CN115869983A - Manganese-nitrogen co-doped carbon nanosheet, preparation method and application - Google Patents
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Abstract
本发明环境材料处理废水领域,提供了一种锰氮共掺杂碳纳米片、制备方法及应用,该方法通过冷冻干燥和碳化过程的两步合成过程,将过渡金属锰成功地锚定在掺杂N的多孔碳上。该材料以三聚氰胺为氮源,葡萄糖为碳源,氯化锰为金属前驱体,一步碳化形成。葡萄糖生成的初级碳中间体通过供体‑受体相互作用与三聚氰胺在热解过程中形成的层状g‑C3N4结合,g‑C3N4作为模板引导碳层沿平面形成碳纳米片结构;三聚氰胺提供丰富的氮原子环境,捕获过渡金属锰,形成高度分散的Mn‑Nx配位键,将氮物种固定在碳纳米片上,提供多种活性氮组分。该材料能够提高催化剂降解有机污染物苯酚速率且具有良好的循环性,降低了金属浸出浓度,不会对环境造成二次污染。
In the field of wastewater treatment of environmental materials, the present invention provides a manganese-nitrogen co-doped carbon nanosheet, a preparation method and an application thereof. The method successfully anchors the transition metal manganese on the doped carbon nanosheet through a two-step synthesis process of freeze-drying and carbonization. N-doped porous carbon. The material uses melamine as a nitrogen source, glucose as a carbon source, and manganese chloride as a metal precursor, and is formed by one-step carbonization. The primary carbon intermediate of glucose generation combines with the layered g-C 3 N 4 formed during the pyrolysis of melamine through donor-acceptor interactions, and g-C 3 N 4 acts as a template to guide the carbon layer along the plane to form carbon nanostructures sheet structure; melamine provides a rich nitrogen atom environment, captures transition metal manganese, forms highly dispersed Mn-Nx coordination bonds, fixes nitrogen species on carbon nanosheets, and provides a variety of active nitrogen components. The material can increase the catalyst degradation rate of organic pollutant phenol and has good circulation, reduces the metal leaching concentration, and will not cause secondary pollution to the environment.
Description
技术领域technical field
本发明环境材料处理废水领域,具体涉及一种锰氮共掺杂碳纳米片、制备方法及应用。The invention relates to the field of waste water treatment of environmental materials, and specifically relates to a manganese-nitrogen co-doped carbon nanosheet, a preparation method and an application.
背景技术Background technique
如今,在废水和水环境中广泛检测到酚类和抗生素污染物。它们的广泛存在对自然和人类健康造成严重影响,即使在低浓度下,它们也引起了全世界的关注。因此,去除水中的这些有机污染物引起了对高效处理技术日益增长的需求。近年来,基于高级氧化过程(AOPs)的过氧单硫酸盐(PMS)活化已被证实是去除有机污染物的最有效方法之一。Today, phenolic and antibiotic contaminants are widely detected in wastewater and water environments. Their widespread presence has serious impacts on nature and human health, and even at low concentrations, they have attracted worldwide attention. Therefore, the removal of these organic pollutants in water has given rise to an increasing demand for efficient treatment technologies. In recent years, the activation of peroxymonosulfate (PMS) based on advanced oxidation processes (AOPs) has been proven to be one of the most effective methods for the removal of organic pollutants.
碳基材料作为一种不耐金属、耐酸碱、比表面积大、活性位点多等优点,作为一种活化PMS的新型多相催化剂受到广泛关注。然而,原始的碳基材料(如碳纳米管、石墨烯、金刚石、生物炭)仍然具有有限的活性官能团、结构缺陷和石墨化程度较低。虽然为了提高碳基材料的催化性能,人们采用了多种改性方法,但锰氮共掺杂碳基材料目前研究较少。Carbon-based materials, as a kind of metal-resistant, acid-base resistant, large specific surface area, and more active sites, have attracted extensive attention as a new type of heterogeneous catalyst for activating PMS. However, pristine carbon-based materials (such as carbon nanotubes, graphene, diamond, and biochar) still have limited active functional groups, structural defects, and a low degree of graphitization. Although a variety of modification methods have been used to improve the catalytic performance of carbon-based materials, there are few studies on manganese-nitrogen co-doped carbon-based materials.
