KR100423413B1 - A chromia/titania catalyst for removing dioxins and a method of removing dioxins by usint the same - Google Patents
A chromia/titania catalyst for removing dioxins and a method of removing dioxins by usint the same Download PDFInfo
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- KR100423413B1 KR100423413B1 KR10-1999-0032743A KR19990032743A KR100423413B1 KR 100423413 B1 KR100423413 B1 KR 100423413B1 KR 19990032743 A KR19990032743 A KR 19990032743A KR 100423413 B1 KR100423413 B1 KR 100423413B1
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- 239000003054 catalyst Substances 0.000 title claims abstract description 55
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 title claims abstract description 54
- 150000002013 dioxins Chemical class 0.000 title claims abstract description 37
- 238000000034 method Methods 0.000 title claims abstract description 24
- QDOXWKRWXJOMAK-UHFFFAOYSA-N dichromium trioxide Chemical compound O=[Cr]O[Cr]=O QDOXWKRWXJOMAK-UHFFFAOYSA-N 0.000 title claims abstract description 13
- WGLPBDUCMAPZCE-UHFFFAOYSA-N Trioxochromium Chemical compound O=[Cr](=O)=O WGLPBDUCMAPZCE-UHFFFAOYSA-N 0.000 claims abstract description 20
- 229910000423 chromium oxide Inorganic materials 0.000 claims abstract description 20
- 239000002912 waste gas Substances 0.000 claims abstract description 20
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 claims abstract 8
- 238000007254 oxidation reaction Methods 0.000 claims description 10
- 230000003647 oxidation Effects 0.000 claims description 9
- 230000001590 oxidative effect Effects 0.000 abstract description 3
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 25
- 229910010413 TiO 2 Inorganic materials 0.000 description 8
- 239000000460 chlorine Substances 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 230000003197 catalytic effect Effects 0.000 description 4
- MVPPADPHJFYWMZ-UHFFFAOYSA-N chlorobenzene Chemical compound ClC1=CC=CC=C1 MVPPADPHJFYWMZ-UHFFFAOYSA-N 0.000 description 4
- 239000011651 chromium Substances 0.000 description 4
- 238000001179 sorption measurement Methods 0.000 description 4
- 229910052801 chlorine Inorganic materials 0.000 description 3
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 239000010970 precious metal Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 2
- 229910004298 SiO 2 Inorganic materials 0.000 description 2
- 231100000770 Toxic Equivalency Factor Toxicity 0.000 description 2
- 239000003463 adsorbent Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 239000002002 slurry Substances 0.000 description 2
- 231100000419 toxicity Toxicity 0.000 description 2
- 230000001988 toxicity Effects 0.000 description 2
- ISPYQTSUDJAMAB-UHFFFAOYSA-N 2-chlorophenol Chemical compound OC1=CC=CC=C1Cl ISPYQTSUDJAMAB-UHFFFAOYSA-N 0.000 description 1
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- GEIAQOFPUVMAGM-UHFFFAOYSA-N ZrO Inorganic materials [Zr]=O GEIAQOFPUVMAGM-UHFFFAOYSA-N 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 238000012824 chemical production Methods 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 125000001309 chloro group Chemical group Cl* 0.000 description 1
- 239000008119 colloidal silica Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 229910052878 cordierite Inorganic materials 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- JSKIRARMQDRGJZ-UHFFFAOYSA-N dimagnesium dioxido-bis[(1-oxido-3-oxo-2,4,6,8,9-pentaoxa-1,3-disila-5,7-dialuminabicyclo[3.3.1]nonan-7-yl)oxy]silane Chemical compound [Mg++].[Mg++].[O-][Si]([O-])(O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2)O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2 JSKIRARMQDRGJZ-UHFFFAOYSA-N 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 229910052737 gold Inorganic materials 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000003987 high-resolution gas chromatography Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- -1 of isomers (Polychlorinated Dibenzo Furans Chemical class 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000008188 pellet Substances 0.000 description 1
