KR20030031512A - A Complex Honeycomb Filter with Carbon Nano-materials for Air Cleaning - Google Patents
A Complex Honeycomb Filter with Carbon Nano-materials for Air Cleaning Download PDFInfo
- Publication number
- KR20030031512A KR20030031512A KR1020030008350A KR20030008350A KR20030031512A KR 20030031512 A KR20030031512 A KR 20030031512A KR 1020030008350 A KR1020030008350 A KR 1020030008350A KR 20030008350 A KR20030008350 A KR 20030008350A KR 20030031512 A KR20030031512 A KR 20030031512A
- Authority
- KR
- South Korea
- Prior art keywords
- carbon
- carbon nanomaterial
- particles
- honeycomb filter
- air purification
- Prior art date
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D39/00—Filtering material for liquid or gaseous fluids
- B01D39/14—Other self-supporting filtering material ; Other filtering material
- B01D39/20—Other self-supporting filtering material ; Other filtering material of inorganic material, e.g. asbestos paper, metallic filtering material of non-woven wires
- B01D39/2055—Carbonaceous material
- B01D39/2058—Carbonaceous material the material being particulate
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D39/00—Filtering material for liquid or gaseous fluids
- B01D39/14—Other self-supporting filtering material ; Other filtering material
- B01D39/20—Other self-supporting filtering material ; Other filtering material of inorganic material, e.g. asbestos paper, metallic filtering material of non-woven wires
- B01D39/2055—Carbonaceous material
- B01D39/2065—Carbonaceous material the material being fibrous
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/24—Particle separators, e.g. dust precipitators, using rigid hollow filter bodies
- B01D46/2403—Particle separators, e.g. dust precipitators, using rigid hollow filter bodies characterised by the physical shape or structure of the filtering element
- B01D46/2418—Honeycomb filters
-
- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21H—PULP COMPOSITIONS; PREPARATION THEREOF NOT COVERED BY SUBCLASSES D21C OR D21D; IMPREGNATING OR COATING OF PAPER; TREATMENT OF FINISHED PAPER NOT COVERED BY CLASS B31 OR SUBCLASS D21G; PAPER NOT OTHERWISE PROVIDED FOR
- D21H19/00—Coated paper; Coating material
- D21H19/36—Coatings with pigments
- D21H19/44—Coatings with pigments characterised by the other ingredients, e.g. the binder or dispersing agent
- D21H19/56—Macromolecular organic compounds or oligomers thereof obtained by reactions only involving carbon-to-carbon unsaturated bonds
-
- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21H—PULP COMPOSITIONS; PREPARATION THEREOF NOT COVERED BY SUBCLASSES D21C OR D21D; IMPREGNATING OR COATING OF PAPER; TREATMENT OF FINISHED PAPER NOT COVERED BY CLASS B31 OR SUBCLASS D21G; PAPER NOT OTHERWISE PROVIDED FOR
- D21H27/00—Special paper not otherwise provided for, e.g. made by multi-step processes
- D21H27/08—Filter paper
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2239/00—Aspects relating to filtering material for liquid or gaseous fluids
- B01D2239/02—Types of fibres, filaments or particles, self-supporting or supported materials
- B01D2239/0258—Types of fibres, filaments or particles, self-supporting or supported materials comprising nanoparticles
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2239/00—Aspects relating to filtering material for liquid or gaseous fluids
- B01D2239/10—Filtering material manufacturing
Abstract
Description
본 발명은 공기 청정기, 건축물의 공조기 및 자동차의 캐빈 필터에 적용될 수 있는 공기 정화용 필터 시스템에 관한 것으로, 종이 허니컴 표면에 다양한 전기화학적 표면처리를 통한 입자 및 분말상의 탄소 나노소재를 코팅 처리하고 이의 양 단면을 홀 가공처리된 부직포 형태의 활성탄소섬유를 부착한 후 프레임 처리하여이루어진 나노 복합필터에 관한 것이다.The present invention relates to an air purifying filter system that can be applied to an air purifier, an air conditioner of a building, and a cabin filter of an automobile. The surface of the honeycomb paper is coated with carbon nanomaterials in the form of particles and powders through various electrochemical surface treatments and the amount thereof. The present invention relates to a nano-composite filter formed by attaching activated carbon fibers in the form of a hole processed non-woven fabric to a cross section, and then processing the frame.