公开于该背景技术部分的信息仅仅旨在增加对本发明的总体背景的理解,而不应当被视为承认或以任何形式暗示该信息构成已为本领域一般技术人员所公知的现有技术。The information disclosed in this Background section is only for enhancing the understanding of the general background of the present invention and should not be taken as an acknowledgment or any form of suggestion that the information constitutes the prior art that is already known to those skilled in the art.
发明内容Contents of the invention
本发明是为了解决上述问题而进行的,目的在于提供一种锰氮共掺杂碳纳米片、制备方法及应用,该材料具有高效降解性能,能够活化过硫酸盐来降解苯酚。The present invention is carried out in order to solve the above problems, and the purpose is to provide a manganese nitrogen co-doped carbon nanosheet, a preparation method and an application. The material has high-efficiency degradation performance and can activate persulfate to degrade phenol.
本发明提供了一种锰氮共掺杂碳纳米片的制备方法,具有这样的特征,包括以下步骤:步骤1,将一定量的氯化锰及氯化锌溶于水中,混合均匀得到A液;步骤2,将一定量的三聚氰胺及葡萄糖溶于水中,混合均匀得到B液;步骤3,将A液缓慢滴加入B液中,得到乳白色沉淀;步骤4,将乳白色沉淀缓慢滴入液氮中急速冷冻,得到冷冻产物;步骤5,将冷冻产物放入冷冻干燥器中在-45℃~-55℃条件下冷冻干燥,研磨真空干燥得到白色粉末;步骤6,将白色粉末在惰性气氛下高温煅烧,得到煅烧产物,研磨并酸浸,干燥得到锰氮共掺杂碳纳米片。The invention provides a method for preparing manganese nitrogen co-doped carbon nanosheets, which has such characteristics and includes the following steps:
在本发明提供的锰氮共掺杂碳纳米片的制备方法中,还可以具有这样的特征:其中,步骤1中,氯化锰为氯化锰四水合物,质量为0.197g~0.394g,氯化锌的质量为0.136g,水的体积为5ml。In the preparation method of manganese nitrogen co-doped carbon nanosheets provided by the present invention, it may also have the following characteristics: wherein, in
在本发明提供的锰氮共掺杂碳纳米片的制备方法中,还可以具有这样的特征:其中,步骤2中,三聚氰胺的质量为5g,葡萄糖的质量为2g,水的体积为25ml。In the preparation method of manganese-nitrogen co-doped carbon nanosheets provided by the present invention, it may also have such features: wherein, in
在本发明提供的锰氮共掺杂碳纳米片的制备方法中,还可以具有这样的特征:其中,步骤3中,将A液缓慢滴加入B液中,滴加过程中持续搅拌,滴加完毕后继续搅拌4h,得到乳白色沉淀。In the preparation method of manganese-nitrogen co-doped carbon nanosheets provided by the present invention, it may also have such a feature: wherein, in
在本发明提供的锰氮共掺杂碳纳米片的制备方法中,还可以具有这样的特征:其中,步骤4中,将静置后的白色沉淀以每秒一滴的速度滴入液氮中进行急速冷冻。In the preparation method of the manganese-nitrogen co-doped carbon nanosheets provided by the present invention, it may also have such a feature: wherein, in
在本发明提供的锰氮共掺杂碳纳米片的制备方法中,还可以具有这样的特征:其中,步骤6中,将干燥产物在氮气气氛下以4℃~6℃的升温速率升温至800℃~900℃高温煅烧。In the preparation method of manganese-nitrogen co-doped carbon nanosheets provided by the present invention, it may also have such a feature: wherein, in step 6, the dried product is heated to 800 °C at a heating rate of 4 ° C to 6 ° C under a nitrogen atmosphere. ℃~900℃ high temperature calcination.
在本发明提供的锰氮共掺杂碳纳米片的制备方法中,还可以具有这样的特征:其中,步骤6中,将煅烧产物在0.5M硫酸中洗涤10h,干燥得到锰氮共掺杂碳纳米片。In the preparation method of manganese-nitrogen co-doped carbon nanosheets provided by the present invention, it may also have such a feature: wherein, in step 6, the calcined product is washed in 0.5M sulfuric acid for 10 h, and dried to obtain manganese-nitrogen co-doped carbon Nanosheets.