- 229910052697 platinum Inorganic materials 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 231100000916 relative toxicity Toxicity 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 238000010998 test method Methods 0.000 description 1
- 231100000167 toxic agent Toxicity 0.000 description 1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/16—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J23/24—Chromium, molybdenum or tungsten
- B01J23/26—Chromium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8668—Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20707—Titanium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20784—Chromium
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Biomedical Technology (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Health & Medical Sciences (AREA)
- Materials Engineering (AREA)
- Organic Chemistry (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Abstract
본 발명은 다이옥신 제거용 크로미아/타이타니아 촉매 및 이를 이용한 다이옥신 제거 방법에 관한 것으로,The present invention relates to a chromia / titania catalyst for dioxin removal and a dioxin removal method using the same,
타이타니아 담체상에 촉매의 총중량을 기준으로 크롬 산화물 1∼50중량%가 담지된 다이옥신 제거용 크로미아/타이타니아 촉매, 및Chromia / titania catalyst for dioxin removal, on which 1 to 50% by weight of chromium oxide is supported on a titania carrier, and
200℃이상의 산화분위기하에 상기 다이옥신 제거용 크로미아/타이타니아 촉매에 처리하고자 하는 다이옥신-함유 폐가스를 공간 속도 5,000hr-1이하로 통과시켜 다이옥신을 산화 제거하는 방법이 제공된다.Provided is a method for oxidizing and removing dioxins by passing a dioxin-containing waste gas to be treated at a dioxin removal chromia / titania catalyst at a temperature of 200 ° C. or higher at a space velocity of 5,000 hr −1 or less.
본 발명에 의하면, 타이타니아에 크롬 산화물을 담지시킨 촉매를 사용함으로써 폐가스 등에 함유된 다이옥신을 보다 효율적으로 제거할 수 있다.According to the present invention, dioxins contained in the waste gas and the like can be more efficiently removed by using a catalyst in which chromium oxide is supported on titania.
Description
본 발명은 다이옥신 제거용 크로미아/타이타니아 촉매 및 이를 이용한 다이옥신 제거 방법에 관한 것으로, 보다 상세하게는 타이타니아 담체상에 크롬 산화물이 담지되어 있는 촉매 및 이를 이용하여 폐가스에 함유된 다이옥신을 효과적으로 제거하는 방법에 관한 것이다.The present invention relates to a chromia / titania catalyst for dioxin removal and a dioxin removal method using the same. More particularly, a catalyst in which chromium oxide is supported on a titania carrier and a method for effectively removing dioxin contained in waste gas using the same. It is about.
다이옥신은 75종의 이성질체가 있는 다이옥신류(Polychlorinated Dibenzo-p-Dioxines, PCDDs)와 135종의 이성질체가 있는 퓨란류(Polychlorinated Dibenzo Furans, PCDFs)를 총칭하여 표현하는 의미로서, 이들 물질들은 염소의 치환 개수혹은 위치에 따라 서로 다른 성질을 갖지만 통상 다이옥신이라고 총칭한다.Dioxin is the generic name for 75 isomers (Polychlorinated Dibenzo-p-Dioxines, PCDDs) and 135 kinds of isomers (Polychlorinated Dibenzo Furans, PCDFs). Although they have different properties depending on the number or location, they are generally referred to as dioxins.
상기 다이옥신은 지용성이고 물에 잘 녹지 않아서 미생물 분해가 어려운 매우 안정한 상태이므로, 자연계에서는 거의 분해되지 않아 그 독성이 실질적으로 거의 영구적이어서 심각한 환경 오염원으로서 알려져 있다.Since the dioxins are fat-soluble and insoluble in water, and very difficult to disintegrate microorganisms, they are hardly decomposed in the natural world, and their toxicity is substantially almost permanent, which is known as a serious environmental pollutant.
상기 총 210가지의 다이옥신 이성질체들이 모두 유사한 물리적, 화학적 성질들을 갖지만 그 독성에 있어서는 각기 차이가 있다. 이중에서도 가장 독성이 큰 것으로 알려진 화합물은 염소 치환 개수가 4개인 2,3,7,8-TCDD로서, 몇몇 나라에서는 다이옥신의 위해성을 평가하기 위해서 상기 2,3,7,8-TCDD를 기준으로 여러 종류의 다이옥신에 대한 상대적 독성을 구하고 그 값을 TEF(Toxidity Equivalency Factors, 독성 등가지수)로 정하고 있다. 이를 이용하여 다이옥신류의 농도를 다음과 같은 TEQ (Toxic Equivalents)개념으로 표현하는 것이 일반적이다.A total of 210 dioxins isomers all have similar physical and chemical properties but differ in their toxicity. Among the most toxic compounds known to be 2,3,7,8-TCDD with 4 chlorine substitutions, in some countries, the 2,3,7,8-TCDD was used to assess the risk of dioxins. The relative toxicity of various types of dioxins is calculated and its value is set as TEF (Toxidity Equivalency Factors). It is common to express the concentration of dioxins using the following concept of TEQ (Toxic Equivalents).
