WO2016036022A1 - Composition for removing harmful gas, preparing method therefor, filter, and air conditioner comprising same - Google Patents

Composition for removing harmful gas, preparing method therefor, filter, and air conditioner comprising same Download PDF

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Publication number
WO2016036022A1
WO2016036022A1 PCT/KR2015/008565 KR2015008565W WO2016036022A1 WO 2016036022 A1 WO2016036022 A1 WO 2016036022A1 KR 2015008565 W KR2015008565 W KR 2015008565W WO 2016036022 A1 WO2016036022 A1 WO 2016036022A1
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weight
parts
composition
filter
mixed solution
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PCT/KR2015/008565
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French (fr)
Korean (ko)
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오원석
박형호
채상열
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주식회사 엘지전자
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption

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  • the present invention relates to a composition for removing noxious gas, a manufacturing method thereof, a filter device and an air conditioner including the same.
  • Airtightening of structures to save energy in buildings is a cause of indoor air pollution. And contaminated indoor air becomes a causative agent of various diseases, which negatively affects the health of residents.
  • pollutants generated indoors may be classified into particulate pollutants such as fine dust and asbestos, gaseous pollutants such as carbon dioxide, formaldehyde, and volatile organic compounds, and biological pollutants such as viruses and fungi.
  • particulate pollutants such as fine dust and asbestos
  • gaseous pollutants such as carbon dioxide, formaldehyde, and volatile organic compounds
  • biological pollutants such as viruses and fungi.
  • Such contaminants may be removed to some extent by filters provided in the process cleaner, the air conditioner and the total heat exchanger.
  • Such a filter has a high removal efficiency of particulate contaminants and biological contaminants, but removes gaseous materials but has a low removal efficiency.
  • the present invention has been made to solve the above problems, and an object of the present invention is to provide a composition for removing harmful gases capable of removing contaminants in the air, a manufacturing method thereof, a filter, and an air conditioner including the same.
  • the acidic material containing the amine group includes para-aminobenzoic acid or sulfanilic acid.
  • the residual amount of solvent contains water (H 2 O).
  • the water has a 70 to 90 parts by weight.
  • the platinum (Pt) is characterized in that it is prepared by reducing hexachloro platinum acid (hydrogen hexachloroplatinate (IV)) to polyvinyl alcohol (Polyvinyl alcohol) and Propolis Extract (Propolis Extract).
  • a method for preparing a noxious gas removal composition comprising: mixing 70 to 90 parts by weight of water and 2 to 10 parts by weight of an acidic material including an amine group (-NH 2 ) to form a first mixed solution; Heating and stirring the first mixed solution to form a second mixed solution; Forming a third mixed solution by mixing 5 to 20 parts by weight of phosphoric acid (H 3 PO 4 ) and 0.001 to 0.005 parts by weight of platinum (Pt) to the second mixed solution; And stirring the third mixed solution.
  • step of heating and stirring the first mixed solution the step of heating and stirring the first mixed solution at 500rpm for 2 hours at 50 to 70 °C.
  • the stirring of the third mixed solution may include stirring the third mixed solution at 500 rpm for 3 hours at 15 to 25 ° C.
  • the filter member A harmful gas removal composition adhering to the filter member, wherein the harmful gas removal composition, 2 to 10 parts by weight of an acidic material containing an amine group (-NH 2 ) and phosphoric acid (H 3 PO 4 ) 5 To 20 parts by weight, platinum (Pt) of 0.001 to 0.005 parts by weight and the remaining amount of the solvent is included.
  • an acidic material containing an amine group (-NH 2 ) and phosphoric acid (H 3 PO 4 ) 5 To 20 parts by weight, platinum (Pt) of 0.001 to 0.005 parts by weight and the remaining amount of the solvent is included.
  • the acidic material containing the amine group includes para-aminobenzoic acid or sulfanilic acid.
  • the residual amount of solvent contains water (H 2 O).
  • the water has a 70 to 90 parts by weight.
  • the filter member may further include a first filter member formed in a flat plate shape; A second filter member formed in a wave shape; And an air passage formed between the first filter member and the second filter member, wherein the first filter member and the second filter member are stacked alternately with each other.
  • the material of the first filter member or the second filter member is characterized in that made of polypropylene.
  • an air conditioner includes a case; An air filtration unit mounted to the case and to which a composition for removing harmful gas is adhered; An air flow unit for flowing air to the air filtration unit; And a heat exchanger for cooling or heating the air filtered by the air filtration unit, wherein the harmful gas removing composition includes 2 to 10 parts by weight of an acidic material including an amine group (-NH 2 ), and phosphoric acid (H 3). PO 4 ) 5 to 20 parts by weight, and 0.001 to 0.005 parts by weight of platinum (Pt) and a residual amount of solvent.
  • an acidic material including an amine group (-NH 2 ), and phosphoric acid (H 3).
  • composition for removing harmful gases According to the composition for removing harmful gases according to the present invention, a manufacturing method, a filter, and an air conditioner including the same, gaseous contaminants such as formaldehyde, ammonia, benzene, toluene, sulfur dioxide, and nitrogen dioxide can be effectively removed.
  • gaseous contaminants such as formaldehyde, ammonia, benzene, toluene, sulfur dioxide, and nitrogen dioxide
  • FIG. 1 is a perspective view of an air conditioner according to an embodiment of the present invention.
  • FIG. 2 is a perspective view of the front door of the air conditioner of FIG. 1 opened.
  • FIG. 2 is a perspective view of the front door of the air conditioner of FIG. 1 opened.
  • FIG. 3 is a front view of a filter mounted on the side filter part, the bottom filter part and the internal filter part of the air conditioner of FIG. 1.
  • FIG. 4 is a cross-sectional view of the filter of FIG. 3.
  • FIG. 1 is a perspective view of an air conditioner according to an embodiment of the present invention
  • Figure 2 is a perspective view of the front door of the air conditioner of Figure 1 is open.
  • the air conditioner 10 rotates by forming a space therein so that a plurality of components can be built therein, forming a case 11 forming an external shape, and a front appearance of the case 11.
  • the front door 12 may be mounted on the case 11, and the operation part 13 mounted on the front surface of the front door 12 may be included.
  • the case 11 includes a first frame 111 on which the front door 12 is mounted, and a second frame 112 mounted on the rear of the first frame 111.
  • Side discharge vanes 21 are mounted at air discharge ports formed at both upper sides of the first frame 111
  • side suction vanes 22 are mounted at air suction ports formed at both lower sides of the first frame 111.
  • an upper surface discharge vane 23 is mounted at an air discharge port formed at an upper side of the first frame 111, and an air suction port 111a is formed at a lower side of the first frame 111.
  • the air conditioner 10 sucks air into the side suction vanes 22 and the air suction ports 111a, and discharges air to the side discharge vanes 21 and the top discharge vanes 23. It may include a flow portion (not shown).
  • the air conditioner 10 may include a heat exchanger (not shown) installed inside the case 11 and exchanging heat with air flowing into the case 11 and a refrigerant.
  • a heat exchanger (not shown) installed inside the case 11 and exchanging heat with air flowing into the case 11 and a refrigerant.
  • a side filter part 31 may be mounted inside the first frame 111 to purify the air flowing into the air intake ports formed at both lower sides of the first frame 111. .
  • a lower surface filter unit 32 may be mounted in the first frame 111 to purify the air flowing into the air inlet 111a formed at the lower side of the first frame 111.
  • an internal filter unit 33 may be further installed inside the first frame 111 to filter the air filtered by the side filter unit 31 and the bottom filter unit 32 once more.
  • the side filter part 31, the bottom filter part 32, and the internal filter part 33 may be referred to as air filter parts in that they filter air introduced into the case 11.
  • FIG. 3 is a front view of a filter mounted on the side filter part, the bottom filter part and the internal filter part of the air conditioner of FIG. 1, and
  • FIG. 4 is a cross-sectional view of the filter of FIG. 3.
  • a filter 40 is included in the side filter part 31, the bottom filter part 32, or the internal filter part 33.
  • the filter 40 may include a first filter member 41 and a second filter member 42.
  • the first filter member 41 is formed in a flat plate shape, and the second filter member 42 is formed in a wave shape or a sand shape.
  • the first filter member 41 and the second filter member 42 are stacked alternately with each other.
  • the filter 40 may further include a composition 50 for removing harmful gas adhered to the surfaces of the first filter member 41 and the second filter member 42.
  • the first filter member 41 and the second filter member 42 may be referred to as carriers in that the harmful gas removing composition 50 is adhered.
  • the harmful gas removing composition 50 may be adhered by spraying or dipping the surfaces of the first filter member 41 and the second filter member 42.
  • the material of the first filter member 41 and the second filter member 42 may be formed of a material to which the harmful gas removing composition 50 is adhered, for example, a polypropylene material.
  • the filter 40 may remove particulate contaminants such as asbestos and biological contaminants such as viruses and fungal bacteria from the air, and the carbon dioxide, formaldehyde, It can also remove gaseous contaminants such as volatile organic compounds.
  • the harmful gas removal composition is 2 to 10 parts by weight of the acidic material containing an amine group (-NH 2 ), 5 to 20 parts by weight of phosphoric acid (H 3 PO 4 ), 0.001 to 0.005 parts by weight of platinum (Pt) and Residual amount of solvent.
  • the remaining amount of the solvent may include 70 to 90 parts by weight of water (H 2 O).
  • Acidic substances containing the amine group include para-aminobenzoic acid or sulfanilic acid.
  • the paraaminobenzoic acid has an amine group (-NH 2 ) and a carboxyl group (-COOH) bonded to the benzene ring, and thus may react chemically with an acidic or basic substance.
  • high volatile lower aldehydes such as formaldehyde and acetaldehyde may be more effectively removed through the imine formation reaction of Formula 1 below.
  • the removal efficiency of high volatile lower aldehydes such as when the paraaminobenzoic acid or sulfanic acid is less than 2 parts by weight in the harmful gas removal composition.
  • the efficiency of removing harmful substances may be deteriorated due to a decrease in specific surface area of the carrier, that is, a reduction in surface area per unit volume.
  • the paraaminobenzoic acid or sulfanic acid in the composition for removing harmful gases is preferably added in the range of 2 to 10 parts by weight.
  • the phosphoric acid can remove ammonia.
  • ammonia removal efficiency is lowered.
  • the phosphoric acid in the composition for removing harmful gases exceeds 20 parts by weight, the removal efficiency of harmful substances is reduced due to the reduction of the specific surface area of the carrier for adsorption. Therefore, the phosphoric acid in the harmful gas removal composition is preferably 5 to 20 parts by weight.
  • the platinum (Pt) serves as a catalyst for effectively reacting lower aldehydes such as formaldehyde and acetaldehyde with amine groups.
  • the platinum may be prepared by reducing hexachloro platinum acid (hydrogen hexachloroplatinate (IV)) with polyvinyl alcohol and Propolis Extract.
  • the platinum acts as a reaction catalyst for hydrogenation (protonation) of the aldehyde, it is possible to increase the lower aldehyde removal efficiency, such as formaldehyde and acetaldehyde.
  • the platinum is preferably added to 0.001 to 0.005 parts by weight to the harmful gas removal composition.
  • the platinum is less than 0.001 parts by weight in the noxious gas removal composition, the catalytic reaction is difficult to be performed smoothly, and when the platinum is more than 0.005 parts by weight in the noxious gas removal composition, the cost-effectiveness is lowered.
  • a mixed solution of 80 parts by weight of water and 5 parts by weight of paraaminobenzoic acid was heated and stirred at 500 rpm for 2 hours using a magnetic stirrer to obtain a temperature of 60 ° C. After 30 minutes of further stirring until the mixed solution reached 25 ° C., 10 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
  • the mixed solution mixed with water and the acidic substance is called the first mixed solution
  • the mixed solution formed after heating and stirring the first mixed solution is called the second mixed solution.
  • the mixed solution formed by mixing phosphoric acid (H 3 PO 4 ) and platinum (Pt) in the second mixed solution is referred to as a third mixed solution.
  • the definition of such a mixed solution can be equally applied to the following examples.
  • the mixed solution of 80 parts by weight of water and 5 parts by weight of sulfanic acid was heated and stirred for 2 hours at a temperature of 60 ° C. at 500 rpm using a magnetic stirrer. After 30 minutes of further stirring until the mixed solution reached 25 ° C., 10 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
  • the mixed solution in which 80 parts by weight of water and 5 parts by weight of paraaminobenzoic acid was mixed was heated and stirred for 2 hours so that the temperature was 60 ° C. while stirring at 500 rpm using a magnetic stirrer.
  • the mixed solution was further stirred for 30 minutes until the room temperature to 25 °C, 10 parts by weight of phosphoric acid was added and stirred for 3 hours at 500 rpm at room temperature to prepare a composition for removing harmful gases.
  • the mixed solution in which 80 parts by weight of water and 1 part by weight of paraaminobenzoic acid was mixed was heated and stirred for 2 hours so that the temperature was 60 ° C. while stirring at 500 rpm using a magnetic stirrer.
  • the mixed solution was further stirred for 30 minutes until the temperature reaches 25 ° C, and then 10 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added thereto, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
  • the mixed solution in which 80 parts by weight of water and 15 parts by weight of paraaminobenzoic acid was mixed was heated and stirred for 2 hours so that the temperature was 60 ° C. while stirring at 500 rpm using a magnetic stirrer.
  • the mixed solution was further stirred for 30 minutes until the temperature reaches 25 ° C, and then 10 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added thereto, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
  • the mixed solution in which 80 parts by weight of water and 15 parts by weight of paraaminobenzoic acid was mixed was heated and stirred for 2 hours so that the temperature was 60 ° C. while stirring at 500 rpm using a magnetic stirrer.
  • the mixed solution was further stirred for 30 minutes until the temperature reaches 25 ° C., and then 2 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added and stirred at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
  • a mixed solution of 80 parts by weight of water and 5 parts by weight of paraaminobenzoic acid was heated and stirred at 500 rpm for 2 hours using a magnetic stirrer to obtain a temperature of 60 ° C. After 30 minutes of further stirring until the mixed solution reached 25 ° C., 25 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
  • Test chamber size 4m 3 8m 3 30m 3 Test gas concentration 10.0 ( ⁇ 10%) ppm 10.0 ( ⁇ 10%) ppm 10.0 ( ⁇ 10%) ppm Specimen Filter Size 340mm x 360mm x 10mm 340mm x 360mm x 10mm 340mm x 360mm x 10mm Test Conditions 5CMM 5CMM 5CMM Test run time 30 minutes 30 minutes 30 minutes 30 minutes 30 minutes
  • the size of the test chamber refers to the volume (m 3 ) of the space filled with the test gas
  • the test conditions are the air flow per minute (CMM, Cubic Meter per Minutes) of the air flowing to the test filter
  • the test body operating time is the test gas Means the time when the filter is filtered.
  • the filter coated with the harmful gas removal composition of Comparative Example 1 has a formaldehyde removal efficiency of 35 to 47.5% level, and the filter coated with the harmful gas removal composition of Example 1 or Example 2 Formaldehyde removal efficiency was lower than 95-99%.
  • the filter coated with the composition for removing harmful gases of Comparative Example 2 had a very low formaldehyde removal efficiency of 5 to 10%.
  • the filter coated with the harmful gas removal composition of Comparative Example 3 had a lower removal efficiency for benzene, toluene, nitrogen dioxide, and sulfur dioxide than Example 1 or Example 2.
  • the high content of paraaminobenzoic acid is believed to be due to a significant decrease in the specific surface area of the filter.
  • the filter coated with the composition for removing harmful gas was inferior in efficiency of removing benzene, toluene, sulfur dioxide, and nitrogen dioxide except formaldehyde due to high phosphoric acid content.

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  • Engineering & Computer Science (AREA)
  • Analytical Chemistry (AREA)
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  • Oil, Petroleum & Natural Gas (AREA)
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Abstract

The present invention relates to a composition for removing a harmful gas, a preparing method therefor, a filter apparatus, and an air conditioner comprising the same. The composition for removing a harmful gas according to an embodiment of the present invention contains 2-10 parts by weight of an acidic material comprising an amine (-NH2) group, 5-20 parts by weight of phosphoric acid (H3PO4), 0.001-0.005 parts by weight of platinum (Pt), and the balance solvent.

Description

유해가스 제거용 조성물, 그 제조 방법, 필터 및 이를 포함하는 공기 조화기Composition for removing noxious gas, preparation method thereof, filter and air conditioner including same
본 발명은, 유해가스 제거용 조성물, 그 제조 방법, 필터장치 및 이를 포함하는 공기 조화기에 관한 것이다. The present invention relates to a composition for removing noxious gas, a manufacturing method thereof, a filter device and an air conditioner including the same.
건물의 에너지 절감을 위한 구조물의 기밀화 등는 실내공기 오염의 한 원인이 된다. 그리고 오염된 실내공기는 각종 질병의 원인물질이 되어, 거주자의 건강에 부정적인 영향을 미친다.Airtightening of structures to save energy in buildings is a cause of indoor air pollution. And contaminated indoor air becomes a causative agent of various diseases, which negatively affects the health of residents.
한편, 실내에서 생성되는 오염물질은 미세먼지, 석면 등과 같은 입자상 오염 물질과 이산화탄소, 포름알데히드, 휘발성 유기화합물 등과 같은 가스상 오염물질과 바이러스, 곰팡이 박테리아 등의 생물학적 오염물질로 구분될 수 있다.Meanwhile, pollutants generated indoors may be classified into particulate pollutants such as fine dust and asbestos, gaseous pollutants such as carbon dioxide, formaldehyde, and volatile organic compounds, and biological pollutants such as viruses and fungi.
이러한 오염물질은, 공정청정기, 공기 조화기 및 전열교환기 등에 구비된 필터에 의해 어느 정도 제거될 수 있다.Such contaminants may be removed to some extent by filters provided in the process cleaner, the air conditioner and the total heat exchanger.
그러나 이러한 필터는, 입자상 오염 물질과 생물학적 오염물질의 제거 효율은 높은 편이었으나, 가스상 물질이 제거되나 제거효율이 낮다는 문제점이 있다.However, such a filter has a high removal efficiency of particulate contaminants and biological contaminants, but removes gaseous materials but has a low removal efficiency.
한편, 본 발명의 배경이 되는 기술은 대한민국 공개특허 제10-2006-0129593호 개시된다.On the other hand, the background art of the present invention is disclosed in Republic of Korea Patent Publication No. 10-2006-0129593.
본 발명은 상기와 같은 문제점을 해결하기 위해 창출된 것으로, 공기 중 오염물질을 제거할 수 있는 유해가스 제거용 조성물, 그 제조 방법, 필터 및 이를 포함하는 공기 조화기의 제공을 목적으로 한다.The present invention has been made to solve the above problems, and an object of the present invention is to provide a composition for removing harmful gases capable of removing contaminants in the air, a manufacturing method thereof, a filter, and an air conditioner including the same.
본 발명의 실시예에 따른 유해가스 제거용 조성물에는, 아민기(-NH2)를 포함하는 산성물질 2 내지 10 중량부와, 인산(H3PO4) 5 내지 20중량부와, 백금(Pt) 0.001 내지 0.005중량부 및 잔량의 용매를 포함한다.In the harmful gas removal composition according to an embodiment of the present invention, 2 to 10 parts by weight of an acidic substance containing an amine group (-NH 2 ), 5 to 20 parts by weight of phosphoric acid (H 3 PO 4 ), and platinum (Pt ) 0.001 to 0.005 parts by weight and the balance of the solvent.
또한, 상기 아민기를 포함하는 산성물질에는, 파라아미노벤조산(para-aminobenzoic acid) 또는 술파닐산(sulfanilic acid)이 포함된다.In addition, the acidic material containing the amine group includes para-aminobenzoic acid or sulfanilic acid.
또한, 상기 잔량의 용매에는, 물(H2O)이 포함된다.In addition, the residual amount of solvent contains water (H 2 O).
또한, 상기 물은 70 내지 90중량부를 가진다.In addition, the water has a 70 to 90 parts by weight.
또한, 상기 백금(Pt)은, 헥사클로로 백금산(hydrogen hexachloroplatinate(Ⅳ))을 폴리비닐알코올(Polyvinyl alcohol) 및 프로폴리스 추출물(Propolis Extract)로 환원시켜 제조되는 것을 특징으로 한다.In addition, the platinum (Pt) is characterized in that it is prepared by reducing hexachloro platinum acid (hydrogen hexachloroplatinate (IV)) to polyvinyl alcohol (Polyvinyl alcohol) and Propolis Extract (Propolis Extract).
다른 측면에 따른 유해가스 제거용 조성물 제조 방법에는, 물 70 내지 90중량부와 아민기(-NH2)를 포함하는 산성물질 2 내지 10 중량부를 혼합하여 제 1 혼합용액을 형성하는 단계; 상기 제 1 혼합용액을 가열 교반하여 제 2 혼합용액을 형성하는 단계; 상기 제 2 혼합용액에 인산(H3PO4) 5 내지 20중량부와 백금(Pt) 0.001 내지 0.005중량부를 혼합하여 제 3 혼합용액을 형성하는 단계; 및 상기 제 3 혼합용액을 교반하는 단계가 포함된다.According to another aspect of the present invention, there is provided a method for preparing a noxious gas removal composition, the method comprising: mixing 70 to 90 parts by weight of water and 2 to 10 parts by weight of an acidic material including an amine group (-NH 2 ) to form a first mixed solution; Heating and stirring the first mixed solution to form a second mixed solution; Forming a third mixed solution by mixing 5 to 20 parts by weight of phosphoric acid (H 3 PO 4 ) and 0.001 to 0.005 parts by weight of platinum (Pt) to the second mixed solution; And stirring the third mixed solution.
또한, 상기 제 1 혼합용액을 가열 교반하는 단계에는, 상기 제 1 혼합용액을 50 내지 70℃에서 2시간 동안 500rpm으로 가열 교반하는 단계가 포함된다.In addition, the step of heating and stirring the first mixed solution, the step of heating and stirring the first mixed solution at 500rpm for 2 hours at 50 to 70 ℃.
또한, 상기 제 3 혼합용액을 교반하는 단계에는, 상기 제 3 혼합용액을 15 내지 25℃에서 3시간 동안 500rpm으로 교반하는 단계가 포함된다.The stirring of the third mixed solution may include stirring the third mixed solution at 500 rpm for 3 hours at 15 to 25 ° C.
또 다른 측면에 따른 필터에는, 필터부재; 상기 필터부재에 점착되는 유해가스 제거용 조성물을 포함하고, 상기 유해가스 제거용 조성물은, 아민기(-NH2)를 포함하는 산성물질 2 내지 10 중량부와, 인산(H3PO4) 5 내지 20중량부와, 백금(Pt) 0.001 내지 0.005중량부 및 잔량의 용매가 포함된다.Filter according to another aspect, the filter member; A harmful gas removal composition adhering to the filter member, wherein the harmful gas removal composition, 2 to 10 parts by weight of an acidic material containing an amine group (-NH 2 ) and phosphoric acid (H 3 PO 4 ) 5 To 20 parts by weight, platinum (Pt) of 0.001 to 0.005 parts by weight and the remaining amount of the solvent is included.
또한, 상기 아민기를 포함하는 산성물질에는, 파라아미노벤조산(para-aminobenzoic acid) 또는 술파닐산(sulfanilic acid)이 포함된다.In addition, the acidic material containing the amine group includes para-aminobenzoic acid or sulfanilic acid.
또한, 상기 잔량의 용매에는, 물(H2O)이 포함된다.In addition, the residual amount of solvent contains water (H 2 O).
또한, 상기 물은 70 내지 90중량부를 가진다.In addition, the water has a 70 to 90 parts by weight.
또한, 상기 필터부재에는, 평판 형상으로 형성된 제 1 필터부재; 물결 형상으로 형성된 제 2 필터부재; 및 상기 제 1 필터부재와 제 2 필터부재의 사이에 형성되는 공기 통로가 포함되며, 상기 제 1 필터부재와 상기 제 2 필터부재는 서로 교호되도록 적층되는 것을 특징으로 한다.The filter member may further include a first filter member formed in a flat plate shape; A second filter member formed in a wave shape; And an air passage formed between the first filter member and the second filter member, wherein the first filter member and the second filter member are stacked alternately with each other.
또한, 상기 제 1 필터부재 또는 상기 제 2 필터부재의 재질은 폴리 프로필렌으로 이루어지는 것을 특징으로 한다.In addition, the material of the first filter member or the second filter member is characterized in that made of polypropylene.
또 다른 측면에 따른 공기 조화기에는, 케이스; 상기 케이스에 장착되며 유해가스 제거용 조성물이 점착된 공기 여과부; 상기 공기 여과부에 공기를 유동시키는 공기 유동부; 및 상기 공기 여과부에서 여과된 공기를 냉각 또는 가열하는 열교환기를 포함하고, 상기 유해가스 제거용 조성물은, 아민기(-NH2)를 포함하는 산성물질 2 내지 10 중량부와, 인산(H3PO4) 5 내지 20중량부와, 백금(Pt) 0.001 내지 0.005중량부 및잔량의 용매가 포함된다.According to yet another aspect, an air conditioner includes a case; An air filtration unit mounted to the case and to which a composition for removing harmful gas is adhered; An air flow unit for flowing air to the air filtration unit; And a heat exchanger for cooling or heating the air filtered by the air filtration unit, wherein the harmful gas removing composition includes 2 to 10 parts by weight of an acidic material including an amine group (-NH 2 ), and phosphoric acid (H 3). PO 4 ) 5 to 20 parts by weight, and 0.001 to 0.005 parts by weight of platinum (Pt) and a residual amount of solvent.
본 발명에 따른 유해가스 제거용 조성물, 그 제조 방법, 필터 및 이를 포함하는 공기 조화기에 의하면, 포름알데히드, 암모니아, 벤젠, 틀루엔, 이산화황 및 이산화질소 등의 가스상 오염물질을 효과적으로 제거할 수 있다.According to the composition for removing harmful gases according to the present invention, a manufacturing method, a filter, and an air conditioner including the same, gaseous contaminants such as formaldehyde, ammonia, benzene, toluene, sulfur dioxide, and nitrogen dioxide can be effectively removed.
도 1은 본 발명의 일 실시 예에 따른 공기 조화기의 사시도이다.1 is a perspective view of an air conditioner according to an embodiment of the present invention.
도 2는 도 1의 공기 조화기의 전면도어가 개방된 모습의 사시도이다.FIG. 2 is a perspective view of the front door of the air conditioner of FIG. 1 opened. FIG.
도 3은 도 1의 공기 조화기의 측면필터부, 하면필터부 및 내부필터부에 장착된 필터의 정면도이다.3 is a front view of a filter mounted on the side filter part, the bottom filter part and the internal filter part of the air conditioner of FIG. 1.
도 4는 도 3의 필터의 단면도이다.4 is a cross-sectional view of the filter of FIG. 3.
이하, 본 발명의 일부 실시 예들을 예시적인 도면을 통해 상세하게 설명한다. 각 도면의 구성요소들에 참조부호를 부가함에 있어서, 동일한 구성요소들에 대해서는 비록 다른 도면상에 표시되더라도 가능한 한 동일한 부호를 가지도록 하고 있음에 유의해야 한다. 또한, 본 발명의 실시 예를 설명함에 있어, 관련된 공지 구성 또는 기능에 대한 구체적인 설명이 본 발명의 실시 예에 대한 이해를 방해한다고 판단되는 경우에는 그 상세한 설명은 생략한다. Hereinafter, some embodiments of the present invention will be described in detail with reference to the accompanying drawings. In adding reference numerals to the components of each drawing, it should be noted that the same reference numerals are assigned to the same components as much as possible even though they are shown in different drawings. In addition, in describing the embodiments of the present invention, when it is determined that a detailed description of a related well-known configuration or function interferes with the understanding of the embodiments of the present invention, the detailed description thereof will be omitted.
이하에서는 도면을 참조하여 본 발명의 일 실시 예에 따른 공기 조화기를 설명한다.Hereinafter, an air conditioner according to an embodiment of the present invention will be described with reference to the drawings.
도 1은 본 발명의 일 실시 예에 따른 공기 조화기의 사시도이고, 도 2는 도 1의 공기 조화기의 전면도어가 개방된 모습의 사시도이다.1 is a perspective view of an air conditioner according to an embodiment of the present invention, Figure 2 is a perspective view of the front door of the air conditioner of Figure 1 is open.
도 1을 참조하면, 상기 공기 조화기(10)는 다수의 부품이 내장될 수 있도록 내부에 공간을 형성하고, 외형을 이루는 케이스(11)와, 상기 케이스(11)의 전면 외관을 형성하며 회동가능하게 상기 케이스(11)에 장착되는 전면도어(12)와, 상기 전면도어(12)의 전면에 장착되는 조작부(13)를 포함한다.Referring to FIG. 1, the air conditioner 10 rotates by forming a space therein so that a plurality of components can be built therein, forming a case 11 forming an external shape, and a front appearance of the case 11. The front door 12 may be mounted on the case 11, and the operation part 13 mounted on the front surface of the front door 12 may be included.
그리고 상기 케이스(11)는 상기 전면도어(12)가 장착되는 제1프레임(111)과, 상기 제1프레임(111)의 후방에 장착되는 상기 제2프레임(112)을 포함한다.The case 11 includes a first frame 111 on which the front door 12 is mounted, and a second frame 112 mounted on the rear of the first frame 111.
상기 제1프레임(111)의 양측 상부에 형성된 공기 토출구에는 측면 토출베인(21)이 장착되고, 상기 제1프레임(111)의 양측 하부에 형성된 공기 흡입구에는 측면 흡입베인(22)이 장착된다. Side discharge vanes 21 are mounted at air discharge ports formed at both upper sides of the first frame 111, and side suction vanes 22 are mounted at air suction ports formed at both lower sides of the first frame 111.
또한 상기 제1프레임(111)의 상측에 형성된 공기 토출구에는 상면 토출베인(23)이 장착되고, 상기 제1프레임(111)의 하측에는 공기가 흡입되는 공기 흡입구(111a)가 형성된다.In addition, an upper surface discharge vane 23 is mounted at an air discharge port formed at an upper side of the first frame 111, and an air suction port 111a is formed at a lower side of the first frame 111.
한편, 상기 공기 조화기(10)는 상기 측면 흡입베인(22) 및 상기 공기 흡입구(111a)로 공기를 흡입하여, 상기 측면 토출베인(21) 및 상면 토출베인(23)으로 공기를 토출시키는 공기 유동부(미도시)를 포함할 수 있다.Meanwhile, the air conditioner 10 sucks air into the side suction vanes 22 and the air suction ports 111a, and discharges air to the side discharge vanes 21 and the top discharge vanes 23. It may include a flow portion (not shown).
또한, 상기 공기 조화기(10)는, 상기 케이스(11)의 내부에 설치되어, 상기 케이스(11)의 내부로 유동하는 공기와 냉매와 열교환시키는 열교환기(미도시)를 포함할 수 있다.In addition, the air conditioner 10 may include a heat exchanger (not shown) installed inside the case 11 and exchanging heat with air flowing into the case 11 and a refrigerant.
도 2를 참조하면, 상기 제1프레임(111)의 내부에는, 상기 제1프레임(111)의 양측 하부에 형성된 공기 흡입구 측으로 유입되는 공기를 정화하기 위한 측면필터부(31)가 장착될 수 있다.Referring to FIG. 2, a side filter part 31 may be mounted inside the first frame 111 to purify the air flowing into the air intake ports formed at both lower sides of the first frame 111. .
그리고 상기 제1프레임(111)의 내부에는 상기 제1프레임(111)의 하측에 형성된 공기 흡입구(111a)로 유입되는 공기를 정화하기 위한 하면필터부(32)가 장착될 수 있다.In addition, a lower surface filter unit 32 may be mounted in the first frame 111 to purify the air flowing into the air inlet 111a formed at the lower side of the first frame 111.
또한 상기 제1프레임(111)의 내부에는 상기 측면필터부(31) 및 상기 하면필터부(32)에서 필터링된 공기를 한번 더 필터링하는 내부필터부(33)가 더 설치될 수 있다.In addition, an internal filter unit 33 may be further installed inside the first frame 111 to filter the air filtered by the side filter unit 31 and the bottom filter unit 32 once more.
상기 측면필터부(31), 상기 하면필터부(32) 및 내부필터부(33)는 상기 케이스(11)의 내부로 유입된 공기를 여과한다는 점에서 공기 여과부로 이름할 수 있다.The side filter part 31, the bottom filter part 32, and the internal filter part 33 may be referred to as air filter parts in that they filter air introduced into the case 11.
도 3은 도 1의 공기 조화기의 측면필터부, 하면필터부 및 내부필터부에 장착된 필터의 정면도이고, 도 4는 도 3의 필터의 단면도이다.3 is a front view of a filter mounted on the side filter part, the bottom filter part and the internal filter part of the air conditioner of FIG. 1, and FIG. 4 is a cross-sectional view of the filter of FIG. 3.
상기 상기 측면필터부(31), 상기 하면필터부(32) 또는 내부필터부(33)에는, 필터(40)가 포함된다.A filter 40 is included in the side filter part 31, the bottom filter part 32, or the internal filter part 33.
상기 필터(40)는 제1필터부재(41)와 제2필터부재(42)를 포함할 수 있다.The filter 40 may include a first filter member 41 and a second filter member 42.
상기 제1필터부재(41)는 평판 형상으로 형성되고, 상기 제2필터부재(42)는 물결 형상 또는 사형으로 형성된다. 그리고 상기 제1필터부재(41)와 상기 제2필터부재(42)는 서로 교호되도록 적층된다.The first filter member 41 is formed in a flat plate shape, and the second filter member 42 is formed in a wave shape or a sand shape. The first filter member 41 and the second filter member 42 are stacked alternately with each other.
그리고 상기 제1필터부재(41)와 상기 제2필터부재(42)의 사이에는 상기 제1필터부재(41)와 상기 제2필터부재(42)에서 여과된 공기가 유동하는 공기 통로(40a)가 형성된다.The air passage 40a through which the air filtered by the first filter member 41 and the second filter member 42 flows between the first filter member 41 and the second filter member 42. Is formed.
그리고 상기 필터(40)는 상기 제1필터부재(41)와 상기 제2필터부재(42)의 표면에 점착된 유해가스 제거용 조성물(50)을 더 포함할 수 있다. 여기서 상기 제1필터부재(41)와 상기 제2필터부재(42)는 상기 유해가스 제거용 조성물(50)이 점착된다는 점에서 담체로 이름할 수 있다.The filter 40 may further include a composition 50 for removing harmful gas adhered to the surfaces of the first filter member 41 and the second filter member 42. The first filter member 41 and the second filter member 42 may be referred to as carriers in that the harmful gas removing composition 50 is adhered.
그리고 상기 유해가스 제거용 조성물(50)은 상기 제1필터부재(41)와 상기 제2필터부재(42)의 표면에 스프레이 또는 침지되어 점착될 수 있다.In addition, the harmful gas removing composition 50 may be adhered by spraying or dipping the surfaces of the first filter member 41 and the second filter member 42.
상기 제1필터부재(41)와 상기 제2필터부재(42)의 재질은, 상기 유해가스 제거용 조성물(50)이 점착될 수 있는 재질, 예컨대, 폴리프로필렌 재질로 성형될 수 있다.The material of the first filter member 41 and the second filter member 42 may be formed of a material to which the harmful gas removing composition 50 is adhered, for example, a polypropylene material.
따라서, 상기 필터(40)는 미세먼지, 공기에서 석면 등과 같은 입자상 오염 물질과 바이러스, 곰팡이 박테리아 등의 생물학적 오염물을 제거할 수 있으며, 상기 유해가스 제거용 조성물(50)에 의해 이산화탄소, 포름알데히드, 휘발성 유기화합물 등과 같은 가스상 오염물질도 제거할 수 있다.Accordingly, the filter 40 may remove particulate contaminants such as asbestos and biological contaminants such as viruses and fungal bacteria from the air, and the carbon dioxide, formaldehyde, It can also remove gaseous contaminants such as volatile organic compounds.
이하에서는 상기 유해가스 제거용 조성물과 그 제조 방법에 대해 설명한다.Hereinafter, the composition for removing the noxious gas and a manufacturing method thereof will be described.
상기 유해가스 제거용 조성물은 아민기(-NH2)를 포함하는 산성물질 2 내지 10 중량부와, 인산(H3PO4) 5 내지 20중량부와, 백금(Pt) 0.001 내지 0.005중량부 및 잔량의 용매를 포함한다. 여기서 상기 잔량의 용매에는, 70 내지 90중량부의 물(H2O)이 포함될 수 있다.The harmful gas removal composition is 2 to 10 parts by weight of the acidic material containing an amine group (-NH 2 ), 5 to 20 parts by weight of phosphoric acid (H 3 PO 4 ), 0.001 to 0.005 parts by weight of platinum (Pt) and Residual amount of solvent. Here, the remaining amount of the solvent may include 70 to 90 parts by weight of water (H 2 O).
상기 아민기를 포함하는 산성물질에는, 파라아미노벤조산(para-aminobenzoic acid) 또는 술파닐산(sulfanilic acid)이 포함된다.Acidic substances containing the amine group include para-aminobenzoic acid or sulfanilic acid.
상기 파라아미노벤조산은 벤젠 고리에 아민기(-NH2)와 카르복실기(-COOH)가 결합되어 있어, 산성 물질 또는 염기성 물질과 화학적으로 반응할 수 있다. 특히, 포름알데히드(formaldehyde)와 아세트알데히드(acetaldehyde) 등의 고 휘발성 저급 알데히드를 아래의 화학식 1의 이민 형성 반응(imine formation reaction)을 통해 보다 효과적으로 제거할 수 있다.The paraaminobenzoic acid has an amine group (-NH 2 ) and a carboxyl group (-COOH) bonded to the benzene ring, and thus may react chemically with an acidic or basic substance. In particular, high volatile lower aldehydes such as formaldehyde and acetaldehyde may be more effectively removed through the imine formation reaction of Formula 1 below.
화학식 1
Figure PCTKR2015008565-appb-C000001
Formula 1
Figure PCTKR2015008565-appb-C000001
한편, 상기 유해가스 제거용 조성물에서 상기 파라아미노벤조산 또는 술파닐산이 2중량부 미만일 경우 등의 고 휘발성 저급 알데히드를의 제거 효율이 떨어진다.On the other hand, the removal efficiency of high volatile lower aldehydes, such as when the paraaminobenzoic acid or sulfanic acid is less than 2 parts by weight in the harmful gas removal composition.
또한 상기 유해가스 제거용 조성물에서 상기 파라아미노벤조산 또는 술파닐산이 10 중량부를 초과하는 경우 담체의 비표면적(比表面積), 즉 단위체적당 표면적의 감소로 인하여 유해물질 제거 효율이 나빠질 수 있다.In addition, when the paraaminobenzoic acid or sulfanic acid exceeds 10 parts by weight in the harmful gas removal composition, the efficiency of removing harmful substances may be deteriorated due to a decrease in specific surface area of the carrier, that is, a reduction in surface area per unit volume.
따라서 상기 유해가스 제거용 조성물에서 상기 파라아미노벤조산 또는 술파닐산은 2 내지 10중량부 범위로 첨가되는 것이 바람직하다Therefore, the paraaminobenzoic acid or sulfanic acid in the composition for removing harmful gases is preferably added in the range of 2 to 10 parts by weight.
상기 인산(H3PO4)은 암모니아를 제거할 수 있다. 상기 유해가스 제거용 조성물에서 상기 인산이 5 중량부 미만일 경우 암모니아 제거 효율이 떨어진다. 그리고 상기 유해가스 제거용 조성물에서 상기 인산이 20중량부를 초과하는 경우 흡착용 담체의 비표면적 감소로 인하여 유해물질 제거효율이 떨어진다. 따라서 상기 유해가스 제거용 조성물에서 상기 인산은 5 내지 20중량부 것이 바람직하다.The phosphoric acid (H 3 PO 4 ) can remove ammonia. When the phosphoric acid is less than 5 parts by weight in the composition for removing harmful gases, ammonia removal efficiency is lowered. And when the phosphoric acid in the composition for removing harmful gases exceeds 20 parts by weight, the removal efficiency of harmful substances is reduced due to the reduction of the specific surface area of the carrier for adsorption. Therefore, the phosphoric acid in the harmful gas removal composition is preferably 5 to 20 parts by weight.
상기 백금(Pt)은 포름알데히드 및 아세트알데히드 등과 같은 저급 알데히드와 아민기가 효과적으로 반응하기 위한 촉매제 역할을 수행한다. The platinum (Pt) serves as a catalyst for effectively reacting lower aldehydes such as formaldehyde and acetaldehyde with amine groups.
상기 백금은, 헥사클로로 백금산(hydrogen hexachloroplatinate(Ⅳ))을 폴리비닐알코올(Polyvinyl alcohol) 및 프로폴리스 추출물(Propolis Extract)로 환원시켜 제조될 수 있다.The platinum may be prepared by reducing hexachloro platinum acid (hydrogen hexachloroplatinate (IV)) with polyvinyl alcohol and Propolis Extract.
특히, 상기 백금은 알데히드의 수소첨가반응(protonation)에 대한 반응 촉매 역할을 수행하기 때문에, 포름알데히드 및 아세트알데히드 등과 같은 저급 알데히드 제거 효율을 상승시킬 수 있다.In particular, since the platinum acts as a reaction catalyst for hydrogenation (protonation) of the aldehyde, it is possible to increase the lower aldehyde removal efficiency, such as formaldehyde and acetaldehyde.
그리고 상기 유해가스 제거용 조성물에 상기 백금는 0.001 내지 0.005중량부로 첨가하는 것이 바람직하다. 상기 유해가스 제거용 조성물에서 상기 백금이 0.001 중량부 미만일 경우 촉매 반응이 원활히 수행되기 어렵고, 상기 유해가스 제거용 조성물에서 상기 백금이 0.005중량부 초과할 경우 상승되는 가격 대비 효율성이 떨어진다.And the platinum is preferably added to 0.001 to 0.005 parts by weight to the harmful gas removal composition. When the platinum is less than 0.001 parts by weight in the noxious gas removal composition, the catalytic reaction is difficult to be performed smoothly, and when the platinum is more than 0.005 parts by weight in the noxious gas removal composition, the cost-effectiveness is lowered.
