WO2020206976A1 - 可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法 - Google Patents
可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法 Download PDFInfo
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8678—Removing components of undefined structure
- B01D53/8687—Organic components
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J31/00—Catalysts comprising hydrides, coordination complexes or organic compounds
- B01J31/26—Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
- B01J31/28—Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of the platinum group metals, iron group metals or copper
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- B01D2257/70—Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
- B01D2257/708—Volatile organic compounds V.O.C.'s
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- the invention relates to a preparation method of a porous organic framework atomic level catalyst, in particular to a preparation method of a porous organic framework atomic level catalyst that can be used for catalytic degradation of VOCs at room temperature.
- Volatile organic compounds are an important class of air pollutants, defined by the World Health Organization as organic compounds with a boiling point of 50-260°C and a saturated vapor pressure of more than 133 Pa at room temperature, including alkanes, alkenes, aromatics and their derivatives, Alcohols, aldehydes and ketones, amines and amides, acids and anhydrides, etc. VOCs are an important class of air pollutants.
- the purpose of the present invention is to overcome the shortcomings of the prior art and provide a method for preparing a noble metal-loaded porous organic framework atomic-level catalyst that can be used for catalytic degradation of VOCs at room temperature.
- the catalyst has atomic-level active sites, has excellent catalytic performance, and can be reused. Catalytic degradation of VOCs under normal temperature conditions.
- the preparation method of the atomic-level active site catalyst with the noble metal supported on the pyridine-amide porous organic framework of the present invention includes the following steps:
- the porous organic framework is completely immersed in a precious metal salt solution of 0.05-0.5 mol/L, ultrasonically treated for 1-5 h, and then allowed to stand at 10-30 °C for 6-12 h to obtain a precious metal-loaded porous Organic framework; the ratio of the mass of the precious metal in the precious metal salt solution to the mass of the porous organic framework is 0.05-0.5%;
- the completed precious metal-loaded pyridine-amide porous organic framework is taken out and placed in a horse boiling furnace at 100-600°C for 2-6 hours to obtain the precious metal-loaded pyridine-amide porous organic framework atomic-level active site catalyst.
- the pyridine-amide porous organic framework has the advantages of simple synthesis, high stability, and easy control of active sites. And the existence of amino groups is conducive to the dispersion of atoms, and the porosity can avoid the phenomenon of agglomeration of atoms to a certain extent, and achieve a real catalyst with atomic-level active sites, thereby obtaining higher catalytic performance.
- VOCs Due to the excellent catalytic performance of this catalyst, VOCs can be catalytically degraded at room temperature, which reduces the energy consumption of practical applications and enhances the safety of practical operations.
- This catalyst has strong stability, can be reused many times, has a long service life, and greatly reduces the cost of industrial applications.
- the preparation method of the precious metal-loaded porous organic framework atomic-level catalyst that can be used for catalytic degradation of VOCs at room temperature of the present invention includes the following steps:
- the oil bath temperature is 40-60°C, and the reaction time is 4-6h. At this temperature, the reaction rate is accelerated, and the damage to the organic framework by high temperature is avoided.
- the porous organic framework is completely immersed in a precious metal salt solution of 0.05-0.5 mol/L, ultrasonically treated for 1-5 h, and then allowed to stand at 10-30 °C for 6-12 h to obtain a precious metal-loaded porous Organic framework.
- the mass ratio of the mass of the precious metal in the precious metal salt solution to the porous organic framework is 0.05-0.5%.
- the noble metal salt solution is any one of HAuCl 4 and H 2 PtCl 6.
- the noble metal salt solution is H 2 PtCl 6 solution, and the Pt atomic grade catalyst has better catalytic performance.
- the ultrasound time is 1.5-3h, which can uniformly load the noble metal onto the pyridine-amide porous organic framework.
- the time is too short, the dispersion is uneven, and the time is too long and time-consuming.
- the completed precious metal-loaded pyridine-amide porous organic framework is taken out and placed in a horse boiling furnace at 100-600°C for 2-6 hours to obtain the precious metal-loaded pyridine-amide porous organic framework atomic-level active site catalyst.
- the calcination temperature is 200-400°C, which avoids high temperature damage to the pyridine-amide porous organic framework.
- the calcination time is 3-6 hours, so that the precious metal can be more stably supported on the porous organic framework.
- the completed Pt metal-loaded pyridine-amide porous organic framework is taken out and placed in a horse boiling furnace at 100° C. for 6 h to obtain the Pt metal-loaded pyridine-amide porous organic framework atomic-level active site catalyst.
- the catalyst of this example was installed in a fixed bed reactor, and methanol, toluene, ethanol, and acetone were used as the evaluation pollutants of the catalytic reaction for catalytic evaluation.
- the catalyst is put into a quartz tube with an inner diameter of 8mm for testing.
- the catalytic reaction device has a length of 40mm, a volatile organic compound solubility of 1000ppm, a space velocity of 25000h -1 , and a reaction temperature of 25°C.
- the catalytic oxidation reaction is carried out under oxygen conditions. The results are shown in Table 1.
- the completed Pt metal-loaded pyridine-amide porous organic framework is taken out and placed in a horse boiling furnace at 200° C. for 5 h to obtain the Pt metal-loaded pyridine-amide porous organic framework atomic-level active site catalyst.
- the catalyst of this example was installed in a fixed bed reactor, and methanol, toluene, ethanol, and acetone were used as the evaluation pollutants of the catalytic reaction for catalytic evaluation.
- the catalyst is put into a quartz tube with an inner diameter of 8mm for testing.
- the catalytic reaction device has a length of 40mm, a volatile organic compound solubility of 1000ppm, a space velocity of 25000h -1 , and a reaction temperature of 25°C.
- the catalytic oxidation reaction is carried out under the condition of ozone. The results are shown in Table 1.
- the completed Pt metal-loaded pyridine-amide porous organic framework is taken out and placed in a horse boiling furnace at 300° C. for 4 hours to obtain the Pt metal-loaded pyridine-amide porous organic framework atomic-level active site catalyst.
- the catalyst of this example was installed in a fixed bed reactor, and methanol, toluene, ethanol, and acetone were used as the evaluation pollutants of the catalytic reaction for catalytic evaluation.
- the catalyst is put into a quartz tube with an inner diameter of 8mm for testing.
- the catalytic reaction device has a length of 40mm, a volatile organic compound solubility of 1000ppm, a space velocity of 25000h -1 , and a reaction temperature of 25°C.
- the catalytic oxidation reaction is carried out under oxygen conditions. The results are shown in Table 1.
- the porous organic framework is completely immersed in a 0.4 mol/L HAuCl 4 solution, ultrasonically treated for 3 hours, and then allowed to stand at 20° C. for 8 hours to obtain a porous organic framework supporting Au metal.
- the mass ratio of the Au element in the HAuCl 4 solution to the pyridine-amide porous organic skeleton is 0.4%.
- the completed Au metal-loaded pyridine-amide porous organic framework is taken out and placed in a horse boiling furnace at 400° C. for 3 h to obtain the Au metal-loaded pyridine-amide porous organic framework atomic-level active site catalyst.
- the catalyst of this example was installed in a fixed bed reactor, and methanol, toluene, ethanol, and acetone were used as the evaluation pollutants of the catalytic reaction for catalytic evaluation.
- the catalyst is put into a quartz tube with an inner diameter of 8mm for testing.
- the catalytic reaction device has a length of 40mm, a volatile organic compound solubility of 1000ppm, a space velocity of 25000h -1 , and a reaction temperature of 25°C.
- the catalytic oxidation reaction is carried out under oxygen conditions. The results are shown in Table 1.
- the porous organic framework is completely immersed in a 0.5 mol/L HAuCl 4 solution, ultrasonically treated for 5 hours, and then allowed to stand at 30° C. for 12 hours to obtain a porous organic framework supporting Au metal.
- the mass ratio of the Au element in the HAuCl 4 solution to the pyridine-amide porous organic skeleton is 0.5%.
- the completed Au metal-supported pyridine-amide porous organic framework was taken out, and placed in a horse boiling furnace at 600° C. for 2 h to obtain the Au metal-supported pyridine-amide porous organic framework atomic-level active site catalyst.
- the catalyst of this example was installed in a fixed bed reactor, and methanol, toluene, ethanol, and acetone were used as the evaluation pollutants of the catalytic reaction for catalytic evaluation.
- the catalyst is put into a quartz tube with an inner diameter of 8mm for testing.
- the catalytic reaction device has a length of 40mm, a volatile organic compound solubility of 1000ppm, a space velocity of 25000h -1 , and a reaction temperature of 25°C.
- the catalytic oxidation reaction is carried out under the condition of ozone. The results are shown in Table 1.
- the pyridine-amide porous organic framework atomic-level active site catalyst loaded with Pt and Au metals has a good degradation rate for methanol, toluene, ethanol, and acetone.
- This catalyst has good degradation rates for a variety of VOCs. Degradation effect.
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Abstract
可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法,步骤为:(a)制备载体,将2,6-二氨基吡啶和1,3,5-苯三甲酰氯加入到含三乙胺的二氯甲烷溶液并搅拌均匀,放置到油浴锅中加热反应,得到含吡啶-酰胺官能团的多孔有机骨架。(b)浸渍负载贵金属,将吡啶-酰胺多孔有机骨架完全浸渍到贵金属盐溶液中,经过超声处理并静置,然后加入硼氢化钠溶液还原贵金属,洗涤干燥后得到负载贵金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂半成品。(c)煅烧,将半成品放置马沸炉中煅烧,煅烧完成后得到成品。该催化剂原子分散度高,可形成原子级活性位点,大大提高催化效率。
Description
本发明涉及多孔有机骨架原子级催化剂的制备方法,尤其涉及可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法。
挥发性有机物(VOCs)是一类重要的空气污染物,世界卫生组织定义为沸点50~260℃、室温下饱和蒸气压超过133Pa的有机化合物,包括烷烃类、烯烃类、芳烃及其衍生物、醇类、醛酮类、胺和酰胺类、酸和酸酐类等。VOCs是一类重要的大气污染物。
我国当前常用的VOCs销毁方式有催化焚烧,低温等离子,紫外光催化等方法,这些方法往往需要高温条件,能耗高,且在处理易燃易爆VOCs时存在安全隐患。
发明内容
本发明的目的在于克服已有技术的缺点,提供可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法,此催化剂有原子级活性位点,催化性能优,可重复使用,可在常温条件下催化降解VOCs。
为了达到上述目的,本发明采用的技术方案是:
本发明贵金属负载在吡啶-酰胺多孔有机骨架的原子级活性位点催化剂制备方法,包括以下步骤:
(a)制备载体:
(1)将三乙胺加入到二氯甲烷溶液中,搅拌均匀得到第一溶液,所述的三乙胺与二氯甲烷体积比为1:10;
(2)将摩尔比为3:1的2,6-二氨基吡啶和1,3,5-苯三甲酰氯加入到所述的第一溶液中并搅拌均匀得到第二溶液;所述的2,6-二氨基吡啶和1,3,5-苯三甲酰氯的总体积与第一溶液的体积比为1:2;
(3)将所述的第二溶液放置在油浴锅中在20-90℃下反应2~8h,生成含有吡啶-酰胺官能团的多孔有机骨架;
(b)浸渍负载贵金属
(1)将所述的多孔有机骨架完全浸渍在0.05-0.5mol/L的贵金属盐溶液中,进行超声处理1-5h,然后在10-30℃下静置6-12h,得到负载贵金属的多孔有机骨架;所述贵金属盐溶液中贵金属的质量与多孔有机骨架的质量比为0.05-0.5%;
(2)将浓度为0.1-0.5mol/l的硼氢化钠溶液逐滴加入到静置后的浸渍有吡啶-酰胺多孔有机骨架的贵金属盐溶液中,剧烈搅拌直到不再产生氢气,使吡啶-酰胺多孔有机骨架负载的贵金属被还原;
(3)将负载了贵金属的多孔有机骨架取出,用去离子水洗涤多次,置于真空干燥箱中,在20-80℃下干燥2-6h;
(c)煅烧
将完成的负载贵金属的吡啶-酰胺多孔有机骨架取出,放置在马沸炉中在100-600℃下煅烧2-6h,得到负载贵金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂。
与已有技术相比,本发明的有益效果如下:
1.吡啶-酰胺多孔有机骨架合成简单,稳定性高,易于调控活性位点等优点。且氨基的存在有利于原子的分散,多孔在一定程度上可以避免原子团聚现象,达到真正的具有原子级活性位点的催化剂,从而获得更高的催化性能。
2.由于此催化剂优异的催化性能,使得VOCs可在常温下被催化降解,降低了实际应用的能耗,增强了实际操作的安全性。
3.此催化剂稳定性强,可多次重复使用,使用寿命长,大大降低工业应用的成本。
下面将结合本发明实施案例,对本发明实施案例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有作出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。
本发明的可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法,包括以下步骤:
(a)制备载体:
(1)将三乙胺加入到二氯甲烷溶液中,搅拌均匀得到第一溶液,所述的三乙胺与二氯甲烷体积比为1:10。
(2)将摩尔比为3:1的2,6-二氨基吡啶和1,3,5-苯三甲酰氯加入到所述的第一溶液中并搅拌均匀得到第二溶液;所述的2,6-二氨基吡啶和1,3,5-苯三甲酰氯的总体积与第一溶液的体积比为1:2。
(3)将所述的第二溶液放置在油浴锅中在20-90℃下反应2~8h,生成含有吡啶-酰胺官能团的多孔有机骨架。
优选的,油浴温度为40-60℃,反应时间为4-6h。在此温度下既加快了反应速率,又避免了高温对有机骨架的破坏。
(b)浸渍负载贵金属
(1)将所述的多孔有机骨架完全浸渍在0.05-0.5mol/L的贵金属盐溶液中,进行超声处理1-5h,然后在10-30℃下静置6-12h,得到负载贵金属的多孔有机骨架。所述贵金属盐溶液中贵金属的质量与多孔有机骨架的质量比为0.05-0.5%。
所属贵金属盐溶液为HAuCl
4、H
2PtCl
6中的任意一种,优选的,贵金属盐溶液为H
2PtCl
6溶液,Pt原子级催化剂具有较好的催化性能。
优选的,超声时间为1.5-3h,可以使贵金属均匀的负载到吡啶-酰胺多孔有机骨架,时间过短,分散不均,时间过长,耗时。
(2)将浓度为0.1-0.5mol/l的硼氢化钠溶液逐滴加入到静置后的浸渍有吡啶-酰胺多孔有机骨架的贵金属盐溶液中,剧烈搅拌直到不再产生氢气,使吡啶-酰胺多孔有机骨架负载的贵金属被还原。
(3)将负载了贵金属的多孔有机骨架取出,用去离子水洗涤多次,置于真空干燥箱中,在20-80℃下干燥2-6h。
(c)煅烧
将完成的负载贵金属的吡啶-酰胺多孔有机骨架取出,放置在马沸炉中在100-600℃下煅烧2-6h,得到负载贵金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂。
优选的,煅烧温度为200-400℃,避免了高温对吡啶-酰胺多孔有机骨架的破坏。优选的,煅烧时间为3-6h,使贵金属更稳定的负载到多孔有机骨架上。
实施例1
(a)制备载体
(1)将三乙胺加入到二氯甲烷溶液中,搅拌均匀得到第一溶液,三乙胺与二氯甲烷体积比为1:10。
(2)将摩尔比为3:1的2,6-二氨基吡啶和1,3,5-苯三甲酰氯加入到所述的第一溶液中并搅拌均匀得到第二溶液;2,6-二氨基吡啶和1,3,5-苯三甲酰氯的总体积与第一溶液的体积比为1:2。
(3)将所述的第二溶液放置在油浴锅中在20℃下反应8h,生成含有吡啶-酰胺官能团的多孔有机骨架。
(b)浸渍负载Pt金属
(1)将所述的多孔有机骨架完全浸渍到0.05mol/L的H
2PtCl
6溶液中,进行超声处理1h,然后在10℃下静置6h,得到负载Pt金属的多孔有机骨架。所述的H
2PtCl
6溶液中Pt元素的质量与吡啶-酰胺多孔有机骨架的质量比为0.05%。
(2)将浓度为0.1mol/l的硼氢化钠溶液逐滴加入到静置后浸渍有吡啶-酰胺多孔有机骨架的溶液中,剧烈搅拌直到不再产生氢气,使吡啶-酰胺多孔有机骨架负载的Pt
4+被还原。
(3)将负载了Pt金属的多孔有机骨架取出,用去离子水洗涤多次,置于真空干燥箱中,在20℃下干燥6h。
(c)煅烧
将完成的负载Pt金属的吡啶-酰胺多孔有机骨架取出,放置在马沸炉中在100℃下煅烧6h,得到负载Pt金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂。
将本实例的催化剂装于固定床反应装置中,以甲醇,甲苯,乙醇,丙酮作为催化反应的评价污染物进行催化评价。催化剂放入内径为8mm的石英管进行测试,催化反应装置长度40mm,挥发性有机物溶度1000ppm,空速25000h
-1,反应温度25℃,在氧气的条件下进行催化氧化反应。结果见表1。
实施例2
(a)制备载体:
(1)将三乙胺加入到二氯甲烷溶液中,搅拌均匀得到第一溶液,三乙胺与二氯甲烷体积比为1:10。
(2)将摩尔比为3:1的2,6-二氨基吡啶和1,3,5-苯三甲酰氯加入到所述的第一溶液中并搅拌均匀得到第二溶液;2,6-二氨基吡啶和1,3,5-苯三甲酰氯总体积与第一溶液的体积比为1:2。
(3)将所述的第二溶液放置在油浴锅中在40℃下反应6h,生成含有吡啶-酰胺官能团的多孔有机骨架。
(b)浸渍负载Pt金属
(1)将所述的多孔有机骨架完全浸渍到0.2mol/L的H
2PtCl
6溶液中,进行超声处理1.5h,然后在20℃下静置8h,得到负载Pt金属的多孔有机骨架。所述的H
2PtCl
6溶液中Pt元素的质量与吡啶-酰胺多孔有机骨架的质量比为0.1%。
(2)将浓度为0.2mol/l的硼氢化钠溶液逐滴加入到静置后浸渍有吡啶-酰胺多孔有机骨架的溶液中,剧烈搅拌直到不再产生氢气,使吡啶-酰胺多孔有机骨架负载的Pt
4+金属被还原。
(3)将负载了Pt金属的多孔有机骨架取出,用去离子水洗涤多次,置于真空干燥箱中,在50℃下干燥4h。
(c)煅烧
将完成的负载Pt金属的吡啶-酰胺多孔有机骨架取出,放置在马沸炉中在200℃下煅烧5h,得到负载Pt金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂。
将本实例的催化剂装于固定床反应装置中,以甲醇,甲苯,乙醇,丙酮作为催化反应的评价污染物进行催化评价。催化剂放入内径为8mm的石英管进行测试,催化反应装置长度40mm,挥发性有机物溶度1000ppm,空速25000h
-1,反应温度25℃,在臭氧的条件下进行催化氧化反应。结果见表1。
实施例3
(a)制备载体:
(1)将三乙胺加入到二氯甲烷溶液中,搅拌均匀得到第一溶液,三乙胺与二氯甲烷体积比为1:10。
(2)将摩尔比为3:1的2,6-二氨基吡啶和1,3,5-苯三甲酰氯加入到所述的第一溶液中并搅拌均匀得到第二溶液;2,6-二氨基吡啶和1,3,5-苯三甲酰氯的总体积与第一溶液的体积比为1:2。
(3)将所述的第二溶液放置在油浴锅中在50℃下反应5h,生成含有吡啶-酰胺官能团的多孔有机骨架。
(b)浸渍负载Pt金属
(1)将所述的多孔有机骨架完全浸渍到0.3mol/L的H
2PtCl
6溶液中,进行超声处理2h,然后在20℃下静置8h,得到负载Pt金属的多孔有机骨架。所述的H
2PtCl
6溶液中Pt元素的质量与吡啶-酰胺多孔有机骨架的质量比为0.2%。
(2)将浓度为0.2mol/l的硼氢化钠溶液逐滴加入到静置后浸渍有吡啶-酰胺多孔有机骨架的溶液中,剧烈搅拌直到不再产生氢气,使吡啶-酰胺多孔有机骨架负载的Pt
4+金属被还原。
(3)将负载了Pt金属的多孔有机骨架取出,用去离子水洗涤多次,置于真空干燥箱中,在60℃下干燥3h。
(c)煅烧
将完成的负载Pt金属的吡啶-酰胺多孔有机骨架取出,放置在马沸炉中在300℃下煅烧4h,得到负载Pt金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂。
将本实例的催化剂装于固定床反应装置中,以甲醇,甲苯,乙醇,丙酮作为催化反应的评价污染物进行催化评价。催化剂放入内径为8mm的石英管进行测试,催化反应装置长度40mm,挥发性有机物溶度1000ppm,空速25000h
-1,反应温度25℃,在氧气的条件下进行催化氧化反应。结果见表1。
实施例4
(a)制备载体:
(1)将三乙胺加入到二氯甲烷溶液中,搅拌均匀得到第一溶液,三乙胺与二氯甲烷体积比为1:10。
(2)将摩尔比为3:1的2,6-二氨基吡啶和1,3,5-苯三甲酰氯加入到所述的第一溶液中并搅拌均匀得到第二溶液;2,6-二氨基吡啶和1,3,5-苯三甲酰氯的总体积与第一溶液的体积比为1:2。
(3)将所述的第二溶液放置在油浴锅中在60℃下反应4h,生成含有吡啶-酰胺官能团的多孔有机骨架。
(b)浸渍负载Au金属
(1)将所述的多孔有机骨架完全浸渍到0.4mol/L的HAuCl
4溶液中,进行超声处理3h,然后在20℃下静置8h,得到负载Au金属的多孔有机骨架。所述的HAuCl
4溶液中Au元素的质量与吡啶-酰胺多孔有机骨架的质量比为0.4%。
(2)将浓度为0.2mol/l的硼氢化钠溶液逐滴加入到静置后浸渍有吡啶-酰胺多孔有机骨架的溶液中,剧烈搅拌直到不再产生氢气,使吡啶-酰胺多孔有机骨架负载的Au
3+金属被还原。
(3)将负载了Au金属的多孔有机骨架取出,用去离子水洗涤多次,置于真空干燥箱中,在70℃下干燥2.5h。
(c)煅烧
将完成的负载Au金属的吡啶-酰胺多孔有机骨架取出,放置在马沸炉中在400℃下煅烧3h,得到负载Au金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂。
将本实例的催化剂装于固定床反应装置中,以甲醇,甲苯,乙醇,丙酮作为催化反应的评价污染物进行催化评价。催化剂放入内径为8mm的石英管进行测试,催化反应装置长度40mm,挥发性有机物溶度1000ppm,空速 25000h
-1,反应温度25℃,在氧气的条件下进行催化氧化反应。结果见表1。
实施例5
(a)制备载体:
(1)将三乙胺加入到二氯甲烷溶液中,搅拌均匀得到第一溶液,三乙胺与二氯甲烷体积比为1:10。
(2)将摩尔比为3:1的2,6-二氨基吡啶和1,3,5-苯三甲酰氯加入到所述的第一溶液中并搅拌均匀得到第二溶液;2,6-二氨基吡啶和1,3,5-苯三甲酰氯的总体积与第一溶液的体积比为1:2。
(3)将所述的第二溶液放置在油浴锅中在90℃下反应2h,生成含有吡啶-酰胺官能团的多孔有机骨架。
(b)浸渍负载Au金属
(1)将所述的多孔有机骨架完全浸渍到0.5mol/L的HAuCl
4溶液中,进行超声处理5h,然后在30℃下静置12h,得到负载Au金属的多孔有机骨架。所述的HAuCl
4溶液中Au元素的质量与吡啶-酰胺多孔有机骨架的质量比为0.5%。
(2)将浓度为0.5mol/l的硼氢化钠溶液逐滴加入到静置后浸渍有吡啶-酰胺多孔有机骨架的溶液中,剧烈搅拌直到不再产生氢气,使吡啶-酰胺多孔有机骨架负载的Au
3+金属被还原。
(3)将负载了Au金属的多孔有机骨架取出,用去离子水洗涤多次,置于真空干燥箱中,在80℃下干燥2h。
(c)煅烧
将完成的负载Au金属的吡啶-酰胺多孔有机骨架取出,放置在马沸炉中在600℃下煅烧2h,得到负载Au金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂。
将本实例的催化剂装于固定床反应装置中,以甲醇,甲苯,乙醇,丙酮作为催化反应的评价污染物进行催化评价。催化剂放入内径为8mm的石英管进行测试,催化反应装置长度40mm,挥发性有机物溶度1000ppm,空速25000h
-1,反应温度25℃,在臭氧的条件下进行催化氧化反应。结果见表1。
表1.常温催化氧化评价结果
从上表可以看到,负载Pt、Au金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂对甲醇、甲苯、乙醇、丙酮有很好的降解率,此催化剂对多种VOCs有较好的降解效果。
Claims (5)
- 可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法,其特征在于包括以下步骤:(a)制备载体:(1)将三乙胺加入到二氯甲烷溶液中,搅拌均匀得到第一溶液,所述的三乙胺与二氯甲烷体积比为1:10;(2)将摩尔比为3:1的2,6-二氨基吡啶和1,3,5-苯三甲酰氯加入到所述的第一溶液中并搅拌均匀得到第二溶液;所述的2,6-二氨基吡啶和1,3,5-苯三甲酰氯的总体积与第一溶液的体积比为1:2;(3)将所述的第二溶液放置在油浴锅中在20-90℃下反应2~8h,生成含有吡啶-酰胺官能团的多孔有机骨架;(b)浸渍负载贵金属(1)将所述的多孔有机骨架完全浸渍在0.05-0.5mol/L的贵金属盐溶液中,进行超声处理1-5h,然后在10-30℃下静置6-12h,得到负载贵金属的多孔有机骨架;所述贵金属盐溶液中贵金属的质量与多孔有机骨架的质量比为0.05-0.5%;(2)将浓度为0.1-0.5mol/l的硼氢化钠溶液逐滴加入到静置后的浸渍有吡啶-酰胺多孔有机骨架的贵金属盐溶液中,剧烈搅拌直到不再产生氢气,使吡啶-酰胺多孔有机骨架负载的贵金属被还原;(3)将负载了贵金属的多孔有机骨架取出,用去离子水洗涤多次,置于真空干燥箱中,在20-80℃下干燥2-6h;(c)煅烧将完成的负载贵金属的吡啶-酰胺多孔有机骨架取出,放置在马沸炉中在 100-600℃下煅烧2-6小时,得到负载贵金属的吡啶-酰胺多孔有机骨架原子级活性位点催化剂。
- 根据权利要求1所述的可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法,其特征在于:所述的步骤(a)中油浴温度为40-60℃,反应时间为4-6h。
- 根据权利要求1或者2所述的可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法,其特征在于:所述贵金属盐溶液为HAuCl 4或者H 2PtCl 6。
- 根据权利要求3所述的可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法,其特征在于:所述的步骤(b)中超声时间为1.5-3h。
- 根据权利要求3所述的可用于常温催化降解VOCs的负载贵金属的多孔有机骨架原子级催化剂的制备方法,其特征在于:所述的步骤(c)中煅烧温度为200-400℃,煅烧时间为3-6h。
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