CN116395713B - A preparation method of Li-SSZ-13 zeolite molecular sieve - Google Patents
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Abstract
本发明公开了一种Li‑SSZ‑13沸石分子筛的制备方法,包括以下步骤:首先将锂源与去离子水混合搅拌均匀后,加入硅源继续搅拌均匀;之后将铝源和结构导向剂OSDA混合搅拌均匀后加入之前的混合溶液中,充分搅拌后得到混合溶胶。将溶胶转移到带有聚四氟乙烯内衬的反应釜中进行反应;将得到的固相产物用去离子水洗涤至中性并烘干、焙烧;最终得到的产物为Li‑SSZ‑13沸石分子筛。该制备方法操作简单,制备的Li‑SSZ‑13沸石分子筛为微孔结构,在气体吸附、催化领域具有良好的应用前景。The invention discloses a method for preparing a Li-SSZ-13 zeolite molecular sieve, comprising the following steps: first, after mixing a lithium source with deionized water and stirring evenly, a silicon source is added and continued to stir evenly; then, an aluminum source and a structure directing agent OSDA are mixed and stirred evenly and added to the previous mixed solution, and a mixed sol is obtained after sufficient stirring. The sol is transferred to a reactor with a polytetrafluoroethylene liner for reaction; the obtained solid phase product is washed with deionized water to neutrality and dried and roasted; the final product is a Li-SSZ-13 zeolite molecular sieve. The preparation method is simple to operate, and the prepared Li-SSZ-13 zeolite molecular sieve is a microporous structure, which has good application prospects in the fields of gas adsorption and catalysis.
Description
技术领域Technical Field
本发明涉及一种Li-SSZ-13沸石分子筛的制备方法,属于沸石分子筛制备与气体吸附领域。The invention relates to a method for preparing a Li-SSZ-13 zeolite molecular sieve, and belongs to the field of zeolite molecular sieve preparation and gas adsorption.
背景技术Background Art
近年来,随着经济的快速发展,科技的迅猛进步,人口急速增长,人们对能源的需求也日益增加,其中化石燃料的消耗急剧上升。化石燃料的燃烧伴随着大量温室气体的排放,导致的后果就是全球变暖,进而使得全球环境和气候的不断恶化。因此,控制大气中CO2的含量是目前迫在眉睫需要解决的问题。In recent years, with the rapid development of economy, rapid progress of science and technology, and rapid population growth, people's demand for energy has also increased, and the consumption of fossil fuels has risen sharply. The burning of fossil fuels is accompanied by the emission of a large amount of greenhouse gases, resulting in global warming, which in turn causes the continuous deterioration of the global environment and climate. Therefore, controlling the content of CO 2 in the atmosphere is an urgent problem that needs to be solved.
沸石分子筛是一种多孔材料,因其具有接近于气体分子大小的孔径,优秀的热稳定性,良好的机械性及化学稳定性在吸附分离领域常被用作吸附剂。SSZ-13沸石分子筛属于CHA型沸石分子筛,具有0.38nm×0.38nm的孔道结构,接近CO2的分子动力学直径,因此在选择性吸附CO2方面更具有优势。Zeolite molecular sieve is a porous material, which is often used as an adsorbent in the field of adsorption separation because of its pore size close to the size of gas molecules, excellent thermal stability, good mechanical and chemical stability. SSZ-13 zeolite molecular sieve belongs to CHA type zeolite molecular sieve, with a pore structure of 0.38nm×0.38nm, close to the molecular dynamics diameter of CO2 , so it has more advantages in selective adsorption of CO2 .
