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CN117923893A - A method for preparing aluminum titanate ceramics - Google Patents

A method for preparing aluminum titanate ceramics Download PDF

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CN117923893A
CN117923893A CN202410339073.7A CN202410339073A CN117923893A CN 117923893 A CN117923893 A CN 117923893A CN 202410339073 A CN202410339073 A CN 202410339073A CN 117923893 A CN117923893 A CN 117923893A
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aluminum titanate
titanium
waste
present
vanadium
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CN117923893B (en
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曹卫刚
郑珑
许亚男
蔡宗英
靳嘉浩
李慧
梁精龙
严红燕
杨宇
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North China University of Science and Technology
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Abstract

本发明属于固废回收技术领域,具体涉及一种钛酸铝陶瓷的制备方法。本发明提供了一种钛酸铝陶瓷的制备方法,包括以下步骤:将钒钛基废选择性催化还原催化剂和氧化铝混合,依次进行压制和烧结,得到所述钛酸铝陶瓷。本发明提供的制备方法以钒钛基废选择性催化还原(SCR)催化剂为原料,与氧化铝粉末进行压制烧结,使废SCR催化剂与氧化铝同时接受高温和压力,有热能和应力去促进粉末颗粒的结合和材料的致密化,得到的钛酸铝陶瓷纯度较高。区别于现有湿法回收工艺中以金属化合物形式回收废SCR催化剂,本发明提供的方法实现了废SCR催化剂的高附加价值利用,并且过程简单,安全环保。

The present invention belongs to the technical field of solid waste recycling, and specifically relates to a method for preparing aluminum titanate ceramics. The present invention provides a method for preparing aluminum titanate ceramics, comprising the following steps: mixing vanadium-titanium-based waste selective catalytic reduction catalyst and alumina, pressing and sintering in sequence, to obtain the aluminum titanate ceramics. The preparation method provided by the present invention uses vanadium-titanium-based waste selective catalytic reduction (SCR) catalyst as raw material, and presses and sinters it with alumina powder, so that the waste SCR catalyst and alumina are subjected to high temperature and pressure at the same time, and thermal energy and stress are used to promote the bonding of powder particles and the densification of materials, and the obtained aluminum titanate ceramics have high purity. Different from the existing wet recovery process in which waste SCR catalysts are recovered in the form of metal compounds, the method provided by the present invention realizes the high added value utilization of waste SCR catalysts, and the process is simple, safe and environmentally friendly.

Description

一种钛酸铝陶瓷的制备方法A method for preparing aluminum titanate ceramics

技术领域Technical Field

本发明属于固废回收技术领域,具体涉及一种钛酸铝陶瓷的制备方法。The invention belongs to the technical field of solid waste recycling, and specifically relates to a method for preparing aluminum titanate ceramics.

背景技术Background technique

钒钛基选择性催化还原(SCR)催化剂主要应用于烟气脱硝处理工艺,此种催化剂在使用过程中,受工作环境的影响会导致其活性组分或微观结构发生变化,进而使其脱硝性能下降,严重时失去活性。根据所用钒钛基SCR催化剂所使用的场所的不同,钒钛基SCR催化剂的组成和含量会有所不同,但是主要物质为二氧化钛,占比达到80%以上,回收再利用价值高。Vanadium-titanium-based selective catalytic reduction (SCR) catalysts are mainly used in flue gas denitration treatment processes. During use, the active components or microstructures of such catalysts will change due to the influence of the working environment, which will reduce their denitration performance and even cause them to lose activity in severe cases. The composition and content of the vanadium-titanium-based SCR catalysts will vary depending on the location where they are used, but the main substance is titanium dioxide, which accounts for more than 80%, and has high recycling value.

目前,对于失去活性的废SCR催化剂,回收处理主要是通过酸溶、碱溶、盐溶等方法提取其中的贵金属,或者通过高温熔炼将其中的金属元素还原成金属单质或合金。但是,由于废SCR催化剂的成分复杂,不同类型和不同产地的废SCR催化剂可能具有不同的性质和成分,因此需要采取不同的处理方法和工艺,且回收利用率较低。At present, the recycling of inactive waste SCR catalysts mainly involves extracting precious metals through acid dissolution, alkali dissolution, salt dissolution, etc., or reducing the metal elements into metal elements or alloys through high-temperature smelting. However, due to the complex composition of waste SCR catalysts, waste SCR catalysts of different types and origins may have different properties and components, so different treatment methods and processes are required, and the recycling rate is low.

发明内容Summary of the invention

本发明的目的在于提供一种钛酸铝陶瓷的制备方法,本发明提供的方法能够实现钒钛基废选择性催化还原催化剂的高效资源化利用,制备出纯度较高的钛酸铝陶瓷。The purpose of the present invention is to provide a method for preparing aluminum titanate ceramics. The method provided by the present invention can achieve efficient resource utilization of vanadium-titanium-based waste selective catalytic reduction catalysts and prepare aluminum titanate ceramics with higher purity.

为了实现上述目的,本发明提供如下技术方案:In order to achieve the above object, the present invention provides the following technical solutions:

本发明提供了一种钛酸铝陶瓷的制备方法,包括以下步骤:The present invention provides a method for preparing aluminum titanate ceramics, comprising the following steps:

将钒钛基废选择性催化还原催化剂和氧化铝混合,依次进行压制和烧结,得到所述钛酸铝陶瓷。The aluminum titanate ceramic is obtained by mixing the vanadium-titanium-based waste selective catalytic reduction catalyst and alumina, pressing and sintering them in sequence.

优选地,所述钒钛基废选择性催化还原催化剂中二氧化钛的质量百分含量为70~100%。Preferably, the mass percentage of titanium dioxide in the vanadium-titanium-based spent selective catalytic reduction catalyst is 70-100%.

优选地,所述钒钛基废选择性催化还原催化剂和氧化铝的质量比为9:10~15。Preferably, the mass ratio of the vanadium-titanium based waste selective catalytic reduction catalyst to alumina is 9:10-15.

优选地,所述混合为球磨;所述球磨的转速为200~600r/min,时间为4~16h。Preferably, the mixing is performed by ball milling; the rotation speed of the ball milling is 200-600 r/min, and the time is 4-16 h.

优选地,所述球磨为湿磨;所述湿磨的分散剂为酒精。Preferably, the ball milling is wet milling; and the dispersant of the wet milling is alcohol.

优选地,所述压制的压力为8~12MPa,保压时间为1~3min。Preferably, the pressing pressure is 8-12 MPa, and the holding time is 1-3 min.

优选地,所述烧结温度为1300~1600℃,保温时间为2~6h。Preferably, the sintering temperature is 1300-1600° C., and the holding time is 2-6 hours.

优选地,所述混合前还包括将所述钒钛基废选择性催化还原催化剂依次进行清洗、干燥、粉碎和过筛。Preferably, before the mixing, the vanadium-titanium based waste selective catalytic reduction catalyst is sequentially washed, dried, crushed and sieved.

优选地,所述清洗为超声清洗;所述超声清洗的时间为8~16h;Preferably, the cleaning is ultrasonic cleaning; the time of the ultrasonic cleaning is 8 to 16 hours;

所述干燥为烘干;所述烘干的温度为60~120℃,时间为12~36h。The drying is oven drying; the oven drying temperature is 60-120° C. and the drying time is 12-36 hours.

优选地,所述过筛的筛网目数为200~600目。Preferably, the mesh size of the sieve is 200-600 meshes.

本发明提供了一种钛酸铝陶瓷的制备方法,包括以下步骤:将钒钛基废选择性催化还原催化剂和氧化铝混合,依次进行压制和烧结,得到所述钛酸铝陶瓷。本发明提供的制备方法以钒钛基废选择性催化还原(SCR)催化剂为原料,与氧化铝粉末进行压制烧结,使废SCR催化剂与氧化铝同时接受高温和压力,用热能和应力去促进粉末颗粒的结合和材料的致密化,得到的钛酸铝陶瓷纯度较高。区别于现有湿法回收工艺中以金属化合物形式回收废SCR催化剂,本发明提供的方法实现了废SCR催化剂的高附加价值利用和固体废物的无害化和资源化,并且过程简单,在回收利用的过程中,无污染性废液或者气体产生,安全环保。The present invention provides a method for preparing aluminum titanate ceramics, comprising the following steps: mixing vanadium-titanium-based waste selective catalytic reduction catalyst and alumina, and pressing and sintering them in sequence to obtain the aluminum titanate ceramics. The preparation method provided by the present invention uses vanadium-titanium-based waste selective catalytic reduction (SCR) catalyst as raw material, and presses and sinters it with alumina powder, so that the waste SCR catalyst and alumina are subjected to high temperature and pressure at the same time, and uses thermal energy and stress to promote the bonding of powder particles and the densification of materials, and the obtained aluminum titanate ceramics have high purity. Different from the existing wet recovery process in which waste SCR catalysts are recovered in the form of metal compounds, the method provided by the present invention realizes the high added value utilization of waste SCR catalysts and the harmlessness and resource utilization of solid wastes, and the process is simple. During the recycling process, no polluting waste liquid or gas is generated, which is safe and environmentally friendly.

附图说明BRIEF DESCRIPTION OF THE DRAWINGS

为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动性的前提下,还可以根据这些附图获得其他的附图。In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the drawings required for use in the embodiments will be briefly introduced below. Obviously, the drawings described below are only some embodiments of the present invention. For ordinary technicians in this field, other drawings can be obtained based on these drawings without paying creative labor.

图1为实施例1所得钛酸铝陶瓷的X射线衍射图谱(上)和钛酸铝标准XRD图谱(下)对照图;FIG1 is a comparison diagram of the X-ray diffraction spectrum of the aluminum titanate ceramic obtained in Example 1 (upper) and the standard XRD spectrum of aluminum titanate (lower);

图2为实施例2所得钛酸铝陶瓷的X射线衍射图谱(上)和钛酸铝标准XRD图谱(下)对照图。FIG2 is a comparison diagram of the X-ray diffraction spectrum of the aluminum titanate ceramic obtained in Example 2 (top) and the standard XRD spectrum of aluminum titanate (bottom).

具体实施方式Detailed ways

本发明提供了一种钛酸铝陶瓷的制备方法,包括以下步骤:The present invention provides a method for preparing aluminum titanate ceramics, comprising the following steps:

将钒钛基废选择性催化还原催化剂和氧化铝混合,依次进行压制和烧结,得到所述钛酸铝陶瓷。The aluminum titanate ceramic is obtained by mixing the vanadium-titanium-based waste selective catalytic reduction catalyst and alumina, pressing and sintering them in sequence.

在本发明中,若无特殊说明,所有原料组分均为本领域技术人员熟知的市售产品。In the present invention, unless otherwise specified, all raw material components are commercially available products well known to those skilled in the art.

在本发明中,所述钒钛基废选择性催化还原催化剂中二氧化钛的质量百分含量优选为70~100%,更优选为80~90%,最优选为86.29%;氧化钨的质量百分含量优选为0~10%,更优选为2~8%,最优选为5.24%;氧化钙的质量百分含量优选为0~3%,更优选为1~2%,最优选为1.40%;氧化硅的质量百分含量优选为0~10%,更优选为2~8%,最优选为4.34%;五氧化二钒的质量百分含量优选为0~5%,更优选为0.5~3%,最优选为0.69%。In the present invention, the mass percentage of titanium dioxide in the vanadium-titanium-based waste selective catalytic reduction catalyst is preferably 70-100%, more preferably 80-90%, and most preferably 86.29%; the mass percentage of tungsten oxide is preferably 0-10%, more preferably 2-8%, and most preferably 5.24%; the mass percentage of calcium oxide is preferably 0-3%, more preferably 1-2%, and most preferably 1.40%; the mass percentage of silicon oxide is preferably 0-10%, more preferably 2-8%, and most preferably 4.34%; the mass percentage of vanadium pentoxide is preferably 0-5%, more preferably 0.5-3%, and most preferably 0.69%.

在本发明中,所述混合前还包括将所述钒钛基废选择性催化还原催化剂依次进行清洗、干燥、粉碎和过筛。In the present invention, the step of washing, drying, crushing and sieving the vanadium-titanium based waste selective catalytic reduction catalyst in sequence before the mixing.

在本发明中,所述清洗优选为超声清洗;所述超声清洗的时间优选为8~16h,更优选为10~14h;所述超声清洗优选在超声波清洗仪中进行;所述清洗的作用为除灰,去除废SCR催化剂中大量尘土。In the present invention, the cleaning is preferably ultrasonic cleaning; the time of the ultrasonic cleaning is preferably 8 to 16 hours, more preferably 10 to 14 hours; the ultrasonic cleaning is preferably carried out in an ultrasonic cleaning instrument; the cleaning serves to remove ash and a large amount of dust from the waste SCR catalyst.

在本发明中,所述干燥优选为烘干;所述烘干的温度优选为60~120℃,更优选为80~100℃;时间优选为12~36h,更优选为18~30h。In the present invention, the drying is preferably oven drying; the oven drying temperature is preferably 60-120° C., more preferably 80-100° C.; the oven drying time is preferably 12-36 h, more preferably 18-30 h.

在本发明中,所述过筛的筛网目数优选为200~600目,更优选为300~500目。In the present invention, the mesh size of the sieve is preferably 200-600 meshes, more preferably 300-500 meshes.

在本发明中,所述钒钛基废选择性催化还原催化剂和氧化铝的质量比优选为9:10~15,更优选为9:10~13,最优选为9:10~11。In the present invention, the mass ratio of the vanadium-titanium-based spent selective catalytic reduction catalyst to alumina is preferably 9:10-15, more preferably 9:10-13, and most preferably 9:10-11.

在本发明中,所述混合为球磨;所述球磨的转速优选为200~600r/min,更优选为300~500r/min;时间优选为4~16h,更优选为8~12h;所述球磨优选为湿磨;所述湿磨的分散剂优选为酒精;本发明对所述酒精的用量没有任何特殊的限定,采用本领域技术人员熟知的球磨分散剂的用量浸没球磨原料即可。In the present invention, the mixing is ball milling; the rotation speed of the ball mill is preferably 200-600 r/min, more preferably 300-500 r/min; the time is preferably 4-16 h, more preferably 8-12 h; the ball milling is preferably wet milling; the dispersant for wet milling is preferably alcohol; the present invention does not have any special limitation on the amount of the alcohol, and the amount of ball milling dispersant well known to those skilled in the art can be used to immerse the ball milling raw materials.

在本发明中,所述球磨后还优选包括烘干;所述烘干的温度优选为60~120℃,更优选为80~100℃;时间优选为12~36h,更优选为18~30h。In the present invention, the ball milling is preferably followed by drying; the drying temperature is preferably 60-120° C., more preferably 80-100° C.; the drying time is preferably 12-36 h, more preferably 18-30 h.

在本发明中,所述压制的压力优选为8~12MPa,更优选为9~11MPa;保压时间优选为1~3min,更优选为2~3min。In the present invention, the pressing pressure is preferably 8-12 MPa, more preferably 9-11 MPa; the holding time is preferably 1-3 min, more preferably 2-3 min.

在本发明中,所述烧结温度优选为1300~1600℃,更优选为1400~1500℃;保温时间优选为2~6h,更优选为3~5h。In the present invention, the sintering temperature is preferably 1300-1600° C., more preferably 1400-1500° C.; the holding time is preferably 2-6 hours, more preferably 3-5 hours.

本发明提供的制备方法以钒钛基废选择性催化还原(SCR)催化剂为原料,与氧化铝粉末进行压制烧结,使废SCR催化剂与氧化铝同时接受高温和压力,有热能和应力去促进粉末颗粒的结合和材料的致密化,得到的钛酸铝陶瓷纯度较高。区别于现有湿法回收工艺中以金属化合物形式回收废SCR催化剂,本发明提供的方法实现了废SCR催化剂的高附加价值利用和固体废物的无害化和资源化,并且过程简单,在回收利用的过程中,无污染性废液或者气体产生,安全环保。本发明所述制备方法中的主要化学反应式为式1:The preparation method provided by the present invention uses vanadium-titanium-based waste selective catalytic reduction (SCR) catalyst as raw material, and presses and sinters it with alumina powder, so that the waste SCR catalyst and alumina are subjected to high temperature and pressure at the same time, and thermal energy and stress are used to promote the bonding of powder particles and the densification of materials, and the obtained aluminum titanate ceramic has a high purity. Different from the existing wet recovery process in which waste SCR catalysts are recovered in the form of metal compounds, the method provided by the present invention realizes the high added value utilization of waste SCR catalysts and the harmlessness and resource utilization of solid waste, and the process is simple. During the recycling process, no polluting waste liquid or gas is generated, which is safe and environmentally friendly. The main chemical reaction formula in the preparation method described in the present invention is Formula 1:

TiO2+Al2O3=Al2TiO5(式1)。TiO 2 +Al 2 O 3 =Al 2 TiO 5 (Formula 1).

为了进一步说明本发明,下面结合附图和实施例对本发明提供的钛酸铝陶瓷的制备方法进行详细地描述,但不能将它们理解为对本发明保护范围的限定。In order to further illustrate the present invention, the preparation method of the aluminum titanate ceramic provided by the present invention is described in detail below in conjunction with the accompanying drawings and examples, but they should not be construed as limiting the protection scope of the present invention.

实施例1Example 1

将块状钒钛基废SCR催化剂置于蒸馏水中,置于超声波清洗仪超声清洗12h。将废SCR催化剂取出,在80℃烘干箱中烘24h,然后将废SCR催化剂粉碎,过400目筛,得到粉碎废SCR催化剂。所述钒钛基废选择性催化还原催化剂中二氧化钛的质量百分含量为86.29%,氧化钨的质量百分含量为5.24%,氧化钙的质量百分含量为1.40%,氧化硅的质量百分含量为4.34%,五氧化二钒的质量百分含量为0.69%。The bulk vanadium-titanium-based waste SCR catalyst is placed in distilled water and ultrasonically cleaned in an ultrasonic cleaner for 12 hours. The waste SCR catalyst is taken out and dried in an 80°C drying oven for 24 hours, and then the waste SCR catalyst is crushed and passed through a 400-mesh sieve to obtain a crushed waste SCR catalyst. The mass percentage of titanium dioxide in the vanadium-titanium-based waste selective catalytic reduction catalyst is 86.29%, the mass percentage of tungsten oxide is 5.24%, the mass percentage of calcium oxide is 1.40%, the mass percentage of silicon oxide is 4.34%, and the mass percentage of vanadium pentoxide is 0.69%.

称取9.25g废SCR催化剂与10.2g氧化铝,放入球磨罐中,加入酒精,使酒精刚好淹没粉末,进行机械球磨,转速为300r/min,时间为12h,将混合均匀的废SCR催化剂与氧化铝放入蒸发皿中,在80℃烘干箱中烘24h,最后将干燥的,混合均与的废SCR催化剂与氧化铝取出,进行压片。Weigh 9.25g of waste SCR catalyst and 10.2g of alumina, put them into a ball mill, add alcohol to make the alcohol just submerge the powder, and perform mechanical ball milling at a speed of 300r/min for 12h. Put the evenly mixed waste SCR catalyst and alumina into an evaporating dish and bake them in an 80℃ drying oven for 24h. Finally, take out the dried, evenly mixed waste SCR catalyst and alumina and press them into tablets.

称取1g混合均匀的废SCR催化剂与氧化铝放入直径为8mm的圆形模具中进行压片,压力为10MPa,时间为2.5min。1 g of the uniformly mixed waste SCR catalyst and alumina was weighed and put into a circular mold with a diameter of 8 mm for tableting at a pressure of 10 MPa for 2.5 min.

将压好的片放入坩埚中,将坩埚放入高温炉中,升温到1500℃,并在1500℃温度下保温4h,保温结束后,随炉冷却到室温,将烧结后的片取出,得到钛酸铝陶瓷。The pressed sheet is placed in a crucible, and the crucible is placed in a high-temperature furnace, heated to 1500°C, and kept at 1500°C for 4 hours. After the insulation is completed, the furnace is cooled to room temperature, and the sintered sheet is taken out to obtain aluminum titanate ceramics.

本实施例所得钛酸铝陶瓷的X射线衍射图谱(上)和钛酸铝标准XRD图谱(下)如图1所示,从图1可以看出,所得钛酸铝陶瓷主相为钛酸铝,其他杂质相含量低,产物纯度较高。The X-ray diffraction spectrum (upper) and the standard XRD spectrum (lower) of the aluminum titanate ceramic obtained in this embodiment are shown in FIG. 1 . As can be seen from FIG. 1 , the main phase of the obtained aluminum titanate ceramic is aluminum titanate, the content of other impurity phases is low, and the product purity is relatively high.

实施例2Example 2

将块状钒钛基废SCR催化剂置于蒸馏水中,置于超声波清洗仪超声清洗12h。将废SCR催化剂取出,在80℃烘干箱中烘24h,然后将废SCR催化剂粉碎,过400目筛,得到粉碎废SCR催化剂。The bulk vanadium-titanium-based waste SCR catalyst was placed in distilled water and ultrasonically cleaned in an ultrasonic cleaner for 12 hours. The waste SCR catalyst was taken out and dried in a drying oven at 80°C for 24 hours, and then the waste SCR catalyst was crushed and passed through a 400-mesh sieve to obtain a crushed waste SCR catalyst.

称取9.25g废SCR催化剂与11.22g氧化铝,放入球磨罐中,加入酒精,使酒精刚好淹没粉末,进行机械球磨,转速为300r/min,时间为12h,将混合均匀的废SCR催化剂与氧化铝放入蒸发皿中,在80℃烘干箱中烘24h,最后将干燥的,混合均与的废SCR催化剂与氧化铝取出,进行压片。Weigh 9.25g of waste SCR catalyst and 11.22g of alumina, put them into a ball mill, add alcohol to make the alcohol just submerge the powder, and perform mechanical ball milling at a speed of 300r/min for 12h. Put the evenly mixed waste SCR catalyst and alumina into an evaporating dish and bake them in an 80℃ drying oven for 24h. Finally, take out the dried, evenly mixed waste SCR catalyst and alumina and press them into tablets.

称取1g混合均匀的废SCR催化剂与氧化铝放入直径为8mm的圆形模具中进行压片,压力为10MPa,时间为2.5min。1 g of the uniformly mixed waste SCR catalyst and alumina was weighed and put into a circular mold with a diameter of 8 mm for tableting at a pressure of 10 MPa for 2.5 min.

将压好的片放入坩埚中,将坩埚放入高温炉中,升温到1500℃,并在1500℃温度下保温4h,保温结束后,随炉冷却到室温,将烧结后的片取出,得到钛酸铝陶瓷。The pressed sheet is placed in a crucible, and the crucible is placed in a high-temperature furnace, heated to 1500°C, and kept at 1500°C for 4 hours. After the insulation is completed, the furnace is cooled to room temperature, and the sintered sheet is taken out to obtain aluminum titanate ceramics.

本实施例所得钛酸铝陶瓷的X射线衍射图谱(上)和钛酸铝标准XRD图谱(下)如图2所示,从XRD图中可以看出,所得钛酸铝陶瓷主相为钛酸铝,其他杂质相含量低,产物纯度较高。The X-ray diffraction pattern (above) and the standard XRD pattern (below) of the aluminum titanate ceramic obtained in this embodiment are shown in FIG. 2 . It can be seen from the XRD pattern that the main phase of the aluminum titanate ceramic obtained is aluminum titanate, the content of other impurity phases is low, and the product purity is relatively high.

尽管上述实施例对本发明做出了详尽的描述,但它仅仅是本发明一部分实施例,而不是全部实施例,还可以根据本实施例在不经创造性前提下获得其他实施例,这些实施例都属于本发明保护范围。Although the above embodiment describes the present invention in detail, it is only a part of the embodiments of the present invention, not all of the embodiments. Other embodiments can be obtained based on this embodiment without creativity, and these embodiments all fall within the protection scope of the present invention.

Claims (10)

1. The preparation method of the aluminum titanate ceramic is characterized by comprising the following steps of:
mixing the vanadium-titanium-based waste selective catalytic reduction catalyst with alumina, and sequentially pressing and sintering to obtain the aluminum titanate ceramic.
2. The preparation method of claim 1, wherein the mass percentage of titanium dioxide in the vanadium-titanium-based spent selective catalytic reduction catalyst is 70-100%.
3. The preparation method according to claim 1 or 2, wherein the mass ratio of the vanadium-titanium-based spent selective catalytic reduction catalyst to alumina is 9: 10-15.
4. The method of claim 1, wherein the mixing is ball milling; the rotation speed of the ball milling is 200-600 r/min, and the time is 4-16 h.
5. The method of claim 4, wherein the ball milling is wet milling; the dispersant for wet milling is alcohol.
6. The method according to claim 1, wherein the pressing pressure is 8-12 mpa and the dwell time is 1-3 min.
7. The preparation method according to claim 1, wherein the sintering temperature is 1300-1600 ℃ and the heat preservation time is 2-6 h.
8. The method according to claim 1 or 4, wherein the mixing is preceded by washing, drying, pulverizing and sieving the vanadium-titanium-based spent selective catalytic reduction catalyst in that order.
9. The method of claim 8, wherein the cleaning is ultrasonic cleaning; the ultrasonic cleaning time is 8-16 hours;
The drying is drying; the temperature of the drying is 60-120 ℃ and the time is 12-36 h.
10. The method of claim 8, wherein the screened mesh number is 200-600 mesh.
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Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101423242A (en) * 2008-11-21 2009-05-06 福州大学 Aluminium titanates material prepared by aluminium section bar plant sludge and preparation method thereof
CN101580387A (en) * 2009-06-25 2009-11-18 福州大学 Aluminium titanate material prepared by waste activated alumina and preparation method thereof
CN105347785A (en) * 2015-11-30 2016-02-24 南京工业大学 Titanium-based ceramic taking waste vanadium-titanium denitration catalyst as raw material and preparation method thereof
CN108341657A (en) * 2018-04-24 2018-07-31 王彩兰 A kind of titanium-base ceramics and its environment-friendly preparation method thereof
CN110075841A (en) * 2019-05-22 2019-08-02 国电科学技术研究院有限公司 With the catalyst for preparing hydrogen and preparation method of waste and old commercial vanadium titanium denitrating catalyst preparation
CN111943696A (en) * 2020-08-05 2020-11-17 辽宁科技大学 Method for preparing aluminum titanate refractory material by using industrial aluminum slag and titanium slag
RU2787859C1 (en) * 2020-08-05 2023-01-13 Федеральное государственное бюджетное образовательное учреждение высшего образования "Вятский государственный университет" Method for preparing aluminum titanate fire-resistant material using industrial aluminum slag and titanium slag

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101423242A (en) * 2008-11-21 2009-05-06 福州大学 Aluminium titanates material prepared by aluminium section bar plant sludge and preparation method thereof
CN101580387A (en) * 2009-06-25 2009-11-18 福州大学 Aluminium titanate material prepared by waste activated alumina and preparation method thereof
CN105347785A (en) * 2015-11-30 2016-02-24 南京工业大学 Titanium-based ceramic taking waste vanadium-titanium denitration catalyst as raw material and preparation method thereof
CN108341657A (en) * 2018-04-24 2018-07-31 王彩兰 A kind of titanium-base ceramics and its environment-friendly preparation method thereof
CN110075841A (en) * 2019-05-22 2019-08-02 国电科学技术研究院有限公司 With the catalyst for preparing hydrogen and preparation method of waste and old commercial vanadium titanium denitrating catalyst preparation
CN111943696A (en) * 2020-08-05 2020-11-17 辽宁科技大学 Method for preparing aluminum titanate refractory material by using industrial aluminum slag and titanium slag
RU2787859C1 (en) * 2020-08-05 2023-01-13 Федеральное государственное бюджетное образовательное учреждение высшего образования "Вятский государственный университет" Method for preparing aluminum titanate fire-resistant material using industrial aluminum slag and titanium slag

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