기존의 공기 정화용 필터의 구성은 미세 먼지를 포집하기 위한 유리섬유 또는 폴리에스터 부직포로 이루어진 Pre-filter와 기체상 유기 오염원의 제거를 위한 활성탄소 섬유 및 필요에 따라 이온성 유해물질 제거를 위한 이온교환 섬유등으로 이루어진 Post-filter를 조합하여 이루어진 Tray 형태의 복합필터 또는 프레임 내부를 모자이크로 처리하여 각각의 필터를 삽입 처리하여 이루어진 모자이크 케미컬 필터로 되어있다. 그러나 이러한 복합필터시스템은 그 구성이 복잡하고 제작 및 유지비용이 클 뿐만 아니라 필터의 차압성능을 저하시켜 교체주기가 짧아지는 문제점이 있다. 또한 다양한 기체상 유기오염원에 대하여 효과적인 흡ㆍ탈착이 이루어지지 않고 오히려 오염원과의 반응에 의한 필터 표면의 염 발생으로 인한 2차 오염의 원인이 된다.Conventional air purification filters consist of pre-filters made of glass fibers or polyester nonwovens to capture fine dust, activated carbon fibers to remove gaseous organic contaminants, and ion exchange to remove ionic harmful substances as needed. It is a mosaic chemical filter made by inserting each filter by processing the inside of the tray complex filter or the frame made by combining the post-filter made of fibers. However, such a complex filter system has a problem in that its configuration is complicated, its manufacturing and maintenance costs are high, and the replacement cycle is shortened by reducing the differential pressure performance of the filter. In addition, the adsorption and desorption of various gaseous organic pollutants are not effective, but rather cause secondary pollution due to salt generation on the surface of the filter by reaction with the pollutant.
따라서 본 발명은 지지체로서 종이 허니컴 표면을 다양한 산 및 알칼리 전해액에서의 전기화학적 표면처리된 입자 및 분말형태의 탄소 나노소재를 코팅처리 한 후 허니컴 필터의 양 단면에 섬유상 활성탄소 부직포를 부착하고 프레임 처리하였다.Therefore, in the present invention, the surface of the paper honeycomb as a support is coated with carbon nanomaterials in the form of particles and powders electrochemically treated in various acid and alkali electrolytes, and then fibrous activated carbon nonwoven fabric is attached to both ends of the honeycomb filter and framed. It was.
본 발명은 특정 기체상 오염원에 대해 탄소 나노소재를 다양한 산성 및 알칼리성의 전해액으로 전기화학적 표면처리를 통하여 효과적으로 흡착, 제거할 수 있으며, 단일 소재에 순차적으로 혼용 표면처리가 가능하다. 또한 차압성능을 고려하여 허니컴의 셀 사이즈를 다양하게 변화시킬 수 있으며, 허니컴 필터 양 면에 부착되는 활성탄소섬유 부직포도 다양한 형태의 셀 크기로 홀 가공하여 부착할 수 있다.The present invention can effectively adsorb and remove carbon nanomaterials with various acidic and alkaline electrolytes for specific gaseous contaminants through electrochemical surface treatment, and can be mixed with a single material sequentially. In addition, the honeycomb cell size can be variously changed in consideration of the differential pressure performance, and the activated carbon fiber nonwoven fabric attached to both sides of the honeycomb filter can also be attached by hole processing in various cell sizes.
