[go: up one dir, main page]

CN112138658B - Preparation method of integral catalyst for purifying tank tail gas - Google Patents

Preparation method of integral catalyst for purifying tank tail gas Download PDF

Info

Publication number
CN112138658B
CN112138658B CN202011057834.8A CN202011057834A CN112138658B CN 112138658 B CN112138658 B CN 112138658B CN 202011057834 A CN202011057834 A CN 202011057834A CN 112138658 B CN112138658 B CN 112138658B
Authority
CN
China
Prior art keywords
mass
aluminum
cerium
mixed oxide
precious metal
Prior art date
Legal status (The legal status 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 status listed.)
Active
Application number
CN202011057834.8A
Other languages
Chinese (zh)
Other versions
CN112138658A (en
Inventor
万杰
吴功德
阚建飞
夏前耀
柏海军
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Xi'an Taimei Power Technology Co ltd
Nanjing Institute of Technology
Original Assignee
Xi'an Taimei Power Technology Co ltd
Nanjing Institute of Technology
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 Xi'an Taimei Power Technology Co ltd, Nanjing Institute of Technology filed Critical Xi'an Taimei Power Technology Co ltd
Priority to CN202011057834.8A priority Critical patent/CN112138658B/en
Publication of CN112138658A publication Critical patent/CN112138658A/en
Application granted granted Critical
Publication of CN112138658B publication Critical patent/CN112138658B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/63Platinum group metals with rare earths or actinides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9445Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC]
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/56Foraminous structures having flow-through passages or channels, e.g. grids or three-dimensional monoliths
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0201Impregnation
    • B01J37/0207Pretreatment of the support
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0215Coating
    • B01J37/0217Pretreatment of the substrate before coating
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/024Multiple impregnation or coating
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/03Precipitation; Co-precipitation
    • B01J37/038Precipitation; Co-precipitation to form slurries or suspensions, e.g. a washcoat
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/082Decomposition and pyrolysis
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts
    • 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

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Combustion & Propulsion (AREA)
  • Biomedical Technology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Catalysts (AREA)

Abstract

The invention discloses a preparation method of an integral catalyst for purifying tank tail gas, which comprises a carrier, a bonding coating and an active substance, wherein the carrier is a pretreated honeycomb ceramic filter body, the bonding coating is an aluminum sol coating, and the active substance is cerium-aluminum mixed oxide loaded with noble metal Pt; the preparation steps of the catalyst are as follows: (1) preparing a carrier, (2) preparing an alumina sol, (3) preparing an active substance, (4) preparing a slurry, and (5) preparing a monolithic catalyst. The monolithic catalyst prepared by the invention not only has good carbon smoke particle oxidation removal capability, but also can realize effective purification of CO, HCs and NOx in tail gas.

Description

一种用于坦克尾气净化整体式催化剂的制备方法Preparation method of integrated catalyst for tank exhaust gas purification

技术领域Technical field

本发明涉及坦克尾气净化催化剂技术,具体的说是一种用于坦克尾气净化整体式催化剂的制备方法。The invention relates to tank exhaust gas purification catalyst technology, specifically a preparation method of an integral catalyst for tank exhaust gas purification.

背景技术Background technique

坦克是具有直射火力、越野能力和装甲防护力的履带式装甲战斗车辆,是现代陆上作战的主要武器之一,有“陆战之王”的美称。坦克通常采用大功率柴油机作为动力系统,具备低转速扭矩大,扭矩范围宽,大冷热温差下能正常使用,持续高负荷运转时间长等特点。坦克尾气是一种由多种组分组成的混合物,主要包括烃类化合物(HC)、氮氧化合物(NOx)以及碳烟颗粒物(soot)。其中,NOx会对人体的眼睛、呼吸系统及中枢神经系统等带来永久损害,并且NOx还是形成酸雨的主要原因;HC为燃油不完全燃烧产物,具有毒性、易燃易爆性和致癌作用等特性,并且HC在日照条件下极易与NOx发生光化学反应,是产生光化学烟雾二次污染的罪魁祸首;碳烟颗粒物直径通常为0.01~10微米,在大气中存留时间久、输运距离长,容易造成大范围的污染,此外,碳烟颗粒物还具有很强的致癌效果,其随呼吸进入人体肺部后极易聚集在肺泡等部位,进而导致呼吸系统疾病、心脏疾病甚至导致癌症。Tanks are tracked armored combat vehicles with direct firepower, cross-country capabilities and armor protection. They are one of the main weapons in modern land combat and are known as the "King of Land Warfare". Tanks usually use high-power diesel engines as the power system, which have the characteristics of large low-speed torque, wide torque range, normal use under large hot and cold temperature differences, and long continuous high-load operation time. Tank exhaust is a mixture composed of multiple components, mainly including hydrocarbons (HC), nitrogen oxides ( NOx ) and soot particles (soot). Among them, NO x can cause permanent damage to the human body's eyes, respiratory system and central nervous system, and NO x is also the main cause of acid rain; HC is a product of incomplete combustion of fuel and is toxic, flammable, explosive and carcinogenic. and other properties, and HC is easily photochemically reacted with NO The distance is long and it is easy to cause large-scale pollution. In addition, soot particles also have a strong carcinogenic effect. After they enter the human lungs with breathing, they can easily accumulate in the alveoli and other parts of the lungs, leading to respiratory diseases, heart diseases and even cancer. .