상기 다이옥신류의 주오염원은 각 나라마다 다르겠지만, 크게 화학물질 제조, 소각공정, 열공정 등으로 나눌 수 있다. 다이옥신류는 염소 유기화학제품의 생산 및 사용도중 부산물로 생성가능하며, 생성된 염소 유기화학제품에도 다이옥신류가 함유될 수 있다. 또한 소각을 포함한 모든 열공정은 클로로페놀과 그 유도체의 중요 생성원이 되며, 이는 곧 다이옥신의 발생을 유도할 수 있다.The main sources of dioxins vary from country to country, but can be broadly divided into chemical production, incineration, and thermal processes. Dioxins may be produced as by-products during the production and use of chlorine organic chemicals, and dioxins may also be contained in the produced chlorine organic chemicals. All thermal processes, including incineration, are also important sources of chlorophenol and its derivatives, which can lead to the generation of dioxins.
따라서 소각로 등의 폐가스에 함유되어 배출되는 다이옥신을 제거하기 위한 여러 방법들이 개발되어 왔다. 그중 대표적인 방법이 활성탄과 같은 흡착제로 다이옥신을 흡착 제거하는 방법과 촉매에 의한 산화방법에 의해 다이옥신을 분해하여 제거하는 방법이다.Therefore, various methods have been developed to remove dioxins contained in waste gases such as incinerators. Representative methods include adsorption and removal of dioxins with an adsorbent such as activated carbon, and methods of decomposing and removing dioxins by oxidation by a catalyst.
상기 활성탄을 이용한 흡착법은 많이 사용되고 있는 방법이지만, 폐가스에 함유된 물과 같은 다른 성분들에 의해 흡착능력이 크게 영향을 받으며, 흡착 완료후 다이옥신을 포함하고 있는 흡착제들을 처리해야 하는 문제점이 있다. 따라서 촉매를 이용한 산화 공정이 다이옥신 제거 방법으로 주목되어 왔다.The adsorption method using the activated carbon is a widely used method, but the adsorption capacity is greatly affected by other components such as water contained in the waste gas, and there is a problem in that the adsorbents containing dioxins must be treated after the adsorption is completed. Therefore, the oxidation process using a catalyst has been attracting attention as a dioxin removal method.
여기서 촉매를 이용한 다이옥신의 완전분해 방법은 다이옥신-함유 가스를 촉매층에 흘려보내 폐가스내에 함께 존재하는 산소와의 산화반응에 의해 다이옥신을 CO2와 H2O, 그리고 HCl 혹은 Cl2로 분해시켜 제거하는 방법이다.Here, the method of completely decomposing dioxins using a catalyst is to remove dioxins into CO 2 and H 2 O, and HCl or Cl 2 by oxidative reaction with oxygen present in the waste gas by flowing a dioxin-containing gas into the catalyst layer. It is a way.
촉매를 사용한 산화방법에 의해 다이옥신을 제거하는데 사용되는 촉매로는 일반적으로 암모니아와 같은 환원제를 이용하여 폐가스중의 질소 산화물을 제거하는 V2O5-WO3-TiO2계 촉매가 많이 사용되고 있다. 공지문헌인 "Chemosphere", Vol.26, No.12, pp.2167-2172, 1993을 보면, NOx를 제거하는데 V2O5-WO3-TiO2계 촉매를 사용하면 200∼350℃의 온도 범위에서 다이옥신을 제거할 수 있다고 개시되어 있다. 또한 일본 특허 제95-75720호를 보면, V2O5-WO3-TiO2로 이루어진 촉매를 사용하여 200∼250℃의 온도 범위에서 다이옥신을 제거한다고 개시되어 있다.As a catalyst used to remove dioxins by an oxidation method using a catalyst, generally, a V 2 O 5 -WO 3 -TiO 2 based catalyst which removes nitrogen oxides in waste gas by using a reducing agent such as ammonia is widely used. In the well-known document "Chemosphere", Vol. 26, No. 12, pp. 2167-2172, 1993, the temperature of 200-350 ° C. is used when V 2 O 5 -WO 3 -TiO 2 -based catalyst is used to remove NOx. It is disclosed that dioxins can be removed in the range. In addition, Japanese Patent No. 95-75720 discloses that dioxins are removed in a temperature range of 200 to 250 ° C using a catalyst composed of V 2 O 5 -WO 3 -TiO 2 .
