JP2009082254A - Basic gas removing filter - Google Patents
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- JP2009082254A JP2009082254A JP2007252910A JP2007252910A JP2009082254A JP 2009082254 A JP2009082254 A JP 2009082254A JP 2007252910 A JP2007252910 A JP 2007252910A JP 2007252910 A JP2007252910 A JP 2007252910A JP 2009082254 A JP2009082254 A JP 2009082254A
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- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 140
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims abstract description 64
- 230000001877 deodorizing effect Effects 0.000 claims abstract description 55
- 229910000147 aluminium phosphate Inorganic materials 0.000 claims abstract description 32
- 239000001488 sodium phosphate Substances 0.000 claims description 43
- LWIHDJKSTIGBAC-UHFFFAOYSA-K potassium phosphate Substances [K+].[K+].[K+].[O-]P([O-])([O-])=O LWIHDJKSTIGBAC-UHFFFAOYSA-K 0.000 claims description 36
- 229910000403 monosodium phosphate Inorganic materials 0.000 claims description 22
- 235000019799 monosodium phosphate Nutrition 0.000 claims description 22
- AJPJDKMHJJGVTQ-UHFFFAOYSA-M sodium dihydrogen phosphate Chemical compound [Na+].OP(O)([O-])=O AJPJDKMHJJGVTQ-UHFFFAOYSA-M 0.000 claims description 22
- ZPWVASYFFYYZEW-UHFFFAOYSA-L dipotassium hydrogen phosphate Chemical compound [K+].[K+].OP([O-])([O-])=O ZPWVASYFFYYZEW-UHFFFAOYSA-L 0.000 claims description 19
- 229910000396 dipotassium phosphate Inorganic materials 0.000 claims description 19
- 235000019797 dipotassium phosphate Nutrition 0.000 claims description 19
- BNIILDVGGAEEIG-UHFFFAOYSA-L disodium hydrogen phosphate Chemical compound [Na+].[Na+].OP([O-])([O-])=O BNIILDVGGAEEIG-UHFFFAOYSA-L 0.000 claims description 19
- 229910000397 disodium phosphate Inorganic materials 0.000 claims description 19
- 235000019800 disodium phosphate Nutrition 0.000 claims description 19
- 229910000402 monopotassium phosphate Inorganic materials 0.000 claims description 17
- 235000019796 monopotassium phosphate Nutrition 0.000 claims description 17
- GNSKLFRGEWLPPA-UHFFFAOYSA-M potassium dihydrogen phosphate Chemical compound [K+].OP(O)([O-])=O GNSKLFRGEWLPPA-UHFFFAOYSA-M 0.000 claims description 17
- 239000008055 phosphate buffer solution Substances 0.000 claims description 12
- 239000007864 aqueous solution Substances 0.000 claims description 11
- 235000011007 phosphoric acid Nutrition 0.000 claims description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 abstract description 31
- 239000007789 gas Substances 0.000 abstract description 24
- 238000004332 deodorization Methods 0.000 abstract description 15
- 230000000694 effects Effects 0.000 abstract description 7
- 239000007853 buffer solution Substances 0.000 abstract description 2
- 229910052799 carbon Inorganic materials 0.000 abstract description 2
- 239000000243 solution Substances 0.000 abstract 1
- 238000001179 sorption measurement Methods 0.000 description 15
- 238000011056 performance test Methods 0.000 description 9
- 235000013162 Cocos nucifera Nutrition 0.000 description 7
- 244000060011 Cocos nucifera Species 0.000 description 7
- 238000000034 method Methods 0.000 description 7
- 235000019645 odor Nutrition 0.000 description 7
- 238000012360 testing method Methods 0.000 description 7
- 239000002253 acid Substances 0.000 description 5
- 239000003463 adsorbent Substances 0.000 description 4
- 230000000052 comparative effect Effects 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- IEQIEDJGQAUEQZ-UHFFFAOYSA-N phthalocyanine Chemical compound N1C(N=C2C3=CC=CC=C3C(N=C3C4=CC=CC=C4C(=N4)N3)=N2)=C(C=CC=C2)C2=C1N=C1C2=CC=CC=C2C4=N1 IEQIEDJGQAUEQZ-UHFFFAOYSA-N 0.000 description 3
- 239000002002 slurry Substances 0.000 description 3
- 229910021536 Zeolite Inorganic materials 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 2
- 239000006185 dispersion Substances 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 239000000835 fiber Substances 0.000 description 2
- 150000002429 hydrazines Chemical class 0.000 description 2