도 1은 본 발명에 따른 나노 복합필터 구조 단면도1 is a cross-sectional view of a nano composite filter structure according to the present invention
도 2는 각 실시예에 따른 암모니아 제거성능 결과도2 is ammonia removal performance results according to each embodiment
도 3은 각 실시예에 따른 아세트 알데히드 제거성능 결과도3 is a result of acetaldehyde removal performance according to each embodiment
도 4는 각 실시예에 따른 톨루엔 제거성능 결과도4 is a result of toluene removal performance according to each embodiment
도 5는 각 실시예에 따른 필터의 압력손실 특성을 나타낸 도면5 is a view showing the pressure loss characteristics of the filter according to each embodiment
* 도면의 주요 부분에 대한 부호의 설명* Explanation of symbols for the main parts of the drawings
1; 종이 허니컴 2; 표면처리된 입자 및 분말상 탄소 나노소재One; Paper honeycomb 2; Surface Treated Particles and Powdered Carbon Nanomaterials
3; 홀 가공처리된 활성탄소 섬유 부직포 4; 알루미늄 프레임3; Hole processed activated carbon fiber nonwoven fabric 4; aluminum frame
본 발명에 의한 탄소 나노소재 복합 허니컴 필터 시스템은 암모니아, 아세트알데히드 및 톨루엔등의 다양한 기체상 유기오염원의 효과적인 제거를 위해 고 비표면적의 입자 및 분말형태의 탄소 나노소재를 다양한 산 및 알칼리 전해액에서 전기화학적 표면처리를 행하였으며, 이후 이를 종이 허니컴에 열 및 자외선 경화를 통해 코팅 처리하였다. 이렇게 제조된 허니컴 필터의 양 단면을 섬유상 활성탄소 부직포를 부착하고 이를 프레임 처리하여 탄소 나노소재 복합 허니컴 필터를 제조하였다.The carbon nanomaterial composite honeycomb filter system according to the present invention is characterized in that carbon nanomaterials having a high specific surface area and powder form of carbon nanomaterials are used in various acid and alkali electrolytes for effective removal of various gaseous organic pollutants such as ammonia, acetaldehyde and toluene. A chemical surface treatment was performed, which was then coated on the paper honeycomb through heat and ultraviolet curing. Both surfaces of the honeycomb filter thus prepared were attached with a fibrous activated carbon nonwoven fabric and then frame-treated to prepare a carbon nanomaterial composite honeycomb filter.
이렇게 제조된 복합 필터를 기체상 유기오염원인 암모니아, 아세트알데히드 및 톨루엔의 제거율을 ASTM P-3687의 기상 흡착법에 의한 증기상 유기화합물 분석을 통해 각각 측정하였으며 그 결과를 도 2 ∼ 도 4에 각각 나타내었다. 각 실시예의 시험에 앞서 필터 시료를 100℃에서 완전히 건조시킨 후 5 ℓ의 밀폐된 유리관에 시료를 주입하고 제거 대상기체를 약 300 ppm(톨루엔의 경우 100 ppm)의 초기농 도로 한쪽 입구로 주입하고 시간의 경과에 따른 주입기체의 농도변화를 측정하였다, 또한 ASTM F-778의 방법에 따라 필터 메디어의 차압성능을 측정하여 그 결과를 도 5에 나타내었다, 각 실시예에 따른 필터는 340 ×340 ×10 cm(가로 ×세로 ×두께)의 크기로 제작하여 시험하였다.The removal rate of ammonia, acetaldehyde and toluene, which are gaseous organic pollutants, was measured by vapor phase organic compound analysis by vapor phase adsorption method of ASTM P-3687, and the results are shown in FIGS. 2 to 4, respectively. It was. Before the test of each example, filter sample was completely dried at 100 ° C, and then the sample was injected into a 5 L sealed glass tube, and the target gas was injected into one inlet at an initial concentration of about 300 ppm (100 ppm for toluene). The change in concentration of the injected gas with time was measured, and the differential pressure performance of the filter media was measured in accordance with the method of ASTM F-778, and the results are shown in FIG. 5. It tested by making into the size of 10 cm (width x length x thickness).
이하, 본 발명에 따른 구체적인 실시예를 기술하였으며, 본 발명의 범위가하기 실시예에 한정되는 것은 아니다.Hereinafter, specific examples according to the present invention have been described, but the scope of the present invention is not limited to the following examples.
[실시예 1]Example 1
고온 열분해방법에 의해 제조 및 고도정제 처리된 고비표면적의 다중벽 탄소나노튜브를 인산(H3PO4) 전해액중에서 전압 50V, 전류 1.0A로 약 5분동안 전기화학적 표면처리 후 건조시켰다. 이를 폴리비닐 아세테이트 (PVAc) 도포된 종이 허니컴에 분산 후 자외선 경화처리하고 알루미늄 플레임으로 마감하여 탄소 나노소재 복합 허니컴 필터를 제작하였다, 이를 상기의 ASTM D-3687의 기상흡착법에 의한 암모니아, 아세트 알데히드 및 톨루엔의 제거, 흡착성능을 실시하였으며 그 결과를 도 2 ∼ 도 4에 각각 나타내었다. 또한 필터의 차압성능을 ASTM F-778 방법에 따라 측정하여 그 결과를 도 5에 나타내었다.The high specific surface area multi-walled carbon nanotubes prepared by the high temperature pyrolysis method were dried after electrochemical surface treatment for about 5 minutes at a voltage of 50 V and a current of 1.0 A in a phosphoric acid (H 3 PO 4 ) electrolyte. It was dispersed in polyvinyl acetate (PVAc) coated paper honeycomb, UV cured, and finished with aluminum flame to produce a carbon nanocomposite composite honeycomb filter, which was prepared by ammonia, acetaldehyde, Toluene was removed and the adsorption performance was performed, and the results are shown in FIGS. 2 to 4, respectively. In addition, the differential pressure performance of the filter was measured according to the ASTM F-778 method and the results are shown in FIG. 5.
[실시예 2]Example 2
고온 열분해방법에 의해 제조 및 고도정제 처리된 고비표면적의 다중벽 탄소나노튜브를 질산(HNO3) 전해액중에서 전압 110V, 전류 5.0A로 약 10분 동안 전기화학적 표면처리 후 건조시켰다. 이를 에틸렌-비닐아세테이트(EVAc)로 도포된 종이 허니컴에 분산 후 열 경화하고 알루미늄 플레임으로 마감하여 탄소 나노소재 복합 허니컴 필터를 제작하였다. 이를 상기의 ASTM D-3687의 기상흡착법에 의한 암모니아, 아세트 알데히드 및 톨루엔의 제거, 흡착성능을 실시하였으며 그 결과를 도 2 ∼ 도 4에 각각 나타내었다. 또한 필터의 차압성능을 ASTM F-778 방법에 따라 측정하여 그 결과를 도 5에 나타내었다.The high specific surface area multi-walled carbon nanotubes prepared and treated by high temperature pyrolysis were dried after electrochemical surface treatment for 10 minutes at a voltage of 110 V and a current of 5.0 A in nitric acid (HNO 3 ) electrolyte. This was dispersed in a paper honeycomb coated with ethylene-vinylacetate (EVAc), heat cured, and finished with an aluminum flame to produce a carbon nanomaterial composite honeycomb filter. The removal and adsorption performance of ammonia, acetaldehyde and toluene by the gas phase adsorption method of ASTM D-3687 were carried out. The results are shown in FIGS. 2 to 4, respectively. In addition, the differential pressure performance of the filter was measured according to the ASTM F-778 method and the results are shown in FIG. 5.
[실시예 3]Example 3
고온 열분해방법에 의해 제조 및 고도정제 처리된 고비표면적의 다중벽 탄소나노튜브를 수산화 나트륨(NaOH) 전해액중에서 전압 25V, 전류 2.0A로 약 1분 동안 전기화학적 표면처리 후 건조시켰다. 이를 폴리비닐 아세테이트 (PVAc) 도포된 종이 허니컴에 분산 후 자외선 경화처리하고 알루미늄 플레임으로 마감하여 탄소 나노소재 복합 허니컴 필터를 제작하였다. 이를 상기의 ASTM D-3687의 기상흡착법에 의한 암모니아, 아세트 알데히드 및 톨루엔의 제거, 흡착성능을 실시하였으며 그 결과를 도 2 ∼ 도 4에 각각 나타내었다. 또한 필터의 차압성능을 ASTM F-778 방법에 따라 측정하여 그 결과를 도 5에 나타내었다.The high specific surface area multi-walled carbon nanotubes prepared by the high temperature pyrolysis method were dried after electrochemical surface treatment for about 1 minute at a voltage of 25 V and a current of 2.0 A in sodium hydroxide (NaOH) electrolyte. This was dispersed in a polyvinyl acetate (PVAc) coated paper honeycomb, UV cured, and finished with aluminum flame to produce a carbon nanomaterial composite honeycomb filter. The removal and adsorption performance of ammonia, acetaldehyde and toluene by the gas phase adsorption method of ASTM D-3687 were carried out. The results are shown in FIGS. 2 to 4, respectively. In addition, the differential pressure performance of the filter was measured according to the ASTM F-778 method and the results are shown in FIG. 5.
[실시예 4]Example 4
고온 열분해방법에 의해 제조 및 고도정제 처리된 고비표면적의 다중벽 탄소나노튜브를 암모니아(NH3) 전해액중에서 전압 250V, 전류 3.0A로 약 5분 동안 전기화학적 표면처리 후 건조시켰다. 이를 에틸렌-비닐아세테이트(EVAc)로 도포된 종이 허니컴에 분산 후 열 경화하고 알루미늄 플레임으로 마감하여 탄소 나노소재 복합 허니컴 필터를 제작하였다. 이를 상기의 ASTM D-3687의 기상흡착법에 의한 암모니아, 아세트 알데히드 및 톨루엔의 제거, 흡착성능을 실시하였으며 그 결과를 도 2 ∼ 도 4에 각각 나타내었다. 또한 필터의 차압성능을 ASTM F-778 방법에 따라 측정하여 그 결과를 도 5에 나타내었다.The high specific surface area multi-walled carbon nanotubes prepared by the high temperature pyrolysis method were dried after electrochemical surface treatment for about 5 minutes at a voltage of 250 V and a current of 3.0 A in an ammonia (NH 3 ) electrolyte. This was dispersed in a paper honeycomb coated with ethylene-vinylacetate (EVAc), heat cured, and finished with an aluminum flame to produce a carbon nanomaterial composite honeycomb filter. The removal and adsorption performance of ammonia, acetaldehyde and toluene by the gas phase adsorption method of ASTM D-3687 were carried out. The results are shown in FIGS. 2 to 4, respectively. In addition, the differential pressure performance of the filter was measured according to the ASTM F-778 method and the results are shown in FIG. 5.
[실시예 5]Example 5
고온 열분해방법에 의해 제조 및 고도정제 처리된 고비표면적의 탄소나노섬유를 황산(H2SO4) 전해액중에서 전압 110V, 전류 4.0A로 약 2분 동안 전기화학적 표면처리 후 건조시켰다. 이를 폴리비닐 아세테이트 (PVAc) 도포된 종이 허니컴에 분산 후 자외선 경화처리하고 알루미늄 플레임으로 마감하여 탄소 나노소재 복합 허니컴 필터를 제작하였다. 이를 상기의 ASTM D-3687의 기상흡착법에 의한 암모니아, 아세트 알데히드 및 톨루엔의 제거, 흡착성능을 실시하였으며 그 결과를 도2 ∼ 도 4에 각각 나타내었다. 또한 필터의 차압성능을 ASTM F-778 방법에 따라 측정하여 그 결과를 도 5에 나타내었다.The high specific surface area carbon nanofibers prepared and treated by the high temperature pyrolysis method were dried after electrochemical surface treatment for about 2 minutes at a voltage of 110 V and a current of 4.0 A in sulfuric acid (H 2 SO 4 ) electrolyte. This was dispersed in a polyvinyl acetate (PVAc) coated paper honeycomb, UV cured, and finished with aluminum flame to produce a carbon nanomaterial composite honeycomb filter. The removal and adsorption performance of ammonia, acetaldehyde and toluene by the gas phase adsorption method of ASTM D-3687 were carried out. The results are shown in FIGS. 2 to 4, respectively. In addition, the differential pressure performance of the filter was measured according to the ASTM F-778 method and the results are shown in FIG. 5.
[실시예 6]Example 6
고온 열분해방법에 의해 제조 및 고도정제 처리된 고비표면적의 탄소나노섬유를 염산(HCl) 전해액중에서 전압 250V, 전류 2.0A로 약 7분 동안 전기화학적 표면처리 후 건조시켰다. 이를 에틸렌-비닐아세테이트 (EVAc)로 도포된 종이 허니컴에 분산 후 열 경화하고 알루미늄 플레임으로 마감하여 탄소 나노소재 복합 허니컴 필터를 제작하였다. 이를 상기의 ASTM D-3687의 기상흡착법에 의한 암모니아, 아세트 알데히드 및 톨루엔의 제거, 흡착성능을 실시하였으며 그 결과를 도 2 ∼ 도 4에 각각 나타내었다. 또한 필터의 차압성능을 ASTM F-778 방법에 따라 측정하여 그 결과를 도 5에 나타내었다.The high specific surface area carbon nanofibers prepared and treated by high temperature pyrolysis were dried after electrochemical surface treatment for about 7 minutes at a voltage of 250 V and a current of 2.0 A in hydrochloric acid (HCl) electrolyte. This was dispersed in a paper honeycomb coated with ethylene-vinylacetate (EVAc), thermally cured, and finished with an aluminum flame to produce a carbon nanomaterial composite honeycomb filter. The removal and adsorption performance of ammonia, acetaldehyde and toluene by the gas phase adsorption method of ASTM D-3687 were carried out. The results are shown in FIGS. 2 to 4, respectively. In addition, the differential pressure performance of the filter was measured according to the ASTM F-778 method and the results are shown in FIG. 5.
[실시예 7]Example 7
고온 열분해방법에 의해 제조 및 고도정제 처리된 고비표면적의 탄소 나노섬유를 염화나트륨(NaCl) 전해액중에서 전압 110V, 전류 5.0A로 약 10분동안 전기화학적 표면처리 후 건조시켰다. 이를 폴리비닐 아세테이트 (PVAc) 도포된 종이 허니컴에 분산 후 자외선 경화처리하고 알루미늄 플레임으로 마감하여 탄소 나노소재 복합 허니컴 필터를 제작하였다. 이를 상기의 ASTM D-3687의 기상흡착법에 의한 암모니아, 아세트 알데히드 및 톨루엔의 제거, 흡착성능을 실시하였으며 그 결과를 도 2 ∼ 도 4에 각각 나타내었다. 또한 필터의 차압성능을 ASTM F-778 방법에 따라 측정하여 그 결과를 도 5에 나타내었다.The high specific surface area carbon nanofibers prepared and treated by high temperature pyrolysis were dried after electrochemical surface treatment for 10 minutes at a voltage of 110 V and a current of 5.0 A in sodium chloride (NaCl) electrolyte. This was dispersed in a polyvinyl acetate (PVAc) coated paper honeycomb, UV cured, and finished with aluminum flame to produce a carbon nanomaterial composite honeycomb filter. The removal and adsorption performance of ammonia, acetaldehyde and toluene by the gas phase adsorption method of ASTM D-3687 were carried out. The results are shown in FIGS. 2 to 4, respectively. In addition, the differential pressure performance of the filter was measured according to the ASTM F-778 method and the results are shown in FIG. 5.
본 발명에 의해 제조된 나노 복합 허니컴 필터는 에어컨, 자동차등의 일반 및 반도체, 제약등의 고청정이 요구되는 공기정화용 필터시스템에 적용될 수 있는 기능성 필터로서 다양한 기체상 유기오염원인 암모니아, 알데히드류 및 톨루엔등의 휘발성 유기화합물등의 효과적인 제거 및 우수한 차압성능과 함께 구조가 간단하고 제작 및 유지가 쉽고 경제적이다.The nanocomposite honeycomb filter manufactured by the present invention is a functional filter that can be applied to an air purification filter system requiring high cleanness such as air conditioners, automobiles, and general semiconductors, pharmaceuticals, and the like. The structure is simple, easy to manufacture and maintain, and economical with effective removal of volatile organic compounds such as toluene and excellent differential pressure performance.
Claims (7)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR10-2003-0008350A KR100489471B1 (en) | 2003-02-10 | 2003-02-10 | A Complex Honeycomb Filter with Carbon Nano-materials for Air Cleaning |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR10-2003-0008350A KR100489471B1 (en) | 2003-02-10 | 2003-02-10 | A Complex Honeycomb Filter with Carbon Nano-materials for Air Cleaning |
Publications (2)
Publication Number | Publication Date |
---|---|
KR20030031512A true KR20030031512A (en) | 2003-04-21 |
KR100489471B1 KR100489471B1 (en) | 2005-05-17 |
Family
ID=29578491
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR10-2003-0008350A KR100489471B1 (en) | 2003-02-10 | 2003-02-10 | A Complex Honeycomb Filter with Carbon Nano-materials for Air Cleaning |
Country Status (1)
Country | Link |
---|---|
KR (1) | KR100489471B1 (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20060099623A (en) * | 2005-03-14 | 2006-09-20 | 김명수 | The manufacture of antimicrobial fine charcoal |
WO2006112563A2 (en) * | 2005-04-20 | 2006-10-26 | Nanophil Co., Ltd. | Filter for air cleaning and its manufacturing method |
KR100738131B1 (en) * | 2005-11-10 | 2007-07-10 | 현대자동차주식회사 | Catalyst coating method of diesel catalyzed particulate filter |
CN108993025A (en) * | 2018-06-11 | 2018-12-14 | 上海哈克过滤科技股份有限公司 | Cellular activated carbon filter and preparation method thereof |
CN113289413A (en) * | 2021-05-25 | 2021-08-24 | 九江市磐泰复合材料有限公司 | Preparation method of high-capacity fluorine glass fiber filtering material |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101527102B1 (en) | 2010-11-26 | 2015-06-10 | (주)바이오니아 | Device for eliminating harmful substance |
-
2003
- 2003-02-10 KR KR10-2003-0008350A patent/KR100489471B1/en active IP Right Grant
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20060099623A (en) * | 2005-03-14 | 2006-09-20 | 김명수 | The manufacture of antimicrobial fine charcoal |
WO2006112563A2 (en) * | 2005-04-20 | 2006-10-26 | Nanophil Co., Ltd. | Filter for air cleaning and its manufacturing method |
WO2006112563A3 (en) * | 2005-04-20 | 2008-04-03 | Nanophil Co Ltd | Filter for air cleaning and its manufacturing method |
KR100738131B1 (en) * | 2005-11-10 | 2007-07-10 | 현대자동차주식회사 | Catalyst coating method of diesel catalyzed particulate filter |
CN108993025A (en) * | 2018-06-11 | 2018-12-14 | 上海哈克过滤科技股份有限公司 | Cellular activated carbon filter and preparation method thereof |
CN113289413A (en) * | 2021-05-25 | 2021-08-24 | 九江市磐泰复合材料有限公司 | Preparation method of high-capacity fluorine glass fiber filtering material |
Also Published As
Publication number | Publication date |
---|---|
KR100489471B1 (en) | 2005-05-17 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US6623715B2 (en) | Complex shaped fiber for particle and molecular filtration | |
Li et al. | MOF-embedded bifunctional composite nanofiber membranes with a tunable hierarchical structure for high-efficiency PM0. 3 purification and oil/water separation | |
CN204816222U (en) | Air purification filter screen | |
CN108404687B (en) | Preparation method of multi-layer functional film for air purification | |
CN104587841B (en) | Conductive filter membrane and preparation method and application thereof | |
KR102230448B1 (en) | Non-woven fabric filter for reducing particulate matter and Method for preparing the same | |
Lee et al. | Polyacrylonitrile nanofiber membranes modified with Ni-based conductive metal organic frameworks for air filtration and respiration monitoring | |
KR101402604B1 (en) | Metal-Complexed carbon Menmbrane and method for preparing the same | |
Kusiak-Nejman et al. | Photocatalytic oxidation of nitric oxide over AgNPs/TiO2-loaded carbon fiber cloths | |
CN111330640B (en) | Piezoelectric catalytic membrane for air purifier and preparation method thereof | |
KR100489471B1 (en) | A Complex Honeycomb Filter with Carbon Nano-materials for Air Cleaning | |
Xu et al. | One stone two birds: a sinter-resistant TiO 2 nanofiber-based unbroken mat enables PM capture and in situ elimination | |
CN111229015A (en) | Modified chemical fiber material for impregnation, preparation method and chemical filter | |
Wang et al. | Harsh environmental-tolerant ZIF-8@ polyphenylene sulfide membrane for efficient oil/water separation and air filtration under extreme conditions | |
KR102120735B1 (en) | Membrane Comprising Metal Substrate Layer and CNT/Chitosan Nano Hybrid Coating Layer and Electrostatic Dust Collector System Comprising the Same | |
US20210322909A1 (en) | Nanoporous metal foam gas and fluid filters | |
Koh et al. | Preparation and modification of an embossed nanofibrous materials for robust filtration performance of PM0. 2 removal | |
Samantara et al. | Functionalized graphene nanocomposites in air filtration applications | |
KR100470878B1 (en) | Nano Composite Honeycomb Filter | |
KR20230088398A (en) | Air purifying device and air purifying method | |
KR100464816B1 (en) | chemical filter using ion exchange resin | |
JP2004057944A (en) | Exhaust gas cleaning equipment | |
CN206852090U (en) | A kind of MOFS materials mouth mask | |
CN106315614A (en) | Preparation method of modified Y-type molecular sieve | |
KR102529173B1 (en) | Graphene-coated cellulose paper electrode and manufacturing method for the same, and fine dust removal apparatus using cellulose paper electrode |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A201 | Request for examination | ||
E902 | Notification of reason for refusal | ||
E701 | Decision to grant or registration of patent right | ||
GRNT | Written decision to grant | ||
FPAY | Annual fee payment |
Payment date: 20130514 Year of fee payment: 9 |
|
FPAY | Annual fee payment |
Payment date: 20140423 Year of fee payment: 10 |
|
FPAY | Annual fee payment |
Payment date: 20150504 Year of fee payment: 11 |
|
FPAY | Annual fee payment |
Payment date: 20160503 Year of fee payment: 12 |
|
FPAY | Annual fee payment |
Payment date: 20170508 Year of fee payment: 13 |
|
FPAY | Annual fee payment |
Payment date: 20180502 Year of fee payment: 14 |
|
FPAY | Annual fee payment |
Payment date: 20190501 Year of fee payment: 15 |