在坦克尾气排气管路上安装尾气净化装置是一种有效而经济的后处理技术,它通常采用过滤器等手段将坦克尾气中碳烟颗粒物进行拦截捕集,使其聚集在净化装置中,但是当碳烟颗粒物积累到一定程度后,会导致尾气背压的增加,影响发动机正常排气,必须用燃烧等手段将其除去,以保住尾气正常的背压,从而实现净化装置再生。如果将催化剂涂覆在过滤器表面,通过催化作用既能将HC氧化成无毒害的CO2,又可以将NO氧化成NO2,并进一步利用NO2较强的氧化能力在低温实现捕集聚集的碳烟颗粒物氧化,就可以实现坦克尾气污染物的有效净化。因此,开发经济高效的坦克尾气净化催化剂有着重要意义的,目前未见有关文献报道。Installing an exhaust purification device on the tank exhaust exhaust pipeline is an effective and economical post-processing technology. It usually uses filters and other means to intercept and capture the soot particles in the tank exhaust and collect them in the purification device. However, When soot particles accumulate to a certain extent, they will increase the back pressure of the exhaust gas and affect the normal exhaust of the engine. They must be removed by combustion and other means to maintain the normal back pressure of the exhaust gas and achieve regeneration of the purification device. If a catalyst is coated on the surface of the filter, HC can be oxidized into non-toxic CO 2 through catalysis, and NO can be oxidized into NO 2 , and the strong oxidation ability of NO 2 can be further used to achieve capture and accumulation at low temperatures. By oxidizing the soot particles, the tank exhaust pollutants can be effectively purified. Therefore, it is of great significance to develop an economical and efficient tank exhaust gas purification catalyst, but there are currently no relevant literature reports.

发明内容Contents of the invention

为了解决上述问题,本发明提供了一种原料安全、制备步骤简单,经济性好,且净化效果好的坦克尾气净化整体式催化剂及制备方法。In order to solve the above problems, the present invention provides an integrated catalyst for tank exhaust gas purification with safe raw materials, simple preparation steps, good economy, and good purification effect, and a preparation method.

为了达到上述目的,本发明是通过以下技术方案来实现的:In order to achieve the above objects, the present invention is achieved through the following technical solutions:

本发明是一种用于坦克尾气净化整体式催化剂的制备方法,催化剂包括载体、粘结涂层和活性物,载体为预处理后的蜂窝陶瓷过滤体,粘结涂层为铝溶胶涂层,活性物为负载贵金属Pt的铈铝混合氧化物;催化剂的制备步骤如下:The invention is a preparation method for an integral catalyst for tank exhaust gas purification. The catalyst includes a carrier, a bonding coating and an active substance. The carrier is a pretreated honeycomb ceramic filter body, and the bonding coating is an aluminum sol coating. The active material is a cerium-aluminum mixed oxide supporting the precious metal Pt; the preparation steps of the catalyst are as follows:

(1)制备载体:将蜂窝陶瓷过滤体置于质量分数为5%~15%的草酸溶液中,加热至85~95℃,预处理6~24h,然后烘干,获得预处理后的蜂窝陶瓷过滤体;(1) Preparation of carrier: Place the honeycomb ceramic filter body in an oxalic acid solution with a mass fraction of 5% to 15%, heat to 85 to 95°C, pretreat for 6 to 24 hours, and then dry to obtain the pretreated honeycomb ceramics filter body;

(2)制备铝溶胶;以拟薄水铝石为铝源,冰醋酸为解胶剂,将拟薄水铝石溶解于去离子水后,加入冰醋酸充分搅拌,获得铝溶胶;(2) Prepare aluminum sol; use pseudo-boehmite as the aluminum source and glacial acetic acid as the deglueing agent. After dissolving the pseudo-boehmite in deionized water, add glacial acetic acid and stir thoroughly to obtain the aluminum sol;

(3)制备活性物:将氧化铝粉末与氧化铈粉末研磨混合,获得混合氧化物粉末;采用等体积浸渍法将适量硝酸铂Pt(NO3)4或氯铂酸H2PtCl6负载到上述混合氧化物粉末上,获得前驱体样品;将所得前驱体样品于120℃烘干1小时,再于500℃煅烧2小时,获得负载贵金属Pt的铈铝混合氧化物;(3) Preparation of active materials: Grind and mix alumina powder and cerium oxide powder to obtain mixed oxide powder; use an equal volume impregnation method to load an appropriate amount of platinum nitrate Pt(NO 3 ) 4 or chloroplatinic acid H 2 PtCl 6 onto the above On the mixed oxide powder, a precursor sample is obtained; the obtained precursor sample is dried at 120°C for 1 hour, and then calcined at 500°C for 2 hours to obtain a cerium-aluminum mixed oxide loaded with precious metal Pt;

(4)制备浆液:将步骤(3)制备的负载贵金属Pt的铈铝混合氧化物加入到步骤(2)制备的铝溶胶中,搅拌混合均匀,加入去离子水,室温陈化,得到混合浆液;(4) Prepare slurry: Add the precious metal Pt-loaded cerium-aluminum mixed oxide prepared in step (3) to the aluminum sol prepared in step (2), stir and mix evenly, add deionized water, and age at room temperature to obtain a mixed slurry. ;

(5)制备整体式催化剂:采用真空抽提法或浸渍法,将混合浆液涂覆在预处理后的蜂窝陶瓷过滤体表面,再将涂覆有混合浆液涂的蜂窝陶瓷过滤体于120℃烘干,在500℃煅烧2小时,重复上述涂覆、烘干、焙烧流程,直至涂覆量达到50g/L以上,获得整体式催化剂。(5) Preparation of monolithic catalyst: Use vacuum extraction method or impregnation method to coat the mixed slurry on the surface of the pretreated honeycomb ceramic filter, and then bake the honeycomb ceramic filter coated with the mixed slurry at 120°C. Dry, calcine at 500°C for 2 hours, and repeat the above coating, drying, and roasting processes until the coating amount reaches more than 50g/L to obtain a monolithic catalyst.

本发明的进一步改进在于:步骤(1)中的蜂窝陶瓷过滤体为壁流式结构,其中,堇青石或莫来石中的一种为蜂窝陶瓷过滤体的主要成分。A further improvement of the present invention is that the honeycomb ceramic filter body in step (1) has a wall flow structure, in which one of cordierite or mullite is the main component of the honeycomb ceramic filter body.

本发明的进一步改进在于:步骤(2)中所加去离子水质量为拟薄水铝石质量的10~20倍,所加冰醋酸质量为拟薄水铝石质量的1~1.5倍。A further improvement of the present invention is that the mass of deionized water added in step (2) is 10-20 times the mass of pseudo-boehmite, and the mass of glacial acetic acid added is 1-1.5 times the mass of pseudo-boehmite.

本发明的进一步改进在于:步骤(3)中氧化铝粉末与氧化铈粉末质量比为3:1~5:1,贵金属Pt负载量为混合氧化物总质量的0.5%~2%。A further improvement of the present invention is that in step (3), the mass ratio of aluminum oxide powder to cerium oxide powder is 3:1 to 5:1, and the loading amount of precious metal Pt is 0.5% to 2% of the total mass of the mixed oxide.

本发明的进一步改进在于:步骤(4)中负载贵金属Pt的铈铝混合氧化物与铝溶胶的质量比为5:1~20:1,所加去离子水质量为负载贵金属Pt的铈铝混合氧化物与铝溶胶总质量的5~20倍,陈化时间为6~12h。A further improvement of the present invention is that in step (4), the mass ratio of the cerium-aluminum mixed oxide loaded with precious metal Pt to the aluminum sol is 5:1 to 20:1, and the mass of the added deionized water is the cerium-aluminum mixed oxide loaded with precious metal Pt. The total mass of oxide and aluminum sol is 5 to 20 times, and the aging time is 6 to 12 hours.

本发明的有益效果是:通过本发明制备的整体式催化剂不仅具有良好的碳烟颗粒氧化去除能力,还能实现尾气中CO、HCs和NOx的有效净化。The beneficial effects of the present invention are: the integrated catalyst prepared by the present invention not only has good soot particle oxidation removal capabilities, but can also achieve effective purification of CO, HC s and NO x in the exhaust gas.

附图说明Description of the drawings

图1是本发明制备的坦克尾气净化整体式催化剂截面示意图。Figure 1 is a schematic cross-sectional view of the integrated catalyst for tank exhaust gas purification prepared by the present invention.

具体实施方式Detailed ways

下面对本发明作进一步描述。以下实施例仅用于更加清楚地说明本发明的技术方案,而不能以此来限制本发明的保护范围。The invention is further described below. The following examples are only used to illustrate the technical solutions of the present invention more clearly, but cannot be used to limit the scope of protection of the present invention.

本发明是一种用于坦克尾气净化整体式催化剂的制备方法,催化剂包括载体1、粘结涂层2和活性物3,载体1为预处理后的蜂窝陶瓷过滤体,粘结涂层2为铝溶胶涂层,活性物3为负载贵金属Pt的铈铝混合氧化物;催化剂的制备步骤如下:The invention is a preparation method for an integral catalyst for tank exhaust gas purification. The catalyst includes a carrier 1, a bonding coating 2 and an active substance 3. The carrier 1 is a pretreated honeycomb ceramic filter body, and the bonding coating 2 is Aluminum sol coating, active material 3 is cerium-aluminum mixed oxide supporting precious metal Pt; the preparation steps of the catalyst are as follows:

(1)制备载体:将蜂窝陶瓷过滤体置于质量分数为5%~15%的草酸溶液中,加热至85~95℃,预处理6~24h,然后烘干,获得预处理后的蜂窝陶瓷过滤体;其中,蜂窝陶瓷过滤体为壁流式结构,其中,堇青石或莫来石中的一种为蜂窝陶瓷过滤体的主要成分:(1) Preparation of carrier: Place the honeycomb ceramic filter body in an oxalic acid solution with a mass fraction of 5% to 15%, heat to 85 to 95°C, pretreat for 6 to 24 hours, and then dry to obtain the pretreated honeycomb ceramic Filter body; wherein, the honeycomb ceramic filter body has a wall flow structure, in which one of cordierite or mullite is the main component of the honeycomb ceramic filter body:

(2)制备铝溶胶;以拟薄水铝石为铝源,冰醋酸为解胶剂,将拟薄水铝石溶解于去离子水后,加入冰醋酸充分搅拌,获得铝溶胶;其中,所加去离子水质量为拟薄水铝石质量的10~20倍,所加冰醋酸质量为拟薄水铝石质量的1~1.5倍;(2) Prepare aluminum sol; use pseudo-boehmite as the aluminum source and glacial acetic acid as the deglueing agent. After dissolving the pseudo-boehmite in deionized water, add glacial acetic acid and stir thoroughly to obtain the aluminum sol; where, The mass of deionized water added is 10 to 20 times the mass of pseudo-boehmite, and the mass of glacial acetic acid added is 1 to 1.5 times the mass of pseudo-boehmite;

(3)制备活性物:将氧化铝粉末与氧化铈粉末研磨混合,获得混合氧化物粉末;采用等体积浸渍法将适量硝酸铂Pt(NO3)4或氯铂酸H2PtCl6负载到上述混合氧化物粉末上,获得前驱体样品;将所得前驱体样品于120℃烘干1小时,再于500℃煅烧2小时,获得负载贵金属Pt的铈铝混合氧化物;其中,氧化铝粉末与氧化铈粉末质量比为5:1~3:1,贵金属Pt负载量为混合氧化物总质量的0.5%~2%;(3) Preparation of active materials: Grind and mix alumina powder and cerium oxide powder to obtain mixed oxide powder; use an equal volume impregnation method to load an appropriate amount of platinum nitrate Pt(NO 3 ) 4 or chloroplatinic acid H 2 PtCl 6 onto the above On the mixed oxide powder, a precursor sample was obtained; the obtained precursor sample was dried at 120°C for 1 hour, and then calcined at 500°C for 2 hours to obtain a cerium-aluminum mixed oxide loaded with precious metal Pt; wherein, the alumina powder and oxide The mass ratio of cerium powder is 5:1 to 3:1, and the loading of precious metal Pt is 0.5% to 2% of the total mass of the mixed oxide;

(4)制备浆液:将步骤(3)制备的负载贵金属Pt的铈铝混合氧化物加入到步骤(2)制备的铝溶胶中,搅拌混合均匀,加入去离子水,室温陈化6h,得到混合浆液;其中,负载贵金属Pt的铈铝混合氧化物与铝溶胶的质量比为20:1~5:1,所加去离子水质量为负载贵金属Pt的铈铝混合氧化物与铝溶胶总质量的5~20倍,陈化时间为6~12h。(4) Preparation of slurry: Add the cerium-aluminum mixed oxide loaded with precious metal Pt prepared in step (3) to the aluminum sol prepared in step (2), stir and mix evenly, add deionized water, and age at room temperature for 6 hours to obtain a mixture Slurry; wherein, the mass ratio of the cerium-aluminum mixed oxide loaded with precious metal Pt to the aluminum sol is 20:1 to 5:1, and the mass of the added deionized water is the total mass of the cerium-aluminum mixed oxide loaded with precious metal Pt and the aluminum sol. 5 to 20 times, and the aging time is 6 to 12 hours.

(5)制备整体式催化剂:采用真空抽提法或浸渍法,将混合浆液涂覆在预处理后的蜂窝陶瓷过滤体表面,再将涂覆有混合浆液涂的蜂窝陶瓷过滤体于120℃烘干,在500℃煅烧2小时,重复上述涂覆、烘干、焙烧流程,直至涂覆量达到50g/L以上,获得整体式催化剂。(5) Preparation of monolithic catalyst: Use vacuum extraction method or impregnation method to coat the mixed slurry on the surface of the pretreated honeycomb ceramic filter, and then bake the honeycomb ceramic filter coated with the mixed slurry at 120°C. Dry, calcine at 500°C for 2 hours, and repeat the above coating, drying, and roasting processes until the coating amount reaches more than 50g/L to obtain a monolithic catalyst.

实施例1Example 1

本发明是一种用于坦克尾气净化整体式催化剂的制备方法,催化剂包括载体、粘结涂层和活性物,载体为预处理后的蜂窝陶瓷过滤体,粘结涂层为铝溶胶涂层,活性物为负载贵金属Pt的铈铝混合氧化物;催化剂的制备步骤如下:The invention is a preparation method for an integral catalyst for tank exhaust gas purification. The catalyst includes a carrier, a bonding coating and an active substance. The carrier is a pretreated honeycomb ceramic filter body, and the bonding coating is an aluminum sol coating. The active material is a cerium-aluminum mixed oxide supporting the precious metal Pt; the preparation steps of the catalyst are as follows:

(1)制备载体:蜂窝陶瓷过滤体为壁流式结构,堇青石为主要成分,将蜂窝陶瓷过滤体置于质量分数为5%的草酸溶液中,加热至85℃,预处理6h,然后烘干,获得预处理后的蜂窝陶瓷过滤体;(1) Preparation of carrier: The honeycomb ceramic filter body has a wall flow structure, and cordierite is the main component. The honeycomb ceramic filter body is placed in an oxalic acid solution with a mass fraction of 5%, heated to 85°C, pretreated for 6 hours, and then baked Dry to obtain the pretreated honeycomb ceramic filter body;

(2)制备铝溶胶:以拟薄水铝石为铝源,冰醋酸为解胶剂,将拟薄水铝石溶解于去离子水后,加入冰醋酸充分搅拌,获得铝溶胶;其中,所加去离子水质量为拟薄水铝石质量的10倍,所加冰醋酸质量为拟薄水铝石质量的1倍;(2) Preparation of aluminum sol: Use pseudo-boehmite as the aluminum source and glacial acetic acid as the deglueing agent. After dissolving the pseudo-boehmite in deionized water, add glacial acetic acid and stir thoroughly to obtain the aluminum sol; where, The mass of deionized water added is 10 times the mass of pseudo-boehmite, and the mass of glacial acetic acid added is 1 times the mass of pseudo-boehmite;

(3)制备活性物:将氧化铝粉末与氧化铈粉末研磨混合,获得混合氧化物粉末;采用等体积浸渍法将适量硝酸铂Pt(NO3)4或氯铂酸H2PtCl6负载到上述混合氧化物粉末上,获得前驱体样品;将所得前驱体样品于120℃烘干1小时,再于500℃煅烧2小时,获得负载贵金属Pt的铈铝混合氧化物;其中,氧化铝粉末与氧化铈粉末质量比为5:1,贵金属Pt负载量为混合氧化物总质量的0.5%;(3) Preparation of active materials: Grind and mix alumina powder and cerium oxide powder to obtain mixed oxide powder; use an equal volume impregnation method to load an appropriate amount of platinum nitrate Pt(NO 3 ) 4 or chloroplatinic acid H 2 PtCl 6 onto the above On the mixed oxide powder, a precursor sample was obtained; the obtained precursor sample was dried at 120°C for 1 hour, and then calcined at 500°C for 2 hours to obtain a cerium-aluminum mixed oxide loaded with precious metal Pt; wherein, the alumina powder and oxide The mass ratio of cerium powder is 5:1, and the loading amount of precious metal Pt is 0.5% of the total mass of the mixed oxide;

(4)制备浆液:将步骤(3)制备的负载贵金属Pt的铈铝混合氧化物加入到步骤(2)制备的铝溶胶中,搅拌混合均匀,加入去离子水,所加去离子水质量为负载贵金属Pt的铈铝混合氧化物与铝溶胶总质量的10倍,室温陈化6h,得到混合浆液;其中,负载贵金属Pt的铈铝混合氧化物与铝溶胶的质量比为20:1;(4) Prepare slurry: Add the cerium-aluminum mixed oxide loaded with precious metal Pt prepared in step (3) to the aluminum sol prepared in step (2), stir and mix evenly, and add deionized water. The mass of the added deionized water is The total mass of cerium-aluminum mixed oxide and aluminum sol loaded with precious metal Pt is 10 times, and aged at room temperature for 6 hours to obtain a mixed slurry; where the mass ratio of cerium-aluminum mixed oxide loaded with precious metal Pt to aluminum sol is 20:1;

(5)制备整体式催化剂:采用真空抽提法,将混合浆液涂覆在预处理后的蜂窝陶瓷过滤体表面,再将涂覆有混合浆液涂的蜂窝陶瓷过滤体于120℃烘干,在500℃煅烧2小时,重复上述涂覆、烘干、焙烧流程3次,涂覆量为52g/L,获得整体式催化剂。(5) Preparation of monolithic catalyst: Use vacuum extraction method to coat the mixed slurry on the surface of the pretreated honeycomb ceramic filter, and then dry the honeycomb ceramic filter coated with the mixed slurry at 120°C. Calculate at 500°C for 2 hours, repeat the above coating, drying, and roasting processes three times. The coating amount is 52g/L to obtain a monolithic catalyst.

实施例2Example 2

与实施例1区别在于:制备步骤(1)的蜂窝陶瓷过滤体的主要成分为莫来石;步骤(3)贵金属Pt负载量为混合氧化物总质量的0.75%;步骤(4)中负载贵金属Pt的铈铝混合氧化物与铝溶胶的质量比为15:1,所加去离子水质量为负载贵金属Pt的铈铝混合氧化物与铝溶胶总质量的5倍,室温陈化时间为6h;步骤(5)采用真空抽提法,将混合浆液涂覆在预处理后的蜂窝陶瓷过滤体表面,再将涂覆有混合浆液涂的蜂窝陶瓷过滤体于120℃烘干,在500℃煅烧2小时,重复上述涂覆、烘干、焙烧流程3次,涂覆量为53g/L。The difference from Example 1 is that: the main component of the honeycomb ceramic filter in the preparation step (1) is mullite; the loading amount of the precious metal Pt in the step (3) is 0.75% of the total mass of the mixed oxide; the precious metal is loaded in the step (4) The mass ratio of Pt's cerium-aluminum mixed oxide and aluminum sol is 15:1, the mass of deionized water added is 5 times the total mass of the cerium-aluminum mixed oxide and aluminum sol loaded with precious metal Pt, and the room temperature aging time is 6 hours; Step (5) uses the vacuum extraction method to coat the mixed slurry on the surface of the pretreated honeycomb ceramic filter, and then dry the honeycomb ceramic filter coated with the mixed slurry at 120°C and calcine at 500°C for 2 hours, repeat the above coating, drying, and roasting processes three times, and the coating amount is 53g/L.

实施例3Example 3

与实施例1区别在于:步骤(1)将蜂窝陶瓷过滤体置于质量分数为8%的草酸溶液中,加热至90℃,预处理12h;步骤(2)中所加去离子水质量为拟薄水铝石质量的12倍,所加冰醋酸质量为拟薄水铝石质量的1.2倍;步骤(3)中贵金属Pt负载量为混合氧化物总质量的1%;步骤(4)中负载贵金属Pt的铈铝混合氧化物与铝溶胶的质量比为12:1,所加去离子水质量为负载贵金属Pt的铈铝混合氧化物与铝溶胶总质量的8倍,室温陈化时间为8h;步骤(5)采用真空抽提法,重复涂覆、烘干、焙烧流程3次,涂覆量为55g/L。The difference from Example 1 is that: in step (1), the honeycomb ceramic filter body is placed in an oxalic acid solution with a mass fraction of 8%, heated to 90°C, and pretreated for 12 hours; in step (2), the mass of deionized water added is 12 times the mass of boehmite, and the mass of glacial acetic acid added is 1.2 times the mass of pseudo-boehmite; the loading of precious metal Pt in step (3) is 1% of the total mass of the mixed oxide; the loading in step (4) The mass ratio of the cerium-aluminum mixed oxide of precious metal Pt to the aluminum sol is 12:1. The mass of deionized water added is 8 times the total mass of the cerium-aluminum mixed oxide and aluminum sol loaded with precious metal Pt. The aging time at room temperature is 8 hours. ; Step (5) uses the vacuum extraction method, repeats the coating, drying, and roasting processes three times, and the coating amount is 55g/L.

实施例4Example 4

与实施例3的区别在于:步骤(1)的蜂窝陶瓷过滤体的主要成分为莫来石;步骤(3)中氧化铝粉末与氧化铈粉末质量比为4.5:1,贵金属Pt负载量为混合氧化物总质量的1.25%;步骤(4)中负载贵金属Pt的铈铝混合氧化物与铝溶胶的质量比为10:1,所加去离子水质量为负载贵金属Pt的铈铝混合氧化物与铝溶胶总质量的12倍,室温陈化时间为8h;步骤(5)重复涂覆、烘干、焙烧流程3次,涂覆量为58g/L。The difference from Example 3 is that: the main component of the honeycomb ceramic filter in step (1) is mullite; in step (3), the mass ratio of alumina powder to cerium oxide powder is 4.5:1, and the loading amount of precious metal Pt is mixed 1.25% of the total mass of the oxide; in step (4), the mass ratio of the cerium-aluminum mixed oxide loaded with precious metal Pt to the aluminum sol is 10:1, and the mass of deionized water added is 10:1. 12 times the total mass of the aluminum sol, and the room temperature aging time is 8 hours; step (5) repeats the coating, drying, and roasting process three times, and the coating amount is 58g/L.

实施例5Example 5

与实施例3的区别在于:步骤(1)将蜂窝陶瓷过滤体置于质量分数为10%的草酸溶液中,加热至90℃,预处理18h;步骤(2)中所加去离子水质量为拟薄水铝石质量的15倍,所加冰醋酸质量为拟薄水铝石质量的1.3倍;步骤(3)中氧化铝粉末与氧化铈粉末质量比为4:1,贵金属Pt负载量为混合氧化物总质量的1.5%;步骤(4)中负载贵金属Pt的铈铝混合氧化物与铝溶胶的质量比为8:1,所加去离子水质量为负载贵金属Pt的铈铝混合氧化物与铝溶胶总质量的15倍,室温陈化时间为10h;步骤(5)中粘结涂层的涂覆量为59g/L。The difference from Example 3 is that: in step (1), the honeycomb ceramic filter body is placed in an oxalic acid solution with a mass fraction of 10%, heated to 90°C, and pretreated for 18 hours; the mass of deionized water added in step (2) is 15 times the mass of pseudo-boehmite, and the mass of glacial acetic acid added is 1.3 times the mass of pseudo-boehmite; in step (3), the mass ratio of alumina powder to cerium oxide powder is 4:1, and the loading amount of precious metal Pt is 1.5% of the total mass of the mixed oxide; in step (4), the mass ratio of the cerium-aluminum mixed oxide loaded with precious metal Pt to the aluminum sol is 8:1, and the mass of the added deionized water is the cerium-aluminum mixed oxide loaded with precious metal Pt It is 15 times the total mass of the aluminum sol, and the aging time at room temperature is 10 hours; the coating amount of the bonding coating in step (5) is 59g/L.

实施例6Example 6

与实施例5的区别在于:步骤(1)蜂窝陶瓷过滤体的主要成分为莫来石,步骤(2)中所加去离子水质量为拟薄水铝石质量的15倍,所加冰醋酸质量为拟薄水铝石质量的1.4倍;步骤(3)中氧化铝粉末与氧化铈粉末质量比为3.5:1,贵金属Pt负载量为混合氧化物总质量的1.75%;步骤(4)中负载贵金属Pt的铈铝混合氧化物与铝溶胶的质量比为7:1,所加去离子水质量为负载贵金属Pt的铈铝混合氧化物与铝溶胶总质量的18倍,室温陈化时间为10h.The difference from Example 5 is that: the main component of the honeycomb ceramic filter in step (1) is mullite, the mass of deionized water added in step (2) is 15 times the mass of pseudo-boehmite, and the glacial acetic acid added The mass is 1.4 times the mass of pseudo-boehmite; in step (3), the mass ratio of alumina powder to cerium oxide powder is 3.5:1, and the precious metal Pt loading is 1.75% of the total mass of the mixed oxide; in step (4) The mass ratio of the cerium-aluminum mixed oxide loaded with precious metal Pt to aluminum sol is 7:1. The mass of deionized water added is 18 times the total mass of the cerium-aluminum mixed oxide loaded with precious metal Pt and aluminum sol. The room temperature aging time is 10h.

实施例7Example 7

与实施例6相比,步骤(1)蜂窝陶瓷过滤体的主要成分为堇青石,将蜂窝陶瓷过滤体置于质量分数为15%的草酸溶液中,加热至95℃,预处理24h;步骤(2)中所加去离子水质量为拟薄水铝石质量的20倍,所加冰醋酸质量为拟薄水铝石质量的1.5倍;步骤(3)中氧化铝粉末与氧化铈粉末质量比为3:1,贵金属Pt负载量为混合氧化物总质量的2%;步骤(4)负载贵金属Pt的铈铝混合氧化物与铝溶胶的质量比为5:1,所加去离子水质量为负载贵金属Pt的铈铝混合氧化物与铝溶胶总质量的20倍,室温陈化时间为12h;步骤(5)中粘结涂层的涂覆量为64g/L。Compared with Example 6, the main component of the honeycomb ceramic filter body in step (1) is cordierite. The honeycomb ceramic filter body is placed in an oxalic acid solution with a mass fraction of 15%, heated to 95°C, and pretreated for 24 hours; step ( The mass of deionized water added in 2) is 20 times the mass of pseudo-boehmite, and the mass of glacial acetic acid added is 1.5 times the mass of pseudo-boehmite; the mass ratio of alumina powder to cerium oxide powder in step (3) is 3:1, and the loading amount of precious metal Pt is 2% of the total mass of the mixed oxide; the mass ratio of the cerium-aluminum mixed oxide and aluminum sol loaded with precious metal Pt in step (4) is 5:1, and the mass of deionized water added is The total mass of the cerium-aluminum mixed oxide and aluminum sol loaded with precious metal Pt is 20 times, and the room temperature aging time is 12 hours; the coating amount of the bonding coating in step (5) is 64g/L.

模拟尾气净化测试Simulated exhaust gas purification test

所制备整体式催化剂置于模拟碳烟再生发生器上进行碳烟上载,上载量为10g/L,在模拟坦克尾气条件下(在10%O2+1000ppmNO+800ppmC3H6,平衡气为N2,空速为100000h-1)进行尾气净化测试,结果如下:The prepared integrated catalyst was placed on a simulated soot regeneration generator for soot uploading. The loading amount was 10g/L. Under simulated tank exhaust conditions (10% O 2 +1000ppmNO+800ppmC 3 H 6 , the balance gas was N 2 , the airspeed is 100000h -1 ) for exhaust gas purification test, the results are as follows:

实车排气烟度测试Real vehicle exhaust smoke test

将所制备整体式催化实施例7封装后,安装于某型坦克车辆顶部,根据《非道路移动柴油机排气烟度限值及测量方法》(GB36886-2018)要求,进行实车排气烟度测试,结果如下:After the prepared integrated catalytic Example 7 was packaged, it was installed on the top of a certain type of tank vehicle. According to the requirements of "Non-road Mobile Diesel Engine Exhaust Smoke Limits and Measurement Methods" (GB36886-2018), the actual vehicle exhaust smoke was measured. Test, the results are as follows:

以上仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明技术原理的前提下,还可以做出若干改进和变形,这些改进和变形也应视为本发明的保护范围。The above are only the preferred embodiments of the present invention. It should be pointed out that for those of ordinary skill in the art, several improvements and deformations can be made without departing from the technical principles of the present invention. These improvements and deformations should also be considered. regarded as the protection scope of the present invention.

Claims (1)

1.一种用于坦克尾气净化整体式催化剂的制备方法,其特征在于:催化剂包括载体、粘结涂层和活性物,所述载体为预处理后的蜂窝陶瓷过滤体,所述蜂窝陶瓷过滤体的主要成分为堇青石;所述粘结涂层为铝溶胶涂层,所述活性物为负载贵金属 Pt 的铈铝混合氧化物;所述催化剂的制备步骤如下:1. A method for preparing an integral catalyst for tank exhaust gas purification, characterized in that: the catalyst includes a carrier, a bonding coating and an active substance, the carrier is a pretreated honeycomb ceramic filter, and the honeycomb ceramic filter The main component of the body is cordierite; the bonding coating is an aluminum sol coating, and the active material is a cerium-aluminum mixed oxide that supports precious metal Pt; the preparation steps of the catalyst are as follows: (1)制备载体:将蜂窝陶瓷过滤体置于质量分数为 15%的草酸溶液中,加热至 95℃,预处理24h,然后烘干,获得预处理后的蜂窝陶瓷过滤体;(1) Preparing the carrier: Place the honeycomb ceramic filter body in an oxalic acid solution with a mass fraction of 15%, heat to 95°C, pretreat for 24 hours, and then dry to obtain the pretreated honeycomb ceramic filter body; (2)制备铝溶胶;以拟薄水铝石为铝源,冰醋酸为解胶剂,将拟薄水铝石溶解于去离子水后,加入冰醋酸充分搅拌,获得铝溶胶;(2) Prepare aluminum sol; use pseudo-boehmite as the aluminum source and glacial acetic acid as the deglueing agent. After dissolving the pseudo-boehmite in deionized water, add glacial acetic acid and stir thoroughly to obtain the aluminum sol; (3)制备活性物:将氧化铝粉末与氧化铈粉末研磨混合,获得混合氧化物粉末;采用等体积浸渍法将硝酸铂 Pt(NO3)4或氯铂酸 H2PtCl6负载到上述混合氧化物粉末上,获得前驱体样品;将所得前驱体样品于120℃烘干 1 小时,再于 500℃煅烧 2 小时,获得负载贵金属 Pt 的铈铝混合氧化物;(3) Preparation of active materials: Grind and mix alumina powder and cerium oxide powder to obtain mixed oxide powder; use an equal volume impregnation method to load platinum nitrate Pt(NO 3 ) 4 or chloroplatinic acid H 2 PtCl 6 into the above mixture. On the oxide powder, a precursor sample was obtained; the obtained precursor sample was dried at 120°C for 1 hour, and then calcined at 500°C for 2 hours to obtain a cerium-aluminum mixed oxide loaded with precious metal Pt; (4)制备浆液:将步骤(3)制备的负载贵金属 Pt 的铈铝混合氧化物加入到步骤(2)制备的铝溶胶中,搅拌混合均匀,加入去离子水,室温陈化,得到混合浆液;(4) Preparation of slurry: Add the cerium-aluminum mixed oxide loaded with precious metal Pt prepared in step (3) to the aluminum sol prepared in step (2), stir and mix evenly, add deionized water, and age at room temperature to obtain a mixed slurry. ; (5)制备整体式催化剂:采用真空抽提法或浸渍法,将混合浆液涂覆在预处理后的蜂窝陶瓷过滤体表面,再将涂覆有混合浆液涂的蜂窝陶瓷过滤体于 120℃烘干,在 500℃煅烧2 小时,重复上述涂覆、烘干、焙烧流程,直至涂覆量达到 64g/L,获得整体式催化剂;(5) Preparation of monolithic catalyst: Use vacuum extraction method or impregnation method to coat the mixed slurry on the surface of the pretreated honeycomb ceramic filter, and then bake the honeycomb ceramic filter coated with the mixed slurry at 120°C. Dry, calcine at 500°C for 2 hours, repeat the above coating, drying, and roasting processes until the coating amount reaches 64g/L to obtain a monolithic catalyst; 步骤(2)中所加去离子水质量为拟薄水铝石质量的 20 倍,所加冰醋酸质量为拟薄水铝石质量的 1.5 倍;The mass of deionized water added in step (2) is 20 times the mass of pseudo-boehmite, and the mass of glacial acetic acid added is 1.5 times the mass of pseudo-boehmite; 步骤(3)中所述氧化铝粉末与氧化铈粉末质量比为 3:1,贵金属 Pt 负载量为混合氧化物总质量的 2%;The mass ratio of alumina powder to cerium oxide powder described in step (3) is 3:1, and the loading of precious metal Pt is 2% of the total mass of the mixed oxide; 步骤(4)中所述负载贵金属 Pt 的铈铝混合氧化物与铝溶胶的质量比为 5:1,所加去离子水质量为负载贵金属 Pt 的铈铝混合氧化物与铝溶胶总质量的20 倍,陈化时间为12h。The mass ratio of the cerium-aluminum mixed oxide and aluminum sol loaded with precious metal Pt as described in step (4) is 5:1, and the mass of deionized water added is 20% of the total mass of the cerium-aluminum mixed oxide loaded with precious metal Pt and aluminum sol. times, and the aging time is 12h.
CN202011057834.8A 2020-09-30 2020-09-30 Preparation method of integral catalyst for purifying tank tail gas Active CN112138658B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202011057834.8A CN112138658B (en) 2020-09-30 2020-09-30 Preparation method of integral catalyst for purifying tank tail gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202011057834.8A CN112138658B (en) 2020-09-30 2020-09-30 Preparation method of integral catalyst for purifying tank tail gas

Publications (2)

Publication Number Publication Date
CN112138658A CN112138658A (en) 2020-12-29
CN112138658B true CN112138658B (en) 2023-09-15

Family

ID=73894351

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202011057834.8A Active CN112138658B (en) 2020-09-30 2020-09-30 Preparation method of integral catalyst for purifying tank tail gas

Country Status (1)

Country Link
CN (1) CN112138658B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114130390B (en) * 2021-10-20 2023-05-12 四川大学 Method for preparing integral torch burning catalyst based on etching method and application

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007083224A (en) * 2005-08-23 2007-04-05 Mazda Motor Corp Diesel particulate filter
CN101203301A (en) * 2005-06-20 2008-06-18 丰田自动车株式会社 Catalysts for exhaust gas purification
EP2042226A2 (en) * 2007-09-27 2009-04-01 Umicore AG & Co. KG Removal of particles from exhaust gas from combustion engines run on a primarily stoichiometric air/fuel mixture
CN102872920A (en) * 2011-07-11 2013-01-16 中国石油化工股份有限公司 Preparation method of catalyst for catalytic combustion of organic exhaust gas
CN103041873A (en) * 2011-10-17 2013-04-17 中国石油化工股份有限公司 Catalytic combustion catalyst and preparation method thereof
CN105749911A (en) * 2016-02-26 2016-07-13 凯龙蓝烽新材料科技有限公司 Preparation method of ammoxidation catalyst
CN106040259A (en) * 2016-06-24 2016-10-26 浙江恒荣环保科技有限公司 Catalyst for catalytic combustion of VOCs and preparation method of catalyst
CN108031472A (en) * 2017-12-01 2018-05-15 杭州尹力环保科技有限公司 A kind of Pd-Pt catalyst for purifying organic waste gas and preparation method thereof
CN109647088A (en) * 2018-12-26 2019-04-19 中自环保科技股份有限公司 A kind of preparation method of low back pressure and high soot filter efficiency diesel particulate filter
CN111672503A (en) * 2020-06-03 2020-09-18 南京工程学院 A kind of supported long-acting formaldehyde purifying agent and preparation method and application thereof

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101203301A (en) * 2005-06-20 2008-06-18 丰田自动车株式会社 Catalysts for exhaust gas purification
JP2007083224A (en) * 2005-08-23 2007-04-05 Mazda Motor Corp Diesel particulate filter
EP2042226A2 (en) * 2007-09-27 2009-04-01 Umicore AG & Co. KG Removal of particles from exhaust gas from combustion engines run on a primarily stoichiometric air/fuel mixture
CN102872920A (en) * 2011-07-11 2013-01-16 中国石油化工股份有限公司 Preparation method of catalyst for catalytic combustion of organic exhaust gas
CN103041873A (en) * 2011-10-17 2013-04-17 中国石油化工股份有限公司 Catalytic combustion catalyst and preparation method thereof
CN105749911A (en) * 2016-02-26 2016-07-13 凯龙蓝烽新材料科技有限公司 Preparation method of ammoxidation catalyst
CN106040259A (en) * 2016-06-24 2016-10-26 浙江恒荣环保科技有限公司 Catalyst for catalytic combustion of VOCs and preparation method of catalyst
CN108031472A (en) * 2017-12-01 2018-05-15 杭州尹力环保科技有限公司 A kind of Pd-Pt catalyst for purifying organic waste gas and preparation method thereof
CN109647088A (en) * 2018-12-26 2019-04-19 中自环保科技股份有限公司 A kind of preparation method of low back pressure and high soot filter efficiency diesel particulate filter
CN111672503A (en) * 2020-06-03 2020-09-18 南京工程学院 A kind of supported long-acting formaldehyde purifying agent and preparation method and application thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
VOCs脱除技术的研究进展;王晓丽等;《广东化工》;20140830;第41卷(第16期);第106-107页 *

Also Published As

Publication number Publication date
CN112138658A (en) 2020-12-29

Similar Documents

Publication Publication Date Title
CN108404975B (en) Oxidation type catalytic system with good low-temperature ignition performance and preparation process thereof
JP3061399B2 (en) Diesel engine exhaust gas purification catalyst and purification method
CN112135685B (en) three way catalyst
CN102631917B (en) Oxidation catalyst for purifying exhaust of diesel vehicle and preparation method for oxidation catalyst
CN106560240B (en) Low temperature oxidation catalyst
CN113304745A (en) Pt-Pd-Rh ternary catalyst and preparation method thereof
CN109589960B (en) A kind of wall-flow catalyst with low noble metal content, preparation method and application thereof
CN104895652B (en) Reduce the granular material discharged catalyzed diesel particulate filter of diesel vehicle and preparation method
WO2020253726A1 (en) Cerium-zirconium-aluminium-based composite material, cgpf catalyst and preparation method therefor
CN111841534A (en) Catalyst for exhaust gas purification
JP2002001124A (en) Exhaust gas purification catalyst and exhaust gas purification method
WO2015005342A1 (en) Nitrogen oxide removal catalyst
WO2020073667A1 (en) Integrated catalyst system for stoichiometric-burn natural gas vehicles and preparation method therefor
CN117241882A (en) Platinum-containing three-way catalyst for tight coupling engine applications
CN112138658B (en) Preparation method of integral catalyst for purifying tank tail gas
JPS60110335A (en) Catalyst for purifying exhaust gas
CN102000507B (en) Reducing gas injection and quadruple-effect catalysis purification system for diesel vehicle tail gas treatment
CN111997718A (en) Post-processing method applied to diesel-natural gas dual-fuel vehicle
CN114251158B (en) Diesel exhaust particulate matter catalytic filter and method for manufacturing same
JP3835025B2 (en) Exhaust gas purification material and exhaust gas purification apparatus using the same
CN104797334A (en) Zoned diesel oxidation catalyst
CN1391983A (en) Purifying catalyst for diesel engine exhaust gas and its preparing method
JP4459346B2 (en) Exhaust gas purification catalyst
CN111821971B (en) Integral catalyst for catalytic regeneration of carbon smoke and preparation method thereof
CN113578307B (en) Efficient vehicle natural gas catalyst and preparation method thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant