CN113477246B - A manganese-containing monolithic electrically assisted metal honeycomb catalyst and its preparation method and application - Google Patents
A manganese-containing monolithic electrically assisted metal honeycomb catalyst and its preparation method and application Download PDFInfo
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- 239000003054 catalyst Substances 0.000 title claims abstract description 88
- 239000011572 manganese Substances 0.000 title claims abstract description 77
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 title claims abstract description 71
- 229910052748 manganese Inorganic materials 0.000 title claims abstract description 65
- 229910052751 metal Inorganic materials 0.000 title claims abstract description 57
- 239000002184 metal Substances 0.000 title claims abstract description 57
- 238000002360 preparation method Methods 0.000 title claims abstract description 18
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 claims abstract description 45
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 claims abstract description 39
- 239000000758 substrate Substances 0.000 claims abstract description 25
- 239000002243 precursor Substances 0.000 claims abstract description 24
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 24
- 238000000034 method Methods 0.000 claims abstract description 20
- 239000007788 liquid Substances 0.000 claims abstract description 19
- 238000001027 hydrothermal synthesis Methods 0.000 claims abstract description 14
- WQZGKKKJIJFFOK-GASJEMHNSA-N Glucose Natural products OC[C@H]1OC(O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-GASJEMHNSA-N 0.000 claims abstract description 13
- WQZGKKKJIJFFOK-VFUOTHLCSA-N beta-D-glucose Chemical compound OC[C@H]1O[C@@H](O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-VFUOTHLCSA-N 0.000 claims abstract description 13
- 239000008103 glucose Substances 0.000 claims abstract description 13
- 239000012286 potassium permanganate Substances 0.000 claims abstract description 13
- 238000003756 stirring Methods 0.000 claims abstract description 11
- 239000012153 distilled water Substances 0.000 claims abstract description 7
- 239000000203 mixture Substances 0.000 claims abstract description 6
- 238000001035 drying Methods 0.000 claims abstract description 3
- 238000006243 chemical reaction Methods 0.000 claims description 37
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 16
- 238000003421 catalytic decomposition reaction Methods 0.000 claims description 14
- 238000005949 ozonolysis reaction Methods 0.000 claims description 8
- 229910000838 Al alloy Inorganic materials 0.000 claims description 5
- 229910052782 aluminium Inorganic materials 0.000 claims description 4
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 4
- 210000001124 body fluid Anatomy 0.000 claims description 4
- 239000010839 body fluid Substances 0.000 claims description 4
- 238000003746 solid phase reaction Methods 0.000 claims description 4
- -1 iron-chromium-aluminum Chemical compound 0.000 claims description 3
- 229910000623 nickel–chromium alloy Inorganic materials 0.000 claims description 2
- 238000006479 redox reaction Methods 0.000 claims description 2
- 230000001105 regulatory effect Effects 0.000 claims description 2
- 239000010935 stainless steel Substances 0.000 claims description 2
- 229910001220 stainless steel Inorganic materials 0.000 claims description 2
- 230000001276 controlling effect Effects 0.000 claims 1
- WABPQHHGFIMREM-UHFFFAOYSA-N lead(0) Chemical compound [Pb] WABPQHHGFIMREM-UHFFFAOYSA-N 0.000 claims 1
- 230000009466 transformation Effects 0.000 claims 1
- 238000000354 decomposition reaction Methods 0.000 abstract description 6
- 238000002156 mixing Methods 0.000 abstract description 3
- 238000004887 air purification Methods 0.000 abstract description 2
- 238000002791 soaking Methods 0.000 abstract 1
- 241000264877 Hippospongia communis Species 0.000 description 36
- 230000000694 effects Effects 0.000 description 9
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 7
- 239000007789 gas Substances 0.000 description 7
- AMWRITDGCCNYAT-UHFFFAOYSA-L hydroxy(oxo)manganese;manganese Chemical compound [Mn].O[Mn]=O.O[Mn]=O AMWRITDGCCNYAT-UHFFFAOYSA-L 0.000 description 6
- 238000000576 coating method Methods 0.000 description 5
- 239000013078 crystal Substances 0.000 description 4
- 229910000510 noble metal Inorganic materials 0.000 description 4
- 239000000843 powder Substances 0.000 description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 238000006722 reduction reaction Methods 0.000 description 3
- 239000012080 ambient air Substances 0.000 description 2
- 239000012298 atmosphere Substances 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Chemical compound O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 description 2
- 230000001590 oxidative effect Effects 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 238000000197 pyrolysis Methods 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 229910000314 transition metal oxide Inorganic materials 0.000 description 2
- 230000000844 anti-bacterial effect Effects 0.000 description 1
- 239000003899 bactericide agent Substances 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 239000002781 deodorant agent Substances 0.000 description 1
- 239000000645 desinfectant Substances 0.000 description 1
- 239000000411 inducer Substances 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000035939 shock Effects 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 229910052723 transition metal Inorganic materials 0.000 description 1
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- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/16—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J23/32—Manganese, technetium or rhenium
- B01J23/34—Manganese
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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
- B01D53/86—Catalytic processes
- B01D53/8671—Removing components of defined structure not provided for in B01D53/8603 - B01D53/8668
- B01D53/8675—Ozone
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- B01J35/50—Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
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- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
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Abstract
Description
技术领域technical field
本发明属于空气净化技术领域,特别涉及一种含锰整体式电辅助金属蜂窝催化剂及其制备方法和在臭氧(O3)催化分解中的应用。The invention belongs to the technical field of air purification, and in particular relates to a manganese-containing monolithic electric-assisted metal honeycomb catalyst, a preparation method thereof and an application in catalytic decomposition of ozone (O 3 ).