[실시예 1] 유해가스 제거용 조성물의 제조Example 1 Preparation of Hazardous Gas Removal Composition
물 80중량부와 파라아미노벤조산 5중량부가 혼합된 혼합용액을 자석교반기를 이용하여 500rpm으로 온도가 60℃가 되도록 2시간 동안 가열 교반하였다. 상기 혼합용액이 25℃가 될 때까지 30분을 추가 교반한 후, 인산 10중량부 및 백금 0.002중량부를 첨가한 후 상온에서 500rpm으로 3시간 교반하여 유해가스 제거용 조성물을 제조하였다.A mixed solution of 80 parts by weight of water and 5 parts by weight of paraaminobenzoic acid was heated and stirred at 500 rpm for 2 hours using a magnetic stirrer to obtain a temperature of 60 ° C. After 30 minutes of further stirring until the mixed solution reached 25 ° C., 10 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
이 때, 상기 조성물을 제조하는 순서대로, 물과 산성물질을 혼합된 혼합용액을 제 1 혼합용액이라 이름하고, 상기 제 1 혼합용액을 가열 교반한 후 형성된 혼합용액을 제 2 혼합용액이라 이름한다. 그리고, 상기 제 2 혼합용액에 인산(H3PO4) 및 백금(Pt)을 혼합하여 형성한 혼합용액을 제 3 혼합용액이라 이름한다. 이러한 혼합용액의 정의는, 아래 실시예에도 동일하게 적용될 수 있다. At this time, in order to prepare the composition, the mixed solution mixed with water and the acidic substance is called the first mixed solution, and the mixed solution formed after heating and stirring the first mixed solution is called the second mixed solution. . The mixed solution formed by mixing phosphoric acid (H 3 PO 4 ) and platinum (Pt) in the second mixed solution is referred to as a third mixed solution. The definition of such a mixed solution can be equally applied to the following examples.
[실시예 2] 유해가스 제거용 조성물의 제조 Example 2 Preparation of Composition for Removing Hazardous Gases
물 80중량부와 술파닐산 5중량부가 혼합된 혼합용액을 자석교반기를 이용하여 500rpm으로 온도가 60℃가 되도록 2시간 동안 가열 교반하였다. 상기 혼합용액이 25℃가 될 때까지 30분을 추가 교반한 후, 인산 10중량부 및 백금 0.002중량부를 첨가한 후 상온에서 500rpm으로 3시간 교반하여 유해가스 제거용 조성물을 제조하였다.The mixed solution of 80 parts by weight of water and 5 parts by weight of sulfanic acid was heated and stirred for 2 hours at a temperature of 60 ° C. at 500 rpm using a magnetic stirrer. After 30 minutes of further stirring until the mixed solution reached 25 ° C., 10 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
[비교예 1]Comparative Example 1
물 80중량부와 파라아미노벤조산 5중량부가 혼합된 혼합용액을, 자석교반기를 이용하여 500rpm으로 교반하면서 온도가 60℃가 되도록 2시간 동안 가열 교반하였다. 상기 혼합용액을 25℃ 상온이 될 때까지 30분 동안 추가 교반한 후, 인산 10중량부를 첨가하고 상온에서 500rpm으로 3시간 동안 교반을 하여 유해가스 제거용 조성물을 제조하였다.The mixed solution in which 80 parts by weight of water and 5 parts by weight of paraaminobenzoic acid was mixed was heated and stirred for 2 hours so that the temperature was 60 ° C. while stirring at 500 rpm using a magnetic stirrer. The mixed solution was further stirred for 30 minutes until the room temperature to 25 ℃, 10 parts by weight of phosphoric acid was added and stirred for 3 hours at 500 rpm at room temperature to prepare a composition for removing harmful gases.
[비교예 2]Comparative Example 2
물 80중량부와 파라아미노벤조산 1중량부가 혼합된 혼합용액을, 자석교반기를 이용하여 500rpm으로 교반하면서 온도가 60℃가 되도록 2시간 동안 가열 교반하였다. 상기 혼합용액을 25℃ 상온이 될 때까지 30분 동안 추가 교반한 후, 인산 10중량부 및 백금 0.002중량부를 첨가하여 상온에서 500rpm으로 3시간 동안 교반을 하여 유해가스 제거용 조성물을 제조하였다.The mixed solution in which 80 parts by weight of water and 1 part by weight of paraaminobenzoic acid was mixed was heated and stirred for 2 hours so that the temperature was 60 ° C. while stirring at 500 rpm using a magnetic stirrer. The mixed solution was further stirred for 30 minutes until the temperature reaches 25 ° C, and then 10 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added thereto, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
[비교예 3]Comparative Example 3
물 80중량부와 파라아미노벤조산 15중량부가 혼합된 혼합용액을, 자석교반기를 이용하여 500rpm으로 교반하면서 온도가 60℃가 되도록 2시간 동안 가열 교반하였다. 상기 혼합용액을 25℃ 상온이 될 때까지 30분 동안 추가 교반한 후, 인산 10중량부 및 백금 0.002중량부를 첨가하여 상온에서 500rpm으로 3시간 동안 교반을 하여 유해가스 제거용 조성물을 제조하였다.The mixed solution in which 80 parts by weight of water and 15 parts by weight of paraaminobenzoic acid was mixed was heated and stirred for 2 hours so that the temperature was 60 ° C. while stirring at 500 rpm using a magnetic stirrer. The mixed solution was further stirred for 30 minutes until the temperature reaches 25 ° C, and then 10 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added thereto, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
[비교예 4][Comparative Example 4]
물 80중량부와 파라아미노벤조산 15중량부가 혼합된 혼합용액을, 자석교반기를 이용하여 500rpm으로 교반하면서 온도가 60℃가 되도록 2시간 동안 가열 교반하였다. 상기 혼합용액을 25℃ 상온이 될 때까지 30분 동안 추가 교반한 후, 인산 2중량부 및 백금 0.002중량부를 첨가하여 상온에서 500rpm으로 3시간 동안 교반을 하여 유해가스 제거용 조성물을 제조하였다.The mixed solution in which 80 parts by weight of water and 15 parts by weight of paraaminobenzoic acid was mixed was heated and stirred for 2 hours so that the temperature was 60 ° C. while stirring at 500 rpm using a magnetic stirrer. The mixed solution was further stirred for 30 minutes until the temperature reaches 25 ° C., and then 2 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added and stirred at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
[비교예 5] [Comparative Example 5]
물 80중량부와 파라아미노벤조산 5중량부가 혼합된 혼합용액을 자석교반기를 이용하여 500rpm으로 온도가 60℃가 되도록 2시간 동안 가열 교반하였다. 상기 혼합용액이 25℃가 될 때까지 30분을 추가 교반한 후, 인산 25중량부 및 백금 0.002중량부를 첨가한 후 상온에서 500rpm으로 3시간 교반하여 유해가스 제거용 조성물을 제조하였다.A mixed solution of 80 parts by weight of water and 5 parts by weight of paraaminobenzoic acid was heated and stirred at 500 rpm for 2 hours using a magnetic stirrer to obtain a temperature of 60 ° C. After 30 minutes of further stirring until the mixed solution reached 25 ° C., 25 parts by weight of phosphoric acid and 0.002 parts by weight of platinum were added, followed by stirring at 500 rpm for 3 hours at room temperature to prepare a composition for removing harmful gases.
[실험예 1]Experimental Example 1
아래의 표 1의 조건으로 실시예 1 및 2와, 비교예 1 내지 5의 유해가스 제거 효율 실험을 진행하였다.The hazardous gas removal efficiency experiments of Examples 1 and 2 and Comparative Examples 1 to 5 were conducted under the conditions of Table 1 below.
표 1
시험챔버 크기 4m3 8m3 30m3
시험가스 농도 10.0(±10%)ppm 10.0(±10%)ppm 10.0(±10%)ppm
시험체 필터 크기 340mm x 360mm x 10mm 340mm x 360mm x 10mm 340mm x 360mm x 10mm
시험체 조건 5CMM 5CMM 5CMM
시험체 작동시간 30분 30분 30분
Table 1
Test chamber size 4m 3 8m 3 30m 3
Test gas concentration 10.0 (± 10%) ppm 10.0 (± 10%) ppm 10.0 (± 10%) ppm
Specimen Filter Size 340mm x 360mm x 10mm 340mm x 360mm x 10mm 340mm x 360mm x 10mm
Test Conditions 5CMM 5CMM 5CMM
Test run time 30 minutes 30 minutes 30 minutes
여기서, 시험챔버의 크기는 시험가스가 채워진 공간의 부피(m3)를 의미하고, 시험체 조건은 시험체 필터로 유동하는 공기의 분당 송풍량(CMM,Cubic Meter per Minutes)이며, 시험체 작동시간은 시험가스를 필터한 시간을 의미한다.Here, the size of the test chamber refers to the volume (m 3 ) of the space filled with the test gas, the test conditions are the air flow per minute (CMM, Cubic Meter per Minutes) of the air flowing to the test filter, the test body operating time is the test gas Means the time when the filter is filtered.
실시예 1에 따른 시험 결과, 즉 유해물질의 제거율은 아래의 표 2와 같다.Test results according to Example 1, that is, the removal rate of harmful substances are shown in Table 2 below.