Hudson等人(Journal of the American Chemical Society,2012,134(4),1970-1973)研究了Cu-/H-SSZ-13沸石分子筛对CO2/N2的吸附性能,发现Cu-/H-SSZ-13沸石分子筛对CO2的吸附性能明显大于N2,其归因于两种气体结合位点的差异。专利CN113387369A公开了一种Cu-SSZ-13分子筛的制备方法,以三价铝源、一价钠源和四价硅源为主要原料,以铜胺络合物和胆碱阳离子作为模板,制备Cu-SSZ-13分子筛;其中,铜胺络合物含有二价铜离子和四乙烯五胺。本发明的方法成本低,且保持了Cu-SSZ-13分子筛在高温条件下较高的催化活性,属于催化领域。专利CN110028081A公开了一种合成纳米级多级孔SSZ-13分子筛的方法。将NaOH、模板剂TMAdaOH和去离子水混合,后加入Al源、Si源得到SSZ-13分子筛合成液,并于超声波振荡器中进行超声震荡,在此过程中加入晶种,高温反应后得到的产物为多级孔SSZ-13分子筛。该方法制备了纳米级多孔级SSZ-13分子筛,但CO2吸附量不高。Hudson et al. (Journal of the American Chemical Society, 2012, 134 (4), 1970-1973) studied the adsorption performance of Cu-/H-SSZ-13 zeolite molecular sieve for CO 2 /N 2 and found that the adsorption performance of Cu-/H-SSZ-13 zeolite molecular sieve for CO 2 was significantly greater than that for N 2 , which was attributed to the difference in the binding sites of the two gases. Patent CN113387369A discloses a method for preparing Cu-SSZ-13 molecular sieve, using trivalent aluminum source, monovalent sodium source and tetravalent silicon source as main raw materials, copper amine complex and choline cation as templates to prepare Cu-SSZ-13 molecular sieve; wherein the copper amine complex contains divalent copper ions and tetraethylene pentamine. The method of the present invention has low cost and maintains the high catalytic activity of Cu-SSZ-13 molecular sieve under high temperature conditions, belonging to the field of catalysis. Patent CN110028081A discloses a method for synthesizing nano-scale multi-level pore SSZ-13 molecular sieve. NaOH, template agent TMAdaOH and deionized water are mixed, and then Al source and Si source are added to obtain SSZ-13 molecular sieve synthesis liquid, which is then ultrasonically oscillated in an ultrasonic oscillator. During this process, seed crystals are added, and the product obtained after high-temperature reaction is a multi-level porous SSZ-13 molecular sieve. This method prepares nano-scale multi-porous SSZ-13 molecular sieves, but the CO 2 adsorption capacity is not high.
发明内容Summary of the invention
本发明目的在于提供了一种Li-SSZ-13沸石分子筛的制备方法,通过直接水热法合成Li-SSZ-13沸石分子筛,与传统的离子交换制备Li-SSZ-13分子筛相比,该方法不需要铵交换及锂交换,与未改性的SSZ-13分子筛相比,比表面积明显提高,吸附性能也有明显提升,制备工艺简单方便,易于实现。The purpose of the present invention is to provide a preparation method of Li-SSZ-13 zeolite molecular sieve. The Li-SSZ-13 zeolite molecular sieve is synthesized by a direct hydrothermal method. Compared with the traditional ion exchange method for preparing Li-SSZ-13 molecular sieve, the method does not require ammonium exchange and lithium exchange. Compared with the unmodified SSZ-13 molecular sieve, the specific surface area is significantly improved, the adsorption performance is also significantly improved, and the preparation process is simple, convenient and easy to implement.
为了实现上述目的,本发明采用如下的技术方案:In order to achieve the above object, the present invention adopts the following technical solution:
一种Li-SSZ-13沸石分子筛的制备方法,包括如下步骤:A method for preparing Li-SSZ-13 zeolite molecular sieve comprises the following steps:
(1)将锂源与去离子水搅拌混合均匀,加入硅源继续搅拌均匀;(1) Stir the lithium source and deionized water to mix evenly, add the silicon source and continue stirring evenly;
(2)将铝源加入结构导向剂OSDA中,加热搅拌混合均匀;(2) adding the aluminum source to the structure directing agent OSDA, heating and stirring to mix evenly;
(3)将步骤(2)中得到的混合溶液加入步骤(1)得到的混合溶液中,充分搅拌一定时间后得到混合溶胶;该溶胶的摩尔组成为:SiO2/Al2O3=10~200,SiO2/LiOH=1~50,SiO2/OSDA=0.8~10,H2O/SiO2=10~500;(3) adding the mixed solution obtained in step (2) to the mixed solution obtained in step (1), and stirring for a certain period of time to obtain a mixed sol; the molar composition of the sol is: SiO2 / Al2O3 = 10-200 , SiO2 /LiOH = 1-50, SiO2 /OSDA = 0.8-10 , H2O / SiO2 = 10-500;
(4)将步骤(3)中得到的混合溶胶转移至带有聚四氟乙烯内衬的反应釜中,放入烘箱进行反应;将反应得到的固相产物用去离子水洗涤至中性并烘干、焙烧,得到Li-SSZ-13沸石分子筛。(4) transferring the mixed sol obtained in step (3) to a reactor lined with polytetrafluoroethylene and placing it in an oven for reaction; washing the solid phase product obtained by the reaction with deionized water until it is neutral, drying and calcining, to obtain Li-SSZ-13 zeolite molecular sieve.
优选的,步骤(1)中,所述的锂源为氢氧化锂、氯化锂、碳酸锂或硫酸锂。Preferably, in step (1), the lithium source is lithium hydroxide, lithium chloride, lithium carbonate or lithium sulfate.
优选的,步骤(1)中,所述的硅源为正硅酸四乙酯、正硅酸四甲酯、气相二氧化硅、硅酸钠、硅溶胶或水玻璃。Preferably, in step (1), the silicon source is tetraethyl orthosilicate, tetramethyl orthosilicate, fumed silica, sodium silicate, silica sol or water glass.
优选的,步骤(2)中,所述的铝源为偏铝酸钠、氢氧化铝、铝薄石、正丁醇铝、异丙醇铝、铝粉或铝箔。Preferably, in step (2), the aluminum source is sodium aluminate, aluminum hydroxide, aluminum ore, aluminum n-butoxide, aluminum isopropoxide, aluminum powder or aluminum foil.
优选的,步骤(2)中,所述的结构导向剂OSDA为N,N,N-三甲基-1-金刚烷基氢氧化铵、N,N,N-三甲基金刚烷基溴化铵、N,N,N-三甲基金刚烷基碘化铵、N,N,N-三甲基苄基溴化铵、N,N,N-三甲基苄基碘化铵、四乙基氢氧化铵或N,N,N-三甲基苄基氢氧化铵。Preferably, in step (2), the structure directing agent OSDA is N,N,N-trimethyl-1-adamantyl ammonium hydroxide, N,N,N-trimethyladamantyl ammonium bromide, N,N,N-trimethyladamantyl ammonium iodide, N,N,N-trimethylbenzyl ammonium bromide, N,N,N-trimethylbenzyl ammonium iodide, tetraethylammonium hydroxide or N,N,N-trimethylbenzyl ammonium hydroxide.
优选的,步骤(2)中,所述的加热温度为50~200℃。Preferably, in step (2), the heating temperature is 50-200°C.
优选的,步骤(3)中,搅拌时间为0.2~7天。Preferably, in step (3), the stirring time is 0.2 to 7 days.
优选的,步骤(4)中,反应温度为120~200℃,反应时间为5~240h。Preferably, in step (4), the reaction temperature is 120-200° C., and the reaction time is 5-240 h.
优选的,步骤(4)中,焙烧环境为氮气、空气、氧气、臭氧或氧气/臭氧混合气,焙烧温度为180~600℃,焙烧时间为4~48h,升温、降温速率为0.2~2℃/min。Preferably, in step (4), the calcination environment is nitrogen, air, oxygen, ozone or an oxygen/ozone mixture, the calcination temperature is 180-600° C., the calcination time is 4-48 hours, and the heating and cooling rates are 0.2-2° C./min.
本发明的有益效果:Beneficial effects of the present invention:
本发明采用直接水热法合成了Li-SSZ-13沸石分子筛,制备方法操作简单。与传统离子交换制备Li-SSZ-13沸石分子筛相比,不需要铵交换-锂交换两步繁琐过程。制备的Li-SSZ-13沸石分子筛为微孔结构,与传统未改性的SSZ-13分子筛相比,比表面积明显提高,对CO2的吸附能力能够达到97.54cm3/g,在吸附、催化领域具有良好的应用前景。本发明公开的直接水热法相比于普通的离子交换法具有步骤简单的有益效果,同时制备的Li-SSZ-13沸石分子筛比未改性的SSZ-13分子筛具有显著高的CO2吸附能力的有益效果。The present invention synthesizes Li-SSZ-13 zeolite molecular sieve by direct hydrothermal method, and the preparation method is simple to operate. Compared with the preparation of Li-SSZ-13 zeolite molecular sieve by traditional ion exchange, the two-step cumbersome process of ammonium exchange-lithium exchange is not required. The prepared Li-SSZ-13 zeolite molecular sieve is a microporous structure, and compared with the traditional unmodified SSZ-13 molecular sieve, the specific surface area is significantly improved, and the adsorption capacity of CO2 can reach 97.54cm3 /g, which has good application prospects in the fields of adsorption and catalysis. The direct hydrothermal method disclosed in the present invention has the beneficial effect of simple steps compared with the ordinary ion exchange method, and the prepared Li-SSZ-13 zeolite molecular sieve has the beneficial effect of significantly higher CO2 adsorption capacity than the unmodified SSZ-13 molecular sieve.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
图1为实施例1~4制备的Li-SSZ-13沸石分子筛的扫描电镜图。FIG. 1 is a scanning electron microscope image of the Li-SSZ-13 zeolite molecular sieve prepared in Examples 1 to 4.
图2为实施例1~4制备的Li-SSZ-13沸石分子筛的X射线衍射图。FIG. 2 is an X-ray diffraction diagram of the Li-SSZ-13 zeolite molecular sieve prepared in Examples 1 to 4.
图3为对比例1制备的传统SSZ-13沸石分子筛的扫描电镜图。FIG3 is a scanning electron microscope image of the conventional SSZ-13 zeolite molecular sieve prepared in Comparative Example 1.
图4为对比例1制备的传统SSZ-13沸石分子筛的X射线衍射图。FIG. 4 is an X-ray diffraction pattern of the conventional SSZ-13 zeolite molecular sieve prepared in Comparative Example 1.
图5为实施例1~4制备的Li-SSZ-13沸石分子筛的低温N2吸附等温线。FIG. 5 is a low temperature N 2 adsorption isotherm of the Li-SSZ-13 zeolite molecular sieve prepared in Examples 1 to 4.
图6为对比例1制备的传统SSZ-13沸石分子筛的低温N2吸附等温线。FIG. 6 is a low temperature N 2 adsorption isotherm of the conventional SSZ-13 zeolite molecular sieve prepared in Comparative Example 1.
图7为实施例1~4制备的Li-SSZ-13沸石分子筛及对比例1制备的传统SSZ-13沸石分子筛在0℃条件下的CO2吸附等温线。FIG. 7 shows the CO 2 adsorption isotherms of the Li-SSZ-13 zeolite molecular sieves prepared in Examples 1 to 4 and the conventional SSZ-13 zeolite molecular sieve prepared in Comparative Example 1 at 0°C.
具体实施方式DETAILED DESCRIPTION
下面结合实施例对本发明做更进一步地解释。下列实施例仅用于说明本发明,但并不用来限定本发明的实施范围。The present invention is further explained below in conjunction with the examples. The following examples are only used to illustrate the present invention, but are not intended to limit the scope of the present invention.
实施例1Example 1
一种Li-SSZ-13沸石分子筛的制备方法,包括如下步骤:A method for preparing Li-SSZ-13 zeolite molecular sieve comprises the following steps:
(1)将锂源氢氧化锂与去离子水搅拌混合均匀,加入硅源气相二氧化硅继续搅拌2h;(1) Stir and mix lithium hydroxide, a lithium source, and deionized water to mix evenly, add fumed silica, a silicon source, and continue stirring for 2 hours;
(2)将铝源氢氧化铝加入结构导向剂OSDA[N,N,N-三甲基-1-金刚烷基氢氧化铵(TMAdaOH)]中,80℃加热搅拌1h;(2) adding aluminum hydroxide, an aluminum source, to the structure directing agent OSDA [N,N,N-trimethyl-1-adamantyl ammonium hydroxide (TMAdaOH)], heating and stirring at 80°C for 1 h;
(3)将步骤(2)中得到的混合溶液加入步骤(1)得到的混合溶液中,充分搅拌5天后得到混合溶胶;该溶胶的摩尔组成为:SiO2/Al2O3=60,SiO2/LiOH=10,SiO2/OSDA=3,H2O/SiO2=50;(3) adding the mixed solution obtained in step (2) to the mixed solution obtained in step (1), and stirring for 5 days to obtain a mixed sol; the molar composition of the sol is: SiO2 / Al2O3 = 60 , SiO2 /LiOH=10, SiO2 /OSDA=3, H2O / SiO2 =50;
(4)将步骤(3)中得到的混合溶胶转移至带有聚四氟乙烯内衬的反应釜中,放入150℃烘箱中进行反应48h;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,得到Li-SSZ-13沸石分子筛。(4) The mixed sol obtained in step (3) is transferred to a reactor with a polytetrafluoroethylene liner, and placed in a 150°C oven for reaction for 48 hours; the solid phase product obtained by the reaction is washed with deionized water until neutral, placed in a 60°C oven for drying overnight, and then placed in a muffle furnace and calcined at 550°C for 6 hours in an air environment, with a heating and cooling rate of 1°C/min to obtain Li-SSZ-13 zeolite molecular sieve.
实施例2Example 2
按实施例1相同的操作步骤,只是步骤(3)中得到的混合溶胶的摩尔组成为:SiO2/Al2O3=60,SiO2/LiOH=50,SiO2/OSDA=3,H2O/SiO2=50;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,得到Li-SSZ-13沸石分子筛。The same operating steps as in Example 1 were followed, except that the molar composition of the mixed sol obtained in step (3) was: SiO2 / Al2O3 = 60 , SiO2 /LiOH=50, SiO2 /OSDA=3, H2O / SiO2 =50; the solid phase product obtained by the reaction was washed with deionized water until neutral, dried in an oven at 60°C overnight, and then placed in a muffle furnace and calcined at 550°C for 6h in an air environment with a heating and cooling rate of 1°C/min to obtain Li-SSZ-13 zeolite molecular sieve.
实施例3Example 3
按实施例1相同的操作步骤,只是步骤(3)中得到的混合溶胶的摩尔组成为:SiO2/Al2O3=60,SiO2/LiOH=20,SiO2/OSDA=3,H2O/SiO2=50;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,得到Li-SSZ-13沸石分子筛。The same operating steps as in Example 1 were followed, except that the molar composition of the mixed sol obtained in step (3) was: SiO2 / Al2O3 = 60 , SiO2 /LiOH=20, SiO2 /OSDA=3, H2O / SiO2 =50; the solid phase product obtained by the reaction was washed with deionized water until neutral, dried in an oven at 60°C overnight, and then placed in a muffle furnace and calcined at 550°C for 6h in an air environment with a heating and cooling rate of 1°C/min to obtain Li-SSZ-13 zeolite molecular sieve.
实施例4Example 4
按实施例1相同的操作步骤,只是步骤(3)中得到的混合溶胶的摩尔组成为:SiO2/Al2O3=60,SiO2/LiOH=1,SiO2/OSDA=3,H2O/SiO2=50;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,得到Li-SSZ-13沸石分子筛。The same operating steps as in Example 1 were followed, except that the molar composition of the mixed sol obtained in step (3) was: SiO2 / Al2O3 = 60 , SiO2 /LiOH=1, SiO2 /OSDA=3, H2O / SiO2 =50; the solid phase product obtained by the reaction was washed with deionized water until neutral, dried in an oven at 60°C overnight, and then placed in a muffle furnace and calcined at 550°C for 6h in an air environment with a heating and cooling rate of 1°C/min to obtain Li-SSZ-13 zeolite molecular sieve.
图1为实施例1~4制备的Li-SSZ-13沸石分子筛的扫描电镜图。可以观察到(a)实施例1制备的Li-SSZ-13沸石分子筛形貌均一,呈立方形,尺寸大小约为3~4μm。(b)实施例2制备的Li-SSZ-13沸石分子筛形貌均一,呈立方形,尺寸大小约为2~3μm。(c)实施例3制备的Li-SSZ-13沸石分子筛形貌均一,呈球形,尺寸大小约为2~3μm。(d)实施例4制备的Li-SSZ-13沸石分子筛形貌均一,呈椭球形,尺寸大小约为2~3μm。Figure 1 is a scanning electron microscope image of the Li-SSZ-13 zeolite molecular sieve prepared in Examples 1 to 4. It can be observed that (a) the Li-SSZ-13 zeolite molecular sieve prepared in Example 1 has a uniform morphology, is cubic, and has a size of about 3 to 4 μm. (b) The Li-SSZ-13 zeolite molecular sieve prepared in Example 2 has a uniform morphology, is cubic, and has a size of about 2 to 3 μm. (c) The Li-SSZ-13 zeolite molecular sieve prepared in Example 3 has a uniform morphology, is spherical, and has a size of about 2 to 3 μm. (d) The Li-SSZ-13 zeolite molecular sieve prepared in Example 4 has a uniform morphology, is ellipsoidal, and has a size of about 2 to 3 μm.
