CN106423134B - A kind of preparation method of base metal soot combustion catalyst - Google Patents
A kind of preparation method of base metal soot combustion catalyst Download PDFInfo
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- 239000003054 catalyst Substances 0.000 title claims abstract description 30
- 239000004071 soot Substances 0.000 title claims abstract description 18
- 238000002360 preparation method Methods 0.000 title claims abstract description 15
- 238000002485 combustion reaction Methods 0.000 title claims abstract description 10
- 239000010953 base metal Substances 0.000 title abstract 2
- 239000006104 solid solution Substances 0.000 claims abstract description 19
- 229910052726 zirconium Inorganic materials 0.000 claims abstract description 3
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 34
- 239000000243 solution Substances 0.000 claims description 23
- 239000000203 mixture Substances 0.000 claims description 20
- 238000003756 stirring Methods 0.000 claims description 11
- 239000003795 chemical substances by application Substances 0.000 claims description 9
- 239000011259 mixed solution Substances 0.000 claims description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 8
- 229910052751 metal Inorganic materials 0.000 claims description 7
- 239000002184 metal Substances 0.000 claims description 7
- 239000000843 powder Substances 0.000 claims description 6
- 239000010970 precious metal Substances 0.000 claims description 6
- OVYTZAASVAZITK-UHFFFAOYSA-M sodium;ethanol;hydroxide Chemical compound [OH-].[Na+].CCO OVYTZAASVAZITK-UHFFFAOYSA-M 0.000 claims description 5
- 150000003754 zirconium Chemical class 0.000 claims description 5
- 238000010438 heat treatment Methods 0.000 claims description 3
- -1 zirconium salt Chemical class 0.000 claims description 2
- 229910052760 oxygen Inorganic materials 0.000 abstract description 7
- 239000011148 porous material Substances 0.000 abstract description 7
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 6
- 239000001301 oxygen Substances 0.000 abstract description 6
- 230000008901 benefit Effects 0.000 abstract description 4
- 238000003860 storage Methods 0.000 abstract description 4
- 229920000428 triblock copolymer Polymers 0.000 abstract description 4
- 229910052777 Praseodymium Inorganic materials 0.000 abstract description 2
- 239000013335 mesoporous material Substances 0.000 abstract description 2
- PUDIUYLPXJFUGB-UHFFFAOYSA-N praseodymium atom Chemical compound [Pr] PUDIUYLPXJFUGB-UHFFFAOYSA-N 0.000 abstract description 2
- QCWXUUIWCKQGHC-UHFFFAOYSA-N Zirconium Chemical compound [Zr] QCWXUUIWCKQGHC-UHFFFAOYSA-N 0.000 abstract 1
- 229910006213 ZrOCl2 Inorganic materials 0.000 abstract 1
- 229910002828 Pr(NO3)3·6H2O Inorganic materials 0.000 description 6
- 230000003197 catalytic effect Effects 0.000 description 6
- 239000000463 material Substances 0.000 description 5
- 239000002245 particle Substances 0.000 description 4
- 238000012546 transfer Methods 0.000 description 4
- 230000009471 action Effects 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 230000003647 oxidation Effects 0.000 description 3
- 238000007254 oxidation reaction Methods 0.000 description 3
- 239000013618 particulate matter Substances 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- 238000002525 ultrasonication Methods 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- 239000002131 composite material Substances 0.000 description 2
- 230000007547 defect Effects 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 238000004949 mass spectrometry Methods 0.000 description 2
- 229910044991 metal oxide Inorganic materials 0.000 description 2
- 150000004706 metal oxides Chemical class 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 229910000510 noble metal Inorganic materials 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 238000010998 test method Methods 0.000 description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- 239000006004 Quartz sand Substances 0.000 description 1
- 239000012494 Quartz wool Substances 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 238000003917 TEM image Methods 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 230000009849 deactivation Effects 0.000 description 1
- 239000002019 doping agent Substances 0.000 description 1
- IDGUHHHQCWSQLU-UHFFFAOYSA-N ethanol;hydrate Chemical compound O.CCO IDGUHHHQCWSQLU-UHFFFAOYSA-N 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 230000008092 positive effect Effects 0.000 description 1
- 238000012805 post-processing Methods 0.000 description 1
- 239000010453 quartz Substances 0.000 description 1
- 229910001404 rare earth metal oxide Inorganic materials 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 229910000314 transition metal oxide Inorganic materials 0.000 description 1
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- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/10—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of rare earths
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
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- F23G7/06—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
- F23G7/07—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases in which combustion takes place in the presence of catalytic material
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Abstract
Description
技术领域technical field
本发明涉及一种非贵金属碳烟燃烧催化剂的制备方法,具体涉及介孔结构的Pr x Zr 1-x O 2 固溶体催化剂的制备方法,属于应用催化技术领域。The invention relates to a preparation method of a non-precious metal soot combustion catalyst, in particular to a preparation method of a PrxZr1 - xO2 solid solution catalyst with a mesoporous structure, and belongs to the technical field of applied catalysis.
背景技术Background technique
碳烟颗粒物(PM)作为柴油车尾气中的主要污染物,是形成雾霾的“罪魁祸首”,对人体健康和生活环境造成了极大的危害。开发清洁能源、发展柴油机机内净化技术和对柴油车尾气进行后处理是控制污染物排放的三个主要方面。然而,受到技术水平和经济成本的约束,清洁燃料和机内净化技术还未能大范围使用。就目前来看,使用专门为机外净化碳烟颗粒物而设计的后处理装置——颗粒过滤器(DPF)来捕集碳烟颗粒物,并将其氧化为CO2,是最直接有效的的方法。但是,碳烟颗粒物的燃烧温度较高,在550~600℃范围内,远高于柴油车尾气实际排放温度范围(200~400℃)。因此,必须使用催化剂来催化PM的燃烧,从而实现DPF的再生使用。As the main pollutant in diesel vehicle exhaust, soot particulate matter (PM) is the "culprit" in the formation of smog, causing great harm to human health and living environment. The development of clean energy, the development of diesel engine purification technology and the aftertreatment of diesel vehicle exhaust are the three main aspects of controlling pollutant emissions. However, due to the constraints of technical level and economic cost, clean fuel and in-plane purification technology have not been widely used. From the current point of view, the most direct and effective method is to use a particulate filter (DPF), a post-processing device specially designed for the purification of soot particles outside the machine to capture soot particles and oxidize them to CO 2 . . However, the combustion temperature of soot particles is relatively high, in the range of 550-600 °C, which is much higher than the actual emission temperature range of diesel vehicle exhaust (200-400 °C). Therefore, a catalyst must be used to catalyze the combustion of PM, thereby realizing the regenerative use of DPF.
用于催化碳烟颗粒氧化的催化剂一般可分为两类,贵金属催化剂和非贵金属催化剂。贵金属催化剂主要以担载量较少的贵金属为活性组分,涂覆在载体表面制成。虽然贵金属催化剂具有优越的催化氧化性能,但是,贵金属催化剂的热稳定性差,遇水易失活,有“硫中毒”反应,生产成本较高等因素使得其在实际应用中受到制约。近年来,以稀土金属氧化物为基体,过渡金属氧化物为掺杂物的复合金属氧化物在催化碳烟燃烧方面表现出了强劲的优势。特别是这种复合金属氧化物形成的固溶体,由于晶格缺陷的存在,对于降低碳烟燃烧的活化能,强化材料的储氧能力,提高催化剂的氧化还原性能具有积极作用。而介孔材料与生俱来的大比表面积、大的孔体积、可控的孔径尺寸对巩固和拓展材料的物理化学性质大有助益。因此,介孔固溶体材料可以作为一种新型的催化碳烟燃烧的催化剂加以研究。Catalysts used to catalyze the oxidation of soot particles can generally be divided into two categories, noble metal catalysts and non-precious metal catalysts. Precious metal catalysts are mainly made of precious metals with less loading as active components, which are coated on the surface of the carrier. Although noble metal catalysts have excellent catalytic oxidation performance, their poor thermal stability, easy deactivation in contact with water, "sulfur poisoning" reactions, and high production costs restrict their practical application. In recent years, composite metal oxides based on rare earth metal oxides and transition metal oxides as dopants have shown strong advantages in catalyzing soot combustion. In particular, the solid solution formed by this composite metal oxide has a positive effect on reducing the activation energy of soot combustion, strengthening the oxygen storage capacity of the material, and improving the redox performance of the catalyst due to the existence of lattice defects. The inherent large specific surface area, large pore volume, and controllable pore size of mesoporous materials are of great help to consolidate and expand the physical and chemical properties of materials. Therefore, mesoporous solid solution materials can be studied as a new type of catalyst for catalyzing soot combustion.
发明内容SUMMARY OF THE INVENTION
本发明提供一种非贵金属碳烟燃烧催化剂的制备方法,具体为介孔结构的Pr x Zr 1-x O 2 固溶体催化剂的制备方法,经过下列各步骤:The invention provides a preparation method of a non-precious metal soot combustion catalyst, specifically a preparation method of a Pr x Zr 1-x O 2 solid solution catalyst with a mesoporous structure, through the following steps:
(1)按照Pr与Zr的摩尔比=x:1-x(其中,0<x≤0.4),分别称取足量的Pr(NO3)3和金属锆盐,在室温下溶于无水乙醇中,配制成浓度为0.4~1mol/L的乙醇溶液,再将二者混合均匀;(1) According to the molar ratio of Pr to Zr=x:1-x (wherein, 0<x≤0.4), respectively weigh enough Pr(NO 3 ) 3 and metal zirconium salt, dissolve in anhydrous at room temperature In ethanol, prepare an ethanol solution with a concentration of 0.4~1mol/L, and then mix the two evenly;
(2)按照(Pr(NO3)3+金属锆盐)与模板剂质量比为20:1~5:1,称取足量的模板剂溶于无水乙醇中,配制成浓度为0.05~0.5g/mL的溶液;(2) According to the mass ratio of (Pr(NO 3 ) 3 + metal zirconium salt) to template agent of 20:1~5:1, weigh a sufficient amount of template agent and dissolve it in absolute ethanol to prepare a concentration of 0.05~ 0.5g/mL solution;
(3)在40~60℃水浴加热并剧烈搅拌的条件下,将模板剂的乙醇溶液逐滴加入到步骤(1)的混合溶液中;(3) Under the condition of heating in a water bath at 40~60°C and vigorous stirring, add the ethanol solution of the template agent dropwise to the mixed solution of step (1);
(4)向步骤(3)制得的混合物中加入NaOH乙醇溶液调节pH为9~10,再持续搅拌3~5h;(4) Add NaOH ethanol solution to the mixture prepared in step (3) to adjust the pH to 9~10, and continue stirring for 3~5h;
(5)将步骤(4)得到的混合物转移到锥形瓶中,在温度为50~70℃,湿度为40~60%的恒温恒湿箱中培养24~48h;(5) Transfer the mixture obtained in step (4) into a conical flask, and cultivate in a constant temperature and humidity box with a temperature of 50-70°C and a humidity of 40-60% for 24-48 hours;
(6)将步骤(5)得到的混合物过滤,用无水乙醇洗涤干净后,在80~120℃下干燥12~24h,将得到的粉末在500~800℃下焙烧3~5h,得到介孔结构的Pr x Zr 1-x O 2 固溶体催化剂。(6) The mixture obtained in step (5) was filtered, washed with absolute ethanol, dried at 80-120 °C for 12-24 h, and the obtained powder was calcined at 500-800 °C for 3-5 h to obtain mesoporous Structure of PrxZr1 - xO2 solid solution catalyst.
所述金属锆盐为Zr(NO3)4或ZrOCl2。The metal zirconium salt is Zr(NO 3 ) 4 or ZrOCl 2 .
所述模板剂为F127或P123。The templating agent is F127 or P123.
本发明的有益效果是:The beneficial effects of the present invention are:
(1)所得的介孔结构的Pr x Zr 1-x O 2 固溶体比表面积大(比表面积为110~140 m2/g),具有较大的孔体积(孔体积为0.17~2.4cc/g),孔隙排列规则;(1) The obtained mesoporous Pr x Zr 1-x O 2 solid solution has a large specific surface area (specific surface area of 110~140 m 2 /g) and a large pore volume (pore volume of 0.17~2.4cc/g) ), the pore arrangement rules;
(2)Pr x Zr 1-x O 2 固溶体中存在的晶格缺陷能够显著提高材料的氧交换能力,掺杂的ZrO2可以大幅提高材料的储氧能力;(2) The lattice defects existing in the Pr x Zr 1-x O 2 solid solution can significantly improve the oxygen exchange capacity of the material, and the doped ZrO 2 can greatly improve the oxygen storage capacity of the material;
(3)Pr x Zr 1-x O固溶体中,镨以Pr6O11的形态存在,Pr6O11具有多重稳定氧化态,在低温下具有比CeO2更高的氧交换能力,尤其是它在经历高温焙烧之后储氧能力不会下降的优点有利于保持催化剂的稳定性,在催化领域具有极其重要的作用。(3) In the Pr x Zr 1-x O solid solution, praseodymium exists in the form of Pr 6 O 11 , which has multiple stable oxidation states and has a higher oxygen exchange capacity than CeO 2 at low temperature, especially it The advantage that the oxygen storage capacity will not decrease after calcination at high temperature is conducive to maintaining the stability of the catalyst, which plays an extremely important role in the field of catalysis.
附图说明Description of drawings
图1是实施例1制得的介孔结构的Pr 0.1 Zr 0.9 O 2 固溶体催化剂的TEM图。1 is a TEM image of the Pr 0.1 Zr 0.9 O 2 solid solution catalyst with a mesoporous structure prepared in Example 1.
具体实施方式Detailed ways
下面结合附图和具体实施方式,对本发明做进一步说明。The present invention will be further described below with reference to the accompanying drawings and specific embodiments.
实施例1Example 1
(1)按Pr与Zr摩尔比=0.1:0.9,称取0.004mol(1.74g) Pr(NO3)3·6H2O和0.036mol(11.6g) ZrOCl2·8H2O,分别溶于10mL和90mL无水乙醇中,经过超声、搅拌之后分别配制成浓度为0.4mol/L的乙醇溶液,并将二者混合均匀;(1) According to the molar ratio of Pr to Zr=0.1:0.9, weigh 0.004mol (1.74g) Pr(NO 3 ) 3 ·6H 2 O and 0.036mol (11.6g) ZrOCl 2 ·8H 2 O and dissolve in 10mL respectively and 90 mL of dehydrated ethanol, after ultrasonication and stirring, were respectively prepared into an ethanol solution with a concentration of 0.4 mol/L, and the two were mixed evenly;
(2)按照(Pr(NO3)3·6H2O+ZrOCl2·8H2O)与模板剂F127的质量比为20:1,称取0.67g三嵌段共聚物F127溶于13mL无水乙醇中,配制成浓度为0.05g/mL的溶液;(2) According to the mass ratio of (Pr(NO 3 ) 3 ·6H 2 O+ZrOCl 2 ·8H 2 O) to template F127 of 20:1, weigh 0.67g of triblock copolymer F127 and dissolve it in 13mL of anhydrous In ethanol, prepare a solution with a concentration of 0.05g/mL;
(3)在40℃下水浴搅拌步骤(1)的混合溶液,将F127的乙醇溶液逐滴加入步骤(1)的混合溶液中;(3) The mixed solution of step (1) was stirred in a water bath at 40°C, and the ethanol solution of F127 was added dropwise to the mixed solution of step (1);
(4)向步骤(3)得到的混合物中加入NaOH乙醇溶液调节pH为9,再持续搅拌3h;(4) Add NaOH ethanol solution to the mixture obtained in step (3) to adjust the pH to 9, and continue stirring for 3h;
(5)将步骤(4)得到的混合物转移到锥形瓶中,在温度为50℃,湿度为40%的恒温恒湿箱中培养48h;(5) Transfer the mixture obtained in step (4) into a conical flask, and cultivate for 48 hours in a constant temperature and humidity box with a temperature of 50°C and a humidity of 40%;
(6)将步骤(5)得到的混合物过滤,用无水乙醇洗涤3次后,在80℃下干燥24h,将得到的粉末在500℃下焙烧5h,得到介孔结构的Pr0.1Zr0.9O 2 固溶体催化剂。(6) The mixture obtained in step (5) was filtered, washed three times with absolute ethanol, dried at 80 °C for 24 h, and the obtained powder was calcined at 500 °C for 5 h to obtain Pr 0.1 Zr 0.9 O with a mesoporous structure 2 solid solution catalyst.
催化活性测试:取90mg制得的Pr0.1Zr0.9O 2 固溶体催化剂与10mg碳烟粉末,混合均匀;再加入300mg 20~40目的石英砂混合均匀,然后放在垫有石英棉的石英管中,置于固定床反应器中,先通入流速为50mL/min的高纯Ar气,在300℃下预处理30min,除去吸附水和易分解的碳酸盐;待反应器冷却至室温,通入流速为200mL/min的10%O2+Ar混合气,并用在线质谱检测尾气;以10℃/min的速率升温至碳烟完全燃烧,根据质谱检测的尾气数据可得,在催化剂作用下碳烟的起燃温度为268℃。Catalytic activity test: Take 90mg of the prepared Pr 0.1 Zr 0.9 O 2 solid solution catalyst and 10mg of soot powder, and mix them evenly; then add 300mg of 20-40 mesh quartz sand and mix them evenly, then put them in a quartz tube padded with quartz wool, Placed in a fixed-bed reactor, first introduced high-purity Ar gas with a flow rate of 50 mL/min, pretreated at 300 °C for 30 minutes to remove adsorbed water and easily decomposed carbonate; after the reactor was cooled to room temperature, introduced A 10% O 2 +Ar mixture with a flow rate of 200 mL/min, and the exhaust gas was detected by on-line mass spectrometry; the temperature was raised at a rate of 10 °C/min until the soot was completely burned. According to the exhaust gas data detected by mass spectrometry, the soot was obtained under the action of the catalyst. The light-off temperature is 268°C.
实施例2Example 2
(1)按Pr与Zr摩尔比=0.2:0.8,称取0.008mol(3.48g) Pr(NO3)3·6H2O和0.032mol(10.31g) ZrOCl2·8H2O,分别溶于16mL和64mL无水乙醇中,经过超声、搅拌之后分别配制成浓度都为0.5mol/L的溶液,并将二者混合均匀;(1) According to the molar ratio of Pr to Zr=0.2:0.8, weigh 0.008mol (3.48g) Pr(NO 3 ) 3 ·6H 2 O and 0.032mol (10.31g) ZrOCl 2 ·8H 2 O and dissolve in 16mL respectively and 64 mL of dehydrated ethanol, respectively, after ultrasonication and stirring, were prepared into solutions with a concentration of 0.5 mol/L, and the two were mixed evenly;
(2)按照(Pr(NO3)3·6H2O+ZrOCl2·8H2O)与模板剂F127的质量比为10:1,称取1.38g三嵌段共聚物F127溶于13.8mL无水乙醇中,配制成浓度为0.1g/mL的溶液;(2) According to the mass ratio of (Pr(NO 3 ) 3 ·6H 2 O+ZrOCl 2 ·8H 2 O) to template F127 of 10:1, weigh 1.38g of triblock copolymer F127 and dissolve it in 13.8mL of In water ethanol, prepare a solution with a concentration of 0.1 g/mL;
(3)在50℃下水浴搅拌步骤(1)中的混合溶液,将F127的乙醇溶液逐滴加入混合液中;(3) The mixed solution in step (1) was stirred in a water bath at 50°C, and the ethanol solution of F127 was added dropwise to the mixed solution;
(4)向步骤(3)得到的混合物中加入NaOH乙醇溶液调节pH为9.5,再持续搅拌4h;(4) Add NaOH ethanol solution to the mixture obtained in step (3) to adjust the pH to 9.5, and continue stirring for 4 hours;
(5)将步骤(4)得到的混合物转移到锥形瓶中,在温度为60℃,湿度为50%的恒温恒湿箱中培养36h;(5) Transfer the mixture obtained in step (4) into a conical flask, and cultivate for 36 hours in a constant temperature and humidity box with a temperature of 60°C and a humidity of 50%;
(6)将步骤(5)得到的混合物过滤,用无水乙醇洗涤3次后,在100℃下干燥18h,将得到的粉末在600℃下焙烧4h,得到介孔结构的Pr0.2Zr0.8O 2 固溶体催化剂。(6) The mixture obtained in step (5) was filtered, washed with absolute ethanol for 3 times, dried at 100 °C for 18 h, and the obtained powder was calcined at 600 °C for 4 h to obtain Pr 0.2 Zr 0.8 O with a mesoporous structure 2 solid solution catalyst.
按实施例1催化活性测试方法对本实施例制得的Pr0.2Zr0.8O 2 固溶体催化剂催化活性进行测试,测试结果,在催化剂作用下碳烟的起燃温度为275℃。The catalytic activity of the Pr 0.2 Zr 0.8 O 2 solid solution catalyst prepared in this example was tested according to the catalytic activity test method of Example 1. The test result showed that the light-off temperature of soot under the action of the catalyst was 275°C.
实施例3Example 3
(1)按Pr与Zr摩尔比=0.3:0.7,称取0.012mol(5.22g) Pr(NO3)3·6H2O和0.028mol(12.02g) Zr(NO3)4·5H2O,分别溶于12mL和28mL无水乙醇中,经过超声、搅拌之后分别配制成浓度都为1mol/L的溶液,并将二者混合均匀;(1) According to the mole ratio of Pr to Zr=0.3:0.7, weigh 0.012mol (5.22g) Pr(NO 3 ) 3 ·6H 2 O and 0.028mol (12.02g) Zr(NO 3 ) 4 ·5H 2 O, Dissolved in 12mL and 28mL of absolute ethanol, respectively, prepared into solutions with a concentration of 1mol/L after ultrasonication and stirring, and mixed the two evenly;
(2)按照(Pr(NO3)3·6H2O+Zr(NO3)4·5H2O)与模板剂P123的质量比为5:1,称取3.45g三嵌段共聚物P123溶于6.9mL无水乙醇中,配制成浓度为0.5g/mL的溶液;(2) According to the mass ratio of (Pr(NO 3 ) 3 ·6H 2 O+Zr(NO 3 ) 4 ·5H 2 O) to template P123 of 5:1, weigh 3.45g of triblock copolymer P123 to dissolve In 6.9mL of absolute ethanol, prepare a solution with a concentration of 0.5g/mL;
(3)在60℃下水浴搅拌步骤(1)中的混合溶液,将P123的乙醇溶液逐滴加入混合液中;(3) stirring the mixed solution in step (1) in a water bath at 60°C, and adding the ethanol solution of P123 to the mixed solution dropwise;
(4)向步骤(3)得到的混合物中加入NaOH乙醇溶液调节pH为10,再持续搅拌5h;(4) Add NaOH ethanol solution to the mixture obtained in step (3) to adjust the pH to 10, and continue stirring for 5h;
(5)将步骤(4)得到的混合物转移到锥形瓶中,在温度为70℃,湿度为60%的恒温恒湿箱中培养24h;(5) Transfer the mixture obtained in step (4) into a conical flask, and cultivate for 24 hours in a constant temperature and humidity box with a temperature of 70°C and a humidity of 60%;
(6)将步骤(5)得到的混合物过滤,用无水乙醇洗涤3次后,在120℃下干燥12h,将得到的粉末在700℃下焙烧3h,得到介孔结构的Pr0.3Zr0.7O 2 固溶体催化剂。(6) The mixture obtained in step (5) was filtered, washed with absolute ethanol for 3 times, dried at 120 °C for 12 h, and the obtained powder was calcined at 700 °C for 3 h to obtain Pr 0.3 Zr 0.7 O with a mesoporous structure 2 solid solution catalyst.
按实施例1催化活性测试方法对本实施例制得的Pr0.3Zr0.7O 2 固溶体催化剂催化活性进行测试,测试结果,在催化剂作用下碳烟的起燃温度为287℃。The catalytic activity of the Pr 0.3 Zr 0.7 O 2 solid solution catalyst prepared in this example was tested according to the catalytic activity test method of Example 1. The test result showed that the light-off temperature of soot under the action of the catalyst was 287°C.
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