本发明还提供了一种锰氮共掺杂碳纳米片,具有这样的特征,由锰氮共掺杂碳纳米片的制备方法制备得到。The present invention also provides a manganese nitrogen co-doped carbon nano sheet, which has such a feature and is prepared by the preparation method of the manganese nitrogen co-doped carbon nano sheet.
本发明还提供了一种锰氮共掺杂碳纳米片在活化过硫酸盐降解苯酚中的应用。The invention also provides an application of manganese nitrogen co-doped carbon nano sheet in activating persulfate to degrade phenol.
在本发明提供的锰氮共掺杂碳纳米片在活化过硫酸盐降解苯酚中的应用中,还可以具有这样的特征:其中,降解液中,苯酚的含量为0.2g/L,过硫酸盐的含量为0.2g/L,锰氮共掺杂碳纳米片的添加量为0.2g/L。In the application of the manganese nitrogen co-doped carbon nanosheets provided by the present invention in the activation of persulfate to degrade phenol, it can also have such characteristics: wherein, in the degradation solution, the content of phenol is 0.2g/L, and the persulfate The content of 0.2g/L, the addition of manganese nitrogen co-doped carbon nanosheets is 0.2g/L.
发明的作用与效果Function and Effect of Invention
根据本发明提供的一种锰氮共掺杂碳纳米片、制备方法及其应用,该方法通过冷冻干燥和碳化过程的两步合成过程,将过渡金属锰成功地锚定在掺杂N的多孔碳上。该材料以三聚氰胺为氮源,葡萄糖为碳源,氯化锰为金属前驱体,一步碳化形成。三聚氰胺在热解过程中形成g-C3N4,葡萄糖生成的初级碳中间体通过供体-受体相互作用与层状g-C3N4结合,g-C3N4作为模板引导碳层沿平面形成碳纳米片结构;其次,三聚氰胺提供丰富的氮原子环境,捕获过渡金属锰,形成高度分散的Mn-Nx配位键,将氮物种固定在碳纳米片上,提供多种活性氮组分。According to a manganese nitrogen co-doped carbon nanosheet, preparation method and application thereof provided by the present invention, the method successfully anchors the transition metal manganese in the N-doped porous through the two-step synthesis process of freeze-drying and carbonization process. on carbon. The material uses melamine as a nitrogen source, glucose as a carbon source, and manganese chloride as a metal precursor, and is formed by one-step carbonization. Melamine forms gC3N4 during pyrolysis, and the primary carbon intermediate produced by glucose binds to layered gC3N4 through donor-acceptor interactions, and gC3N4 acts as a template to guide the carbon layer along the plane to form carbon nanoparticles Secondly, melamine provides a rich nitrogen atom environment, captures the transition metal manganese, forms highly dispersed Mn-Nx coordination bonds, fixes nitrogen species on carbon nanosheets, and provides a variety of active nitrogen components.
本发明以葡萄糖作为碳底物固定氮原子,以防止在高温加热过程中氮原子的损失率过高,有助于在碳基材料中形成了Mn-Nx配位键的高密度和均匀分布。随着温度升高,g-C3N4进一步热解产生大量含氮气体,导致碳纳米片卷曲出现介孔碳骨架结构,不仅有效避免了碳层的重叠,而且增加了氮位点固定在碳骨架上的可能性。过渡金属和氮共掺杂的碳基材料可以有效调节原始碳材料的电子结构,提高催化活性;此外掺杂的过渡金属以M-Nx配位键的形式存在于材料内部,被外层的碳壳所保护使得金属浸出的浓度减少,有效提高碳基材料在催化反应中的耐久性。The invention uses glucose as a carbon substrate to fix nitrogen atoms to prevent excessive loss of nitrogen atoms during high-temperature heating, and contributes to the formation of high density and uniform distribution of Mn-Nx coordination bonds in carbon-based materials. As the temperature increases, gC 3 N 4 is further pyrolyzed to produce a large amount of nitrogen-containing gas, which leads to the curling of carbon nanosheets and the mesoporous carbon skeleton structure, which not only effectively avoids the overlapping of carbon layers, but also increases the number of nitrogen sites fixed on the carbon skeleton. on possibility. Carbon-based materials co-doped with transition metals and nitrogen can effectively adjust the electronic structure of the original carbon materials and improve the catalytic activity; in addition, the doped transition metals exist in the interior of the material in the form of M-Nx coordination bonds, and the outer layer of carbon The protection of the shell reduces the concentration of metal leaching, effectively improving the durability of carbon-based materials in catalytic reactions.
