[go: up one dir, main page]

TW201134549A - Preparation of zirconia-ceria-supported nano-palladium catalysts and its application in destruction of volatile organic compounds in air - Google Patents

Preparation of zirconia-ceria-supported nano-palladium catalysts and its application in destruction of volatile organic compounds in air Download PDF

Info

Publication number
TW201134549A
TW201134549A TW099111548A TW99111548A TW201134549A TW 201134549 A TW201134549 A TW 201134549A TW 099111548 A TW099111548 A TW 099111548A TW 99111548 A TW99111548 A TW 99111548A TW 201134549 A TW201134549 A TW 201134549A
Authority
TW
Taiwan
Prior art keywords
catalyst
temperature
hours
oxide
oxidized
Prior art date
Application number
TW099111548A
Other languages
Chinese (zh)
Inventor
Yu-Wen Chen
Yi-Wen Chen
Original Assignee
Univ Nat Central
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Univ Nat Central filed Critical Univ Nat Central
Priority to TW099111548A priority Critical patent/TW201134549A/en
Publication of TW201134549A publication Critical patent/TW201134549A/en

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Catalysts (AREA)

Abstract

This invention declares the preparation of zirconium-cerium dioxide-supported nano-palladium catalysts and the process of destruction of volatile organic compounds in air stream to remove volatile organic compounds using zirconium-cerium dioxide-supported nano palladium catalysts. The palladium particle size is between 2 and 6 nm and supported on mixed oxide ZrO2-CeO2. Zr/Ce molar ratios are between 1/9 and 5/5. Destruction of volatile organic compounds in air stream over these catalysts is carried out in a fixed bed reactor to remove volatile organic compounds.

Description

201134549 無指定代表圖 五、本案若有化學鱗’請揭示最能齡㈣ w% Pd/ Cei-xZrx〇2為本發明製備之觸媒,w ^ ^ ·201134549 No representative representative figure 5. If there is chemical scale in this case, please reveal the most age (4) w% Pd/ Cei-xZrx〇2 is the catalyst prepared by the invention, w ^ ^ ·

Cei-XZrx02)中之把佔全部觸媒重量之百分率,’χ二° $ =為賴耳數’一:1,觸媒==Cei-XZrx02) is the percentage of total catalyst weight, 'χ二° $ = 赖耳' one: 1, catalyst ==

CnHm + m/2 〇2 + n C02 + ⑽ η2〇 〇CnHm + m/2 〇2 + n C02 + (10) η2〇 〇

以上為此項發餐化學反應式,其巾Cniim騎機廢氣之成分。 六、發明說明: 【發明所屬之技術領域】 本發明揭示-種製備承載於氧化錯及二氧化鈽之把觸媒方 法,及-種在奈恤承氧化做二氧化鈽之觸聰化下,在 空氣中有機廢氣與氧氣反應以去除有機廢氣之方法;其中錯及飾 係依不同莫耳比例混合,錯/鈽莫耳比為1/9至5/5之間,承載之 ㈣粒直徑為2與6奈米之間;本發明以含杨/氧化錯_二氧^ _媒在有機廢氣於空齡,使㈣絲反應^,叫除有機廢 氣。 x 【先前技術】 近年由於工業發展迅速帶動經濟成長,相對也造成環境的 污染,_是轉體產業絲造雕中料献量揮發性有機物 (VolatUe 0rganic c〇mp〇unds,v〇Cs)逸散於空氣中,伴隨而 來的污染是業界無法聽的。職是指含雜⑽之=甲 2 201134549 烷碳氫的揮發物質,如苯、甲苯、含氮之胺類等等,在正常情況 下,沸點在25(TC以下。而VOCs大部分屬於有害性空氣污染物, 人體長期曝露於VOCs的環境中,即使在低濃度下,也會產生中 母或致癌性腫瘤等現象。此外,大氣中的v〇Cs具高度光化學活 ]生[由糸外光照射產生臭氧、PAN (per〇xy acethy 1 trate)、 PM Cpemxy benzene nitrate)等高氧化性污染物,對人體的刺 ΟThe above is the chemical reaction type of this meal, and the composition of the towel Cniim rider exhaust. VI. Description of the Invention: [Technical Field to Which the Invention Is Applicable] The present invention discloses a method for preparing a catalyst supported by oxidizing and cerium oxide, and a species in which the cerium is oxidized to make cerium oxide. A method in which organic waste gas reacts with oxygen in the air to remove organic waste gas; wherein the wrong and the decorative system are mixed according to different molar ratios, and the wrong/钸 molar ratio is between 1/9 and 5/5, and the (four) particle diameter is Between 2 and 6 nm; the present invention contains the organic waste gas at the age of the organic waste gas in the presence of the oxidized oxidized _dioxane medium, and the organic gas is removed. x [Prior Art] In recent years, due to the rapid development of industrial development, the economic growth has also caused environmental pollution. _ is the volatile organic matter in the silk carving industry (VolatUe 0rganic c〇mp〇unds, v〇Cs) Scattered in the air, the accompanying pollution is inaudible to the industry. Jobs refer to volatile substances containing aza (10) = A 2 201134549 alkane hydrocarbons, such as benzene, toluene, nitrogen-containing amines, etc. Under normal conditions, the boiling point is below 25 (TC). VOCs are mostly harmful. Air pollutants, long-term exposure to VOCs in the human body, even at low concentrations, can cause mid-mother or carcinogenic tumors. In addition, the v〇Cs in the atmosphere are highly photochemically active [from the outside Light irradiation produces high oxidizing pollutants such as ozone, PAN (per〇xy acethy 1 trate), PM Cpemxy benzene nitrate, etc.

激性與危害性細,因此,如何降低這些污染物對環境及人體的 傷害’是研究者須努力的目標。 VOCs的處理方法大致可分為以下兩種:一為破壞 (destnictiQn) ’其包括高溫與觸媒減賴原,以及生物遽床 法’在此機制下將有機污祕轉化為二氧化碳和水丨另一為回收 (聰败y),彻魏、_冷凝與薄齡料方法,將污染物 自排放廢氣中轉移或回收,使其成為乾淨氣體。早期對勵大 =使用南溫燃燒法處理’且在氧氣充足、溫度和反應時間均足夠 化,任何碳氫化合物皆可經由燃燒過程而氧化成二氧化碳和水, 惡臭的氣體均能經燃燒成為無味無害的氣體,而排放至大氣中, 機揮發性氣麵卿,各__料同,因此以燃燒方 里有機揮發性氣體所需達到的爐内溫度亦不同,対多種有 #作發以體混合’姆溫度及條件較加複雜’—般直燃爐的 =度料氣七邱九百度甚至更高才能去除大部份的 理L但加熱同時也需耗去大量能源(電熱、柴油),因此造成處 的增加。所以目前1上大辣_雜燒法去除V0Cs, 3 201134549 觸媒燃燒法比直接燃燒法的優點為:⑴可低溫處理有機污染物 (2)能源效率高⑶產物對環境無污染(產物為二氧化碳和水)。 處理有機污染物之觸媒主要分為⑴低活性但是價位便宜的 金屬氧化物(Cr03、Exciting and harmful, so how to reduce the harm of these pollutants to the environment and the human body is the goal that researchers must work hard. The treatment methods of VOCs can be roughly divided into the following two types: one is destruction (destnictiQn) 'it includes high temperature and catalytic reduction, and the biological trampoline method' converts organic pollution into carbon dioxide and water in this mechanism. One is for recycling (constant y), Che Wei, _ condensation and thinner materials method, the pollutants are transferred or recovered from the exhaust gas to make it a clean gas. In the early stage, it was treated with the south temperature combustion method and was sufficient in oxygen, temperature and reaction time. Any hydrocarbon can be oxidized into carbon dioxide and water through the combustion process, and the malodorous gas can be burned to become odorless. Harmless gas, and discharged into the atmosphere, the machine volatile gas surface, each __ the same, so the temperature of the furnace to achieve the organic volatile gas in the burning side is also different, 対 a variety of Mixing 'm temperature and conditions are more complicated' - the direct burning furnace = the gas of Qi Qiu Jiu Baidu or even higher to remove most of the L but heating also consumes a lot of energy (electric heating, diesel), Therefore, the increase is caused. Therefore, at present, the advantages of the catalyzed combustion method are that the V0Cs are removed, and the advantages of the direct combustion method are: (1) low temperature treatment of organic pollutants (2) high energy efficiency (3) no pollution to the environment (product is carbon dioxide) And water). Catalysts for handling organic pollutants are mainly classified into (1) low-activity but inexpensive metal oxides (Cr03,