图2为实施例1~4制备的Li-SSZ-13沸石分子筛的X射线衍射图。可以观察到各个SiO2/LiOH条件下制备的Li-SSZ-13沸石分子筛为典型的CHA特征衍射峰,无明显杂峰,且峰强度高;实施例4峰强度相对降低,可能是由于LiOH的浓度增加,混合溶胶的pH值上升,对分子筛的生长消融作用大于促进作用,抑制了分子筛的合成。Figure 2 is an X-ray diffraction diagram of the Li-SSZ-13 zeolite molecular sieve prepared in Examples 1 to 4. It can be observed that the Li-SSZ-13 zeolite molecular sieve prepared under various SiO 2 /LiOH conditions has a typical CHA characteristic diffraction peak, no obvious impurity peak, and high peak intensity; the peak intensity of Example 4 is relatively reduced, which may be due to the increase in the concentration of LiOH and the increase in the pH value of the mixed sol, which has a greater ablation effect on the growth of the molecular sieve than a promotion effect, thereby inhibiting the synthesis of the molecular sieve.
实施例5Example 5
按实施例1相同的操作步骤,只是步骤(3)中得到的混合溶胶的摩尔组成为:SiO2/Al2O3=200,SiO2/LiOH=10,SiO2/OSDA=3,H2O/SiO2=50;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,所得的Li-SSZ-13沸石分子筛在0℃,P/P0=1条件下,CO2吸附量为85.32cm3/g。The same operating steps as in Example 1 were followed, except that the molar composition of the mixed sol obtained in step (3) was: SiO 2 /Al 2 O 3 =200, SiO 2 /LiOH=10, SiO 2 /OSDA=3, H 2 O/SiO 2 =50; the solid phase product obtained by the reaction was washed with deionized water until neutral, placed in a 60°C oven for drying overnight, and then placed in a muffle furnace and calcined at 550°C for 6h in an air environment with a heating and cooling rate of 1°C/min. The obtained Li-SSZ-13 zeolite molecular sieve had a CO 2 adsorption capacity of 85.32 cm 3 /g at 0°C and P/P 0 =1.
实施例6Example 6
按实施例1相同的操作步骤,只是步骤(3)中得到的混合溶胶的摩尔组成为:SiO2/Al2O3=10,SiO2/LiOH=10,SiO2/OSDA=3,H2O/SiO2=50;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,所得的Li-SSZ-13沸石分子筛在0℃,P/P0=1条件下,CO2吸附量为88.55cm3/g。The same operating steps as in Example 1 were followed, except that the molar composition of the mixed sol obtained in step (3) was: SiO 2 /Al 2 O 3 =10, SiO 2 /LiOH=10, SiO 2 /OSDA=3, H 2 O/SiO 2 =50; the solid phase product obtained by the reaction was washed with deionized water until neutral, placed in a 60°C oven for drying overnight, and then placed in a muffle furnace and calcined at 550°C for 6h in an air environment with a heating and cooling rate of 1°C/min. The obtained Li-SSZ-13 zeolite molecular sieve had a CO 2 adsorption capacity of 88.55 cm 3 /g at 0°C and P/P 0 =1.
实施例7Example 7
按实施例1相同的操作步骤,只是步骤(3)中得到的混合溶胶的摩尔组成为:SiO2/Al2O3=60,SiO2/LiOH=10,SiO2/OSDA=10,H2O/SiO2=10;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,所得的Li-SSZ-13沸石分子筛在0℃,P/P0=1条件下,CO2吸附量为90.32cm3/g。The same operating steps as in Example 1 were followed, except that the molar composition of the mixed sol obtained in step (3) was: SiO 2 /Al 2 O 3 =60, SiO 2 /LiOH=10, SiO 2 /OSDA=10, H 2 O/SiO 2 =10; the solid phase product obtained by the reaction was washed with deionized water until neutral, placed in a 60°C oven for drying overnight, and then placed in a muffle furnace and calcined at 550°C for 6h in an air environment with a heating and cooling rate of 1°C/min. The obtained Li-SSZ-13 zeolite molecular sieve had a CO 2 adsorption capacity of 90.32 cm 3 /g at 0°C and P/P 0 =1.
实施例8Example 8
按实施例1相同的操作步骤,只是步骤(3)中得到的混合溶胶的摩尔组成为:SiO2/Al2O3=60,SiO2/LiOH=10,SiO2/OSDA=0.8,H2O/SiO2=500;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,所得的Li-SSZ-13沸石分子筛在0℃,P/P0=1条件下,CO2吸附量为88.47cm3/g。The same operating steps as in Example 1 were followed, except that the molar composition of the mixed sol obtained in step (3) was: SiO 2 /Al 2 O 3 =60, SiO 2 /LiOH=10, SiO 2 /OSDA=0.8, H 2 O/SiO 2 =500; the solid phase product obtained by the reaction was washed with deionized water until neutral, placed in a 60°C oven for drying overnight, and then placed in a muffle furnace and calcined at 550°C for 6h in an air environment with a heating and cooling rate of 1°C/min. The obtained Li-SSZ-13 zeolite molecular sieve had a CO 2 adsorption capacity of 88.47 cm 3 /g at 0°C and P/P 0 =1.
实施例9Example 9
按实施例1相同的操作步骤,只是步骤(1)中加入的锂源为氢氧化锂和氯化锂,硅源为硅溶胶,步骤(2)中加入的铝源为偏铝酸钠,结构导向剂OSDA为N,N,N-三甲基金刚烷基溴化铵;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,所得的Li-SSZ-13沸石分子筛在0℃,P/P0=1条件下,CO2吸附量为90.32cm3/g。The same operating steps as in Example 1 were followed, except that the lithium source added in step (1) was lithium hydroxide and lithium chloride, the silicon source was silica sol, the aluminum source added in step (2) was sodium aluminate, and the structure directing agent OSDA was N,N,N-trimethyladamantyl ammonium bromide. The solid phase product obtained by the reaction was washed with deionized water until neutral, dried in an oven at 60°C overnight, and then placed in a muffle furnace and calcined at 550°C for 6h in an air environment with a heating and cooling rate of 1°C/min. The obtained Li-SSZ-13 zeolite molecular sieve had a CO 2 adsorption capacity of 90.32 cm 3 /g at 0°C and P/P 0 =1.
实施例10Example 10
按实施例1相同的操作步骤,只是步骤(3)中搅拌的时间为0.2天,步骤(4)中反应的温度为200℃,反应时间为5h;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在氧气/臭氧混合环境中,180℃焙烧48h,升温、降温速率为2℃/min,所得的Li-SSZ-13沸石分子筛在0℃,P/P0=1条件下,CO2吸附量为83.76cm3/g。The same operating steps as in Example 1 were followed, except that the stirring time in step (3) was 0.2 days, the reaction temperature in step (4) was 200° C., and the reaction time was 5 hours. The solid phase product obtained by the reaction was washed with deionized water until neutral, placed in a 60° C. oven for drying overnight, and then placed in a muffle furnace and calcined at 180° C. for 48 hours in an oxygen/ozone mixed environment with a heating and cooling rate of 2° C./min. The obtained Li-SSZ-13 zeolite molecular sieve had a CO 2 adsorption capacity of 83.76 cm 3 /g at 0° C. and P/P 0 =1.
实施例11Embodiment 11
按实施例1相同的操作步骤,只是步骤(3)中搅拌的时间为7天,步骤(4)中反应的温度为120℃,反应时间为240h;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在氧气环境下,600℃焙烧4h,升温、降温速率为0.2℃/min,所得的Li-SSZ-13沸石分子筛在0℃,P/P0=1条件下,CO2吸附量为80.49cm3/g。The same operating steps as in Example 1 were followed, except that the stirring time in step (3) was 7 days, the reaction temperature in step (4) was 120°C, and the reaction time was 240 hours; the solid phase product obtained by the reaction was washed with deionized water until neutral, placed in a 60°C oven for drying overnight, and then placed in a muffle furnace and calcined at 600°C for 4 hours in an oxygen environment, with a heating and cooling rate of 0.2°C/min. The obtained Li-SSZ-13 zeolite molecular sieve had a CO 2 adsorption capacity of 80.49 cm 3 /g at 0°C and P/P 0 =1.
对比例1Comparative Example 1
(1)将钠源氢氧化钠与去离子水搅拌混合均匀,加入硅源气相二氧化硅继续搅拌2h;(1) Stir and mix sodium hydroxide (sodium source) and deionized water evenly, add fumed silica (silicon source) and continue stirring for 2 hours;
(2)将铝源氢氧化铝加入结构导向剂OSDA[N,N,N-三甲基-1-金刚烷基氢氧化铵(TMAdaOH)]中,80℃加热搅拌1h;(2) adding aluminum hydroxide, an aluminum source, to the structure directing agent OSDA [N,N,N-trimethyl-1-adamantyl ammonium hydroxide (TMAdaOH)], heating and stirring at 80°C for 1 h;
(3)将步骤(2)中得到的混合溶液加入步骤(1)得到的混合溶液中,充分搅拌24h后得到混合溶胶;该溶胶的摩尔组成为:SiO2/Al2O3=200,SiO2/NaOH=5,SiO2/OSDA=5,H2O/SiO2=100;(3) adding the mixed solution obtained in step (2) to the mixed solution obtained in step (1), and stirring for 24 hours to obtain a mixed sol; the molar composition of the sol is: SiO 2 /Al 2 O 3 = 200, SiO 2 /NaOH = 5, SiO 2 /OSDA = 5, H 2 O/SiO 2 = 100;
(4)将步骤(3)中得到的混合溶胶转移至带有聚四氟乙烯内衬的反应釜中,放入160℃烘箱中进行反应4天;将反应得到的固相产物用去离子水洗涤至中性,放入60℃烘箱烘干过夜,之后放入马弗炉中,在空气环境下,550℃焙烧6h,升温、降温速率为1℃/min,得到SSZ-13沸石分子筛。(4) The mixed sol obtained in step (3) is transferred to a reactor with a polytetrafluoroethylene liner, and placed in a 160°C oven for reaction for 4 days; the solid phase product obtained by the reaction is washed with deionized water until neutral, placed in a 60°C oven for drying overnight, and then placed in a muffle furnace and calcined at 550°C for 6h in an air environment, with a heating and cooling rate of 1°C/min to obtain SSZ-13 zeolite molecular sieve.
图5和图6为实施例1~4和对比例1制备的Li-SSZ-13和SSZ-13沸石分子筛的低温N2吸附等温线,由图可见实施例1~4和对比例1呈现I型吸附等温线,测试结果也表明,主要孔结构由微孔组成;实施例1~4的比表面积相对对比例1也有明显的提高。Figures 5 and 6 are the low-temperature N2 adsorption isotherms of Li-SSZ-13 and SSZ-13 zeolite molecular sieves prepared in Examples 1 to 4 and Comparative Example 1. It can be seen from the figures that Examples 1 to 4 and Comparative Example 1 present Type I adsorption isotherms. The test results also show that the main pore structure is composed of micropores; the specific surface area of Examples 1 to 4 is also significantly improved relative to Comparative Example 1.
图7为实施例1~4制备的Li-SSZ-13沸石分子筛及对比例1制备的传统SSZ-13沸石分子筛在0℃条件下的CO2吸附等温线。测试结果表明,Li-SSZ-13沸石分子筛的CO2吸附性能对比传统SSZ-13沸石分子筛有很大的提高,吸附容量最高可以达到97.54cm3/g。Figure 7 shows the CO 2 adsorption isotherms of the Li-SSZ-13 zeolite molecular sieves prepared in Examples 1 to 4 and the conventional SSZ-13 zeolite molecular sieve prepared in Comparative Example 1 at 0°C. The test results show that the CO 2 adsorption performance of the Li-SSZ-13 zeolite molecular sieve is greatly improved compared with the conventional SSZ-13 zeolite molecular sieve, and the maximum adsorption capacity can reach 97.54 cm 3 /g.
表1实施例与对比例低温N2物理吸附数据Table 1 Low temperature N2 physical adsorption data of examples and comparative examples
*由HK模型算得。 * Calculated by HK model.
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