因此本发明通过锰氮共掺杂工程改性了碳基材料,提高催化剂降解有机污染物苯酚的速率且具有良好的循环性,降低了金属浸出浓度,不会对环境造成二次污染。Therefore, the present invention modifies the carbon-based material through manganese-nitrogen co-doping engineering, improves the rate of catalyst degradation of organic pollutant phenol and has good circulation, reduces metal leaching concentration, and does not cause secondary pollution to the environment.
附图说明Description of drawings
图1是本发明中实施例1的锰氮共掺杂碳纳米片扫描电镜示意图;Fig. 1 is the scanning electron microscope schematic diagram of the manganese nitrogen co-doped carbon nanosheet of
图2是本发明中实施例1的锰氮共掺杂碳纳米片的透射电镜示意图;Fig. 2 is the transmission electron microscope schematic diagram of the manganese nitrogen co-doped carbon nanosheet of
图3是本发明中的不同种类催化剂对苯酚去除效果的影响;Fig. 3 is the impact of different types of catalysts on the phenol removal effect among the present invention;
图4是本发明中的不同催化剂投加量对苯酚去除效果的影响;Fig. 4 is the impact of different catalyst dosages on the phenol removal effect among the present invention;
图5是本发明中的锰氮共掺杂碳纳米片的重复利用效果图。Fig. 5 is an effect diagram of the repeated utilization of manganese and nitrogen co-doped carbon nanosheets in the present invention.
具体实施方式Detailed ways
为了使本发明实现的技术手段、创作特征、达成目的与功效易于明白了解,以下结合实施例及附图对本发明一种锰氮共掺杂碳纳米片、制备方法及应用作具体阐述。In order to make the technical means, creative features, goals and effects of the present invention easy to understand, a manganese-nitrogen co-doped carbon nanosheet, preparation method and application of the present invention will be described in detail below in conjunction with the examples and accompanying drawings.
如无特殊说明,以下实施例中所用到的各原料均为市售产品,所用到的各设备均为市售常规设备。Unless otherwise specified, all raw materials used in the following examples are commercially available products, and all equipment used are commercially available conventional equipment.
过硫酸盐为过一硫酸氢钾。The persulfate is potassium hydrogen persulfate.
本发明提供的锰氮共掺杂碳纳米片的制备方法,具体包括以下步骤:The preparation method of the manganese nitrogen co-doped carbon nanosheet provided by the present invention specifically comprises the following steps:
步骤1,将一定量的氯化锰四水合物及氯化锌溶于超纯水溶液中,混合均匀得到A液;
步骤2,将一定量的三聚氰胺及葡萄糖溶于超纯水溶液中,混合均匀得到B液;
步骤3,将A液缓慢滴加入B液中,滴加过程中持续搅拌,滴加完毕后继续搅拌4h,得到乳白色沉淀;Step 3: Slowly add liquid A to liquid B dropwise, continuously stir during the dropwise addition, and continue to stir for 4 hours after the dropwise addition is completed, to obtain a milky white precipitate;
步骤4,将乳白色沉淀缓慢滴入液氮中急速冷冻,得到冷冻产物;
步骤5,将冷冻产物放入冷冻干燥器中在-45℃~-55℃条件下冷冻干燥,研磨真空干燥得到白色粉末;
步骤6,将白色粉末在氮气气氛下高温煅烧,得到煅烧产物,研磨并酸浸,干燥得到锰氮共掺杂碳纳米片。Step 6, calcining the white powder at high temperature under a nitrogen atmosphere to obtain a calcined product, grinding, acid leaching, and drying to obtain manganese-nitrogen co-doped carbon nanosheets.