표 2
챔버크기 포름알데히드 암모니아 벤젠 틀루엔 이산화황 이산화질소
4m3 99.0% 99.0% 100.0% 100.0% 100.0% 100.0%
8m3 95.0% 95.0% 100.0% 98.0% 100.0% 100.0%
30m3 99.0% 99.0% 100.0% 100.0% 100.0% 100.0%
TABLE 2
Chamber size Formaldehyde ammonia benzene Toluen Sulfur dioxide Nitrogen dioxide
4m 3 99.0% 99.0% 100.0% 100.0% 100.0% 100.0%
8m 3 95.0% 95.0% 100.0% 98.0% 100.0% 100.0%
30m 3 99.0% 99.0% 100.0% 100.0% 100.0% 100.0%
실시예 2의 시험 결과는 아래의 표 3와 같다.Test results of Example 2 are shown in Table 3 below.
표 3
챔버크기 포름알데히드 암모니아 벤젠 틀루엔 이산화황 이산화질소
4m3 99.0% 99.0% 100.0% 100.0% 100.0% 100.0%
8m3 95.0% 95.0% 100.0% 98.0% 100.0% 100.0%
30m3 99.0% 99.0% 100.0% 100.0% 100.0% 100.0%
TABLE 3
Chamber size Formaldehyde ammonia benzene Toluen Sulfur dioxide Nitrogen dioxide
4m 3 99.0% 99.0% 100.0% 100.0% 100.0% 100.0%
8m 3 95.0% 95.0% 100.0% 98.0% 100.0% 100.0%
30m 3 99.0% 99.0% 100.0% 100.0% 100.0% 100.0%
비교예 1의 시험 결과는 아래의 표 4와 같다.Test results of Comparative Example 1 are shown in Table 4 below.
표 4
챔버크기 포름알데히드 암모니아 벤젠 틀루엔 이산화황 이산화질소
4m3 45.0% 99.0% 100.0% 100.0% 100.0% 100.0%
8m3 35.0% 95.0% 100.0% 95.0% 100.0% 100.0%
30m3 47.5% 97.5% 100.0% 100.0% 100.0% 100.0%
Table 4
Chamber size Formaldehyde ammonia benzene Toluen Sulfur dioxide Nitrogen dioxide
4m 3 45.0% 99.0% 100.0% 100.0% 100.0% 100.0%
8m 3 35.0% 95.0% 100.0% 95.0% 100.0% 100.0%
30m 3 47.5% 97.5% 100.0% 100.0% 100.0% 100.0%
표 4에서 볼 수 있듯이, 비교예 1의 유해가스 제거용 조성물이 코팅된 필터는 포름알데히드 제거 효율은 35~47.5% 수준으로, 실시예 1 또는 실시예 2의 유해가스 제거용 조성물이 코팅된 필터의 포름알데히드 제거 효율 95~99% 보다 낮았다.As shown in Table 4, the filter coated with the harmful gas removal composition of Comparative Example 1 has a formaldehyde removal efficiency of 35 to 47.5% level, and the filter coated with the harmful gas removal composition of Example 1 or Example 2 Formaldehyde removal efficiency was lower than 95-99%.
첨가된 백금촉매가 포름알데히드 제거 속도에 영향을 미치는 것으로 판단할 수 있다.It can be judged that the added platinum catalyst affects the rate of formaldehyde removal.
비교예 2의 시험 결과는 아래의 표 5와 같다.Test results of Comparative Example 2 are shown in Table 5 below.
표 5
챔버크기 포름알데히드 암모니아 벤젠 틀루엔 이산화황 이산화질소
4m3 10.0% 99.0% 100.0% 100.0% 100.0% 100.0%
8m3 5.0% 95.0% 100.0% 95.0% 100.0% 100.0%
30m3 10.0% 97.5% 100.0% 100.0% 100.0% 100.0%
Table 5
Chamber size Formaldehyde ammonia benzene Toluen Sulfur dioxide Nitrogen dioxide
4m 3 10.0% 99.0% 100.0% 100.0% 100.0% 100.0%
8m 3 5.0% 95.0% 100.0% 95.0% 100.0% 100.0%
30m 3 10.0% 97.5% 100.0% 100.0% 100.0% 100.0%
표 5에서 볼 수 있듯이, 비교예 2의 유해가스 제거용 조성물이 코팅된 필터는 포름알데히드 제거 효율은 5~10% 수준으로 매우 낮았다.As shown in Table 5, the filter coated with the composition for removing harmful gases of Comparative Example 2 had a very low formaldehyde removal efficiency of 5 to 10%.
파라아미노벤조산이 포름알데히드 제거에 미치는 영향이 매우 높음을 알 수 있다.It can be seen that the effect of paraaminobenzoic acid on the removal of formaldehyde is very high.
비교예 3의 시험 결과는 아래의 표 6와 같다.Test results of Comparative Example 3 are shown in Table 6 below.
표 6
챔버크기 포름알데히드 암모니아 벤젠 틀루엔 이산화황 이산화질소
4m3 99.0% 99.0% 70.0% 80.0% 80.0% 65.0%
8m3 90.0% 95.0% 60.0% 70.0% - -
30m3 99.0% 97.5% 70.0% 80.0% 65.0% 62.0%
Table 6
Chamber size Formaldehyde ammonia benzene Toluen Sulfur dioxide Nitrogen dioxide
4m 3 99.0% 99.0% 70.0% 80.0% 80.0% 65.0%
8m 3 90.0% 95.0% 60.0% 70.0% - -
30m 3 99.0% 97.5% 70.0% 80.0% 65.0% 62.0%
표 6에서 볼 수 있듯이, 비교예 3의 유해가스 제거용 조성물이 코팅된 필터는 벤젠, 톨루엔, 이산화질소 및 이산화황에 대한 제거 효율이 실시예 1 또는 실시예 2보다 낮았다.As shown in Table 6, the filter coated with the harmful gas removal composition of Comparative Example 3 had a lower removal efficiency for benzene, toluene, nitrogen dioxide, and sulfur dioxide than Example 1 or Example 2.
파라아미노벤조산의 높은 함량으로 인하여 필터의 비표면적이 크게 감소한 것에 기인한 것으로 판단된다.The high content of paraaminobenzoic acid is believed to be due to a significant decrease in the specific surface area of the filter.
비교예 4의 시험 결과는 아래의 표 7와 같다.Test results of Comparative Example 4 are shown in Table 7 below.
표 7
챔버크기 포름알데히드 암모니아 벤젠 틀루엔 이산화황 이산화질소
4m3 99.0% 65.0% 100.0% 100.0% 100.0% 95.0%
8m3 90.0% 45.0% 100.0% 100.0% 100.0% 100.0%
30m3 99.0% 60.0% 100.0% 100.0% 100.0% 100.0%
TABLE 7
Chamber size Formaldehyde ammonia benzene Toluen Sulfur dioxide Nitrogen dioxide
4m 3 99.0% 65.0% 100.0% 100.0% 100.0% 95.0%
8m 3 90.0% 45.0% 100.0% 100.0% 100.0% 100.0%
30m 3 99.0% 60.0% 100.0% 100.0% 100.0% 100.0%
비교예 4는 인산 첨가량이 낮아 경우 암모니아의 제거효율이 떨어졌다.In Comparative Example 4, the removal efficiency of ammonia was lowered when the phosphoric acid addition amount was low.
비교예 5의 시험 결과는 아래의 표 8와 같다.Test results of Comparative Example 5 are shown in Table 8 below.
표 8
챔버크기 포름알데히드 암모니아 벤젠 틀루엔 이산화황 이산화질소
4m3 99.0% 100.0% 80.0% 75.0% 20.0% 15.0%
8m3 85.0% 99.0% 75.0% 55.0% - -
30m3 85.0% 97.5% 80.0% 80.0% 10.0% 5.0%
Table 8
Chamber size Formaldehyde ammonia benzene Toluen Sulfur dioxide Nitrogen dioxide
4m 3 99.0% 100.0% 80.0% 75.0% 20.0% 15.0%
8m 3 85.0% 99.0% 75.0% 55.0% - -
30m 3 85.0% 97.5% 80.0% 80.0% 10.0% 5.0%
비교예 5는 유해가스 제거용 조성물이 코팅된 필터는 높은 인산 함량으로 인하여 포름알데히드를 제외한 벤젠, 틀루엔, 이산화황 및 이산화질소의 제거 효율이 떨어졌다.In Comparative Example 5, the filter coated with the composition for removing harmful gas was inferior in efficiency of removing benzene, toluene, sulfur dioxide, and nitrogen dioxide except formaldehyde due to high phosphoric acid content.
위와 같은 실시예 및 다수의 비교예 결과를 통하여, 본 실시예에서 제안된 유해가스 제거용 조성물이 설정된 중량부만큼 포함되었을 때, 유해가스 제거율이 높게 형성됨을 알 수 있다.Through the results of the above examples and a plurality of comparative examples, it can be seen that when the harmful gas removal composition proposed in this embodiment is included by the set weight part, the harmful gas removal rate is formed high.
본 실시예에 따르면, 포름알데히드, 암모니아, 벤젠, 틀루엔, 이산화황 및 이산화질소 등의 가스상 오염물질을 효과적으로 제거할 수 있으므로, 산업상 이용가능성이 현저하다.According to this embodiment, since it is possible to effectively remove gaseous contaminants such as formaldehyde, ammonia, benzene, toluene, sulfur dioxide and nitrogen dioxide, industrial applicability is remarkable.

Claims (15)

  1. 아민기(-NH2)를 포함하는 산성물질 2 내지 10 중량부와, 인산(H3PO4) 5 내지 20중량부와, 백금(Pt) 0.001 내지 0.005중량부 및 잔량의 용매를 포함하는 유해가스 제거용 조성물.2 to 10 parts by weight of an acidic substance containing an amine group (-NH 2 ), 5 to 20 parts by weight of phosphoric acid (H 3 PO 4 ), 0.001 to 0.005 parts by weight of platinum (Pt) and a residual amount of a solvent Composition for gas removal.
  2. 제 1 항에 있어서,The method of claim 1,
    상기 아민기를 포함하는 산성물질에는, 파라아미노벤조산(para-aminobenzoic acid) 또는 술파닐산(sulfanilic acid)이 포함되는 유해가스 제거용 조성물.The acidic material containing the amine group, para-aminobenzoic acid (para-aminobenzoic acid) or sulfanilic acid (sulfanilic acid) composition for removing harmful gases.
  3. 제 1 항에 있어서,The method of claim 1,
    상기 잔량의 용매에는, 물(H2O)이 포함되는 유해가스 제거용 조성물.The residual amount of the solvent, water (H 2 O) composition for removing harmful gas.
  4. 제 3 항에 있어서,The method of claim 3, wherein
    상기 물은 70 내지 90중량부를 가지는 유해가스 제거용 조성물.The water has a composition for removing harmful gases having 70 to 90 parts by weight.
  5. 제 1 항에 있어서,The method of claim 1,
    상기 백금(Pt)은, 헥사클로로 백금산(hydrogen hexachloroplatinate(Ⅳ))을 폴리비닐알코올(Polyvinyl alcohol) 및 프로폴리스 추출물(Propolis Extract)로 환원시켜 제조되는 것을 특징으로 하는 유해가스 제거용 조성물.The platinum (Pt) is a composition for removing harmful gases, characterized in that produced by reducing hexachloro platinum acid (hydrogen hexachloroplatinate (IV)) to polyvinyl alcohol (Polyvinyl alcohol) and Propolis Extract (Propolis Extract).
  6. 물 70 내지 90중량부와 아민기(-NH2)를 포함하는 산성물질 2 내지 10 중량부를 혼합하여 제 1 혼합용액을 형성하는 단계;Mixing 70 to 90 parts by weight of water and 2 to 10 parts by weight of an acidic substance including an amine group (-NH 2 ) to form a first mixed solution;
    상기 제 1 혼합용액을 가열 교반하여 제 2 혼합용액을 형성하는 단계;Heating and stirring the first mixed solution to form a second mixed solution;
    상기 제 2 혼합용액에 인산(H3PO4) 5 내지 20중량부와 백금(Pt) 0.001 내지 0.005중량부를 혼합하여 제 3 혼합용액을 형성하는 단계; 및Forming a third mixed solution by mixing 5 to 20 parts by weight of phosphoric acid (H 3 PO 4 ) and 0.001 to 0.005 parts by weight of platinum (Pt) to the second mixed solution; And
    상기 제 3 혼합용액을 교반하는 단계를 포함하는 유해가스 제거용 조성물 제조 방법.Method for producing a composition for removing harmful gases comprising the step of stirring the third mixed solution.
  7. 제 6 항에 있어서,The method of claim 6,
    상기 제 1 혼합용액을 가열 교반하는 단계에는,In the step of heating and stirring the first mixed solution,
    상기 제 1 혼합용액을 50 내지 70℃에서 2시간 동안 500rpm으로 가열 교반하는 단계가 포함되는 유해가스 제거용 조성물 제조 방법.Method for producing a composition for removing harmful gas comprising the step of heating and stirring the first mixed solution at 500 rpm for 2 hours at 50 to 70 ℃.
  8. 제 6 항에 있어서,The method of claim 6,
    상기 제 3 혼합용액을 교반하는 단계에는,In the step of stirring the third mixed solution,
    상기 제 3 혼합용액을 15 내지 25℃에서 3시간 동안 500rpm으로 교반하는 단계가 포함되는 유해가스 제거용 조성물 제조 방법.Method for producing a composition for removing harmful gases comprising the step of stirring the third mixed solution at 15 rpm to 500 rpm for 3 hours.
  9. 필터부재;Filter member;
    상기 필터부재에 점착되는 유해가스 제거용 조성물을 포함하고,Contains a composition for removing harmful gas adhered to the filter member,
    상기 유해가스 제거용 조성물은, 아민기(-NH2)를 포함하는 산성물질 2 내지 10 중량부와, 인산(H3PO4) 5 내지 20중량부와, 백금(Pt) 0.001 내지 0.005중량부 및 잔량의 용매를 포함하는 필터.The harmful gas removal composition is 2 to 10 parts by weight of an acidic material containing an amine group (-NH 2 ), 5 to 20 parts by weight of phosphoric acid (H 3 PO 4 ), 0.001 to 0.005 parts by weight of platinum (Pt) And a residual amount of solvent.
  10. 제 9 항에 있어서,The method of claim 9,
    상기 아민기를 포함하는 산성물질에는, 파라아미노벤조산(para-aminobenzoic acid) 또는 술파닐산(sulfanilic acid)이 포함되는 필터.The acidic material containing the amine group, a filter containing para-aminobenzoic acid (sulfanilic acid) or para-aminobenzoic acid (sulfanilic acid).
  11. 제 9 항에 있어서,The method of claim 9,
    상기 잔량의 용매에는, 물(H2O)이 포함되는 필터.The residual amount of solvent, the filter containing water (H 2 O).
  12. 제 11 항에 있어서,The method of claim 11,
    상기 물은 70 내지 90중량부를 가지는 필터.The water filter having a 70 to 90 parts by weight.
  13. 제 9 항에 있어서,The method of claim 9,
    상기 필터부재에는,The filter member,
    평판 형상으로 형성된 제 1 필터부재; A first filter member formed in a flat plate shape;
    물결 형상으로 형성된 제 2 필터부재; 및A second filter member formed in a wave shape; And
    상기 제 1 필터부재와 제 2 필터부재의 사이에 형성되는 공기 통로가 포함되며, An air passage is formed between the first filter member and the second filter member,
    상기 제 1 필터부재와 상기 제 2 필터부재는 서로 교호되도록 적층되는 것을 특징으로 하는 필터.And the first filter member and the second filter member are stacked alternately with each other.
  14. 제 13 항에 있어서,The method of claim 13,
    상기 제 1 필터부재 또는 상기 제 2 필터부재의 재질은 폴리 프로필렌으로 이루어지는 것을 특징으로 하는 필터.The filter of claim 1, wherein the first filter member or the second filter member is made of polypropylene.
  15. 케이스;case;
    상기 케이스에 장착되며 유해가스 제거용 조성물이 점착된 공기 여과부;An air filtration unit mounted to the case and to which a composition for removing harmful gas is adhered;
    상기 공기 여과부에 공기를 유동시키는 공기 유동부; 및An air flow unit for flowing air to the air filtration unit; And
    상기 공기 여과부에서 여과된 공기를 냉각 또는 가열하는 열교환기를 포함하고,It includes a heat exchanger for cooling or heating the air filtered in the air filter,
    상기 유해가스 제거용 조성물은, 아민기(-NH2)를 포함하는 산성물질 2 내지 10 중량부와, 인산(H3PO4) 5 내지 20중량부와, 백금(Pt) 0.001 내지 0.005중량부 및잔량의 용매를 포함하는 공기 조화기.The harmful gas removal composition is 2 to 10 parts by weight of an acidic material containing an amine group (-NH 2 ), 5 to 20 parts by weight of phosphoric acid (H 3 PO 4 ), 0.001 to 0.005 parts by weight of platinum (Pt) And a residual amount of solvent.
PCT/KR2015/008565 2014-09-03 2015-08-17 Composition for removing harmful gas, preparing method therefor, filter, and air conditioner comprising same WO2016036022A1 (en)

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