CuO)及(2)高活性’但是價位也高的貴重金屬CuO) and (2) high activity, but expensive metals

(Pt、Rh、Pd、Ag、Au),本報告選擇蝴媒是縣相較於其他貴 重金屬(Pt、Ag、Au、Rh),免觸媒擁有⑴較低價格⑺好的氧化 活性⑶高溫耐久性,騎重金屬,原子序46,週絲上和銘、 鎳同族,與錢、朗列’蚁—種過渡金屬,灰白色,延展性極 好’易於泣,其㈣伽,但_綠射其他元素更易受酸 賴,把·點達18观可耐高溫,工業上,纪-般是作為精 選銅和_石時的副產品㈣得的。另外,它可吸取自己體積· 倍的氫氣。擔體_的研究是觸_化反射極為重要的主題, 藉由擔體的支射明加觸潍成分的表面積,改變觸媒的性(Pt, Rh, Pd, Ag, Au), the choice of the butterfly in this report is compared with other precious metals (Pt, Ag, Au, Rh), free from catalyst (1) lower price (7) good oxidation activity (3) high temperature Durability, riding heavy metal, atomic order 46, Zhousi Shang and Ming, nickel family, with money, Lang Li 'ant-species transition metal, gray white, excellent ductility' easy to weep, its (four) gamma, but _ green shoot other The elements are more susceptible to acid stagnation, and the point is up to 18 degrees to withstand high temperatures. Industrially, it is generally used as a by-product of selected copper and _shishi (four). In addition, it can absorb hydrogen in its own volume. The study of the support _ is a very important subject of the touch-reflection, and the nature of the catalyst is changed by the surface of the support and the surface area of the touch component.

質,增加反應的活性及選擇性,大構低貴重金屬觸媒的製備成 本。 甲苯是-種澄清、無色的液體,具有嶋的味道,與苯同為 芳香族碳氫化合物’麵今實際應财f常代財相#毒性的苯 作為有機溶劑使用’他的許多性f跟苯很相像,但與笨的氧化反 應不同’甲苯的氧化反應並不在苯環上,而在甲基上發生。因此 甲苯的氧化產物n極少量在苯的氧化反應巾財出現的副 產品(具有強致癌性的環氧化物>wu [Catal Today第63卷⑼州 第419頁至426頁]等人發現以活性碳作為擔體的白金觸媒,可將 4 201134549 甲本元全氧化於低溫200°C以下,其中活性碳可於氮氣流中加熱 至400 C或800 C,並且用氳氟酸清洗去除表面雜質或礦物質。Quality, increase the activity and selectivity of the reaction, and the cost of preparation of a large structure of low precious metal catalyst. Toluene is a kind of clarified, colorless liquid with a scent of scent, and it is an aromatic hydrocarbon with benzene. In fact, it should be used as an organic solvent. Benzene is very similar, but unlike the stupid oxidation reaction, the oxidation reaction of toluene does not occur on the benzene ring but on the methyl group. Therefore, the oxidation product n of toluene is extremely small in the by-product of oxidation reaction of benzene (epoxy with strong carcinogenicity > wu [Catal Today, Vol. 63 (9), pp. 419-426], etc. Carbon as a platinum catalyst for the support, can fully oxidize 4 201134549 A low temperature below 200 ° C, wherein the activated carbon can be heated to 400 C or 800 C in a nitrogen stream, and cleaned with fluoric acid to remove surface impurities Or minerals.

Luo [Appl. Catal. B: Environ.第 69 卷(2007)第 213 頁至 218 頁]等 人以Ce〇rY2〇共氧化物做為擔體製備鈀觸媒’並將觸媒以水洗 塗佈附著於蜂窩狀陶瓷上,發現以5〇〇。〇鍛燒的觸媒可於21〇〇C 將曱苯完全氧化,觸媒除了要活性好之外其耐久性也是很重要的 因素,研究者將觸媒在200至240°C之間重複升溫降溫川艺共8 〇 次’在此30小時内發現觸媒活性並無明顯的改變,顯示出其重 複性與穩定性。Hosseini [Catalysis Today,第 122 卷(2007)第 391 頁至396頁]等人則分別利用沉積沉殺法與含浸法,將金與纪擔載 於具多孔性結構的高表面積二氧化鈦擔體上,其活性大小為 0.5%Pd-l%Au/TiO2>1.5% Pd/ TiO2>0.5% Pd/ Ti02>l% Au -0.5% Pd/ Ti02 > 1% Au/Ti02 > Ti02,活性最佳的 〇.5%Pd-l%Au/Ti〇2能在230 °C將甲苯完全氧化。Liu等人 D [Journal of Hazardous Materials,第 149 卷(2007)第 742 頁至 746 頁]則將氧化鋁與利用共沉澱法製備的二氧化鈽與二氧化鍅共氧 化物做為混合擔體,並推雜紀與猛做為添加物,利用含浸法製備 白金觸媒’實驗證明以釔與錳做為添加物的 Pt^AlzCVCeojZi^Yo.iMniuOx觸媒有較高的活性,於216。(:時甲 苯完全氧化的轉化率能達到90 %。Zheng等人[Catal. Comrmm. 第9卷(2008)第990頁至994頁]利用不鏽鋼作為擔體,以陽極氧 化程序做製備,並且鍛燒於⑺⑻它下,可得活性最佳觸媒,對甲 5 201134549 本元全轉化溫度為21〇c。Qingba〇等人[Chin J Catal.第 29 卷 (2〇〇8)第373頁至3了8頁]利用ζΓ〇2易於交換氧原子的四方相以 及耐磨損、耐高溫、耐腐蝕等特性,將之與Ce〇2做適當比例的 結合’結果顯不以Pd/Ceo.sZi^CVsubstrate單石型觸媒,鍛燒溫 度於400C,反應溫度為2l(TC下可得97%的曱苯轉化率。 國内現有的專利,有關飽觸專歡部分都在加氫及氫化的 應用’並沒有在空氣環境下進行曱苯氧化反應,並且並無使用氧 〇 储—二氧化鈽混合性氧化物作為擔體,在25〇。〇以下進行反 應’國内目刖有關把觸媒應用專利列於表一,國外目前有關飽觸 媒應用專利列於表二。由已公開專利中,未有如本發明所揭示利 用奈米把承載於氧化錯及二氧化鈽觸媒應用在有機廢氣去除的 方法。 〇 表一國内相關專利檢索 公告號 公告日 ------------ 專利名稱 1 200842125 2008/11/1 --~—---- 負栽型離子液體奈米鈀觸媒選擇性氫化共 軛雙烯之方法 1 200304850 2003/10/16 ~~^—----- #機:廢氣之處理方法及奘詈Luo [Appl. Catal. B: Environ. Vol. 69 (2007) pp. 213-218] et al. prepared a palladium catalyst using CeCrY2〇 co-oxide as a support and coated the catalyst with water. Attached to the honeycomb ceramic, it was found to be 5 〇〇. The calcined catalyst can completely oxidize terpene at 21 ° C. The durability of the catalyst is also important in addition to its activity. The researchers repeatedly heat the catalyst between 200 and 240 ° C. Cooling Chuanyi a total of 8 times 'has found no significant change in the activity of the catalyst within 30 hours, showing its repeatability and stability. Hosseini [Catalysis Today, Vol. 122 (2007) pp. 391-396] and others used the sedimentation method and the impregnation method to carry the gold and the tributary on the high surface area titanium dioxide support with porous structure. The activity is 0.5% Pd-1% Au/TiO2> 1.5% Pd/TiO2> 0.5% Pd/Ti02>1% Au-0.5% Pd/Ti02 > 1% Au/Ti02 > Ti02, the best activity 〇.5% Pd-1% Au/Ti〇2 can completely oxidize toluene at 230 °C. Liu et al. [Journal of Hazardous Materials, Vol. 149 (2007), pp. 742-746] uses alumina as a mixed carrier of ceria and cerium oxide coprecipitates prepared by coprecipitation. The Pt^AlzCVCeojZi^Yo.iMniuOx catalyst with ruthenium and manganese as additives was proved to have higher activity at 216 by using the impregnation method to prepare the platinum catalyst. (: The conversion rate of complete oxidation of toluene can reach 90%. Zheng et al. [Catal. Comrmm. Vol. 9 (2008) pp. 990-994] use stainless steel as a support, prepare by anodizing procedure, and forge Boiled under (7) (8), it can obtain the best activity of the catalyst, and the total conversion temperature of the A 5 201134549 element is 21〇c. Qingba〇 et al. [Chin J Catal. Vol. 29 (2〇〇8), p. 373) 3 8 pages] Using ζΓ〇2 to easily exchange the tetragonal phase of oxygen atoms and the characteristics of wear resistance, high temperature resistance, corrosion resistance, etc., and to make a proper ratio with Ce〇2, the result is not Pd/Ceo.sZi ^CVsubstrate monolithic catalyst, calcination temperature is 400C, reaction temperature is 2l (97% conversion of toluene can be obtained under TC. Domestic patents, hydrogenation and hydrogenation in the full-charged part The application ' does not carry out the oxidation reaction of benzene in the air environment, and does not use the sulphur storage - cerium oxide mixed oxide as the support, and reacts at 25 〇. 国内The application patents are listed in Table 1. The foreign patents on saturated catalyst applications are listed in Table 2. In the patent, there is no method for utilizing nanometer to apply the oxidization and cerium oxide catalyst to the organic waste gas removal as disclosed in the present invention. 一 Table 1 Domestic Patent Search Bulletin Announcement Day ------- ----- Patent Name 1 200842125 2008/11/1 --~----- Method for Selective Hydrogenation of Conjugated Diene by Negative Ionic Liquid Nano-Palladium Catalyst 1 200304850 2003/10/16 ~~ ^—----- #机: Waste gas treatment method and 奘詈

6 201134549 表二國外相關專利檢索 N 0. Patent No. --------- Date — Title 1 US6458741 2002/10/01 ~ — Catalysts for low-temperature destruction 2 5753583 of volatile organic compounds in air 1998/05/19 Supported palladium catalyst 【發明内容】 射本發明揭示—種製備承載於氧化錯及二氧化錦之妃觸媒之 ▲造方法二及一種在奈米鈀承載於氧化锆及二氧化鈽之觸媒催化 〇 了 ’在空^有機廢氣與氧氣反應以去除有機廢氣之方法;其中 氧化錯及二氧化鈽係依不同莫耳比例混合,氧化錯/二氧化飾莫耳 比為1/9至5/5之間,承載之!巴顆粒直徑在2與6奈米之間。本 ^月以含有16/氧錄—二氧轉舰在錢魏於找中,使用 填充床反應器’以去除有機廢氣。 【實施方式】 實施方式.]: 將 Ce(N03)3 · 6H2〇 (cerium nitrate hexahydrate)和Zr0(N03)2 · D 2Η2〇 (Zirc〇nium oxynitrate dihydrate)依照不同比例溶於去離子水 中製成金屬鹽溶液,再以氨水(amm〇nias〇luti〇n)為鹼液進行共沉 殿’之後進行過濾水洗,70至lOOt:之間之任一溫度乾燥2至1〇小 時,並在300至600 t:任一溫度下煅燒4至16小時之間,即可得 CeuZrxOr共沉澱法觸媒。 實施例1 : 7 201134549 1. 取 9.3477 g 的 Ce(N〇3)3.6H2〇 和 0.6393 g 的 ZrO(N03)2 · 2H20 溶於400 ml的去離子水中。 2. 量取25 wt.%的氨水400如。 3 ·將配製好的金屬鹽溶液和氨水以丨〇 ml/min定量滴定,且攪拌。 4.將上述的黃色溶液,利用抽氣過濾裝置進行過濾水洗,並以 去離子水洗滌濾餅至水洗濾液約ρΗ$8,並於70 r真空乾燥 2小時。 Ο 5·再將黃色粉末以10 °c/min的升溫速率,升溫至500。(:鍛燒, 持續8小時’即可得到dgCe^Zro.A-共沉澱法觸媒。 實施例2 : 1. 取 8.3578g 的 Ce(N03)r6H20 和 1.3168g 的 Zr0(N03)2.2H20 溶於400 ml的去離子水中。 2. 量取25 wt.%的氨水400 ml。 3. 將配製好的金屬鹽溶液和氨水以1〇ml/min定量滴定,且擾 〇 拌。 4. 將上述的黃色溶液,利用抽氣過濾裝置進行過濾水洗,並以 去離子水洗滌濾餅至水洗濾液約PHS8,並於70。(:真空乾燥 2小時。 5·再將黃色粉末以°C/min的升溫速率,煅燒至5〇〇 〇c,持繼 8小時’即可得到4gCea8Zr〇.2〇r共沉殿法觸媒。 眚施方式2 初濕含浸法為先測量擔體的孔洞體積,即先測量須多少的水 8 201134549 量可使擔體達到微濕的臨界點。製備Cei_xZrxOr初濕含浸法觸 媒,首先要取適量的Ce〇2測試其孔洞體積,緩慢的將去離子水滴 入擔體中並授拌之,確保去離子水能填充於孔洞内,當擔體達到 微濕時,去離子水的體積即為擔體的孔洞體積。隨後取適量的6 201134549 Table 2 Foreign related patent search N 0. Patent No. --------- Date — Title 1 US6458741 2002/10/01 ~ — Catalysts for low-temperature destruction 2 5753583 of volatile organic compounds in air 1998/05/19 Supported palladium catalyst [Summary of the Invention] The present invention discloses a method for preparing a ruthenium catalyst supported on oxidized and oxidized bismuth and a method for carrying nano zirconia on zirconia and cerium oxide. The catalyst catalyzes the method of removing the organic waste gas by reacting the organic exhaust gas with oxygen; wherein the oxidation fault and the cerium oxide are mixed according to different molar ratios, and the oxidation/smoothing molar ratio is 1/9. Between 5/5, bear it! The bar particles are between 2 and 6 nm in diameter. This month, the 16/Oxygen-dioxo-transfer ship was used in Qian Weiyu to use a packed bed reactor to remove organic waste gas. [Embodiment] Embodiment.]: Ce(N03)3 · 6H2 〇 (cerium nitrate hexahydrate) and Zr0(N03)2 · D 2Η2〇 (Zirc〇nium oxynitrate dihydrate) are dissolved in deionized water according to different ratios. The metal salt solution is further filtered and washed with ammonia water (amm〇nias〇luti〇n) as an alkali solution, and then dried at any temperature between 70 and 100 t: 2 to 1 hour, and at 300 to 600 t: calcined at any temperature for 4 to 16 hours to obtain a CeuZrxOr coprecipitation catalyst. Example 1: 7 201134549 1. 9.3477 g of Ce(N〇3)3.6H2〇 and 0.6393 g of ZrO(N03)2 · 2H20 were dissolved in 400 ml of deionized water. 2. Measure 25 wt.% of ammonia 400. 3 • Quantitatively titrate the prepared metal salt solution and ammonia water in 丨〇 ml/min and stir. 4. The above yellow solution was filtered and washed with an air suction filter, and the filter cake was washed with deionized water to a water-washed filtrate of about ρ Η $8, and dried under vacuum at 70 rpm for 2 hours. Ο 5· The yellow powder was further heated to 500 at a heating rate of 10 ° C/min. (: calcination, for 8 hours) to obtain dgCe^Zro.A-coprecipitation catalyst. Example 2: 1. Take 8.3578g of Ce(N03)r6H20 and 1.3168g of Zr0(N03)2.2H20 In 400 ml of deionized water. 2. Measure 25 wt.% of ammonia water 400 ml. 3. Quantitatively titrate the prepared metal salt solution and ammonia water at 1 〇ml/min, and stir the mixture. The yellow solution was filtered and washed with a suction filter, and the filter cake was washed with deionized water to a water-washed filtrate of about PHS8 at 70. (: vacuum drying for 2 hours. 5. Re-slall yellow powder at ° C/min Heating rate, calcined to 5〇〇〇c, for 8 hours, can get 4gCea8Zr〇.2〇r common sedimentation method. 眚2 method The initial wetness method first measures the pore volume of the support, ie First measure the amount of water required. The amount of 201134549 can make the support reach the critical point of microwetting. To prepare the Cei_xZrxOr incipient wetness catalyst, firstly, take the appropriate amount of Ce〇2 to test the pore volume, and slowly drop the deionized water into the load. In the body and mix it, to ensure that the deionized water can be filled in the hole, when the support reaches a slightly wet, deionized water Void volume is the product of the carrier body is then appropriate amount of

ZrO(N〇3)2 · 2H2〇溶於先前所測出來的水量後,緩慢地將金屬鹽 溶液滴入Ce〇2觸媒中,使溶液能夠完全吸入孔洞中,7〇至1〇〇。〇 之間之任一溫度乾燥2至10小時’並在3〇〇至6〇〇 任一溫度下, 〇 煅燒4至16小時之間,即可得Ce^xZrxCV初濕含浸法觸媒。 實施例3 : 1. 取2.7789 g的Ce〇2測試其孔洞體積,緩慢的將去離子水滴入 擔體中並攪拌之,確保去離子水能填充於孔洞内,當擔體達到 微濕時,去離子水的體積即為擔體的孔洞體積。 2. 取0.4795 g的Zr〇(N〇3)2 · 2氏0溶於先前所測出來的水量後, 緩慢地將金屬鹽溶液滴入Ce〇2觸媒中,使溶液能夠完全吸入 ϋ 間隙中。 3. 以C真空乾燥2小時,再以1〇 °c/min升溫至500 °C後, 維持在500 〇C煅燒8小時,即可得3 g的Cea9Zr()1〇2_初濕含 浸法觸媒 實施例4 : L取2.5445 g的Ce〇2測試其孔洞體積,緩慢的將去離子水滴 入擔體中並搜拌之’確保去離子水能填充於孔洞内,當擔體達 到微濕時’去離子水的體積即為擔體的孔洞體積。 9 201134549 2. 取0.9877 g的Zr0(N03)2 . 2H20溶於先前所測出來的水量 後’緩慢地將金屬鹽溶液滴入Ce〇2觸媒中,使溶液能夠完全 吸入間隙中。 3. 以°C真空乾燥2小時,再以1〇 °C/min升溫至500 〇C後, 維持在500煅燒8小時,即可得3 g的Ce〇.8ZrG.2〇2-初濕含 浸法觸媒。 實施方式3 i 〇 先測試出觸媒的初濕含水量,再將適量Pd(N〇3)2 · 2H2〇溶於測出 來的水里中’緩慢地將金屬鹽溶液滴入適量的Cei-xZrx〇2-共沉殿 法觸媒中’使溶液能夠完全吸入孔洞中;7〇至1〇〇〇c之間之任一 溫度乾燥2至1〇小時,並在3〇〇至6〇〇艺任一溫度下锻燒4至 16小時之間,即可得到pd/ Cei处晶-共沉澱法觸媒;將觸媒pd/ CeniZnOr·共沉澱法’將觸媒置於填充反應床反應器内,進行在空 氣中完全氧化甲笨的反應,以連續式觸媒填充床反應器進行實 0 驗;控制流量,並在固定溫度下,進行反應。 實施例5 : 1. 測試出觸媒的初濕含水量,再將〇〇518gpd(N〇3)2 · 2h2〇溶於 測出來的水量中’緩慢地將金屬鹽溶液滴入2g的Ce〇.9Zr〇.1〇2_ 共/儿;叙法觸媒中,使溶液能夠完全吸入孔洞中; 2. 以70 C真空乾燥2 h,再以1〇 °C/min升溫至5〇〇 〇C後,維持 在500 C锻燒8h,即可得到lwt%pd/Ce〇9Zr〇i〇2_共沉澱法觸 201134549 媒; 3. 將觸媒lwt.%Pd/Cea9Zrai〇2-共沉澱法,置於U型觸媒填充反 應床内’進行在空氣中氧化甲苯的反應,以連續式觸媒填充床 反應器進行實驗; 4. 控制流量為每分鐘10〇毫升,在室溫下通入反應器中’管子内 外直徑為0.9公分及1.3公分,長度21公分,中間有〇.5公分 之融熔石英砂,以擔載反應之觸媒,但可以透氣; Ο 5·秤取觸媒重量0.5 g置入U型石英管中,曱苯的飽和器置水浴 中控制溫度為30 °C,觸媒反應溫度由室溫升溫至300 °C,以4 °C/min的速率升溫5分鐘後,到達反應溫度時,控制在此溫 度’ 10分鐘後進行反應測試; 6·進料流速經由質量流量控制器(MassFlow Controller,一般簡稱 MFC)控制,先以少量空氣經裝有進料曱苯的錐形瓶帶出進料 的蒸氣後,再藉由另一空氣稀釋調整進料濃度,通過U型觸 〇 媒填充反應床,反應後的氣體流經氣相層析儀,再由火焰游離 價測器分析。反應結果如下’且轉化率如圖四。 上述實施方式之反應結果如下;其中甲苯轉化率定義如下: 甲苯轉化率=(進口曱苯濃度-出口甲笨濃度),口甲笨漢度。 由這些結果證實本發明之觸媒能有效去除空氣中之有機廢氣(甲 苯)。 11 201134549 溫度 丨50丨70 (°C) 1 …….…h———」__ 90 110 130 ! 150| 170 1 190 210 230 250 270 出口曱;1.8 I 1.6 笨濃度1 '(g/rn3) 1 -....................................... „,,ί --------------- 1.4 1.2 0.9 0.6 0.3 1 1 0.05 0.01 0 0 0 實施例6 : 〇 i·測試出觸媒的初濕含水量’再將0.0518g Pd(N03)2 · 2H20溶 於測出來的水量中’緩慢地將金屬鹽溶液滴入2g的 Cea8Zr0.2〇2-共沉澱法觸媒中,使溶液能夠完全吸入間隙中; 2. 以70 C真空乾燥2小時,再以1〇 °c/min升溫至5〇〇 〇c後, 維持在500。(:锻燒8小時,即可得到lwt%Pd/Ce〇8Zr〇2〇2j 沉澱法觸媒; 3. 將觸媒iwt%Pd/Ce〇8Zr〇2〇2_共沉澱法,置於u型觸媒填充反 〇 應床内’進行在空氣中氧化?苯的反應,以連續式觸媒填充床 反應器進行實驗; 4·控制流量為每分鐘刚冑升’在室溫下通入反應器中 ,管子内 外直控為〇·9公分及U公分,長度21公分,中間有0.5公分 之融溶石英砂’以擔載反應之觸媒,但可以透氣; 5.秤取觸媒重量G.5S置人U型石英管中,曱苯的飽和器置水 心中控制溫度為3G t,觸媒反應溫度由5G。(:升溫至300 t, 乂4 C/min喊率升溫5分鐘後,到達反應溫度時控制在此 12 201134549 溫度ίο分鐘後進行反應測試; 6.進料流速經由質流控制器(MassFlow Controller,一般簡稱 MFC)控制’先以少量空氣經裝有進料曱苯的錐形瓶帶出進料 的蒸氣後,再藉由另一空氣稀釋調整進料濃度,(甲苯的MFC 比控制在7/93),通過U型觸媒填充反應床,反應後的氣體(即 通過觸媒床之氣體)流經氣相層析儀(GC) ’再由火焰游離偵測 器(FID)分析。反應結果如下,且轉化率如圖四。 〇 上述實施方式之反應結果如下;其中甲苯轉化率定義如下: 曱苯轉化率=(進口曱苯濃度一出口甲苯濃度)+進口曱苯濃度。 由這些結果證實本發明之觸媒能有效去除空氣中之有機廢氣(曱 苯)。 溫度(°C) 50 70 90 110 130 150 170 190 210 230 250 270 出口曱| 1.8 笨濃度 (g/m1 2 3) 1.7 1.6 ............................... 1.4 1.2 0.9 0.6 0.4 0.3 0.01 V : 0 實施例7 : 13 1 測試出觸媒的初濕含水量,再將〇.〇518g pd(N〇3)2 · 2H2〇溶 於測出來的水量中’緩慢地將金屬鹽溶液滴入2g的 Ce0_9Zrai〇r初濕含浸法觸媒中,使溶液能夠完全吸入間隙中; 2 以70 °C真空乾燥2小時’再以1〇 °C/min升溫至500後, 3 維持在500 °C煅燒8小時,即可得到lwt.%Pd/Ce()9Zr()1〇r初 201134549 濕含浸法觸媒; 3. 將觸媒lwt%Pd/Ce〇.9Zrai02-初濕含浸法,置於U型觸媒填充 反應床内,進行在空氣中氧化曱苯的反應,以連續式觸媒填 充床反應器進行實驗; 4. 控制流量為每分鐘10〇毫升,在室溫下通入反應器中,管子内 外直徑為0.9公分及1.3公分,長度21公分,中間有0.5公分 之融熔石英砂,以擔載反應之觸媒,但可以透氣; Ο 5.秤取觸媒重量0.5 g置入U型石英管中,曱苯的飽和器置水 浴中控制溫度為30 °C,觸媒反應溫度由50 °C升溫至300 X:, 以4 °C/min的速率升溫5分鐘後,到達反應溫度時控制在此 溫度10分鐘後進行反應測試;After ZrO(N〇3)2 · 2H2〇 is dissolved in the previously measured amount of water, the metal salt solution is slowly dropped into the Ce〇2 catalyst to allow the solution to completely inhale into the pores, 7〇 to 1〇〇. The temperature between any of 〇 is dried for 2 to 10 hours' and at any temperature of 3 〇〇 to 6 ,, 煅 is calcined for 4 to 16 hours to obtain a Ce^xZrxCV incipient wetness impregnation catalyst. Example 3: 1. 2.7789 g of Ce〇2 was used to test the pore volume, and the deionized water was slowly dripped into the support and stirred to ensure that the deionized water could be filled in the pores. When the support reached a slightly wet condition, The volume of deionized water is the pore volume of the support. 2. After dissolving 0.4795 g of Zr〇(N〇3)2 · 2·0 in the previously measured amount of water, slowly slowly drop the metal salt solution into the Ce〇2 catalyst to allow the solution to completely inhale the gap. in. 3. Dry in C vacuum for 2 hours, then increase the temperature to 500 °C at 1 ° ° C / min, and then heat at 500 ° C for 8 hours to obtain 3 g of Cea9Zr () 1 〇 2 _ initial wet impregnation method Catalyst Example 4: L Take 2.5445 g of Ce〇2 to test the pore volume, slowly drop the deionized water into the support and mix it to ensure that the deionized water can be filled in the pores, when the support reaches the micro-wet The volume of deionized water is the pore volume of the support. 9 201134549 2. Take 0.9877 g of Zr0(N03)2. 2H20 dissolved in the previously measured amount of water. Slowly drop the metal salt solution into the Ce〇2 catalyst to allow the solution to completely absorb the gap. 3. Dry in vacuum at °C for 2 hours, then raise the temperature to 500 〇C at 1 °C/min, and then heat at 500 for 8 hours to obtain 3 g of Ce〇.8ZrG.2〇2-incipient wetness impregnation. Law catalyst. Embodiment 3 i First test the initial moisture content of the catalyst, and then dissolve the appropriate amount of Pd(N〇3)2 · 2H2 〇 in the measured water. Slowly, the metal salt solution is dropped into the appropriate amount of Cei- xZrx〇2-Common in the bath system to enable the solution to completely inhale into the hole; dry at any temperature between 7〇 and 1〇〇〇c for 2 to 1 hour, and at 3〇〇 to 6〇〇 The pd/Cei crystal-coprecipitation catalyst can be obtained by calcining at any temperature for 4 to 16 hours; the catalyst pd/CeniZnOr·coprecipitation method is used to place the catalyst in the packed reaction bed reactor. Inside, the reaction of completely oxidizing in the air is carried out, and the reactor is continuously tested in a continuous catalyst packed bed reactor; the flow rate is controlled, and the reaction is carried out at a fixed temperature. Example 5: 1. The initial moisture content of the catalyst was measured, and 〇〇518gpd(N〇3)2 · 2h2〇 was dissolved in the measured amount of water. 'The metal salt solution was slowly dropped into 2 g of Ce〇. .9Zr〇.1〇2_ total/child; in the Syrian catalyst, the solution can be completely inhaled into the hole; 2. Dry at 70 C for 2 h, then heat up to 5 °C at 1 °C/min. , maintained at 500 C for 8h, can get lwt%pd/Ce〇9Zr〇i〇2_ coprecipitation method 201134549 medium; 3. Catalyst lwt.%Pd/Cea9Zrai〇2-coprecipitation method, set The reaction of oxidizing toluene in air is carried out in a U-type catalyst packed reaction bed, and the experiment is carried out in a continuous catalyst packed bed reactor; 4. The flow rate is 10 〇ml per minute, and the reactor is introduced at room temperature. The inside and outside diameter of the pipe is 0.9 cm and 1.3 cm, the length is 21 cm, and there is a fused quartz sand of 〇5 cm in the middle to support the catalyst of the reaction, but it can be ventilated; Ο 5·Weighing catalyst weight 0.5 g Placed in a U-shaped quartz tube, the temperature of the sulphurizer in the water bath is controlled at 30 °C, the temperature of the catalyst is raised from room temperature to 300 °C, and the temperature is raised at a rate of 4 °C/min. After the minute, when the reaction temperature is reached, control the reaction at this temperature for '10 minutes. 6. The feed flow rate is controlled by a mass flow controller (MassFlow Controller, generally referred to as MFC), and the feed is first filled with a small amount of air. After the benzene cone bottle takes out the steam of the feed, the feed concentration is adjusted by another air dilution, and the reaction bed is filled by the U-type contact medium, and the reacted gas flows through the gas chromatograph and then by the flame. Free price analyzer analysis. The reaction results are as follows' and the conversion rate is shown in Fig. 4. The results of the reaction of the above embodiment are as follows; wherein the toluene conversion rate is defined as follows: Toluene conversion rate = (Important benzene concentration - outlet 笨 stupid concentration), mouth arbitrage. From these results, it was confirmed that the catalyst of the present invention can effectively remove organic exhaust gas (toluene) in the air. 11 201134549 Temperature 丨50丨70 (°C) 1 ..........h———”__ 90 110 130 ! 150| 170 1 190 210 230 250 270 Exit 曱; 1.8 I 1.6 Stupid 1 '(g/rn3) 1 -....................................... „,, ί ----- ---------- 1.4 1.2 0.9 0.6 0.3 1 1 0.05 0.01 0 0 0 Example 6: 〇i·Test the initial moisture content of the catalyst' and then add 0.0518g Pd(N03)2 · 2H20 Dissolve in the measured amount of water 'slowly drop the metal salt solution into 2g of Cea8Zr0.2〇2-coprecipitation catalyst to make the solution completely inhaled into the gap; 2. Dry at 70 C for 2 hours, then After heating to 5〇〇〇c at 1〇°c/min, it is maintained at 500. (: After calcination for 8 hours, lwt% Pd/Ce〇8Zr〇2〇2j precipitation catalyst can be obtained; 3. Will touch The medium iwt%Pd/Ce〇8Zr〇2〇2_ coprecipitation method is placed in the u-type catalyst filled 〇 〇 ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' Experiment; 4. Control flow rate is just ascending every minute. Pass into the reactor at room temperature. The direct control inside and outside the tube is 〇·9 cm and U cm, the length is 21 cm, and there is 0.5 in the middle. The dissolved quartz sand is used to support the reaction catalyst, but it can be ventilated; 5. The weight of the catalyst is taken in the G.5S U-shaped quartz tube, and the temperature of the sulphurizer in the water is controlled to be 3G t The catalyst reaction temperature is 5G. (: The temperature is raised to 300 t, and the 乂4 C/min call rate is raised for 5 minutes. When the reaction temperature is reached, the reaction is controlled after the temperature of 12 201134549 ίο minutes. 6. The feed flow rate is passed. The mass flow controller (MassFlow Controller, generally referred to as MFC) controls 'first take a small amount of air through the conical flask containing the feed benzene to bring out the steam of the feed, and then adjust the feed concentration by another air dilution, ( The MFC ratio of toluene is controlled at 7/93), and the reaction bed is filled by U-type catalyst. The reacted gas (ie, the gas passing through the catalyst bed) flows through the gas chromatograph (GC) and is detected by flame free. (FID) analysis. The reaction results are as follows, and the conversion rate is shown in Figure 4. The reaction results of the above embodiment are as follows; wherein the conversion of toluene is defined as follows: conversion of toluene = (injected toluene concentration - outlet toluene concentration) + import Benzene concentration. From these results, it was confirmed that the catalyst of the present invention can Effectively removes organic waste gas (toluene) in the air. Temperature (°C) 50 70 90 110 130 150 170 190 210 230 250 270 Export 曱 | 1.8 Stupid concentration (g/m1 2 3) 1.7 1.6 ...... ......................... 1.4 1.2 0.9 0.6 0.4 0.3 0.01 V : 0 Example 7 : 13 1 Test the initial moisture content of the catalyst Then, 〇.〇518g pd(N〇3)2 · 2H2〇 is dissolved in the measured amount of water' Slowly, the metal salt solution is dropped into 2g of Ce0_9Zrai〇r incipient wetness impregnation catalyst to make the solution completely In the suction gap; 2 vacuum drying at 70 °C for 2 hours' and then heating to 500 °C at 1 ° ° C / min, 3 maintained at 500 ° C for 8 hours, you can get lwt.% Pd / Ce () 9Zr ( ) 1〇r initial 201134549 wet impregnation catalyst; 3. The catalyst lwt%Pd/Ce〇.9Zrai02-incipient wetness impregnation method is placed in a U-type catalyst packed reaction bed to carry out oxidation of benzene in air. The reaction was carried out in a continuous catalyst packed bed reactor; 4. The control flow rate was 10 〇ml per minute, and it was introduced into the reactor at room temperature. The inner and outer diameters of the tube were 0.9 cm and 1.3 cm, and the length was 21 cm. Has a 0.5 cm melting quartz sand to The catalyst for carrying the reaction, but it can be ventilated; Ο 5. The weight of the catalyst is 0.5 g and placed in a U-shaped quartz tube. The temperature of the sulphurizer in the water bath is controlled at 30 °C, and the temperature of the catalyst is 50 °. C is heated to 300 X:, after heating at a rate of 4 ° C / min for 5 minutes, when the reaction temperature is reached, the reaction test is carried out after 10 minutes at this temperature;

6·進料流速經由質流控制器(MassFlow Controller,一般簡稱 MFC)控制,先以少量空氣經裝有進料曱苯的錐形瓶帶出進料 的蒸氣後’再藉由另一空氣稀釋調整進料濃度,(甲苯的MFC 〇 比控制在7/93),通過U型觸媒填充反應床,反應後的氣體(即 通過觸媒床之氣體)流經氣相層析儀(GC) ’再由火焰游離彳貞測 器(FID)分析。反應結果如下,且轉化率如圖四。 上述實施方式之反應結果如下;其中甲苯轉化率定義如下. 甲苯轉化率=(進口甲苯濃度一出口甲笨濃度進口曱苯濃产。 由這些結果證實本發明之觸媒能有效去除空氣中之有機廢氣(甲 笨)。 、 14 201134549 溫度 50 ; ; j 70 90 1 no ...........'....•μ,.....···. 130 150) 170 190 210 .............................................................................................................. 230 , 250 I 270 | 1 (°C) ! ! !丨 ί 1出口曱丨1.8 1.6 1.4 I 1.2 0.9 0.5 0.2 0.01 0 ο 1 〇 丨 ο I ; |苯濃度 I I i (g/m3) : ί 1 1 ; 實施例8 : Q h測試出觸媒的初濕含水量,再將0.0518gPd(NO3)2 · 2H20溶於 測出來的水量中,緩慢地將金屬鹽溶液滴入2g的Ce〇8Zr〇2〇r 初濕含浸法觸媒中,使溶液能夠完全吸入間隙中; 2·以70 C真空乾燥2小時,再以1〇 ^/min升溫至500 °C後, 維持在500 °C煅燒8小時’即可得到lwt %pd/Ce() 8ZrG2〇2_初 濕含浸法觸媒; 3. 將觸媒lwt.%Pd/Ce〇_8Zr〇.202-初濕含浸法,置於U型觸媒填充 〇 反應床内’進行在空氣中氧化甲苯的反應,以連續式觸媒填充 床反應器進行實驗; 4. 控制流量為每分鐘1〇〇毫升,在室溫下通入反應器中,管子内 外直徑為〇.9公分及1.3公分,長度21公分,中間有〇.5公分 之融熔石英砂,以擔載反應之觸媒,但可以透氣; 5. 秤取觸媒重量G.5g置人u型石英f中,甲苯的飽和器置水浴 中控制溫度為30 ,觸媒反應溫度由50 °C升溫至300。(:,以 4 C/min的速率升溫5分鐘後,到達反應溫度時控制在此溫 15 201134549 度10分鐘後進行反應測試; 6.進料流速經由質流控制器(MassFlow Controller,一般簡稱 MFC)控制,先以少量空氣經裝有進料曱苯的錐形瓶帶出進料 的蒸氣後,再藉由另一空氣稀釋調整進料濃度,(曱苯的MFC 比控制在7/93),通過U型觸媒填充反應床,反應後的氣體(即 通過觸媒床之氣體)流經氣相層析儀(GC),再由火焰游離偵測 器(FID)分析。反應結果如下,且轉化率如圖四。 〇 上述實施方式之反應結果如下;其中曱苯轉化率定義如下: 曱笨轉化率=(進口曱苯濃度—出口曱苯濃度)+進口曱苯濃度。 由這些結果證實本發明之觸媒能有效去除空氣中之有機廢氣(曱 苯)。 溫度(c) |苯濃度 Oi (g/m3) 50 出口甲丨1.8 70 90 | ........i 110 130 150 170 ............................. 190 210 230 250 270 1.6 1.4 1.3 1.2 1.1 0.9 0.4 0.1 0.01 0 0 【圖式簡單說明】 圖一各觸媒粉末之XRD圖譜 圖一各觸媒BET表面積與元素分析結果 圖二 lwto/oPd/Ceo.gZriniVlw 粉末觸媒之 TEM 影像 圖四各觸媒對T苯氧化之轉化率 圖五各觸對甲苯完全氧化之耐久性測試 16 201134549 【主要元件符號說明】 無主要元件符號說明6. The feed flow rate is controlled by a mass flow controller (MassFlow Controller, generally referred to as MFC). First, a small amount of air is taken out of the feed vapor through a conical flask containing the feed benzene, and then diluted by another air. Adjust the feed concentration (the MFC enthalpy ratio of toluene is controlled at 7/93), fill the reaction bed with a U-type catalyst, and the reacted gas (ie, the gas passing through the catalyst bed) flows through the gas chromatograph (GC). 'After the flame free detector (FID) analysis. The reaction results are as follows, and the conversion rate is shown in Fig. 4. The reaction results of the above embodiments are as follows; wherein the toluene conversion rate is defined as follows. Toluene conversion rate = (imported toluene concentration - exporting a stupid concentration of imported benzene and benzene is abundantly produced. From these results, it was confirmed that the catalyst of the present invention can effectively remove organic matter in the air. Exhaust gas (A stupid). , 14 201134549 Temperature 50 ; ; j 70 90 1 no ...........'....•μ,.....···. 130 150) 170 190 210 ................................................ .................................................. ............230 , 250 I 270 | 1 (°C) ! ! !丨ί 1Export 曱丨1.8 1.6 1.4 I 1.2 0.9 0.5 0.2 0.01 0 ο 1 〇丨ο I ; Benzene concentration II i (g/m3): ί 1 1 ; Example 8: Q h was tested for the initial wet moisture content of the catalyst, and then 0.0518 g of Pd(NO3) 2 · 2H20 was dissolved in the measured amount of water, slowly The metal salt solution was dropped into 2 g of Ce〇8Zr〇2〇r in the incipient wetness impregnation catalyst to allow the solution to completely absorb into the gap; 2. Dry at 70 C for 2 hours, then raise the temperature to 1 〇^/min. After 500 °C, it can be calcined at 500 °C for 8 hours to get lwt %pd/Ce() 8ZrG2 2_Incipient wetness impregnation catalyst; 3. Catalyst lwt.%Pd/Ce〇_8Zr〇.202-incipient wetness impregnation method, placed in U-type catalyst filled 〇 reaction bed 'to oxidize toluene in air The reaction was carried out in a continuous catalyst packed bed reactor; 4. The control flow rate was 1 〇〇ml per minute, and it was introduced into the reactor at room temperature. The inner and outer diameters of the tube were 9.9 cm and 1.3 cm, and the length was 21 cm, with 〇5 cm of molten quartz sand in the middle to support the catalyst of the reaction, but it can be ventilated; 5. Weighing the weight of the catalyst G.5g placed in the u-type quartz f, the saturator of the toluene The temperature in the water bath is controlled at 30, and the temperature of the catalyst is raised from 50 °C to 300. (:, after heating at a rate of 4 C/min for 5 minutes, the reaction temperature is controlled at this temperature 15 201134549 degrees for 10 minutes after reaching the reaction temperature; 6. The feed flow rate is passed through a mass flow controller (MassFlow Controller, generally referred to as MFC) ) control, first take a small amount of air through the cone containing the feed benzene to bring out the steam of the feed, and then adjust the feed concentration by another air dilution (the MFC ratio of benzene is controlled at 7/93) The reaction bed is filled by a U-type catalyst, and the reacted gas (ie, the gas passing through the catalyst bed) flows through a gas chromatograph (GC) and is analyzed by a flame free detector (FID). The reaction results are as follows. And the conversion rate is shown in Figure 4. The reaction results of the above embodiments are as follows; wherein the conversion of toluene is defined as follows: 曱 stupid conversion rate = (imported benzene concentration - export benzene concentration) + imported benzene concentration. The catalyst of the invention can effectively remove organic waste gas (nonylbenzene) in the air. Temperature (c) | benzene concentration Oi (g/m3) 50 export armor 1.8 70 90 | ........i 110 130 150 170 ............................. 190 210 230 250 270 1.6 1.4 1.3 1.2 1.1 0.9 0. 4 0.1 0.01 0 0 [Simple description of the diagram] Figure 1 XRD pattern of each catalyst powder BET surface area and elemental analysis results of each catalyst Figure 2 TEM image of the powder catalyst of lwto/oPd/Ceo.gZriniVlw Conversion rate of T-benzene oxidation by the medium Figure 5 Endurance test of complete oxidation of each pair of toluene 16 201134549 [Explanation of main component symbols] No main component symbol description

Claims (1)

201134549 七、申請專利範圍: 1. 一種製祕氧祕及二氧化氣合氧錄德觸媒的方 法’其包括:以含浸法製備之氧化錯及二氧化飾混合氧化物, 錯與錦混合之莫耳比例為1/9至5/5之間,在巴重量百分比〇5 至2 Wt%之間,其特徵是以初濕含浸法製備氧化备二氧化飾 之複合氧化物’ 70至就之間乾燥2至1〇小時,並在遍 任—溫度下域4至16小時之間,再时浸法縣 洛液與其氧化物放在水中,接著在7〇至卿。c之間乾⑻ 至10小時,緩慢升溫至_ 後’轉在最後溫度緞燒 4至16小時。 i種製造承載於氧化錯及二氧化鈽混合氧化物德觸媒的方 法,錯與飾混合之莫耳比例為1/9至5/5之間,纪重量百分比 〇·5至2 wt·%之間’其特徵是以共沉殿法製備氧化錯二氧化飾 〇 之複合氧化物,70至峨之燥2至1()小時,並在· 至60(rc任一溫度下锻燒4至16小時之間,再以含浸法將把 讀與其氧化物放在水中,接著在7G至⑽。c抽氣乾燥2 至10小時’緩慢升溫遍至_ °C後,維持在最後溫度锻燒 4至16小時。 3·:種去时財含有曱苯財法,其仙含有奈統承載於 氧化鍅及二氧化鈽混合氧化物之觸媒,在空氣中,於5〇至 300°C之間之任一溫度下反應,使甲苯完全氧化。 《如申請專利細第3項的方法,其中时浸法製備之氧化錯及 18 201134549 -減氣合物,錯_齡之料_為 如申物麵第3項的方法,其h共沉岭^75之間。 及二氧化佩合物,物喊合之料_為ι/9= 氧之: .如申明專利範圍第3項的方法,其巾以含浸法製備之奈米把觸 媒’鍛燒溫度維持在3〇〇至600 °C之間。 如申請專利範圍第3項的方法,其中含有奈米鈀承載於氧化錯 及二氧化鈽之觸媒中,其中鈀重量百分比是〇 5裏2%之間。201134549 VII. Scope of application for patents: 1. A method for the production of secret oxygen and oxygen dioxide and oxygen-catalyzed catalysts, which includes: an oxidized and oxidized mixed oxide prepared by impregnation, mixed with bromine The molar ratio is between 1/9 and 5/5, and between 5% and 2% by weight of the bar. It is characterized by the preparation of the oxidized oxidized composite oxide '70 by the incipient wetness method. It is dried for 2 to 1 hour, and between 4 and 16 hours in the sub-period-temperature zone, and then the infusion of the salt and its oxide in the water, followed by 7 to qing. Dry between c (8) to 10 hours, slowly heat up to _ after 'turning to the final temperature satin for 4 to 16 hours. A method for producing a mixed catalyst of oxidized and cerium oxide mixed oxide, wherein the molar ratio of the wrong mixed material is between 1/9 and 5/5, and the weight percentage is 〇·5 to 2 wt·%. Between the characteristics of the composite oxide is prepared by the common sinking method, 70 to 峨 dry 2 to 1 () hours, and at ~ to 60 (rc at any temperature for 4 to Between 16 hours, the read and its oxides are placed in water by impregnation, then dried at 7G to (10).c for 2 to 10 hours. After slowly heating up to _ °C, the calcination is maintained at the final temperature. Up to 16 hours. 3:: When the time is gone, it contains the benzene benzene method, which contains the catalyst of Natto supported on cerium oxide and cerium oxide mixed oxide, in air, between 5 〇 and 300 ° C. The reaction is carried out at any temperature to completely oxidize the toluene. The method of the third aspect of the patent application, wherein the oxidization error prepared by the time immersion method and 18 201134549 - a gas-reducing compound, the material of the wrong age is as a product The method of the third item, the h is between the sag and the sulphate, and the smear of the smear is ι/9 = oxygen: . The method of the invention comprises the nanometer prepared by the impregnation method, wherein the calcining temperature of the catalyst is maintained between 3 Torr and 600 ° C. The method of claim 3, wherein the nano palladium is contained in the oxidation fault. And the catalyst of cerium oxide, wherein the weight percentage of palladium is between 2% and 2%. 1919
TW099111548A 2010-04-13 2010-04-13 Preparation of zirconia-ceria-supported nano-palladium catalysts and its application in destruction of volatile organic compounds in air TW201134549A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
TW099111548A TW201134549A (en) 2010-04-13 2010-04-13 Preparation of zirconia-ceria-supported nano-palladium catalysts and its application in destruction of volatile organic compounds in air

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
TW099111548A TW201134549A (en) 2010-04-13 2010-04-13 Preparation of zirconia-ceria-supported nano-palladium catalysts and its application in destruction of volatile organic compounds in air

Publications (1)

Publication Number Publication Date
TW201134549A true TW201134549A (en) 2011-10-16

Family

ID=46751555

Family Applications (1)

Application Number Title Priority Date Filing Date
TW099111548A TW201134549A (en) 2010-04-13 2010-04-13 Preparation of zirconia-ceria-supported nano-palladium catalysts and its application in destruction of volatile organic compounds in air

Country Status (1)

Country Link
TW (1) TW201134549A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI488690B (en) * 2011-12-07 2015-06-21 國立中央大學 The method of preparation of cerium oxide-manganese oxide supported nano-palladium catalysts and its application in destruction of volatile organic compounds in air

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI488690B (en) * 2011-12-07 2015-06-21 國立中央大學 The method of preparation of cerium oxide-manganese oxide supported nano-palladium catalysts and its application in destruction of volatile organic compounds in air

Similar Documents

Publication Publication Date Title
TWI442972B (en) Gold-palladium supported on ceria catalyst and its application in removing organic gases
Liu et al. Direct molten polymerization synthesis of highly active samarium manganese perovskites with different morphologies for VOC removal
Mao et al. Metal support interaction in Pt nanoparticles partially confined in the mesopores of microsized mesoporous CeO2 for highly efficient purification of volatile organic compounds
Wang et al. Synergistic effects of multicomponents produce outstanding soot oxidation activity in a Cs/Co/MnO x catalyst
Xie et al. Efficient removal of methane over cobalt-monoxide-doped AuPd nanocatalysts
Luo et al. High-surface area CuO–CeO2 catalysts prepared by a surfactant-templated method for low-temperature CO oxidation
Xu et al. Preparation, characterization, and kinetic study of a core–shell Mn3O4@ SiO2 nanostructure catalyst for CO oxidation
Azambre et al. Probing the Surface of Ceria− Zirconia Catalysts Using NO x Adsorption/Desorption: A First Step Toward the Investigation of Crystallite Heterogeneity
Chen et al. Ni/CeO2 nanocatalysts with optimized CeO2 support morphologies for CH4 oxidation
JP5864444B2 (en) Exhaust gas purification catalyst and exhaust gas purification catalyst structure
CN110075848B (en) Catalyst for removing non-methane total hydrocarbons in total hydrocarbons, preparation and application
Zhou et al. Enhanced Catalytic Combustion Performance of Toluene over a Novel Co–CeO x Monolith Catalyst
Deng et al. Effect of coating modification of cordierite carrier on catalytic performance of supported NiMnO3 catalysts for VOCs combustion
Zhang et al. Improvement of air/fuel ratio operating window and hydrothermal stability for Pd-only three-way catalysts through a Pd–Ce2Zr2O8 superstructure interaction
CN106964348A (en) Formaldehyde pollutant room-temperature catalytic oxidation catalyst and preparation method and application thereof
Promhuad et al. Effect of metal oxides (CeO2, ZnO, TiO2, and Al2O3) as the support for silver-supported catalysts on the catalytic oxidation of diesel particulate matter
CN103551141A (en) A Pt/MOx Catalyst and Its Application in Catalytic Combustion of Toluene
CN111151247A (en) A supported catalyst and its preparation method and application
Zhou et al. Preparation of a monolith MnO x–CeO 2/La–Al 2 O 3 catalyst and its properties for catalytic oxidation of toluene
CN103212406B (en) MnOx catalyst for catalytic elimination of benzene series in air and preparation method thereof
CN102909031B (en) Catalyst used for catalyzing and eliminating toluene in air and preparation method of catalyst
Zeng et al. Morphologically uniform Pd/FexMn3− xO4-HP interfaces as the high-performance model catalysts for catalytic combustion of volatile organic compound
Zhang et al. CeO2-ZrO2-La2O3-Al2O3 composite oxide and its supported palladium catalyst for the treatment of exhaust of natural gas engined vehicles
Min et al. Catalytic combustion of toluene over platinum supported on Ce–Zr–O solid solution modified by Y and Mn
TWI488690B (en) The method of preparation of cerium oxide-manganese oxide supported nano-palladium catalysts and its application in destruction of volatile organic compounds in air