背景技术Background technique
臭氧(O3)由于强氧化性,常作为消毒剂、杀菌剂和除臭剂等得到广泛应用,但是臭氧在使用过程中利用效率不高会导致较多残留。这些未被处理的臭氧直接排入大气,会对各种生命体及其生存环境产生危害,因此我国《环境空气质量标准》(GB3095-2012)明确规定环境空气中臭氧1小时均值不大于0.16mg/m3。Ozone (O 3 ) is widely used as a disinfectant, bactericide, and deodorant due to its strong oxidizing properties. However, the inefficient use of ozone during use will result in more residues. These untreated ozone is directly discharged into the atmosphere, which will cause harm to various living organisms and their living environment. Therefore, China's "Ambient Air Quality Standard" (GB3095-2012) clearly stipulates that the average value of ozone in ambient air for one hour is not more than 0.16mg /m 3 .
目前处理臭氧的方法主要有活性炭法、热解法、等离子体分解法和催化分解法。活性炭法通过吸附作用去除臭氧,但存在吸附容量不高和需要经常更换的不足。热解法通过燃烧分解臭氧,但只适用高浓度臭氧处理。等离子体分解法通过高压放电产生等离子体分解臭氧,但存在操作复杂且电能消耗高等缺点。而催化分解法可以较好地弥补以上方法的不足,对臭氧的去除率也比较高,是当前研究和应用最多的臭氧处理方法。At present, the methods for treating ozone mainly include activated carbon method, pyrolysis method, plasma decomposition method and catalytic decomposition method. The activated carbon method removes ozone through adsorption, but it has the disadvantages of low adsorption capacity and frequent replacement. The pyrolysis method decomposes ozone by burning, but it is only suitable for high-concentration ozone treatment. The plasma decomposition method generates plasma to decompose ozone through high-voltage discharge, but there are disadvantages such as complicated operation and high power consumption. The catalytic decomposition method can better make up for the shortcomings of the above methods, and the removal rate of ozone is relatively high. It is currently the most researched and applied ozone treatment method.
现有技术中臭氧分解催化剂主要分为贵金属催化剂、含过渡金属氧化物催化剂和含锰催化剂。其中贵金属催化剂由于价格昂贵限制了其大规模工业运用;而含过渡金属氧化物催化剂的低温臭氧分解效率不够高。相对而言,含锰催化剂通过对单一二氧化锰体系掺杂贵金属、非贵金属元素及过渡金属元素等,可以有效增强催化剂的低温臭氧分解效率。但含锰催化剂在实际应用中存在使用寿命短和抗水能力差的不足,这主要是因为在臭氧分解反应的氧化气氛中,催化剂中低化学价态Mn3+被氧化为高化学价态Mn4+的速率比较快,而Mn4+还原回Mn3+的速率比较慢,从而引起催化剂中Mn3+与Mn4+相互转化速率出现失衡,导致催化剂表面活性氧空位数量不断减少,催化剂逐渐失活。当前研究者主要通过对含锰催化剂进行掺杂改性的方式,增强催化剂中Mn4+向Mn3+的还原反应速率,从而维持表面活性氧空位数量,提高催化剂使用寿命。而在臭氧分解反应中通过简单的直流电辅助方式提高含锰催化剂的使用寿命和抗水能力,目前还未见报道。Ozonolysis catalysts in the prior art are mainly classified into noble metal catalysts, transition metal oxide catalysts and manganese-containing catalysts. Among them, the high price of noble metal catalysts limits its large-scale industrial application; while the low-temperature ozone decomposition efficiency of catalysts containing transition metal oxides is not high enough. Relatively speaking, the manganese-containing catalyst can effectively enhance the low-temperature ozone decomposition efficiency of the catalyst by doping a single manganese dioxide system with noble metals, non-noble metal elements, and transition metal elements. However, manganese-containing catalysts have short service life and poor water resistance in practical applications. This is mainly because in the oxidizing atmosphere of the ozonolysis reaction, low chemical valence Mn 3+ in the catalyst is oxidized to high chemical valence Mn The rate of 4+ is relatively fast, while the rate of reduction of Mn 4+ back to Mn 3+ is relatively slow, which causes an imbalance in the mutual conversion rate of Mn 3+ and Mn 4+ in the catalyst, resulting in a continuous decrease in the number of active oxygen vacancies on the surface of the catalyst, and the catalyst gradually Inactivate. At present, researchers mainly increase the reduction reaction rate of Mn 4+ to Mn 3+ in the catalyst by doping and modifying the manganese-containing catalyst, so as to maintain the number of active oxygen vacancies on the surface and improve the service life of the catalyst. However, in the ozonolysis reaction, the service life and water resistance of manganese-containing catalysts are improved by a simple DC-assisted method, which has not been reported yet.
当前含锰催化剂从宏观形态上主要有颗粒型和整体式催化剂两种。其中颗粒型催化剂床层压降高,不适合处理高空速的臭氧气体。而对于整体式催化剂常以活性炭蜂窝、陶瓷蜂窝和金属蜂窝为规整载体,如中国专利CN102600861B和CN109261164A通过先制备催化剂粉体,然后配制催化剂浆液,最后通过浸泡-涂覆工艺负载在蜂窝载体上,制成成型的整体式催化剂,这样在使用时能够有效降低床层压降,在低温、高空速和高湿度条件下实现有效去除臭氧。相对活性炭蜂窝和陶瓷蜂窝,金属蜂窝载体表面一般光滑无孔,比表面积很低,采用传统浸泡-涂覆工艺很难均匀牢固负载含锰催化活性组分。但是,金属基底具有可加工性更高和抗震性更强的优点,而且金属蜂窝导电性能优良,也更适合采用直流电辅助方式增强含锰催化剂的稳定性和抗水能力。At present, there are mainly two types of manganese-containing catalysts in terms of macroscopic morphology: granular catalysts and monolithic catalysts. Among them, the pressure drop of the granular catalyst bed is high, which is not suitable for treating ozone gas with high space velocity. For monolithic catalysts, active carbon honeycombs, ceramic honeycombs and metal honeycombs are often used as regular carriers. For example, Chinese patents CN102600861B and CN109261164A prepare catalyst powder first, then prepare catalyst slurry, and finally load it on the honeycomb carrier by soaking-coating process. It is made into a shaped monolithic catalyst, which can effectively reduce the pressure drop of the bed during use, and achieve effective ozone removal under the conditions of low temperature, high space velocity and high humidity. Compared with activated carbon honeycomb and ceramic honeycomb, the surface of metal honeycomb carrier is generally smooth and non-porous, and the specific surface area is very low. It is difficult to uniformly and firmly support manganese-containing catalytic active components by traditional soaking-coating process. However, the metal substrate has the advantages of higher processability and stronger shock resistance, and the metal honeycomb has excellent electrical conductivity, and is more suitable for the DC-assisted method to enhance the stability and water resistance of the manganese-containing catalyst.
发明内容Contents of the invention
为了克服现有技术中存在的缺点和不足,本发明的首要目的在于提供一种含锰整体式电辅助金属蜂窝催化剂的制备方法,该制备方法操作简单,对任意形状的金属基底均适用,制得的催化剂中含锰活性组分在金属基底上负载牢固且分散均匀,具有活性高、导电性好、易于工业运用的特点。In order to overcome the shortcomings and deficiencies in the prior art, the primary purpose of the present invention is to provide a method for preparing a monolithic electric-assisted metal honeycomb catalyst containing manganese. The preparation method is simple to operate and is applicable to metal substrates of any shape. The manganese-containing active component in the obtained catalyst is firmly loaded and evenly dispersed on the metal substrate, and has the characteristics of high activity, good conductivity and easy industrial application.
本发明的再一目的在于提供一种上述制备方法制备得到的含锰整体式电辅助金属蜂窝催化剂。Another object of the present invention is to provide a monolithic electro-assisted metal honeycomb catalyst containing manganese prepared by the above preparation method.
本发明的又一目的在于提供一种上述含锰整体式电辅助金属蜂窝催化剂在直流电辅助条件下催化氧化分解臭氧的应用,具有反应稳定性高和抗水能力强的特性。Another object of the present invention is to provide the application of the manganese-containing monolithic electro-assisted metal honeycomb catalyst to catalyze, oxidize, and decompose ozone under the condition of direct current assistance, which has the characteristics of high reaction stability and strong water resistance.
本发明的目的通过下述技术方案实现:The object of the present invention is achieved through the following technical solutions:
一种含锰整体式电辅助金属蜂窝催化剂的制备方法,包括以下操作步骤:A method for preparing a manganese-containing monolithic electrically assisted metal honeycomb catalyst, comprising the following steps:
(1)金属基底的表面预处理:将金属蜂窝基底浸泡在0.5-2.0mol/L盐酸溶液中超声3-20min除去表面氧化物,然后用水冲洗干净;(1) Surface pretreatment of the metal substrate: Soak the metal honeycomb substrate in 0.5-2.0mol/L hydrochloric acid solution for 3-20min to remove surface oxides, then rinse with water;
(2)含锰前驱体液的配制:将高锰酸钾、乙酸和葡萄糖溶液混合,持续搅拌0.5-4h后,得到含锰前驱体液,将其置于水热反应釜中;高锰酸钾、乙酸和葡萄糖在含锰前驱体液中的浓度分别为0.05-0.30mol/L、0.05-1.20mol/L和0.01-0.10mol/L;(2) Preparation of manganese-containing precursor body fluid: mix potassium permanganate, acetic acid and glucose solution, and continue stirring for 0.5-4h to obtain manganese-containing precursor body fluid, which is placed in a hydrothermal reaction kettle; potassium permanganate, The concentrations of acetic acid and glucose in the manganese-containing precursor liquid are 0.05-0.30mol/L, 0.05-1.20mol/L and 0.01-0.10mol/L, respectively;
(3)将经过步骤(1)预处理后的金属蜂窝基底浸泡在步骤(2)所得含锰前驱体液中,在100-200℃水热反应5-40h;然后取出在蒸馏水中超声2-20min;最后在50-150℃干燥5-20h,得到含锰整体式电辅助金属蜂窝催化剂,其中锰元素的质量百分数为10-70wt.%。(3) Soak the metal honeycomb substrate pretreated in step (1) in the manganese-containing precursor liquid obtained in step (2), and conduct a hydrothermal reaction at 100-200°C for 5-40h; then take it out and ultrasonicate it in distilled water for 2-20min ; Finally, dry at 50-150° C. for 5-20 hours to obtain a manganese-containing monolithic electric-assisted metal honeycomb catalyst, wherein the mass percentage of manganese element is 10-70wt.%.
所述金属蜂窝基底的材质是不锈钢、铁铬铝合金、镍铬合金、金属铝或铝合金。The material of the metal honeycomb base is stainless steel, iron-chromium-aluminum alloy, nickel-chromium alloy, metal aluminum or aluminum alloy.
步骤(1)中所述盐酸溶液的浓度为0.8-1.3mol/L,所述超声时间为8-15min。The concentration of the hydrochloric acid solution in step (1) is 0.8-1.3mol/L, and the ultrasonic time is 8-15min.
步骤(2)中所述搅拌的转速为600-1500r/min,搅拌的时间为1.5-2h。The rotating speed of stirring described in step (2) is 600-1500r/min, and the time of stirring is 1.5-2h.
步骤(3)中所述水热反应温度为120-160℃,水热时间为10-24h。The hydrothermal reaction temperature in step (3) is 120-160°C, and the hydrothermal time is 10-24h.
步骤(3)中所述超声时间为5-10min,所述干燥温度为80-120℃。The ultrasonic time in step (3) is 5-10 min, and the drying temperature is 80-120°C.
一种由上述的制备方法制得的含锰整体式电辅助金属蜂窝催化剂,其特征在于:所述催化剂中锰元素的质量百分含量为10-70%。A manganese-containing monolithic electrically assisted metal honeycomb catalyst prepared by the above-mentioned preparation method is characterized in that the mass percentage of manganese element in the catalyst is 10-70%.
上述的含锰整体式电辅助金属蜂窝催化剂在臭氧催化分解中的应用。Application of the above manganese-containing monolithic electrically assisted metal honeycomb catalyst in the catalytic decomposition of ozone.
所述臭氧催化分解是在气固相反应装置上进行:将含锰整体式电辅助金属蜂窝催化剂置于反应管中,催化剂两端接通导线连接直流电源;在通入臭氧气体进行反应时,通过直流电源向催化剂施加稳定的电流,以辅助调控催化剂中氧化还原反应电子得失速率,进而控制催化剂中Mn3+与Mn4+相互转化速率达到动态平衡,维持表面活性氧空位数量,提高催化剂臭氧分解的反应稳定性和抗水能力。The catalytic decomposition of ozone is carried out on a gas-solid phase reaction device: the manganese-containing monolithic electric-assisted metal honeycomb catalyst is placed in the reaction tube, and the two ends of the catalyst are connected to a direct current power supply; when the ozone gas is fed into the reaction, Apply a stable current to the catalyst through a DC power supply to assist in regulating the rate of electron gain and loss in the oxidation-reduction reaction in the catalyst, and then control the mutual conversion rate of Mn 3+ and Mn 4+ in the catalyst to achieve a dynamic balance, maintain the number of active oxygen vacancies on the surface, and increase the ozone of the catalyst Decomposition reaction stability and water resistance.
本发明与传统浸泡-涂覆工艺制备整体式含锰催化剂有本质的区别。传统浸泡-涂覆工艺制备整体式含锰催化剂,一般需要预先制备含锰活性组分粉体,再通过涂覆把粉体负载到蜂窝载体上。而本发明不需要预先制备含锰活性组分粉体,只需要直接把金属蜂窝置于含锰前驱体液中,利用金属基底自身的还原性作为诱导剂,使含锰前驱体优先在金属基底表面还原析出形成锰氧化物晶核,并进一步围绕锰氧化物晶核在溶液中软模板剂的引导下逐渐长大,最终在金属基底表面形成具有特定晶型和形貌的含锰活性组分颗粒。通过把这些在金属基底表面优先生成的锰氧化物晶核作为后续长大的基点,新形成的含锰活性组分颗粒不但可以在金属基底表面均匀分散,而且可以牢固地结合在金属基底表面。The present invention is essentially different from the preparation of the monolithic manganese-containing catalyst by the traditional soaking-coating process. The preparation of monolithic manganese-containing catalysts by the traditional soaking-coating process generally requires the preparation of manganese-containing active component powders in advance, and then the powders are loaded onto the honeycomb carrier by coating. However, the present invention does not need to pre-prepare the manganese-containing active component powder, and only needs to directly place the metal honeycomb in the manganese-containing precursor liquid, and use the reducibility of the metal substrate itself as an inducer to make the manganese-containing precursor preferentially on the surface of the metal substrate Manganese oxide crystal nuclei are formed by reduction and precipitation, and then gradually grow around the manganese oxide crystal nuclei under the guidance of the soft template agent in the solution, and finally form manganese-containing active component particles with specific crystal form and morphology on the surface of the metal substrate. By using these manganese oxide crystal nuclei preferentially formed on the surface of the metal substrate as the starting point for subsequent growth, the newly formed manganese-containing active component particles can not only be uniformly dispersed on the surface of the metal substrate, but also firmly bonded to the surface of the metal substrate.
本发明相对于现有技术具有如下的优点及效果:Compared with the prior art, the present invention has the following advantages and effects:
(1)本发明催化剂中含锰活性组分可以在金属蜂窝基底表面牢固负载且分散均匀;(1) The manganese-containing active component in the catalyst of the present invention can be firmly supported and uniformly dispersed on the surface of the metal honeycomb substrate;
(2)制得的催化剂导电性能优良,可通过直流电辅助方式有效提升催化剂臭氧分解反应的稳定性和抗水能力;(2) The prepared catalyst has excellent electrical conductivity, and the stability and water resistance of the catalyst's ozonolysis reaction can be effectively improved by means of direct current assistance;
(3)本发明催化剂的制备方法简单,操作方便,对金属构件形状没有要求,对各类金属基底适用性强。(3) The preparation method of the catalyst of the present invention is simple, the operation is convenient, there is no requirement on the shape of metal components, and the applicability to various metal substrates is strong.
具体实施方式Detailed ways
下面结合实施例对本发明作进一步详细的描述,但本发明的实施方式不限于此。The present invention will be further described in detail below in conjunction with examples, but the embodiments of the present invention are not limited thereto.
实施例1Example 1
将长宽高分别为12×12×8mm约0.23g的金属铝蜂窝基底浸泡在0.8mol/L盐酸溶液中超声15min除去表面氧化物,然后用水冲洗干净;将高锰酸钾、乙酸和葡萄糖溶液混合,在1000r/min持续搅拌1.5h后,得到含锰前驱体液(高锰酸钾、乙酸和葡萄糖在含锰前驱体液中的浓度分别为0.14mol/L、0.56mol/L和0.04mol/L),将其置于水热反应釜中;将预处理后的金属蜂窝浸泡在含锰前驱体液中,在140℃水热反应24h;然后取出在蒸馏水中超声5min;最后在100℃干燥10h,得到锰元素质量百分含量52%的含锰整体式电辅助金属蜂窝催化剂。Soak a metal aluminum honeycomb substrate with a length, width, and height of about 0.23g in 0.8mol/L hydrochloric acid solution for 15 minutes to remove surface oxides, and then rinse with water; potassium permanganate, acetic acid and glucose solution Mixing, after 1.5h of continuous stirring at 1000r/min, obtain manganese-containing precursor liquid (concentrations of potassium permanganate, acetic acid and glucose in manganese-containing precursor liquid are respectively 0.14mol/L, 0.56mol/L and 0.04mol/L ), put it in a hydrothermal reaction kettle; soak the pretreated metal honeycomb in the manganese-containing precursor liquid, and conduct a hydrothermal reaction at 140°C for 24h; then take it out and ultrasonicate it in distilled water for 5min; finally dry it at 100°C for 10h, A manganese-containing monolithic electro-assisted metal honeycomb catalyst with a manganese content of 52% by mass is obtained.
本实施例得到的催化剂样品置于反应管中,两端接通导线连接直流电源,在通入臭氧气体进行反应时,通过直流电源向催化剂施加稳定的电流,从而实现直流电辅助反应的方式,用于臭氧催化分解活性测试。The catalyst sample obtained in this example is placed in a reaction tube, and the two ends are connected to a DC power supply. When the ozone gas is fed into the reaction, a stable current is applied to the catalyst through the DC power supply, thereby realizing the DC-assisted reaction mode. In the ozone catalytic decomposition activity test.
实施例2Example 2
将长宽高分别为12×12×8mm约0.25g的铝合金蜂窝基底浸泡在1.3mol/L盐酸溶液中超声8min除去表面氧化物,然后用水冲洗干净;将高锰酸钾、乙酸和葡萄糖溶液混合,在1500r/min持续搅拌1h后,得到含锰前驱体液(高锰酸钾、乙酸和葡萄糖在含锰前驱体液中的浓度分别为0.30mol/L、1.20mol/L和0.10mol/L),将其置于水热反应釜中;将预处理后的金属蜂窝浸泡在含锰前驱体液中,在120℃水热反应24h;然后取出在蒸馏水中超声5min;最后在80℃干燥20h,得到锰元素质量百分含量67%的含锰整体式电辅助金属蜂窝催化剂。Soak an aluminum alloy honeycomb substrate with a length, width, and height of about 0.25g in 1.3mol/L hydrochloric acid solution for 8 minutes to remove surface oxides, and then rinse with water; potassium permanganate, acetic acid and glucose solution Mix, and continue stirring at 1500r/min for 1 hour to obtain a manganese-containing precursor liquid (concentrations of potassium permanganate, acetic acid and glucose in the manganese-containing precursor liquid are 0.30mol/L, 1.20mol/L and 0.10mol/L, respectively) , put it in a hydrothermal reaction kettle; soak the pretreated metal honeycomb in the manganese-containing precursor liquid, and conduct a hydrothermal reaction at 120°C for 24h; then take it out and ultrasonicate it in distilled water for 5min; finally dry it at 80°C for 20h to obtain Manganese-containing monolithic electric-assisted metal honeycomb catalyst with a mass percentage of manganese element of 67%.
本实施例得到的催化剂样品置于反应管中,两端接通导线连接直流电源,在通入臭氧气体进行反应时,通过直流电源向催化剂施加稳定的电流,从而实现直流电辅助反应的方式,用于臭氧催化分解活性测试。The catalyst sample obtained in this example is placed in a reaction tube, and the two ends are connected to a DC power supply. When the ozone gas is fed into the reaction, a stable current is applied to the catalyst through the DC power supply, thereby realizing the DC-assisted reaction mode. In the ozone catalytic decomposition activity test.
实施例3Example 3
将长宽高分别为12×12×8mm约0.23g的金属铝蜂窝基底浸泡在1.0mol/L盐酸溶液中超声10min除去表面氧化物,然后用水冲洗干净;将高锰酸钾、乙酸和葡萄糖溶液混合,在600r/min持续搅拌2h后,得到含锰前驱体液(高锰酸钾、乙酸和葡萄糖在含锰前驱体液中的浓度分别为0.05mol/L、0.05mol/L和0.01mol/L),将其置于水热反应釜中;将预处理后的金属蜂窝浸泡在含锰前驱体液中,在160℃水热反应30h;然后取出在蒸馏水中超声10min;最后在120℃干燥5h,得到锰元素质量百分含量23%的含锰整体式电辅助金属蜂窝催化剂。Soak a metal aluminum honeycomb substrate with a length, width and height of about 0.23g in 1.0mol/L hydrochloric acid solution for 10 minutes to remove surface oxides, and then rinse with water; potassium permanganate, acetic acid and glucose solution Mixing, after continuous stirring at 600r/min for 2h, a manganese-containing precursor liquid was obtained (concentrations of potassium permanganate, acetic acid and glucose in the manganese-containing precursor liquid were 0.05mol/L, 0.05mol/L and 0.01mol/L respectively) , put it in a hydrothermal reaction kettle; soak the pretreated metal honeycomb in the manganese-containing precursor liquid, and conduct a hydrothermal reaction at 160°C for 30h; then take it out and ultrasonicate it in distilled water for 10min; finally dry it at 120°C for 5h to obtain A manganese-containing monolithic electro-assisted metal honeycomb catalyst with a mass percentage of manganese element of 23%.
本实施例得到的催化剂样品置于反应管中,两端接通导线连接直流电源,在通入臭氧气体进行反应时,通过直流电源向催化剂施加稳定的电流,从而实现直流电辅助反应的方式,用于臭氧催化分解活性测试。The catalyst sample obtained in this example is placed in a reaction tube, and the two ends are connected to a DC power supply. When the ozone gas is fed into the reaction, a stable current is applied to the catalyst through the DC power supply, thereby realizing the DC-assisted reaction mode. In the ozone catalytic decomposition activity test.
实施例4Example 4
将直径14mm和高8mm约2.40g的圆柱状铁铬铝蜂窝基底浸泡在1.2mol/L盐酸溶液中超声10min除去表面氧化物,然后用水冲洗干净;将高锰酸钾、乙酸和葡萄糖溶液混合,在1200r/min持续搅拌3h后,得到含锰前驱体液(高锰酸钾、乙酸和葡萄糖在含锰前驱体液中的浓度分别为0.25mol/L、1.00mol/L和0.05mol/L),将其置于水热反应釜中;将预处理后的金属蜂窝浸泡在含锰前驱体液中,在140℃水热反应12h;然后取出在蒸馏水中超声5min;最后在100℃干燥10h,得到锰元素质量百分含量15%的含锰整体式电辅助金属蜂窝催化剂。Soak a cylindrical iron-chromium-aluminum honeycomb substrate with a diameter of 14mm and a height of about 2.40g in a 1.2mol/L hydrochloric acid solution for 10 minutes to remove surface oxides, and then rinse with water; mix potassium permanganate, acetic acid and glucose solution, After stirring continuously at 1200r/min for 3h, the manganese-containing precursor liquid (concentrations of potassium permanganate, acetic acid and glucose in the manganese-containing precursor liquid were respectively 0.25mol/L, 1.00mol/L and 0.05mol/L) was obtained. It is placed in a hydrothermal reaction kettle; the pretreated metal honeycomb is soaked in the manganese-containing precursor liquid, and hydrothermally reacted at 140°C for 12h; then taken out and ultrasonicated in distilled water for 5min; finally dried at 100°C for 10h to obtain manganese element A manganese-containing monolithic electric-assisted metal honeycomb catalyst with a mass percentage of 15%.
本实施例得到的催化剂样品置于反应管中,两端接通导线连接直流电源,在通入臭氧气体进行反应时,通过直流电源向催化剂施加稳定的电流,从而实现直流电辅助反应的方式,用于臭氧催化分解活性测试。The catalyst sample obtained in this example is placed in a reaction tube, and the two ends are connected to a DC power supply. When the ozone gas is fed into the reaction, a stable current is applied to the catalyst through the DC power supply, thereby realizing the DC-assisted reaction mode. In the ozone catalytic decomposition activity test.
应用实施例1(无直流电辅助反应时)Application Example 1 (when there is no direct current auxiliary reaction)
将实施例1得到的催化剂,在自制的气固相反应装置上,进行无直流电辅助的臭氧催化分解活性考察。反应在常压和室温进行,臭氧入口浓度为20ppm,相对湿度为90%,空速为50000h-1,使用臭氧检测仪检测出口臭氧浓度。The catalyst obtained in Example 1 was tested on the ozone catalytic decomposition activity without direct current assistance on a self-made gas-solid phase reaction device. The reaction was carried out at normal pressure and room temperature, the inlet concentration of ozone was 20ppm, the relative humidity was 90%, the space velocity was 50000h -1 , and the ozone concentration at the outlet was detected by an ozone detector.
结果显示:实施例1制得的臭氧分解催化剂,在无直流电辅助时,在高湿度反应条件下臭氧转化效率在0.5h内就从95%快速降到了45%。由此可见,本发明制备的催化剂在无直流电辅助反应时,催化剂的使用寿命和抗水能力较差。The result shows: the ozonolysis catalyst prepared in embodiment 1, when there is no direct current assistance, the ozone conversion efficiency drops rapidly from 95% to 45% within 0.5h under high humidity reaction conditions. It can be seen that the catalyst prepared by the present invention has poor service life and water resistance when there is no direct current auxiliary reaction.
应用实施例2(有直流电辅助反应时)Application example 2 (when there is direct current auxiliary reaction)
将实施例1得到的催化剂,在自制的气固相反应装置上,进行有直流电辅助的臭氧催化分解活性考察,即将整体式金属蜂窝催化剂置于反应管中,催化剂两端接通导线连接直流电源,在通入臭氧气体进行反应时,通过直流电源向催化剂施加稳定的电流,从而实现直流电辅助反应的方式。反应在常压和室温进行,臭氧入口浓度为20ppm,相对湿度为90%,空速为50000h-1,使用臭氧检测仪检测出口臭氧浓度。With the catalyst obtained in Example 1, on the self-made gas-solid phase reaction device, carry out the ozone catalytic decomposition activity investigation with direct current assistance, be about to place the integrated metal honeycomb catalyst in the reaction tube, and connect the two ends of the catalyst to the direct current power supply , when the ozone gas is fed into the reaction, a stable current is applied to the catalyst through the DC power supply, so as to realize the DC-assisted reaction method. The reaction was carried out at normal pressure and room temperature, the inlet concentration of ozone was 20ppm, the relative humidity was 90%, the space velocity was 50000h -1 , and the ozone concentration at the outlet was detected by an ozone detector.
结果显示:实施例1制得的臭氧分解催化剂,在有直流电辅助时,在高湿度条件持续反应10h,臭氧转化效率在92-95%之间上下波动,基本保持不变。由此可见,本发明制备的催化剂在有直流电辅助反应时,即使是在高湿度反应条件下依然具有优良的反应稳定性和抗水能力。The results show that: the ozonolysis catalyst prepared in Example 1, when assisted by direct current, continues to react for 10 hours under high humidity conditions, the ozone conversion efficiency fluctuates between 92-95%, and basically remains unchanged. It can be seen that the catalyst prepared by the present invention still has excellent reaction stability and water resistance even under high-humidity reaction conditions when direct current is assisted in the reaction.
对实施例2-4制得的臭氧分解催化剂也进行有、无直流电辅助反应时臭氧催化分解测试,可以得到与实施例1相似的活性测试结果:即在有直流电辅助反应时,本发明制备的催化剂都具备优越的反应稳定性和抗水能力。The ozonolysis catalyst prepared in Examples 2-4 is also tested for ozone catalytic decomposition with and without direct current assisted reaction, and the activity test result similar to that of Example 1 can be obtained: that is, when there is direct current assisted reaction, the present invention prepares The catalysts all have superior reaction stability and water resistance.
上述实施例为本发明较佳的实施方式,但本发明的实施方式并不受上述实施例的限制,其他的任何未背离本发明的精神实质与原理下所作的改变、修饰、替代、组合、简化,均应为等效的置换方式,都包含在本发明的保护范围之内。The above-mentioned embodiment is a preferred embodiment of the present invention, but the embodiment of the present invention is not limited by the above-mentioned embodiment, and any other changes, modifications, substitutions, combinations, Simplifications should be equivalent replacement methods, and all are included in the protection scope of the present invention.
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