- 239000008363 phosphate buffer Substances 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- RYFMWSXOAZQYPI-UHFFFAOYSA-K trisodium phosphate Chemical compound [Na+].[Na+].[Na+].[O-]P([O-])([O-])=O RYFMWSXOAZQYPI-UHFFFAOYSA-K 0.000 description 2
- 229910000406 trisodium phosphate Inorganic materials 0.000 description 2
- 235000019801 trisodium phosphate Nutrition 0.000 description 2
- 239000010457 zeolite Substances 0.000 description 2
- 229920002972 Acrylic fiber Polymers 0.000 description 1
- 229920000049 Carbon (fiber) Polymers 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- 229920006318 anionic polymer Polymers 0.000 description 1
- 230000003139 buffering effect Effects 0.000 description 1
- 229920006317 cationic polymer Polymers 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000001934 delay Effects 0.000 description 1
- 239000002781 deodorant agent Substances 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 238000007654 immersion Methods 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 239000011147 inorganic material Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 150000007522 mineralic acids Chemical class 0.000 description 1
- 239000011301 petroleum pitch Substances 0.000 description 1
- 239000011941 photocatalyst Substances 0.000 description 1
- 229920000098 polyolefin Polymers 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000002459 sustained effect Effects 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Images
Abstract
Description
本発明は、冷蔵庫内、トイレ等のいやな臭いを取り除くフィルター材等として使用し、特にアンモニアガス等の塩基性ガスを効率的に吸着し、その効果の持続性を飛躍的に向上したフィルターに関する技術である。 The present invention relates to a filter that is used as a filter material or the like for removing unpleasant odors in refrigerators, toilets, etc., and that particularly adsorbs basic gases such as ammonia gas efficiently and dramatically improves the sustainability of the effect. Technology.
消臭フィルターは、様々な用途に利用されており、その消臭方法は活性炭やゼオライト等の吸着材を利用した吸着タイプと、オゾンや光触媒、金属フタロシアニン錯体等により悪臭物質を分解除去する触媒タイプ、あるいはこの吸着タイプと触媒タイプを併用した併用タイプに分けられる。 Deodorizing filters are used in various applications, and the deodorizing method is an adsorption type using an adsorbent such as activated carbon or zeolite, and a catalyst type that decomposes and removes malodorous substances by ozone, photocatalyst, metal phthalocyanine complex, etc. Or, it can be divided into a combination type in which this adsorption type and a catalyst type are used in combination.
出願人は、特許文献１において、金属フタロシアニン錯体、ヒドラジン誘導体等を活性炭混紗紙に担持させ、ｐＨ値を変えた２種類のフィルターを作成しアンモニア、硫化水素、酢酸等のガスを効率よく分解除去するフィルターを提案している。 In the patent document 1, the applicant made a metal phthalocyanine complex, a hydrazine derivative, etc. supported on activated carbon kneaded paper, created two types of filters with different pH values, and efficiently decomposed gases such as ammonia, hydrogen sulfide, and acetic acid. Suggests a filter to remove.
しかしながら、特許文献１の技術において、さらに塩基性ガスの吸着能力を上げ、有効時間を長くするために、例えば、活性炭混紗紙に多くの酸を付着させて吸着能力を上げようとしても、基材が加水分解して強度が低下し使えないものしか得られないことから、フィルターの容積を大きくして吸着能力を上げる程度しか方法が考えられなかった。本発明では、フィルターの大きさを変えずに、従来よりもさらに吸着能力を増大させ、有効寿命が長く、塩基性ガスの消臭に特に効果を発揮する消臭フィルターの開発を行うものである。
本発明は多くの悪臭ガスのうち特にトイレ等に多く発生する、アンモニアガス等の塩基性ガスの消臭に極めて有効で、かつ消臭効果の持続するメンテナンスフリーの消臭フィルターを提供することを課題としている。 The present invention is to provide a maintenance-free deodorizing filter that is extremely effective for deodorizing basic gases such as ammonia gas that are generated frequently in toilets and the like among many offensive odor gases, and that maintains the deodorizing effect. It is an issue.
本発明は、塩基性ガスを効率よく吸着し、消臭効果の持続する消臭フィルターを提供すべく鋭意検討を行なった結果、活性炭混抄紙で構成したハニカム形状のフィルターを、リン酸緩衝溶液で処理することによって、塩基性ガスの消臭効果が飛躍的に持続する消臭フィルターを、安価に簡単に提供できることを見出し、本発明に至ったものである。前記課題を解決するために本発明は以下の手段を提供する。 As a result of intensive studies to provide a deodorizing filter that efficiently adsorbs basic gas and maintains the deodorizing effect, the present invention has developed a honeycomb-shaped filter composed of activated carbon mixed paper with a phosphate buffer solution. As a result of the treatment, the inventors have found that a deodorizing filter in which the deodorizing effect of the basic gas is dramatically maintained can be easily provided at low cost, and the present invention has been achieved. In order to solve the above problems, the present invention provides the following means.
［１］活性炭混抄紙からなる消臭フィルターであって、リン酸緩衝溶液にて処理し、ｐＨ値が１．２〜３．８の低いｐＨ環境を維持していることに特徴のある消臭フィルター。 [1] A deodorizing filter made of activated carbon mixed paper, which is characterized by being treated with a phosphate buffer solution and maintaining a low pH environment having a pH value of 1.2 to 3.8. filter.
［２］前記リン酸緩衝溶液は、リン酸１〜１０重量％と、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種を１〜１０重量％含む水溶液であることに特徴のある前項１に記載の消臭フィルター。 [2] The phosphate buffer solution contains 1 to 10% by weight of phosphoric acid and at least one selected from monosodium phosphate, disodium phosphate, monopotassium phosphate, and dipotassium phosphate. 2. The deodorizing filter according to item 1 above, characterized in that the aqueous solution contains 10% by weight.
［３］前記リン酸緩衝溶液にて処理した消臭フィルターにおいて、活性炭混抄紙１ｇに対し、リン酸２５〜２５０ｍｇと、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種を２５〜２５０ｍｇ固着していることに特徴のある前項１又は２に記載の消臭フィルター。
[3] In the deodorizing filter treated with the phosphate buffer solution, 25 to 250 mg of phosphoric acid, monosodium phosphate, disodium phosphate, monopotassium phosphate, dipotassium phosphate with respect to 1 g of the activated carbon mixed paper. 3. The deodorizing filter according to
［４］前記活性炭混抄紙は、活性炭を４０〜８０重量％担持させてなる活性炭混抄紙である前項１〜３のいずれかの項に記載の消臭フィルター。 [4] The deodorizing filter according to any one of items 1 to 3, wherein the activated carbon mixed paper is an activated carbon mixed paper having 40 to 80% by weight of activated carbon supported thereon.
第１の発明では、活性炭混抄紙からなる消臭フィルターは、リン酸緩衝溶液にて処理しているので、ｐＨ値が１．２〜３．８の低いｐＨ環境が維持され、アンモニアガスのような塩基性悪臭ガスを確実に活性炭に吸着し消臭する。吸着した塩基性悪臭ガスは、消臭フィルター周囲のｐＨ値を上げ吸着反応を遅らせてしまうのであるが、リン酸緩衝液で処理されているので、多少の酸や塩基が増えたりしても、リン酸緩衝液はｐＨ値の変動を防止する働きがあることから、消臭効果を長く持続することが可能となり、メンテナンスフリーの消臭フィルターとすることができる。 In the first invention, the deodorizing filter made of activated carbon mixed paper is treated with a phosphate buffer solution, so that a low pH environment having a pH value of 1.2 to 3.8 is maintained, and ammonia gas is used. The basic odor gas is surely adsorbed on activated carbon and deodorized. Adsorbed basic malodorous gas increases the pH value around the deodorizing filter and delays the adsorption reaction, but since it is treated with phosphate buffer, even if some acid or base increases, Since the phosphate buffer has a function of preventing the pH value from changing, the deodorizing effect can be maintained for a long time, and a maintenance-free deodorizing filter can be obtained.
第２の発明では、前記リン酸緩衝溶液は、リン酸１〜１０重量％と、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種を１〜１０重量％含む水溶液であるので、ｐＨ値を１．２〜３．８の低い環境に維持することができ、活性炭の強力な吸着力によって塩基性悪臭ガスが吸着される。リン酸が１重量％を下回ったり、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種が１重量％を下回ると、消臭フィルターを低いｐＨ環境に維持することができないので消臭効果が早くなくなってしまう。また、リン酸が１０重量％を上回ったり、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種が１０重量％を上回っても、経済的な消臭効果をえることにならない。 In the second invention, the phosphate buffer solution is 1 to 10% by weight of phosphoric acid and at least one selected from monosodium phosphate, disodium phosphate, monopotassium phosphate, and dipotassium phosphate. Therefore, the pH value can be maintained in a low environment of 1.2 to 3.8, and the basic malodorous gas is adsorbed by the strong adsorption power of the activated carbon. When phosphoric acid is less than 1% by weight, or at least one selected from monosodium phosphate, disodium phosphate, monopotassium phosphate, and dipotassium phosphate is less than 1% by weight, the deodorizing filter is removed. Since it cannot be maintained in a low pH environment, the deodorizing effect is quickly lost. Even if phosphoric acid exceeds 10% by weight or at least one selected from monosodium phosphate, disodium phosphate, monopotassium phosphate and dipotassium phosphate exceeds 10% by weight, It will not give a deodorizing effect.
第３の発明では、活性炭混抄紙１ｇに対し、リン酸２５〜２５０ｍｇと、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種を２５〜２５０ｍｇ固着しているので、低いｐＨ環境に維持することができ十分な吸着効果と持続力が得られる。リン酸が２５ｍｇを下回り、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種が２５ｍｇを下回る担持量では、低いＰＨ環境に維持することができず、塩基性ガスの十分な吸着量とならない。また、リン酸が２５０ｍｇを上回り、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種が２５０ｍｇを上回って担持させても、塩基性ガスの十分に大きな吸着量とはならず、耐久性も向上するわけではない。 In 3rd invention, 25 g of at least 1 sort (s) selected from 25-250 mg of phosphoric acid and monosodium phosphate, disodium phosphate, monopotassium phosphate, and dipotassium phosphate with respect to 1 g of activated carbon mixed paper. Since ˜250 mg is fixed, a low pH environment can be maintained, and a sufficient adsorption effect and sustainability can be obtained. When the amount of phosphoric acid is less than 25 mg and at least one selected from monosodium phosphate, disodium phosphate, monopotassium phosphate, and dipotassium phosphate is less than 25 mg, a low PH environment should be maintained. The basic gas cannot be adsorbed sufficiently. Further, even if phosphoric acid exceeds 250 mg and at least one selected from monosodium phosphate, disodium phosphate, monopotassium phosphate and dipotassium phosphate exceeds 250 mg, the basic gas However, the adsorption amount is not sufficiently large, and the durability is not improved.
第４の発明では、前記活性炭混抄紙は活性炭を４０〜８０重量％担持させてあるので十分な吸着効果が得られる。４０重量％を下回る活性炭の担持量では、塩基性ガスの十分な吸着量とならない。また、８０重量％を上回って活性炭を担持させても、十分に大きな吸着量とはならず、活性炭混抄紙の強度も得られず好ましくない。 In 4th invention, since the said activated carbon mixed paper carries 40-80 weight% of activated carbon, sufficient adsorption effect is acquired. If the amount of activated carbon supported is less than 40% by weight, the amount of basic gas adsorbed is not sufficient. Further, even if the activated carbon is supported above 80% by weight, the adsorbed amount is not sufficiently large, and the strength of the activated carbon mixed paper cannot be obtained, which is not preferable.
本発明の消臭フィルターについて、さらに詳しく説明する。本発明の消臭フィルターを構成する活性炭混抄紙は通常の湿式抄紙法により製造できる。例えば活性炭と天然パルプを水に添加し、水スラリーを作成する。そのスラリーを攪拌しながら所定の固形分濃度に調整し、その後カチオン系ポリマー又はアニオン系ポリマーを添加し、得られた凝集体水分散液を抄紙機を使い湿式抄紙法によりシート化し、乾燥処理を行ない活性炭混抄紙を得る。この活性炭混抄紙を、コルゲート加工機を用いハニカム形状に加工しフィルターの形状にする。 The deodorizing filter of the present invention will be described in more detail. The activated carbon mixed paper constituting the deodorizing filter of the present invention can be produced by a normal wet paper making method. For example, activated carbon and natural pulp are added to water to create a water slurry. The slurry is adjusted to a predetermined solid content concentration with stirring, and then a cationic polymer or an anionic polymer is added, and the resulting aggregate aqueous dispersion is formed into a sheet by a wet papermaking method using a paper machine, followed by a drying treatment. To obtain activated carbon mixed paper. This activated carbon mixed paper is processed into a honeycomb shape using a corrugating machine to obtain a filter shape.
この活性炭混抄紙によるハニカムフィルターは活性炭の強い吸着力によって悪臭ガスの吸着体の役割をなすものである。本発明に使用する活性炭としては、椰子殻活性炭、石油ピッチ系球状活性炭、活性炭素繊維、木質系活性炭等の活性炭系炭素多孔質体が、吸着比表面積が非常に高いことから好ましく用いられる。中でも、椰子殻活性炭が好ましい。活性炭混抄紙における活性炭の担持量は、４０〜８０重量％担持させるのが好ましく、４０重量％を下回る活性炭の担持量では、塩基性ガスの十分な吸着能力が得られない。また、８０重量％を上回って活性炭を担持させたとしても、活性炭混抄紙が脆くなりフィルター材としての強度が得られず好ましくない。 The honeycomb filter made of the activated carbon mixed paper serves as an adsorbent for malodorous gas due to the strong adsorption power of the activated carbon. As the activated carbon used in the present invention, activated carbon-based carbon porous bodies such as coconut shell activated carbon, petroleum pitch-based spherical activated carbon, activated carbon fiber, and wood-based activated carbon are preferably used because of their very high specific adsorption surface area. Of these, coconut shell activated carbon is preferable. The supported amount of activated carbon in the activated carbon mixed paper is preferably 40 to 80% by weight. If the amount of activated carbon is less than 40% by weight, sufficient adsorption ability of basic gas cannot be obtained. Further, even if the activated carbon is supported by more than 80% by weight, the activated carbon mixed paper becomes brittle and the strength as a filter material cannot be obtained, which is not preferable.
また、この活性炭混抄紙に使用する繊維は天然パルプ、ポリオレフィン及びアクリル繊維などのフィブリル化繊維を用いればよいが、消臭加工のし易さからも天然パルプが好ましい。 The fibers used in the activated carbon mixed paper may be fibrillated fibers such as natural pulp, polyolefin and acrylic fibers, but natural pulp is preferred from the viewpoint of ease of deodorization.
緩衝液は弱酸と、その塩を共存させた水溶液が一般的で、多少の酸や塩基が加えられたり、蒸発や希釈によって濃度が変化しても、ほとんどｐＨ値が変動しない作用をもつものである。本発明においては、弱酸としてリン酸、その塩としてリン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種を好適に用いる。リン酸は、不揮発性の多価無機酸で、ｐＨ値を１．２〜３．８の低いｐＨ値環境に維持し、特にアンモニアガスのような塩基性悪臭ガスを確実に活性炭に吸着し消臭する補助的な役割をなす。 The buffer solution is generally an aqueous solution in which a weak acid and its salt coexist, and even if some acid or base is added or the concentration changes due to evaporation or dilution, the pH value hardly changes. is there. In the present invention, at least one selected from phosphoric acid as a weak acid and monosodium phosphate, disodium phosphate, monopotassium phosphate, and dipotassium phosphate as a salt thereof is preferably used. Phosphoric acid is a non-volatile polyvalent inorganic acid and maintains a low pH value environment of 1.2 to 3.8. In particular, basic malodorous gas such as ammonia gas is reliably adsorbed on activated carbon and extinguished. It plays an auxiliary role to smell.
リン酸緩衝溶液は、リン酸１〜１０重量％と、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種を１〜１０重量％含む水溶液で、リン酸が１重量％を下回ったり、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種が１重量％を下回ると、緩衝液としての緩衝効果がなくなり、ｐＨ値の変動を防止する働きが弱くなってしまい、消臭効果を長く持続することができない。また、リン酸が１０重量％を上回ったり、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種が１０重量％を上回ると、活性炭混抄紙からリン酸緩衝溶液の脱離が生じるため好ましくない。 The phosphate buffer solution contains 1 to 10% by weight of phosphoric acid and 1 to 10% by weight of at least one selected from monosodium phosphate, disodium phosphate, monopotassium phosphate, and dipotassium phosphate. When the phosphoric acid is less than 1% by weight in an aqueous solution, or at least one selected from monosodium phosphate, disodium phosphate, monopotassium phosphate and dipotassium phosphate is less than 1% by weight, The buffering effect as a liquid is lost, the function of preventing fluctuations in pH value is weakened, and the deodorizing effect cannot be sustained for a long time. In addition, when phosphoric acid exceeds 10% by weight, or when at least one selected from monosodium phosphate, disodium phosphate, monopotassium phosphate and dipotassium phosphate exceeds 10% by weight, activated carbon is mixed. This is not preferable because the phosphate buffer solution is detached from the paper.
リン酸緩衝溶液のリン酸及びリン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種の活性炭混抄紙１ｇ当りの担持量は、リン酸２５〜２５０ｍｇ、リン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種２５〜２５０ｍｇとするのがよい。２５ｍｇを下回ると塩基性悪臭ガスを消臭する繰返し耐久性が低下するので好ましくない。２５０ｍｇを上回って担持すると、活性炭の細孔が塞がれてしまい吸着性能が低下することになり好ましくない。より好ましくは５０〜１５０ｍｇとするのがよい。 The amount of the phosphate buffer solution per gram of at least one activated carbon mixed paper selected from phosphoric acid and monosodium phosphate, disodium phosphate, monopotassium phosphate, dipotassium phosphate is 25 phosphoric acid. It is good to set it as 25-250 mg of at least 1 sort (s) chosen from -250 mg, monosodium phosphate, disodium phosphate, monopotassium phosphate, and dipotassium phosphate. If it is less than 25 mg, the repeated durability for deodorizing the basic malodorous gas is not preferable. If the amount exceeds 250 mg, the pores of the activated carbon are blocked and the adsorption performance is lowered, which is not preferable. More preferably, it is good to set it as 50-150 mg.
活性炭混抄紙にリン酸及びリン酸一ナトリウム、リン酸二ナトリウム、リン酸一カリウム、リン酸二カリウムの中から選択される少なくとも1種を担持さす方法は、リン酸緩衝溶液に、活性炭混抄紙を浸漬し乾燥すればよい。また、活性炭混抄紙の状態で浸漬し乾燥してもよいし、ハニカム形状に加工しフィルターの形状で浸漬し乾燥してもよい。 The method of supporting at least one selected from phosphoric acid and monosodium phosphate, disodium phosphate, monopotassium phosphate and dipotassium phosphate on the activated carbon mixed paper is as follows. May be dipped and dried. Further, it may be dipped in an activated carbon mixed paper and dried, or may be processed into a honeycomb shape and dipped in a filter shape and dried.
また、本発明の消臭フィルターにおいて、前記活性炭混抄紙にさらに他の消臭剤や臭気吸着剤や添加剤等を担持せしめた構成を採用しても良い。他の消臭剤としては例えば、金属フタロシアニン錯体、ヒドラジン誘導体やポリビニルアミン化合物を例示できる。また、臭気吸着剤としては、活性炭の他に、ゼオライト等の多孔質無機物質を例示できる。 Moreover, in the deodorizing filter of this invention, you may employ | adopt the structure which carry | supported other deodorizing agents, an odor adsorbent, an additive, etc. further on the said activated carbon mixed paper. Examples of other deodorants include metal phthalocyanine complexes, hydrazine derivatives, and polyvinylamine compounds. Examples of the odor adsorbent include porous inorganic materials such as zeolite in addition to activated carbon.
次ぎに実施例により、本発明を具体的に説明する。なお実施例におけるアンモニアガスの消臭性能の測定は次のように行った。
（アンモニアガス消臭性能）
消臭フィルターから切り出した円形試験片（直径５０ｍｍ厚さ２２．５ｍｍ）を、円筒管の中間位置に配置されたサンプルホルダーに固定し、円筒の一端から毎分１１．８リットル（面風速０．１ｍ／ｓｅｃ）の通気を行なうファンをセットした試験キットを用意し、試験キットの端から濃度が８０ｐｐｍのアンモニアガスを注入し、試験キットの他の端から出てくる空気を、検知管を使って採取し、その濃度を測定しアンモニアガスの除去率（％）を算出した。この試験を連続し３０分ごとに除去率（％）を測定し、消臭能力が０近くになるまで繰返して性能維持試験とした。
Next, the present invention will be described specifically by way of examples. In addition, the measurement of the deodorizing performance of ammonia gas in the examples was performed as follows.
(Ammonia gas deodorization performance)
A circular test piece (diameter: 50 mm, thickness: 22.5 mm) cut out from the deodorizing filter is fixed to a sample holder disposed at an intermediate position of the cylindrical tube, and 11.8 liters per minute (surface air velocity of 0. 1) from one end of the cylinder. Prepare a test kit with a fan that can ventilate 1m / sec), inject ammonia gas with a concentration of 80ppm from the end of the test kit, and use the detector tube to extract air from the other end of the test kit. The concentration was measured and the ammonia gas removal rate (%) was calculated. This test was continuously performed, and the removal rate (%) was measured every 30 minutes, and the test was repeated until the deodorizing ability was close to 0 to obtain a performance maintenance test.
＜実施例１＞
椰子殻活性炭７０重量部と天然パルプ３０重量部を水２００重量部に添加し、水スラリーを作成する。得られた凝集体水分散液を抄紙機を使い湿式抄紙法によりシート化し、乾燥処理を行ない活性炭混抄紙を得る。この時、活性炭混抄紙は、椰子殻活性炭を７０重量％担持させていた。次に、この活性炭混抄紙をコルゲート加工機を用いハニカム形状に加工しフィルターの形状にした。次にこのフィルターをリン酸５重量％と、リン酸一ナトリウム５重量％含む水溶液に浸漬し、乾燥してｐＨ値が２．０の低いｐＨ環境の消臭フィルターを作成た。この時リン酸の活性炭混抄紙１ｇ当りへの担持量は１３ｍｇで、リン酸一ナトリウムの活性炭混抄紙１ｇ当りへの担持量は１３ｍｇであった。上記のアンモニアガス消臭性能試験をおこないアンモニアガス除去率の変化を図１のグラフにして記載した。
<Example 1>
70 parts by weight of coconut shell activated carbon and 30 parts by weight of natural pulp are added to 200 parts by weight of water to prepare a water slurry. The obtained aggregate aqueous dispersion is formed into a sheet by a wet papermaking method using a paper machine and dried to obtain an activated carbon mixed paper. At this time, the activated carbon mixed paper supported 70% by weight of coconut shell activated carbon. Next, this activated carbon mixed paper was processed into a honeycomb shape using a corrugating machine to obtain a filter shape. Next, this filter was immersed in an aqueous solution containing 5% by weight of phosphoric acid and 5% by weight of monosodium phosphate and dried to prepare a deodorizing filter having a low pH value of 2.0. At this time, the carrying amount of phosphoric acid per 1 g of the activated carbon mixed paper was 13 mg, and the carrying amount of monosodium phosphate per 1 g of the activated carbon mixed paper was 13 mg. The above-mentioned ammonia gas deodorization performance test was conducted, and the change in the ammonia gas removal rate was shown in the graph of FIG.
＜実施例２＞
次に、実施例１において、リン酸５重量％と、リン酸二ナトリウム５重量％含む水溶液に浸漬した以外は実施例１と同様にして、消臭フィルターを得た。なお、この時のｐＨ値が３．１で、リン酸の活性炭混抄紙１ｇ当りへの担持量は１３ｍｇであった。また、リン酸二ナトリウムの活性炭混抄紙１ｇ当りへの担持量は１３ｍｇであった。上記のアンモニアガス消臭性能試験をおこないアンモニアガス除去率の変化を図１のグラフにして記載した。
<Example 2>
Next, a deodorizing filter was obtained in the same manner as in Example 1 except that it was immersed in an aqueous solution containing 5% by weight of phosphoric acid and 5% by weight of disodium phosphate. The pH value at this time was 3.1, and the supported amount of phosphoric acid per gram of activated carbon mixed paper was 13 mg. The amount of disodium phosphate supported on 1 g of the activated carbon mixed paper was 13 mg. The above-mentioned ammonia gas deodorization performance test was conducted, and the change in the ammonia gas removal rate was shown in the graph of FIG.
＜比較例１＞
次に、実施例１において、リン酸５重量％と、リン酸三ナトリウム５重量％含む水溶液に浸漬した以外は実施例１と同様にして、ｐＨ値が２．６の低いｐＨ値環境の消臭フィルターを得た。なお、この時のリン酸の活性炭混抄紙１ｇ当りへの担持量は１３ｍｇであった。また、リン酸三ナトリウムの活性炭混抄紙１ｇ当りへの担持量は１３ｍｇであった。上記のアンモニアガス消臭性能試験をおこないアンモニアガス除去率の変化をグラフにして記載した。
<Comparative Example 1>
Next, in Example 1, except for immersion in an aqueous solution containing 5% by weight of phosphoric acid and 5% by weight of trisodium phosphate, the low pH value environment having a pH value of 2.6 was eliminated in the same manner as in Example 1. An odor filter was obtained. At this time, the supported amount of phosphoric acid per 1 g of the activated carbon mixed paper was 13 mg. The amount of trisodium phosphate supported on 1 g of the activated carbon mixed paper was 13 mg. The above ammonia gas deodorization performance test was conducted and the change of the ammonia gas removal rate was described as a graph.
＜実施例３＞
次に、実施例１において、椰子殻活性炭３０重量部とした以外は実施例１と同様にして、消臭フィルターを得た。上記のアンモニアガス消臭性能試験をおこなったところ、実施例１には及ばないが良好な消臭性能が得られた。
<Example 3>
Next, a deodorizing filter was obtained in the same manner as in Example 1 except that 30 parts by weight of coconut shell activated carbon was used. When the above ammonia gas deodorization performance test was performed, good deodorization performance was obtained although it did not reach Example 1.
＜実施例４＞
次に、実施例１において、リン酸８重量％と、リン酸一ナトリウム９重量％含む水溶液に浸漬し、乾燥してｐＨ値が１．９の低いｐＨ環境の消臭フィルターを作成した以外は実施例１と同様にして、消臭フィルターを得た。この時のリン酸の活性炭混抄紙１ｇ当りへの担持量は２０ｍｇであった。また、リン酸一ナトリウムの活性炭混抄紙１ｇ当りへの担持量は２３ｍｇであった。グラフにはしていないが実施例１と同様にアンモニアガス除去性能を長く維持した消臭フィルターとすることができた。
<Example 4>
Next, in Example 1, a deodorizing filter having a low pH value of 1.9 was prepared by immersing in an aqueous solution containing 8% by weight of phosphoric acid and 9% by weight of monosodium phosphate and drying. A deodorizing filter was obtained in the same manner as in Example 1. At this time, the amount of phosphoric acid supported on 1 g of the activated carbon mixed paper was 20 mg. The amount of monosodium phosphate supported on 1 g of the activated carbon mixed paper was 23 mg. Although not shown in the graph, a deodorizing filter having a long ammonia gas removal performance as in Example 1 was obtained.
＜実施例５＞
次に、実施例１において、リン酸５重量％と、リン酸二カリウム５重量％含む水溶液に浸漬した以外は実施例１と同様にして、消臭フィルターを得た。なお、この時のｐＨ値が３．１で、リン酸の活性炭混抄紙１ｇ当りへの担持量は１３ｍｇであった。また、リン酸二カリウムの活性炭混抄紙１ｇ当りへの担持量は１３ｍｇであった。上記のアンモニアガス消臭性能試験をおこなったが、実施例１とほぼ同じアンモニアガス除去率であった。
<Example 5>
Next, a deodorizing filter was obtained in the same manner as in Example 1 except that it was immersed in an aqueous solution containing 5% by weight of phosphoric acid and 5% by weight of dipotassium phosphate. The pH value at this time was 3.1, and the supported amount of phosphoric acid per gram of activated carbon mixed paper was 13 mg. The amount of dipotassium phosphate supported on 1 g of the activated carbon mixed paper was 13 mg. The above ammonia gas deodorization performance test was conducted, and the ammonia gas removal rate was almost the same as in Example 1.
＜比較例２＞
実施例１において、リン酸のみ５重量％含む水溶液に浸漬した以外は実施例１と同様にして、消臭フィルターを得た。なお、この時のｐＨ値が１．４で、リン酸の活性炭混抄紙１ｇ当りへの担持量は１３ｍｇであった。上記のアンモニアガス消臭性能試験をおこないアンモニアガス除去率の変化をグラフにして記載したが、アンモニアガス除去性能を長く維持できなかった。
<Comparative example 2>
In Example 1, a deodorizing filter was obtained in the same manner as in Example 1 except that it was immersed in an aqueous solution containing only 5% by weight of phosphoric acid. The pH value at this time was 1.4, and the amount of phosphoric acid supported on 1 g of the activated carbon mixed paper was 13 mg. The above ammonia gas deodorization performance test was conducted and the change of the ammonia gas removal rate was described as a graph, but the ammonia gas removal performance could not be maintained for a long time.
＜比較例３＞
椰子殻活性炭を１０重量部とした以外は実施例１と同様にして、消臭フィルターを得た。この時、活性炭混抄紙は、椰子殻活性炭を２５重量％担持させていた。上記のアンモニアガス消臭性能試験をおこなったがアンモニアガス除去能力のかなり低い消臭フィルターであった。
<Comparative Example 3>
A deodorizing filter was obtained in the same manner as in Example 1 except that 10 parts by weight of coconut shell activated carbon was used. At this time, the activated carbon mixed paper supported 25% by weight of coconut shell activated carbon. The ammonia gas deodorizing performance test was performed, but the deodorizing filter had a considerably low ammonia gas removing ability.
＜比較例４＞
実施例１において、フィルターをリン酸５重量％と、リン酸一ナトリウム５重量％含む水溶液に浸漬しないでそのまま消臭フィルターとした。ｐＨ値は７．５であった。上記のアンモニアガス消臭性能試験をおこなったがアンモニアガス除去能力の持続性のない消臭フィルターであった。
<Comparative example 4>
In Example 1, the filter was used as it was without being immersed in an aqueous solution containing 5% by weight of phosphoric acid and 5% by weight of monosodium phosphate. The pH value was 7.5. The ammonia gas deodorizing performance test was performed, but the deodorizing filter had no sustainability for removing ammonia gas.
本発明の技術は、冷蔵庫内、トイレ等の不快な臭いを取り除く消臭フィルター材として開発したが、特にアンモニア等の塩基性ガスを効率的に吸着し、その効果の持続性を飛躍的に向上したことから、塩基性ガスが大量に発生する設備の消臭フィルターとして広く利用される。 The technology of the present invention was developed as a deodorizing filter material that removes unpleasant odors in refrigerators, toilets, etc. Especially, it effectively adsorbs basic gases such as ammonia and dramatically improves the sustainability of its effects. Therefore, it is widely used as a deodorizing filter for equipment that generates a large amount of basic gas.
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| JPS5695334A (en) * | 1979-12-28 | 1981-08-01 | Takeda Chem Ind Ltd | Regeneration method of active carbon carrying phosphorus compound |
| JPH06181972A (en) * | 1992-12-18 | 1994-07-05 | Kanebo Ltd | Deodorant for cigarette smell |
| JP2007229092A (en) * | 2006-02-28 | 2007-09-13 | Suminoe Textile Co Ltd | Cigarette smoke deodorizing filter |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| JPS5695334A (en) * | 1979-12-28 | 1981-08-01 | Takeda Chem Ind Ltd | Regeneration method of active carbon carrying phosphorus compound |
| JPH06181972A (en) * | 1992-12-18 | 1994-07-05 | Kanebo Ltd | Deodorant for cigarette smell |
| JP2007229092A (en) * | 2006-02-28 | 2007-09-13 | Suminoe Textile Co Ltd | Cigarette smoke deodorizing filter |
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| CN110711605A (en) * | 2019-10-13 | 2020-01-21 | 西安凯立新材料股份有限公司 | Active carbon carrier treatment method, preparation method and application of palladium-carbon catalyst |
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