速度で供給し、各試験脱臭材を通過した後の出口側でアセトアルデヒドガスの濃度測定を行った。測定は、ガステック社製のガス検知管を使用してガス通過120分後のそれぞれについて行った。出口濃度から各試験脱臭材によって除去されたアセトアルデヒドガスの除去率を求めた。結果を図4に示す。 Next, 12 to 14 g of each test deodorizing material impregnated and impregnated with phosphoric acid in this manner was filled into a cylindrical container of 25 mmφ, and acetaldehyde gas adjusted to 10 ppm from the inlet side of each test deodorizing material was 1.0 m / The concentration of acetaldehyde gas was measured at the outlet side after feeding at the linear velocity of s and passing through each test deodorizing material. The measurement was performed for each gas passage 120 minutes after using a gas detection tube manufactured by Gastec. The removal rate of the acetaldehyde gas removed by each test deodorizing material was determined from the outlet concentration. The results are shown in FIG.
図4の結果から、リン酸の含浸添着量が増加するに伴って除去率の低下はあるもののアミン臭気を低減できることを見出した。ペレット状物100重量部に対して15重量部以上となるようにリン酸を含浸添着した場合でも、アセトアルデヒド除去性能としては30%の良好な除去率を維持することが確認できた。
複合臭気(厨房臭気)1パス除去特性試験
参考例3の試験脱臭材と比較例1の試験脱臭材とを用意した。
From the results shown in FIG. 4, it was found that the amine odor can be reduced although the removal rate decreases as the amount of impregnated and impregnated phosphoric acid increases. Even when phosphoric acid was impregnated and impregnated so as to be 15 parts by weight or more with respect to 100 parts by weight of the pellets, it was confirmed that a good removal rate of 30% was maintained as the acetaldehyde removal performance.
Compound odor (kitchen odor) 1-pass removal characteristics test
The test deodorizing material of Reference Example 3 and the test deodorizing material of Comparative Example 1 were prepared.
いわゆる4大悪臭といわれるアンモニア、トリメチルアミン、メチルメルカプタン、硫化水素の他、アルデヒド類や揮発性有機化合物(VOC)、低級脂肪酸を含んでいる厨房臭気を、現実の店舗においてガスバックに採取した。 In addition to ammonia, trimethylamine, methyl mercaptan, and hydrogen sulfide, which are the so-called four major malodors, kitchen odors containing aldehydes, volatile organic compounds (VOC), and lower fatty acids were collected in gas bags at actual stores.
次に、用意した実施例3および比較例1の各試験脱臭材12〜14gを、25mmφの円筒状容器に充填し、各試験脱臭材の入口側から厨房臭気を1.0m/sの線速度で供給し、各試験脱臭材を通過した後の出口側で臭気強度(濃度)の測定を行った。測定は、新コスモス電気社製の「においセンサーXP329」(商品名)を使用し、測定器の表示値による判定を行った。結果を表3に示す。 Next, 12 to 14 g of each test deodorizing material prepared in Example 3 and Comparative Example 1 was filled in a cylindrical container of 25 mmφ, and the kitchen odor from the entrance side of each test deodorizing material was a linear velocity of 1.0 m / s. The odor intensity (concentration) was measured on the outlet side after passing through each test deodorizing material. For the measurement, “Odor sensor XP329” (trade name) manufactured by Shin Cosmos Electric Co., Ltd. was used, and the determination was made based on the display value of the measuring instrument. The results are shown in Table 3.
清浄空気1パス除去特性試験
参考例3の試験脱臭材を用意した。また、この参考例3の試験脱臭材にリン酸を5%含浸添着し、それ以外は参考例3と同様に構成した実施例1の試験脱臭材と、参考例3の試験脱臭材におけるカルボジヒドラジドの添加量を15重量部に変更し、それ以外は参考例3と同様に構成した参考例5の試験脱臭材と、参考例5の試験脱臭材にリン酸を5%含浸添着し、それ以外は参考例5と同様に構成した実施例3の試験脱臭材と、参考例3の試験脱臭材におけるカルボジヒドラジドの添加量を20重量部に変更し、それ以外は参考例3と同様に構成した比較例11の試験脱臭材と、この比較例11の試験脱臭材にリン酸を5%含浸添着し、それ以外は比較例11と同様に構成した比較例12の試験脱臭材とを用意した。
Clean air 1-pass removal characteristic test
The test deodorizing material of Reference Example 3 was prepared. Also, the phosphoric acid to the test deodorant of Reference Example 3 and 5% impregnation impregnation, otherwise the test deodorant of Example 1 configured in the same manner as in Reference Example 3, carbodihydrazide in the test deodorant of Example 3 change amount of the additive to 15 parts by weight, otherwise the test deodorant of example 5 was constituted in the same manner as in reference example 3, the phosphoric acid to the test deodorant of example 5 was 5% impregnating and adding, otherwise The test deodorizing material of Example 3 configured in the same manner as in Reference Example 5 and the amount of carbodihydrazide added in the test deodorizing material of Reference Example 3 were changed to 20 parts by weight, and the other configurations were the same as in Reference Example 3. A test deodorizing material of Comparative Example 11 and a test deodorizing material of Comparative Example 12 configured in the same manner as Comparative Example 11 except that 5% phosphoric acid was impregnated and impregnated into the test deodorizing material of Comparative Example 11 were prepared.
次に、用意した実施例1、実施例3、参考例3、参考例5、比較例11および比較例12の各試験脱臭材12〜14gを、25mmφの円筒状容器に充填し、各試験脱臭材の入口側から清浄空気を1.0m/sの線速度で供給し、各試験脱臭材を通過した後の出口側で臭気強度(濃度)の測定を行った。測定は、新コスモス電気社製の「においセンサーXP329」(商品名)を使用し、測定器の表示値による判定を行った。結果を表4に示す。 Next, 12 to 14 g of each test deodorizing material prepared in Example 1, Example 3, Reference Example 3, Reference Example 5 , Comparative Example 11 and Comparative Example 12 was filled in a cylindrical container of 25 mmφ, and each test deodorization was performed. Clean air was supplied at a linear velocity of 1.0 m / s from the inlet side of the material, and the odor intensity (concentration) was measured on the outlet side after passing through each test deodorizing material. For the measurement, “Odor sensor XP329” (trade name) manufactured by Shin Cosmos Electric Co., Ltd. was used, and the determination was made based on the display value of the measuring instrument. The results are shown in Table 4.
各種換気装置などに装着する脱臭材として利用できる。 It can be used as a deodorizing material to be installed in various ventilation devices.
Claims (1)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2006349349A JP5221872B2 (en) | 2006-12-26 | 2006-12-26 | Deodorizing material |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2006349349A JP5221872B2 (en) | 2006-12-26 | 2006-12-26 | Deodorizing material |
Publications (3)
| Publication Number | Publication Date |
|---|---|
| JP2008154918A JP2008154918A (en) | 2008-07-10 |
| JP2008154918A5 JP2008154918A5 (en) | 2010-01-21 |
| JP5221872B2 true JP5221872B2 (en) | 2013-06-26 |
Family
ID=39656455
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2006349349A Active JP5221872B2 (en) | 2006-12-26 | 2006-12-26 | Deodorizing material |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP5221872B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102247807B (en) * | 2011-05-17 | 2013-09-25 | 江苏麦阁吸附剂有限公司 | Preparation method and usage of modified attapulgite adsorption material |
| CN103041425A (en) * | 2012-12-28 | 2013-04-17 | 青岛信锐德科技有限公司 | Air freshener with natural minerals |
Family Cites Families (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH10235129A (en) * | 1997-02-25 | 1998-09-08 | Matsushita Electric Works Ltd | Filter |
| JP2003169841A (en) * | 2001-12-05 | 2003-06-17 | Nanmokumura Shinrin Kumiai | Deodorant and method of preparing the same |
| WO2004058311A1 (en) * | 2002-12-24 | 2004-07-15 | Toagosei Co., Ltd. | Deodorant with excellent water resistance |
| JP2004275520A (en) * | 2003-03-17 | 2004-10-07 | Aisin Seiki Co Ltd | Aldehyde remover |
| JP2006075312A (en) * | 2004-09-09 | 2006-03-23 | Otsuka Chemical Co Ltd | Deodorant composition having superior heat resistance and molding using the same |
-
2006
- 2006-12-26 JP JP2006349349A patent/JP5221872B2/en active Active
Also Published As
| Publication number | Publication date |
|---|---|
| JP2008154918A (en) | 2008-07-10 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US8071081B2 (en) | Reduction of airborne malodors using hydrogen peroxide and a catalyst-coated media | |
| JP6807834B2 (en) | Filtration device for air purifiers | |
| CN105658247A (en) | Deodorizing filter | |
| EP3213775B1 (en) | Method for producing deodorizer and method for producing deodorizing processed product | |
| KR102225310B1 (en) | Filter cartridge for an air purifier | |
| JP2008543369A (en) | Vapor phase hydrogen peroxide deodorant | |
| JP5221872B2 (en) | Deodorizing material | |
| JP5221871B2 (en) | Deodorizing material | |
| TWI229000B (en) | Deodorizer, process for producing the same, and method of deodorization | |
| JP4094046B2 (en) | Deodorized fabric and method for deodorizing fabric | |
| KR20100008612A (en) | Deodorizing filter for removing stench of food waste disposer system | |
| JP2004024330A (en) | Deodorant | |
| EP2065060B1 (en) | Air freshener anti-humidity tablet | |
| JPH042350A (en) | Aldehyde removing agent | |
| JP2006116093A (en) | Deodorant and deodorant composition using artificial zeolite | |
| JPH1071193A (en) | Air cleaning agent and deodorant filter | |
| JP2950683B2 (en) | Air purifier and air purifier | |
| JPH0584283A (en) | Deodorant | |
| JP2002200149A (en) | Deodorant | |
| JPH1199194A (en) | Deodorizing composition, deodorizing apparatus and deodorizing method using the same | |
| JP6756543B2 (en) | Deodorant | |
| KR20210103449A (en) | Hybrid-complx filters generating oxygen | |
| JPH1099418A (en) | Deodorizing filter | |
| JP2005287913A (en) | Hybrid type mineral material for adsorption and removal of odorous component and hazardous component | |
| JP2007261906A (en) | Porous particles |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20091126 |
|
| A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20091126 |
|
| A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20120724 |
|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20120918 |
|
| A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20121023 |
|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20121220 |
|
| TRDD | Decision of grant or rejection written | ||
| A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20130226 |
|
| A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20130308 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20160315 Year of fee payment: 3 |
|
| R150 | Certificate of patent or registration of utility model |
Free format text: JAPANESE INTERMEDIATE CODE: R150 Ref document number: 5221872 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |