CN110385125A - A kind of potassium doping MnO2Catalyst and preparation method thereof - Google Patents
A kind of potassium doping MnO2Catalyst and preparation method thereof Download PDFInfo
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- 238000002360 preparation method Methods 0.000 title claims abstract description 30
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 title claims 13
- 229910052700 potassium Inorganic materials 0.000 title claims 13
- 239000011591 potassium Substances 0.000 title claims 13
- 239000003054 catalyst Substances 0.000 claims abstract description 94
- WVDDGKGOMKODPV-UHFFFAOYSA-N Benzyl alcohol Chemical compound OCC1=CC=CC=C1 WVDDGKGOMKODPV-UHFFFAOYSA-N 0.000 claims abstract description 48
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Chemical compound O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 claims abstract description 42
- 235000019445 benzyl alcohol Nutrition 0.000 claims abstract description 16
- 239000012855 volatile organic compound Substances 0.000 claims abstract description 16
- 238000010992 reflux Methods 0.000 claims abstract description 13
- 238000006243 chemical reaction Methods 0.000 claims abstract description 7
- 238000001035 drying Methods 0.000 claims abstract description 5
- 230000003647 oxidation Effects 0.000 claims description 14
- 238000007254 oxidation reaction Methods 0.000 claims description 14
- CTQNGGLPUBDAKN-UHFFFAOYSA-N O-Xylene Chemical compound CC1=CC=CC=C1C CTQNGGLPUBDAKN-UHFFFAOYSA-N 0.000 claims description 13
- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 claims description 6
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 claims description 6
- 238000006479 redox reaction Methods 0.000 claims description 5
- 238000006555 catalytic reaction Methods 0.000 claims description 3
- 239000002243 precursor Substances 0.000 abstract description 39
- 238000000034 method Methods 0.000 abstract description 11
- 230000000694 effects Effects 0.000 abstract description 8
- 239000007789 gas Substances 0.000 abstract description 8
- 239000010815 organic waste Substances 0.000 abstract description 5
- 239000012286 potassium permanganate Substances 0.000 abstract description 5
- 238000001354 calcination Methods 0.000 abstract description 4
- 230000008569 process Effects 0.000 abstract description 3
- 238000007084 catalytic combustion reaction Methods 0.000 abstract description 2
- 239000000126 substance Substances 0.000 abstract description 2
- 239000002994 raw material Substances 0.000 abstract 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 55
- 239000011572 manganese Substances 0.000 description 38
- 230000007935 neutral effect Effects 0.000 description 23
- 239000012153 distilled water Substances 0.000 description 22
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 16
- 230000003197 catalytic effect Effects 0.000 description 16
- 238000003756 stirring Methods 0.000 description 8
- 238000012546 transfer Methods 0.000 description 7
- 229910052760 oxygen Inorganic materials 0.000 description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 5
- 230000000052 comparative effect Effects 0.000 description 5
- 239000001301 oxygen Substances 0.000 description 5
- AMWRITDGCCNYAT-UHFFFAOYSA-L hydroxy(oxo)manganese;manganese Chemical compound [Mn].O[Mn]=O.O[Mn]=O AMWRITDGCCNYAT-UHFFFAOYSA-L 0.000 description 4
- 150000002500 ions Chemical class 0.000 description 4
- 229940078552 o-xylene Drugs 0.000 description 4
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 4
- 238000005033 Fourier transform infrared spectroscopy Methods 0.000 description 3
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- 231100000719 pollutant Toxicity 0.000 description 3
- 229910001414 potassium ion Inorganic materials 0.000 description 3
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 3
- 230000010718 Oxidation Activity Effects 0.000 description 2
- 238000000026 X-ray photoelectron spectrum Methods 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- 150000001555 benzenes Chemical class 0.000 description 2
- 230000003247 decreasing effect Effects 0.000 description 2
- 238000007323 disproportionation reaction Methods 0.000 description 2
- 239000007800 oxidant agent Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000010453 quartz Substances 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 238000001157 Fourier transform infrared spectrum Methods 0.000 description 1
- 239000006004 Quartz sand Substances 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- 150000001340 alkali metals Chemical class 0.000 description 1
- 238000006065 biodegradation reaction Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
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- 125000000524 functional group Chemical group 0.000 description 1
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- 238000001027 hydrothermal synthesis Methods 0.000 description 1
- 125000002887 hydroxy group Chemical group [H]O* 0.000 description 1
- 238000005470 impregnation Methods 0.000 description 1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- 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
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- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
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- B01J23/32—Manganese, technetium or rhenium
- B01J23/34—Manganese
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Abstract
本发明涉及化工催化剂技术领域,具体公开一种钾掺杂MnO2催化剂及其制备方法。所述制备方法,包括如下步骤:将MnO2前驱体加入到KOH溶液中,回流反应,产物经干燥和焙烧得到钾掺杂MnO2催化剂。本发明提供的制备方法,工艺简单,操作方便,以高锰酸钾和苯甲醇为原料,制得K+和‑OH同时掺杂的KOH‑OMS‑2催化剂,对VOCs有机废气的催化燃烧活性增强,低温处理效率提高。
The invention relates to the technical field of chemical catalysts, and specifically discloses a potassium-doped MnO2 catalyst and a preparation method thereof. The preparation method comprises the following steps: adding the MnO 2 precursor into the KOH solution, refluxing the reaction, drying and calcining the product to obtain the potassium-doped MnO 2 catalyst. The preparation method provided by the invention has simple process and convenient operation. Using potassium permanganate and benzyl alcohol as raw materials, the KOH-OMS-2 catalyst doped with K + and -OH at the same time is prepared, and has catalytic combustion activity to VOCs organic waste gas Enhanced, low temperature processing efficiency is improved.
Description
技术领域technical field
本发明涉及化工催化剂技术领域,尤其涉及一种钾掺杂MnO2催化剂及其制备方法。The invention relates to the technical field of chemical catalysts, in particular to a potassium-doped MnO2 catalyst and a preparation method thereof.
背景技术Background technique
目前,解决VOCs污染问题的首要任务是处理苯系污染物。现有处理苯系污染物的方法包括催化氧化法、吸附吸收法、生物降解法、光催化氧化法和等离子处理法等。其中,催化氧化法由于其突出的优点是能将VOCs充分转化为无污染的CO2和H2O,已经被认为是最有应用前景的治理技术。催化氧化法中的关键点是催化剂的选择,锰氧化合物是该方法中最常见的一种催化剂。At present, the primary task to solve the problem of VOCs pollution is to deal with benzene series pollutants. Existing methods for treating benzene series pollutants include catalytic oxidation, adsorption and absorption, biodegradation, photocatalytic oxidation, and plasma treatment. Among them, the catalytic oxidation method has been considered as the most promising treatment technology due to its outstanding advantage of fully converting VOCs into non-polluting CO 2 and H 2 O. The key point in the catalytic oxidation method is the choice of catalyst, and manganese oxide is the most common catalyst in this method.
MnO2的晶型有很多,其中氧化物八面体分子筛(OMS-2)长期以来一直被用作高活性,低成本,去除挥发性有机化合物(VOCs)环保催化剂。它具有多孔结构,含有混合价态的Mn物种,特别是,它具有疏水性,提高了其对水的稳定性。因此,OMS-2在催化氧化VOCs过程中表现出优异的效果。相关研究发现,将KOH或者碱金属K等掺入MnO2可以提高催化活性。目前,K+改性的MnO2的制备方法主要有浸渍法、水热法和固体研磨法等。然而,现有技术制备过程相对繁杂,且K+离子多存在于分子筛的孔道中,不能将其均匀地掺杂于MnO2晶格中。There are many crystal forms of MnO 2 , among which oxide octahedral molecular sieves (OMS-2) have long been used as highly active, low-cost, environmentally friendly catalysts for the removal of volatile organic compounds (VOCs). It has a porous structure, contains Mn species in mixed valence states, and in particular, it is hydrophobic, which improves its stability to water. Therefore, OMS-2 exhibited excellent performance in the catalytic oxidation of VOCs. Related studies have found that doping KOH or alkali metal K into MnO 2 can improve the catalytic activity. At present, the preparation methods of K + modified MnO2 mainly include impregnation method, hydrothermal method and solid grinding method, etc. However, the preparation process of the prior art is relatively complicated, and K + ions mostly exist in the pores of molecular sieves, which cannot be uniformly doped in the MnO 2 lattice.
发明内容Contents of the invention
针对现有技术存在的上述问题,本发明提供一种钾掺杂MnO2催化剂及其制备方法。Aiming at the above-mentioned problems in the prior art, the present invention provides a potassium-doped MnO2 catalyst and a preparation method thereof.
为达到上述发明目的,本发明实施例采用了如下的技术方案:In order to achieve the above-mentioned purpose of the invention, the embodiment of the present invention adopts the following technical solutions:
一种钾掺杂MnO2催化剂的制备方法,包括如下步骤:A kind of potassium-doped MnO The preparation method of catalyst, comprises the steps:
将MnO2前驱体加入到KOH溶液中,回流反应,产物经干燥和焙烧得到钾掺杂MnO2催化剂KOH-OMS-2,其中,MnO2前驱体中Mn4+占Mn元素总量的88-92%。The MnO2 precursor is added to the KOH solution, reflux reaction, the product is dried and roasted to obtain the potassium-doped MnO2 catalyst KOH-OMS-2, wherein, Mn 4+ in the MnO2 precursor accounts for 88- of the total amount of Mn elements 92%.
相对于现有技术,本发明提供的钾掺杂MnO2催化剂的制备方法,将MnO2前驱体在KOH溶液中回流,MnO2前驱体中的Mn3+离子在碱性环境中发生歧化反应,得到的Mn2+因少量溶于水中而减少了Mn的含量,形成了Mn空位,体系中的K+定位于Mn空位附近,代替Mn离子,与O离子成键,使K+离子掺杂至MnO2晶格间,同时碱性环境又可使-OH吸附于MnO2表面,经过焙烧后,得到K+和-OH同时掺杂的MnO2催化剂KOH-OMS-2。该方法工艺简单,节能环保,操作方便,使K+均匀地掺杂于MnO2晶格中。With respect to prior art, the preparation method of potassium-doped MnO 2 catalyst provided by the present invention, MnO 2 precursor is refluxed in KOH solution, and the Mn 3+ ion in MnO 2 precursor produces disproportionation reaction in alkaline environment, The obtained Mn 2+ reduces the content of Mn due to a small amount of dissolution in water, forming Mn vacancies, and the K + in the system is located near the Mn vacancies, replacing Mn ions, and forming bonds with O ions, so that K + ions are doped to Between the MnO 2 lattice, the alkaline environment can make -OH adsorb on the surface of MnO 2 , and after calcination, the MnO 2 catalyst KOH-OMS-2 doped with K + and -OH at the same time is obtained. The method has the advantages of simple process, energy saving and environmental protection, and convenient operation, so that K + is uniformly doped in the MnO 2 crystal lattice.
进一步地,所述KOH与MnO2前驱体摩尔比为2-8:0.115,提供碱性环境,同时提供K+和-OH对前驱体进行掺杂。Further, the molar ratio of KOH to the MnO 2 precursor is 2-8:0.115, providing an alkaline environment, and at the same time providing K + and -OH to dope the precursor.
进一步地,所述回流反应时间为4-24h,保证反应的充分,使前驱体形成足够的Mn空位,使K+离子掺杂至MnO2晶格间。Further, the reflux reaction time is 4-24 hours to ensure sufficient reaction, so that sufficient Mn vacancies are formed in the precursor, and K + ions are doped into the interlattice of MnO 2 .
进一步地,所述焙烧温度为400-500℃,时间为4-6h。将催化剂变为稳态结构,提升催化剂的结构强度,保证催化剂的活性和稳定性。Further, the calcination temperature is 400-500°C, and the time is 4-6h. Change the catalyst into a stable structure, improve the structural strength of the catalyst, and ensure the activity and stability of the catalyst.
进一步地,所述MnO2前驱体的制备方法为:将苯甲醇加入到高锰酸钾溶液中,发生氧化还原反应,经洗涤、干燥后,制得MnO2前驱体。所得MnO2前驱体中Mn多以Mn4+存在,Mn4+/(Mn3++Mn4+)为88-92%。且具有更多的氧空位,具有更高的催化活性。Further, the preparation method of the MnO 2 precursor is as follows: adding benzyl alcohol into the potassium permanganate solution, a redox reaction occurs, and after washing and drying, the MnO 2 precursor is obtained. In the obtained MnO 2 precursor, Mn mostly exists as Mn 4+ , and Mn 4+ /(Mn 3+ +Mn 4+ ) is 88-92%. And with more oxygen vacancies, it has higher catalytic activity.
进一步地,所述苯甲醇与高锰酸钾的摩尔比为0.5-5:1,以高锰酸钾为氧化剂,苯甲醇为还原剂,将苯甲醇滴入高锰酸钾中,形成氧化剂过量的环境,更有利于MnO2的生成,制备得到MnO2前驱体,多余的苯甲醇附着在MnO2前驱体表面,在焙烧过程中脱离,使MnO2比表面积增大和氧空位增加。Further, the molar ratio of benzyl alcohol to potassium permanganate is 0.5-5:1, potassium permanganate is used as an oxidizing agent, benzyl alcohol is used as a reducing agent, and benzyl alcohol is dropped into potassium permanganate to form an excess of oxidizing agent The environment is more conducive to the formation of MnO 2 , and the MnO 2 precursor is prepared. The excess benzyl alcohol adheres to the surface of the MnO 2 precursor and detaches during the roasting process, which increases the specific surface area of MnO 2 and the oxygen vacancies.
进一步地,所述氧化还原反应温度为10-15℃,时间为20-24h,保证氧化还原反应的顺利进行,形成MnO2前驱体。Further, the oxidation-reduction reaction temperature is 10-15° C., and the time is 20-24 hours, so as to ensure the smooth progress of the oxidation-reduction reaction and form the MnO 2 precursor.
进一步地,所述干燥温度为100-120℃,时间为10-12h。Further, the drying temperature is 100-120° C., and the drying time is 10-12 hours.
本发明还提供了钾掺杂MnO2催化剂,由上述的钾掺杂MnO2催化剂的制备方法制得。The present invention also provides a potassium-doped MnO 2 catalyst, which is prepared by the above-mentioned preparation method of a potassium-doped MnO 2 catalyst.
本发明提供的催化剂,由于MnO2晶格间中掺杂有K+,MnO2表面吸附有-OH,既可引起晶格氧的不稳定,同时造成氧配位不饱和,增加活性氧物种的数量,从而使该催化剂具有更高的活性和催化能力。In the catalyst provided by the present invention, because K + is doped between the MnO 2 lattices and -OH is adsorbed on the surface of MnO 2 , it can cause lattice oxygen instability and at the same time cause oxygen coordination unsaturation, increasing the concentration of active oxygen species. quantity, so that the catalyst has higher activity and catalytic ability.
本发明还提供了上述钾掺杂MnO2催化剂在催化氧化VOCs中的应用。The present invention also provides the application of the above potassium-doped MnO2 catalyst in the catalytic oxidation of VOCs.
进一步地,所述VOCs为苯、甲苯或二甲苯中的至少一种。Further, the VOCs are at least one of benzene, toluene or xylene.
进一步地,催化氧化温度为100~300℃,优选地,催化氧化温度为110~220℃。Further, the catalytic oxidation temperature is 100-300°C, preferably, the catalytic oxidation temperature is 110-220°C.
本发明提供的钾掺杂MnO2催化剂在催化氧化VOCs中的应用,用于低温催化氧化VOCs有机废气,催化氧化VOCs有机废气时的T100,T50和T20(T100,T50和T20分别指CO2的产率为100%,50%和20%时的温度)低于未经KOH溶液处理的OMS-2(MnO2前驱体直接焙烧制得)的相应温度。KOH-OMS-2对VOCs有机废气的催化氧化活性增强,低温处理效率提高。Potassium-doped MnO provided by the invention The application of the catalyst in catalytic oxidation of VOCs, for low-temperature catalytic oxidation of VOCs organic waste gas, T 100 during catalytic oxidation of VOCs organic waste gas, T 50 and T 20 (T 100 , T 50 and T 20 refer to the temperature when the yield of CO 2 is 100%, 50% and 20%, respectively) is lower than the corresponding temperature of OMS-2 (prepared by direct calcination of MnO 2 precursor) without KOH solution treatment. The catalytic oxidation activity of KOH-OMS-2 on VOCs organic waste gas is enhanced, and the low-temperature treatment efficiency is improved.
附图说明Description of drawings
图1是本发明实施例中KOH-OMS-2催化剂与OMS-2催化剂的催化剂活性测试图;Fig. 1 is the catalyst activity test figure of KOH-OMS-2 catalyst and OMS-2 catalyst in the embodiment of the present invention;
图2是本发明实施例中KOH-OMS-2催化剂与OMS-2催化剂的XRD谱图;Fig. 2 is the XRD spectrogram of KOH-OMS-2 catalyst and OMS-2 catalyst in the embodiment of the present invention;
图3是本发明实施例中KOH-OMS-2催化剂的SEM图;Fig. 3 is the SEM figure of KOH-OMS-2 catalyst in the embodiment of the present invention;
图4是OMS-2催化剂的SEM图;Fig. 4 is the SEM figure of OMS-2 catalyst;
图5是本发明实施例中KOH-OMS-2催化剂的EDX图谱;Fig. 5 is the EDX collection of illustrative plates of KOH-OMS-2 catalyst in the embodiment of the present invention;
图6是OMS-2催化剂的EDX图谱;Fig. 6 is the EDX collection of illustrative plates of OMS-2 catalyst;
图7是本发明实施例中KOH-OMS-2催化剂与OMS-2催化剂的FT-IR图谱;Fig. 7 is the FT-IR spectrum of KOH-OMS-2 catalyst and OMS-2 catalyst in the embodiment of the present invention;
图8、图9及图10是本发明实施例中KOH-OMS-2催化剂与OMS-2催化剂的XPS图谱。Figure 8, Figure 9 and Figure 10 are the XPS spectra of the KOH-OMS-2 catalyst and the OMS-2 catalyst in the examples of the present invention.
具体实施方式Detailed ways
为了使本发明的目的、技术方案及优点更加清楚明白,以下结合实施例,对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅仅用以解释本发明,并不用于限定本发明。In order to make the object, technical solution and advantages of the present invention more clear, the present invention will be further described in detail below in conjunction with the examples. It should be understood that the specific embodiments described here are only used to explain the present invention, not to limit the present invention.
实施例1Example 1
一种钾掺杂MnO2催化剂的制备方法,包括如下步骤:A kind of potassium-doped MnO The preparation method of catalyst, comprises the steps:
S1:取3.16g(0.02mol)的KMnO4完全溶于50mL蒸馏水中,得到KMnO4溶液,取2.1mL(0.02mol)的苯甲醇逐滴加入到KMnO4溶液中,滴加完毕后,在15℃水浴中搅拌反应24h,抽滤,水洗至中性后乙醇洗涤,再用水洗至中性,于110℃干燥12h,得到MnO2前躯体,其中,MnO2前驱体中Mn4+占Mn元素总量的92%;S1: Take 3.16g (0.02mol) of KMnO 4 completely dissolved in 50mL of distilled water to obtain a KMnO 4 solution, take 2.1mL (0.02mol) of benzyl alcohol and add it dropwise to the KMnO 4 solution. Stir and react in a water bath at ℃ for 24 hours, filter with suction, wash with water until neutral, wash with ethanol, then wash with water until neutral, and dry at 110℃ for 12 hours to obtain the MnO 2 precursor, wherein Mn 4+ in the MnO 2 precursor accounts for the Mn element 92% of the total;
S2:取33.6g(0.6mol)KOH于50mL烧杯中,蒸馏水溶解后,将KOH溶液转入100mL容量瓶中,用蒸馏水稀释至刻度,摇匀,配制成6M的KOH溶液。量取23mL配制好的KOH溶液于100mL圆底烧瓶中,加入1g(11.5mmol)的上述MnO2前躯体,加热回流反应12h,抽滤并水洗至中性,于110℃干燥12h后,400℃焙烧6h,得到钾掺杂MnO2催化剂KOH-OMS-2。S2: Take 33.6g (0.6mol) KOH in a 50mL beaker, dissolve it in distilled water, transfer the KOH solution into a 100mL volumetric flask, dilute to the mark with distilled water, shake well, and prepare a 6M KOH solution. Measure 23mL of the prepared KOH solution into a 100mL round bottom flask, add 1g (11.5mmol) of the above-mentioned MnO2 precursor, heat to reflux for 12h, filter with suction and wash with water until neutral, dry at 110°C for 12h, then dry at 400°C Calcined for 6h, the potassium-doped MnO 2 catalyst KOH-OMS-2 was obtained.
实施例2Example 2
一种钾掺杂MnO2催化剂的制备方法,包括如下步骤:A kind of potassium-doped MnO The preparation method of catalyst, comprises the steps:
S1:取3.16g(0.02mol)的KMnO4完全溶于50mL蒸馏水中,得到KMnO4溶液,取2.1mL(0.02mol)的苯甲醇逐滴加入到KMnO4溶液中,滴加完毕后,在10℃水浴中搅拌反应24h,抽滤,水洗至中性后乙醇洗涤,再用水洗至中性,于110℃干燥12h,得到MnO2前躯体,其中,MnO2前驱体中Mn4+占Mn元素总量的92%;S1: Take 3.16g (0.02mol) of KMnO 4 completely dissolved in 50mL of distilled water to obtain a KMnO 4 solution, take 2.1mL (0.02mol) of benzyl alcohol and add it dropwise to the KMnO 4 solution. Stir and react in a water bath at ℃ for 24 hours, filter with suction, wash with water until neutral, wash with ethanol, then wash with water until neutral, and dry at 110℃ for 12 hours to obtain the MnO 2 precursor, wherein Mn 4+ in the MnO 2 precursor accounts for the Mn element 92% of the total;
S2:取11.2g(0.2mol)KOH于50mL烧杯中,蒸馏水溶解后,将KOH溶液转入100mL容量瓶中,用蒸馏水稀释至刻度,摇匀,配制成2M的KOH溶液。量取23mL配制好的KOH溶液于100mL圆底烧瓶中,加入1g(11.5mmol)的上述MnO2前驱体,加热回流反应12h,抽滤并水洗至中性,于110℃干燥12h后,400℃焙烧6h,得到钾掺杂MnO2催化剂KOH-OMS-2。S2: Take 11.2g (0.2mol) KOH in a 50mL beaker, dissolve it in distilled water, transfer the KOH solution into a 100mL volumetric flask, dilute to the mark with distilled water, shake well, and prepare a 2M KOH solution. Measure 23mL of the prepared KOH solution into a 100mL round bottom flask, add 1g (11.5mmol) of the above MnO 2 precursor, heat to reflux for 12h, filter with suction and wash with water until neutral, dry at 110°C for 12h, then dry at 400°C Calcined for 6h, the potassium-doped MnO 2 catalyst KOH-OMS-2 was obtained.
实施例3Example 3
一种钾掺杂MnO2催化剂的制备方法,包括如下步骤:A kind of potassium-doped MnO The preparation method of catalyst, comprises the steps:
S1:取3.16g(0.02mol)的KMnO4完全溶于50mL蒸馏水中,得到KMnO4溶液,取1.05mL(0.001mol)的苯甲醇逐滴加入到KMnO4溶液中,滴加完毕后,在10℃水浴中搅拌反应20h,抽滤,水洗至中性后乙醇洗涤,再用水洗至中性,于120℃干燥10h,得到MnO2前躯体,其中,MnO2前驱体中Mn4+占Mn元素总量的90%;S1: Take 3.16g (0.02mol) of KMnO 4 completely dissolved in 50mL of distilled water to obtain a KMnO 4 solution, take 1.05mL (0.001mol) of benzyl alcohol and add it dropwise to the KMnO 4 solution. Stir and react in a water bath at ℃ for 20 h, filter with suction, wash with water until neutral, then wash with ethanol, then wash with water until neutral, and dry at 120 °C for 10 h to obtain the MnO 2 precursor, wherein Mn 4+ in the MnO 2 precursor accounts for the Mn element 90% of the total amount;
S2:取44.8g(0.8mol)KOH于50mL烧杯中,蒸馏水溶解后,将KOH溶液转入100mL容量瓶中,用蒸馏水稀释至刻度,摇匀,配制成8M的KOH溶液。量取23mL配制好的KOH溶液于100mL圆底烧瓶中,加入1g(11.5mmol)的上述MnO2前驱体,加热回流反应12h,抽滤并水洗至中性,于120℃干燥10h后,400℃焙烧6h,得到钾掺杂MnO2催化剂KOH-OMS-2。S2: Take 44.8g (0.8mol) KOH in a 50mL beaker, dissolve it in distilled water, transfer the KOH solution into a 100mL volumetric flask, dilute to the mark with distilled water, shake well, and prepare an 8M KOH solution. Measure 23mL of the prepared KOH solution into a 100mL round-bottomed flask, add 1g (11.5mmol) of the above-mentioned MnO 2 precursor, heat to reflux for 12h, filter with suction and wash with water until neutral, dry at 120°C for 10h, then dry at 400°C Calcined for 6h, the potassium-doped MnO 2 catalyst KOH-OMS-2 was obtained.
实施例4Example 4
一种钾掺杂MnO2催化剂的制备方法,包括如下步骤:A kind of potassium-doped MnO The preparation method of catalyst, comprises the steps:
S1:取3.16g(0.02mol)的KMnO4完全溶于50mL蒸馏水中,得到KMnO4溶液,取4.2mL(0.04mol)的苯甲醇逐滴加入到KMnO4溶液中,滴加完毕后,在15℃水浴中搅拌反应23h,抽滤,水洗至中性后乙醇洗涤,再用水洗至中性,于110℃干燥12h,得到MnO2前躯体,其中,MnO2前驱体中Mn4+占Mn元素总量的89%;S1: Take 3.16g (0.02mol) of KMnO 4 and completely dissolve it in 50mL of distilled water to obtain a KMnO 4 solution, take 4.2mL (0.04mol) of benzyl alcohol and add it dropwise to the KMnO 4 solution. Stir and react in a water bath at ℃ for 23 hours, filter with suction, wash with water until neutral, then wash with ethanol, then wash with water until neutral, and dry at 110℃ for 12 hours to obtain the MnO 2 precursor, wherein Mn 4+ in the MnO 2 precursor accounts for the Mn element 89% of the total;
S2:取33.6g(0.6mol)KOH于50mL烧杯中,蒸馏水溶解后,将KOH溶液转入100mL容量瓶中,用蒸馏水稀释至刻度,摇匀,配制成6M的KOH溶液。量取23mL配制好的KOH溶液于100mL圆底烧瓶中,加入1g(11.5mmol)的上述MnO2前驱体,加热回流反应4h,抽滤并水洗至中性,于110℃干燥12h后,400℃焙烧6h,得到钾掺杂MnO2催化剂KOH-OMS-2。S2: Take 33.6g (0.6mol) KOH in a 50mL beaker, dissolve it in distilled water, transfer the KOH solution into a 100mL volumetric flask, dilute to the mark with distilled water, shake well, and prepare a 6M KOH solution. Measure 23mL of the prepared KOH solution into a 100mL round bottom flask, add 1g (11.5mmol) of the above-mentioned MnO 2 precursor, heat to reflux for 4h, filter with suction and wash with water until neutral, dry at 110°C for 12h, then dry at 400°C Calcined for 6h, the potassium-doped MnO 2 catalyst KOH-OMS-2 was obtained.
实施例5Example 5
一种钾掺杂MnO2催化剂的制备方法,包括如下步骤:A kind of potassium-doped MnO The preparation method of catalyst, comprises the steps:
S1:取3.16g(0.02mol)的KMnO4完全溶于50mL蒸馏水中,得到KMnO4溶液,取10.5mL(0.1mol)的苯甲醇逐滴加入到KMnO4溶液中,滴加完毕后,在15℃水浴中搅拌反应24h,抽滤,水洗至中性后乙醇洗涤,再用水洗至中性,于110℃干燥12h,得到MnO2前躯体,其中,MnO2前驱体中Mn4+占Mn元素总量的88%;S1: Take 3.16g (0.02mol) of KMnO 4 completely dissolved in 50mL of distilled water to obtain a KMnO 4 solution, take 10.5mL (0.1mol) of benzyl alcohol and add it dropwise to the KMnO 4 solution. Stir and react in a water bath at ℃ for 24 hours, filter with suction, wash with water until neutral, wash with ethanol, then wash with water until neutral, and dry at 110℃ for 12 hours to obtain the MnO 2 precursor, wherein Mn 4+ in the MnO 2 precursor accounts for the Mn element 88% of the total;
S2:取33.6g(0.6mol)KOH于50mL烧杯中,蒸馏水溶解后,将KOH溶液转入100mL容量瓶中,用蒸馏水稀释至刻度,摇匀,配制成6M的KOH溶液。量取23mL配制好的KOH溶液于100mL圆底烧瓶中,加入1g(11.5mmol)的上述MnO2前驱体,加热回流反应24h,抽滤并水洗至中性,于110℃干燥12h后,400℃焙烧6h,得到钾掺杂MnO2催化剂KOH-OMS-2。S2: Take 33.6g (0.6mol) KOH in a 50mL beaker, dissolve it in distilled water, transfer the KOH solution into a 100mL volumetric flask, dilute to the mark with distilled water, shake well, and prepare a 6M KOH solution. Measure 23mL of the prepared KOH solution into a 100mL round-bottomed flask, add 1g (11.5mmol) of the above-mentioned MnO 2 precursor, heat to reflux for 24h, filter with suction and wash with water until neutral, dry at 110°C for 12h, then dry at 400°C Calcined for 6h, the potassium-doped MnO 2 catalyst KOH-OMS-2 was obtained.
实施例6Example 6
一种钾掺杂MnO2催化剂的制备方法,包括如下步骤:A kind of potassium-doped MnO The preparation method of catalyst, comprises the steps:
S1:取3.16g(0.02mol)的KMnO4完全溶于50mL蒸馏水中,得到KMnO4溶液,取2.1mL(0.02mol)的苯甲醇逐滴加入到KMnO4溶液中,滴加完毕后,在15℃水浴中搅拌反应24h,抽滤,水洗至中性后乙醇洗涤,再用水洗至中性,于100℃干燥12h,得到MnO2前躯体,其中,MnO2前驱体中Mn4+占Mn元素总量的92%;S1: Take 3.16g (0.02mol) of KMnO 4 completely dissolved in 50mL of distilled water to obtain a KMnO 4 solution, take 2.1mL (0.02mol) of benzyl alcohol and add it dropwise to the KMnO 4 solution. Stir and react in a water bath at ℃ for 24 hours, filter with suction, wash with water until neutral, then wash with ethanol, then wash with water until neutral, and dry at 100℃ for 12 hours to obtain the MnO 2 precursor, wherein Mn 4+ in the MnO 2 precursor accounts for the Mn element 92% of the total;
S2:取33.6g(0.6mol)KOH于50mL烧杯中,蒸馏水溶解后,将KOH溶液转入100mL容量瓶中,用蒸馏水稀释至刻度,摇匀,配制成6M的KOH溶液。量取23mL配制好的KOH溶液于100mL圆底烧瓶中,加入1g(11.5mmol)的上述MnO2前驱体,加热回流反应12h,抽滤并水洗至中性,于100℃干燥12h后,450℃焙烧5h,得到钾掺杂MnO2催化剂KOH-OMS-2。S2: Take 33.6g (0.6mol) KOH in a 50mL beaker, dissolve it in distilled water, transfer the KOH solution into a 100mL volumetric flask, dilute to the mark with distilled water, shake well, and prepare a 6M KOH solution. Measure 23mL of the prepared KOH solution into a 100mL round bottom flask, add 1g (11.5mmol) of the above-mentioned MnO 2 precursor, heat to reflux for 12h, filter with suction and wash with water until neutral, dry at 100°C for 12h, then dry at 450°C Calcined for 5h to obtain potassium-doped MnO 2 catalyst KOH-OMS-2.
实施例7Example 7
一种钾掺杂MnO2催化剂的制备方法,包括如下步骤:A kind of potassium-doped MnO The preparation method of catalyst, comprises the steps:
S1:取3.16g(0.02mol)的KMnO4完全溶于50mL蒸馏水中,得到KMnO4溶液,取2.1mL(0.02mol)的苯甲醇逐滴加入到KMnO4溶液中,滴加完毕后,在15℃水浴中搅拌反应24h,抽滤,水洗至中性后乙醇洗涤,再用水洗至中性,于110℃干燥11h,得到MnO2前躯体,其中,MnO2前驱体中Mn4+占Mn元素总量的92%;S1: Take 3.16g (0.02mol) of KMnO 4 completely dissolved in 50mL of distilled water to obtain a KMnO 4 solution, take 2.1mL (0.02mol) of benzyl alcohol and add it dropwise to the KMnO 4 solution. Stir and react in a water bath at ℃ for 24 hours, filter with suction, wash with water until neutral, wash with ethanol, then wash with water until neutral, and dry at 110℃ for 11 hours to obtain the MnO 2 precursor, wherein Mn 4+ in the MnO 2 precursor accounts for the Mn element 92% of the total;
S2:取33.6g(0.6mol)KOH于50mL烧杯中,蒸馏水溶解后,将KOH溶液转入100mL容量瓶中,用蒸馏水稀释至刻度,摇匀,配制成6M的KOH溶液。量取23mL配制好的KOH溶液于100mL圆底烧瓶中,加入1g(11.5mmol)的上述MnO2前驱体,加热回流反应12h,抽滤并水洗至中性,于110℃干燥11h后,500℃焙烧4h,得到钾掺杂MnO2催化剂KOH-OMS-2。S2: Take 33.6g (0.6mol) KOH in a 50mL beaker, dissolve it in distilled water, transfer the KOH solution into a 100mL volumetric flask, dilute to the mark with distilled water, shake well, and prepare a 6M KOH solution. Measure 23mL of the prepared KOH solution into a 100mL round bottom flask, add 1g (11.5mmol) of the above-mentioned MnO 2 precursor, heat to reflux for 12h, filter with suction and wash with water until neutral, dry at 110°C for 11h, then dry at 500°C Calcined for 4h, the potassium-doped MnO 2 catalyst KOH-OMS-2 was obtained.
为了更好的说明本发明的技术方案,下面还通过对比例和本发明的实施例做进一步的对比。In order to better illustrate the technical solution of the present invention, a further comparison is made below through comparative examples and examples of the present invention.
对比例1Comparative example 1
一种MnO2催化剂的制备方法,包括如下步骤:A kind of MnO The preparation method of catalyst, comprises the steps:
取3.16g(0.02mol)的KMnO4完全溶于50mL蒸馏水中,得到KMnO4溶液,取2.1mL(0.02mol)的苯甲醇逐滴加入到KMnO4溶液中,滴加完毕后,在15℃水浴中搅拌反应24h,抽滤,水洗至中性后乙醇洗涤,再用水洗至中性,于110℃干燥11h,400℃焙烧6h,得到OMS-2催化剂。Take 3.16g (0.02mol) of KMnO 4 and dissolve it completely in 50mL of distilled water to obtain a KMnO 4 solution. Take 2.1mL (0.02mol) of benzyl alcohol and add it dropwise to the KMnO 4 solution. Stir in medium temperature for 24 hours, filter with suction, wash with water until neutral, then wash with ethanol, then wash with water until neutral, dry at 110°C for 11h, and calcined at 400°C for 6h to obtain OMS-2 catalyst.
为了更好的说明本发明实施例提供的钾掺杂MnO2催化剂的特性,下面将实施例1制备的钾掺杂MnO2催化剂与对比例1制备的OMS-2催化剂进行催化剂活性评价测试。In order to better illustrate the characteristics of the potassium-doped MnO2 catalyst provided in the examples of the present invention, the potassium-doped MnO2 catalyst prepared in Example 1 and the OMS-2 catalyst prepared in Comparative Example 1 were evaluated for catalyst activity.
催化剂活性评价:采用内径为4mm的石英管作为连续流动反应装置。首先在40-60目的筛子中筛取直径为0.3~0.45mm的催化剂颗粒。称取0.5g催化剂与1.5g石英砂混合均匀后装入石英管中,然后插入加热炉中。流量为40mL/min的N2负载0.04vol.%的邻二甲苯与10mL/min的O2混合,用气体质量流量计控制气体的流速,在石英玻璃管中进行气固催化反应。邻二甲苯(o-xylene)通过毛细管柱进入分析仪分离后并进行分析,CO2通过填充柱分离,经转化炉转化为CH4后进行分析。反应条件:0.04vol.%的o-xylene,20%O2/N2平衡,气体总流量为50mL/min,W/F=0.60g.s.mL-1。T100,T50和T20(T100,T50和T20分别指CO2产率为100%、50%和20%时的温度)结果如表1和图1所示。Catalyst activity evaluation: A quartz tube with an inner diameter of 4mm was used as a continuous flow reaction device. First, sieve catalyst particles with a diameter of 0.3-0.45 mm in a 40-60 mesh sieve. Weigh 0.5g of catalyst and 1.5g of quartz sand, mix them evenly, put them into a quartz tube, and then insert into a heating furnace. The flow rate of 40mL/min N2 load 0.04vol.% o-xylene mixed with 10mL/min O2 , the flow rate of the gas was controlled by a gas mass flow meter, and the gas-solid catalytic reaction was carried out in a quartz glass tube. Ortho-xylene (o-xylene) enters the analyzer through a capillary column for separation and analysis. CO 2 is separated through a packed column and converted to CH 4 through a reformer for analysis. Reaction conditions: 0.04vol.% o-xylene, 20% O 2 /N 2 balance, total gas flow rate of 50 mL/min, W/F=0.60 gsmL -1 . The results of T 100 , T 50 and T 20 (T 100 , T 50 and T 20 refer to the temperatures when the CO 2 yields are 100%, 50% and 20% respectively) are shown in Table 1 and FIG. 1 .
表1Table 1
由上表和图1数据可知,本发明提供的KOH-OMS-2催化剂催化氧化400ppm邻二甲苯时的T100,T50和T20比未经KOH溶液处理的OMS-2催化剂的相应温度分别降低了10℃,18℃和23℃。说明,KOH-OMS-2催化剂对污染物的催化燃烧活性增强,低温处理效率明显提高。本发明其他实施例中提供的KOH-OMS-2催化剂与实施例1具有相当的效果。From the above table and Fig. 1 data as can be known, T 100 when the KOH-OMS-2 catalyst catalytic oxidation 400ppm o-xylene provided by the present invention, T 50 and T 20 than the corresponding temperature of the OMS-2 catalyst that KOH solution is not processed respectively Decreased by 10°C, 18°C and 23°C. It shows that the catalytic combustion activity of KOH-OMS-2 catalyst to pollutants is enhanced, and the low temperature treatment efficiency is obviously improved. The KOH-OMS-2 catalyst provided in other embodiments of the present invention has a comparable effect to that of embodiment 1.
为了更好的说明本发明实施例提供的钾掺杂MnO2催化剂的特性,下面将实施例1制备的KOH-OMS-2催化剂与对比例1制备的OMS-2催化剂进行XRD、SEM、EDX、FT-IR及XPS相关分析。In order to better illustrate the potassium-doped MnO2 catalyst characteristic that the embodiment of the present invention provides, the following KOH-OMS-2 catalyst prepared by Example 1 and the OMS-2 catalyst prepared by Comparative Example 1 are carried out XRD, SEM, EDX, FT-IR and XPS correlation analysis.
KOH-OMS-2催化剂与OMS-2催化剂的XRD谱图如图2所示,由XRD可得,本发明实施例成功的合成了MnO2前驱体OMS-2(氧化锰八面体分子筛晶型),且KOH-OMS-2催化剂中的K+高度分散于OMS-2之间,使K+均匀地掺杂于MnO2晶格中。OMS-2催化剂与KOH-OMS-2催化剂的扫SEM图分别如图3和图4所示,SEM结果表明经KOH回流反应后OMS-2颗粒变小。OMS-2催化剂与KOH-OMS-2催化剂的能量色散型X射线光谱仪(EDX)图谱分别如图5和图6所示,EDX表明,与OMS-2相比,KOH-OMS-2中Mn的含量减少了3.5%,而K的含量增加了3.5%,说明K替换了Mn而掺杂在了MnO2晶格间。OMS-2催化剂与KOH-OMS-2催化剂的傅立叶(FT-IR)红外图谱如图7所示,FT-IR中位于715cm-1,574cm-1,526cm-1和471cm-1的谱峰表示OMS-2中[MnO6]结构单元的存在,3400cm-1和1600cm-1确定OH官能团的存在,说明MnO2表面吸附有-OH。The XRD spectrogram of KOH-OMS-2 catalyzer and OMS-2 catalyzer is as shown in Figure 2, can obtain by XRD, the embodiment of the present invention successfully synthesized MnO 2 precursor OMS-2 (manganese oxide octahedral molecular sieve crystal form) , and the K + in the KOH-OMS-2 catalyst is highly dispersed among the OMS-2, so that K + is uniformly doped in the MnO 2 lattice. The scanning SEM images of the OMS-2 catalyst and the KOH-OMS-2 catalyst are shown in Figure 3 and Figure 4, respectively. The SEM results show that the OMS-2 particles become smaller after the KOH reflux reaction. The energy dispersive X-ray spectrometer (EDX) patterns of OMS-2 catalyst and KOH-OMS-2 catalyst are shown in Fig. 5 and Fig. 6 respectively, and EDX shows, compared with OMS-2, the content of Mn in KOH-OMS-2 The content of Mn decreased by 3.5%, while the content of K increased by 3.5%, indicating that K replaced Mn and was doped in the MnO 2 lattice. The Fourier (FT-IR) infrared spectra of OMS-2 catalyst and KOH-OMS-2 catalyst are shown in Figure 7, and the spectral peaks at 715cm -1 , 574cm -1 , 526cm -1 and 471cm -1 in FT-IR represent The presence of [MnO 6 ] structural units in OMS-2, 3400 cm -1 and 1600 cm -1 confirmed the presence of OH functional groups, indicating that -OH was adsorbed on the surface of MnO 2 .
OMS-2催化剂与KOH-OMS-2催化剂的XPS图谱如图8、9及10所示,其中,图8为OMS-2催化剂与KOH-OMS-2催化剂的Mn2p结果,KOH-OMS-2中Mn4+含量略有增加,说明MnO2前驱体中Mn3+发生歧化反应,产生Mn4+和Mn2+,Mn2+溶于水中而Mn4+存于体系中,所以含量增加。图9为K2p结果,表明K是以离子形式掺杂于OMS-2中;图10为O1s结果,表明经KOH回流后,引起O结合能高移,其周围的电子密度变小,另外,KOH-OMS-2中表面羟基OH含量较OMS-2有所增加,说明本发明催化剂为K+和-OH同时掺杂MnO2的KOH-OMS-2催化剂。The XPS spectra of OMS-2 catalyst and KOH-OMS-2 catalyst are shown in Figure 8, 9 and 10, wherein, Figure 8 is the Mn2p result of OMS-2 catalyst and KOH-OMS-2 catalyst, in KOH-OMS-2 The content of Mn 4+ increased slightly, indicating that the disproportionation reaction of Mn 3+ in the MnO 2 precursor produced Mn 4+ and Mn 2+ . Mn 2+ was dissolved in water while Mn 4+ existed in the system, so the content increased. Figure 9 is the result of K2p, indicating that K is doped in OMS-2 in the form of ions; Figure 10 is the result of O1s, indicating that after KOH reflux, the binding energy of O is high, and the electron density around it becomes smaller. In addition, KOH The surface hydroxyl OH content in -OMS-2 is increased compared with OMS-2, indicating that the catalyst of the present invention is a KOH-OMS-2 catalyst in which K + and -OH are simultaneously doped with MnO 2 .
由以上数据可得,本发明提供的钾掺杂MnO2催化剂的制备方法,将MnO2前驱体在KOH溶液中回流,得到K+和-OH同时掺杂的KOH-OMS-2催化剂,K+均匀地掺杂于MnO2晶格中,-OH吸附在MnO2表面,使得催化剂对VOCs有机废气的催化氧化活性增强,且低温处理效率提高。Can obtain from above data, the preparation method of potassium-doped MnO2 catalyst provided by the present invention, MnO2 precursor is refluxed in KOH solution, obtain the KOH-OMS-2 catalyst that K + and -OH are doped at the same time, K + Evenly doped in the MnO 2 lattice, -OH is adsorbed on the surface of MnO 2 , which enhances the catalytic oxidation activity of the catalyst for VOCs organic waste gas, and improves the low-temperature treatment efficiency.
以上所述仅为本发明的较佳实施例而已,并不用以限制本发明,凡在本发明的精神和原则之内所作的任何修改、等同替换或改进等,均应包含在本发明的保护范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Any modifications, equivalent replacements or improvements made within the spirit and principles of the present invention shall be included in the protection of the present invention. within range.
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