한편, 미국특허 제5,254,794호에서는 TiO2, SiO2, ZrO2등으로 이루어진 담체에 Pt와 같은 귀금속을 담지한 촉매를 사용하여 다이옥신을 제거한다고 개시되어 있다. 그리고 일본 특허 제95-163877호 및 유럽 특허 0,645,172A1에서는 SiO2-B2O3-Al2O3등으로 이루어진 담체에 Pt, Au와 같은 두가지 금속을 담지한 촉매를 사용하고 있는데, 이 경우 V2O5-WO3-TiO2촉매나 TiO2에 Pt를 담지한 촉매보다 훨씬 성능이 우수한 것으로 개시하고 있다.On the other hand, US Patent No. 5,254,794 discloses the removal of dioxins using a catalyst supporting a precious metal such as Pt on a carrier made of TiO 2 , SiO 2 , ZrO 2 , and the like. In Japanese Patent No. 95-163877 and European Patent 0,645,172 A1, a catalyst having two metals such as Pt and Au is used on a carrier made of SiO 2 -B 2 O 3 -Al 2 O 3 . It is disclosed that the performance is much higher than that of a catalyst supported by 2O 5 -WO 3 -TiO 2 or Pt supported on TiO 2 .
그러나 이들 V2O5-WO3-TiO2촉매나 귀금속 담지 촉매들은 단가가 매우 높으므로 보다 경제적이면서 다이옥신 제거에 우수한 성능을 나타내는 촉매가 여전히 요구시된다.However, since these V 2 O 5 -WO 3 -TiO 2 catalysts and precious metal supported catalysts are very expensive, there is still a need for a catalyst that is more economical and shows excellent performance in dioxin removal.
이에 본 발명의 목적은 종래의 V2O5-WO3-TiO2촉매나 귀금속 담지 촉매에 비해 보다 저렴하며 다이옥신 제거에 우수한 성능을 나타내는 타이타니아 담체에 크롬 산화물이 담지된 촉매를 제공하려는데 있다.Accordingly, an object of the present invention is to provide a catalyst in which chromium oxide is supported on a titania carrier which is cheaper than a conventional V 2 O 5 -WO 3 -TiO 2 catalyst or a precious metal supported catalyst and exhibits excellent performance in removing dioxins.
본 발명의 다른 목적은 타이타니아 담체에 크롬 산화물이 담지된 촉매를 사용하여 폐가스내에 함유되어 있는 다이옥신을 효과적으로 제거하는 방법을 제공하고자 하는데 있다.Another object of the present invention is to provide a method for effectively removing dioxins contained in waste gas by using a catalyst in which chromium oxide is supported on a titania carrier.
도 1은 본 발명의 방법에 의해 크로미아/타이타니아 촉매를 사용할 경우 반응 온도에 따른 다이옥신 제거율을 나타낸 그래프이고,1 is a graph showing the dioxin removal rate according to the reaction temperature when using the chromia / titania catalyst by the method of the present invention,
도 2는 본 발명의 방법에 의해 크로미아/타이타니아 촉매를 사용할 경우 공간 속도에 따른 다이옥신 제거율을 나타낸 그래프이다.Figure 2 is a graph showing the dioxin removal rate according to the space velocity when using the chromia / titania catalyst by the method of the present invention.
본 발명의 일견지에 의하면,According to one aspect of the invention,
타이타니아 담체상에 촉매의 총중량을 기준으로 크롬 산화물 1∼50중량%가 담지된 다이옥신 제거용 크로미아/타이타니아 촉매가 제공된다.There is provided a chromia / titania catalyst for dioxin removal, carrying 1 to 50% by weight of chromium oxide, based on the total weight of the catalyst on a titania carrier.
본 발명의 제2 견지에 의하면,According to the second aspect of the present invention,
200℃이상의 산화분위기하에 상기 제 일견지의 다이옥신 제거용 크로미아/타이타니아 촉매에 처리하고자 하는 다이옥신-함유 폐가스를 공간 속도 5,000hr-1이하로 통과시켜 다이옥신을 산화 제거하는 방법이 제공된다.Provided is a method for oxidizing and removing dioxins by passing a dioxin-containing waste gas to be treated to the dioxin removing chromia / titania catalyst of the first aspect under an oxidation atmosphere of 200 ° C. or higher at a space velocity of 5,000 hr −1 or less.
이하, 본 발명을 상세히 설명한다.Hereinafter, the present invention will be described in detail.
폐가스 등에 함유된 다이옥신을 제거하기 위해서는 우선 타이타니아 담체상에 촉매의 총중량을 기준으로 크롬 산화물 1∼50중량%를 담지시킨 촉매를 제조한다.In order to remove dioxins contained in the waste gas and the like, first, a catalyst having 1 to 50% by weight of chromium oxide based on the total weight of the catalyst on a titania carrier is prepared.
여기서 상기 크롬 산화물은 일반적으로 산화수가 3가인 Cr2O3와 산화수가 6가인 CrO3가 혼합된 형태로 존재하며 이들 양자 모두 사용가능하나, 6가의 비율이 높을수록 촉매활성이 높으므로 CrO3형태의 비율이 높은 것이 보다 바람직하다.Wherein the chromium oxide is therefore usually oxidation number trivalent Cr 2 O 3 and the oxidation state is 6 Cain CrO 3 is present in a mixed form, and one or all of the both can be used, the higher the hexavalent ratio higher catalytic activity as CrO 3 form It is more preferable that the ratio of is high.
상기 크롬 산화물의 담지량은 촉매의 총중량을 기준으로 1∼50중량%이며, 바람직하게는 5∼40중량%이다. 크롬 산화물의 함량이 너무 낮게 되면 크롬 산화물에 의한 효과가 적어 촉매 활성이 낮으며, 50중량%를 초과하면 크롬 산화물이 촉매 표면에 잘 분산되지 않기 때문에 촉매 활성이 오히려 크게 감소하게 되므로 바람직하지 않다.The supported amount of chromium oxide is 1 to 50% by weight, preferably 5 to 40% by weight based on the total weight of the catalyst. If the content of chromium oxide is too low, the effect of chromium oxide is low and the catalytic activity is low. If the content of chromium oxide is more than 50% by weight, chromium oxide does not disperse well on the surface of the catalyst.
이와 같이 제조된 촉매를 이용하여 다이옥신을 제거시 사용하는 촉매의 형태는 특별히 제한하는 것은 아니나, 미세한 분말 혹은 펠릿 형태, 혹은 촉매를 필터나 하니콤형 반응기에 코팅하거나 직접 하니콤형 반응기로 성형하여 사용할 수 있다.The type of catalyst used for removing dioxins using the catalyst prepared as described above is not particularly limited, but may be used in the form of a fine powder or pellet, or the catalyst may be coated on a filter or a honeycomb reactor or directly molded into a honeycomb reactor. have.
상기와 같은 크로미아/타이타니아 촉매는 폐가스중의 다이옥신 화합물 제거에 사용된다. 이때 크로미아/타이타니아 촉매는 200℃이상의 산화분위기하에 다이옥신-함유 폐가스를 통과시켜 다이옥신을 산화시킨다. 200℃이하의 온도에서는 촉매의 활성이 감소되므로 효과적이지 않다. Such chromia / titania catalysts are used to remove dioxins in waste gas. At this time, the chromia / titania catalyst oxidizes dioxin by passing a dioxin-containing waste gas under an oxidation atmosphere of 200 ° C. or higher. At temperatures below 200 ° C., the activity of the catalyst is reduced and therefore not effective.
이와 같이 200℃이상의 온도에서 처리하고자 하는 다이옥신-함유 폐가스를 통과시키면 하기식 1 내지는 2와 같은 산화반응에 의해 다이옥신이 분해되어 제거된다. 또한 이때 공간 속도는 다이옥신의 제거 효율이 99%정도가 되도록 최대 5,000hr-1정도인 것이 바람직하다.As such, when the dioxin-containing waste gas to be treated at a temperature of 200 ° C. or more is passed, dioxin is decomposed and removed by an oxidation reaction such as the following Formulas 1 to 2. In this case, the space velocity is preferably about 5,000hr −1 at maximum so that the removal efficiency of dioxins is about 99%.
이하, 실시예를 통하여 본 발명을 상세히 설명한다.Hereinafter, the present invention will be described in detail through examples.
<실시예><Example>
하기 실시예는 나아가 본 발명의 다양한 견지를 예시하는 것으로, 본 발명의 범위를 이에 한정하는 것은 아니다.The following examples further illustrate various aspects of the invention and do not limit the scope thereof.
실시예 1 :크롬 산화물 담지량에 따른 클로로벤젠의 제거율Example 1: Removal rate of chlorobenzene according to the amount of chromium oxide supported
Cr(NO3)3ㆍ9H2O 1.3g을 증류수에 녹인 다음 110℃에서 건조시킨 타이타니아 50g에 가하면서 잘 혼합시켰다. 이 슬러리 용액을 가열하여 완전 건조시킨 다음 110℃ 건조기에서 재차 완전 건조시키고, 450℃의 공기중에서 소성시켜 촉매의 총중량 기준으로 크롬 산화물 1%가 담지된 촉매를 제조하였다.1.3 g of Cr (NO 3 ) 3 9H 2 O was dissolved in distilled water and then mixed well with 50 g of titania dried at 110 ° C. The slurry solution was completely dried by heating, then completely dried again in a 110 ° C. drier, and calcined in air at 450 ° C. to prepare a catalyst having 1% of chromium oxide based on the total weight of the catalyst.
마찬가지 방법으로 크롬 산화물이 촉매의 총중량을 기준으로 5, 12, 25, 40, 50%인 촉매를 제조하였다.In a similar manner, catalysts were prepared in which the chromium oxide was 5, 12, 25, 40, 50% based on the total weight of the catalyst.
이와 같이 제조된 촉매들을 고정층 연속 흐름식 반응기를 사용하여 반응 온도 250℃, 공간속도(유량/촉매부피) 30,000hr-1에서 다이옥신과 구조는 유사하나 분해하기는 더 어려운 클로로벤젠 30ppm이 공기중에 포함된 가스를 모사반응물로 사용하여 제거 효율을 측정하고 그 결과를 하기표 1에 나타내었다.The catalysts prepared in this manner contained 30 ppm of chlorobenzene in air, which is similar in structure to Dioxin but more difficult to decompose, at a reaction temperature of 250 ° C. and a space velocity (flow rate / catalytic volume) of 30,000hr −1 using a fixed bed continuous flow reactor. The removed gas was used as a simulated reactant to measure the removal efficiency and the results are shown in Table 1 below.
상기표 1에서 보듯이, 크롬 산화물의 함량이 증가함에 따라 제거율도 증가하나, 40%이상이 되면 제거율이 감소되는 것을 알 수 있다.As shown in Table 1, as the content of the chromium oxide increases, the removal rate also increases, but it can be seen that the removal rate decreases when more than 40%.
실시예 2:반응온도에 따른 폐가스중의 다이옥신 제거율Example 2 Dioxin Removal Rate in Waste Gas According to Reaction Temperature
담체인 분말 형태의 타이타니아에 물을 첨가한 후 여기에 콜로이드 형태의 실리카를 바인더로서 타이타니아 중량을 기준으로 약10% 정도 첨가하였다.Water was added to powdered titania, which is a carrier, and about 10% by weight of titania was added as a binder in the form of colloidal silica.
이 슬러리 용액을 잘 혼합하면서 코디어라이트(Cordierite) 재질의 하니콤형 반응기를 침지후 꺼내서 타이타니아가 하니콤 표면에 코팅되도록 한 다음 건조기에서 건조시켰다.The honeycomb reactor made of Cordierite was immersed and removed while the slurry solution was mixed well, and the titania was coated on the honeycomb surface, and then dried in a dryer.
이와 같이 하여 타이타니아가 코팅된 하니콤 반응기를 물에 용해된 Cr(NO3)3용액에 침지후 꺼내서 건조시킴으로써 Cr(NO3)3가 표면에 담지된 촉매를 제조하였다. 이와 같이 제조된 촉매를 450℃에서 공기중에서 소성하여 사용하였다.Thus, a catalyst having Cr (NO 3 ) 3 supported on the surface thereof was prepared by immersing the Titania-coated honeycomb reactor in Cr (NO 3 ) 3 solution dissolved in water, followed by drying. The catalyst thus prepared was calcined in air at 450 ° C. and used.
상기와 같이 제조된 촉매를 사용하여 NOx 200ppm 및 다이옥신 1∼3ng/Nm³이 함유된 연소 폐가스에 존재하는 다이옥신의 제거 효율을 측정하였다. 제거율 실험은 약 700Nm3/hr의 폐가스를 처리할 수 있는 파일럿 장치에서 실시하였으며, 촉매 반응기 입출구의 다이옥신 농도를 측정함으로써 제거율을 분석하였다.The removal efficiency of dioxins present in the combustion waste gas containing 200 ppm of NOx and 1 to 3 ng / Nm³ of NOx was measured using the catalyst prepared as described above. The removal rate experiment was carried out in a pilot apparatus capable of treating about 700 Nm 3 / hr of waste gas, and the removal rate was analyzed by measuring the dioxin concentration at the catalytic reactor inlet and outlet.
폐가스에 포함된 다이옥신의 농도 측정은 국내 대기오염 공정 시험법에 나와있는 방법에 따라 폐가스를 채집하고, 정제와 농축 과정을 거친 후 고분해능 가스 크로마토그래피/질량분석기(GC/MS)를 이용하여 분석하였다.The concentration of dioxins contained in the waste gas was analyzed using high resolution gas chromatography / mass spectrometer (GC / MS) after collecting waste gas, purifying and concentrating according to the method described in the domestic air pollution process test method. .
상기와 같이 촉매 반응기 입출구에서 공간속도(유량/촉매 반응기 부피)가 5,000hr-1인 조건하에 반응 온도를 달리하면서 다이옥신 농도를 분석하여 측정한 결과를 도 1에 도시하였다.As described above, the results obtained by analyzing the dioxin concentration while varying the reaction temperature under the condition that the space velocity (flow rate / catalyst reactor volume) is 5,000hr −1 at the catalyst reactor inlet and outlet are shown in FIG. 1.
도 1에서 보듯이, 온도 증가에 따라 다이옥신의 제거율은 증가하였으며, 325℃이상에서는 더이상 효율은 개선되지 않았으며, 다이옥신의 제거율은 99%에 달함을 알 수 있다.As shown in Figure 1, the removal rate of dioxins increased with increasing temperature, the efficiency was no longer improved at more than 325 ℃, it can be seen that the removal rate of dioxins reaches 99%.
실시예 3 : 공간 속도에 따른 다이옥신 제거율Example 3 Dioxin Removal Rate According to Space Velocity
325℃에서 공간 속도를 달리한 것을 제외하고는 실시예 2와 동일한 방법을 반복하여 다이옥신 제거율 변화를 측정하고, 그 결과를 도 2에 도시하였다.Except that the space velocity was changed at 325 ℃, the same method as in Example 2 was repeated to measure the change in dioxin removal rate, the results are shown in FIG.
도 2에서 보듯이, 공간속도가 5,000hr-1이하일 경우에 다이옥신 제거율이 99%정도로 매우 우수하다는 것을 확인할 수 있다.As shown in Figure 2, when the space velocity is 5,000hr -1 or less, it can be seen that the dioxin removal rate is very excellent, about 99%.
상기한 바에 따르면, 타이타니아에 크롬 산화물을 적정량 담지시킨 촉매를 사용함으로써 폐가스 등에 함유된 다이옥신을 보다 효율적으로 제거할 수 있다.According to the above, it is possible to more efficiently remove dioxins contained in the waste gas and the like by using a catalyst in which a suitable amount of chromium oxide is supported on titania.
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