上述步骤1中,氯化锰四水合物质量为0.197g~0.394g,氯化锌质量为0.136g,超纯水体积为5ml。步骤2中,三聚氰胺质量为5g,葡萄糖质量为2g,超纯水体积为25ml。步骤4中,将静置后的白色沉淀以每秒一滴的速度滴入液氮中进行急速冷冻。In the
步骤6中,将白色粉末在氮气气氛下以4℃~6℃的升温速率升温至800℃~900℃高温煅烧,得到黑色煅烧产物,将所获得的煅烧产物研磨并在0.5M硫酸中洗涤10h,再进一步用去离子水清洗2~4次,洗涤干燥得到锰氮共掺杂碳纳米片。In step 6, the white powder is calcined at a high temperature of 800°C to 900°C under a nitrogen atmosphere at a heating rate of 4°C to 6°C to obtain a black calcined product, which is ground and washed in 0.5M sulfuric acid for 10 hours , and further washed with deionized water for 2 to 4 times, washed and dried to obtain manganese nitrogen co-doped carbon nanosheets.
依照上述制备方法制备得到的锰氮共掺杂碳纳米片作为催化剂,活化过硫酸盐用来降解苯酚,降解苯酚的具体过程为:Manganese nitrogen co-doped carbon nanosheets prepared according to the above preparation method are used as catalysts to activate persulfate to degrade phenol. The specific process of degrading phenol is as follows:
步骤S1,配置含有苯酚、锰氮共掺杂碳纳米片及过硫酸盐的降解液,然后在恒温条件下进行降解;Step S1, configuring a degradation solution containing phenol, manganese nitrogen co-doped carbon nanosheets and persulfate, and then performing degradation under constant temperature conditions;
步骤S2,在给定的时间内,取0.9mL样品,通过0.22μm膜过滤器过滤,然后用0.1ml甲醇溶液在玻璃瓶中淬灭,过滤后采用高效液相色谱法进行分析,得到对应时间的污染物浓度,5分钟后结束降解。Step S2, within a given time, take 0.9mL sample, filter it through a 0.22μm membrane filter, then quench it with 0.1ml methanol solution in a glass bottle, analyze it by high performance liquid chromatography after filtration, and obtain the corresponding time Concentration of pollutants, the degradation ends after 5 minutes.
上述降解实验中,降解液中苯酚浓度为0.2g/L,过硫酸盐浓度为0.2g/L,催化剂的添加量为0.2g/L,pH值为7.0,室温条件下进行。降解液中加入磷酸氢钠缓冲溶液,稳定溶液pH值为7。In the above degradation experiment, the concentration of phenol in the degradation solution was 0.2g/L, the concentration of persulfate was 0.2g/L, the amount of catalyst added was 0.2g/L, the pH value was 7.0, and it was carried out at room temperature. Sodium hydrogen phosphate buffer solution was added to the degradation solution, and the pH value of the stable solution was 7.
<实施例1><Example 1>
本实施例制备一种锰氮共掺杂碳纳米片,氯化锰四水合物、氯化锌、三聚氰胺、葡萄糖的质量分别为0.197g、0.136g、5g、2g,具体操作为:In this example, a manganese nitrogen co-doped carbon nanosheet is prepared. The masses of manganese chloride tetrahydrate, zinc chloride, melamine, and glucose are respectively 0.197g, 0.136g, 5g, and 2g. The specific operations are as follows:
步骤1,将0.197g氯化锰四水合物及0.136g氯化锌溶于5ml超纯水溶液中,混合均匀得到A液;
步骤2,将5g三聚氰胺及2g葡萄糖溶于25ml超纯水溶液中,混合均匀得到B液;
步骤3,将A液缓慢滴加入B液中,滴加过程中持续搅拌,滴加完毕后继续搅拌一段时间,搅拌时间为4h,得到乳白色沉淀;
步骤4,将乳白色沉淀缓慢滴入液氮中急速冷冻,以每秒一滴的速度滴入液氮中进行急速冷冻,得到冷冻产物;
步骤5,将冷冻产物放入冷冻干燥器中在-45℃~-55℃条件下冷冻干燥,研磨真空干燥得到白色粉末;
步骤6,将白色粉末在氮气气氛下以4℃~6℃的升温速率升温至800℃~900℃高温煅烧,得到黑色煅烧产物,研磨并在0.5M硫酸中洗涤10h,再进一步用去离子水清洗2~4次,洗涤干燥得到锰氮共掺杂碳纳米片,标记为Mn-N@C-1。Step 6: Calcining the white powder in a nitrogen atmosphere at a heating rate of 4°C to 6°C to 800°C to 900°C to obtain a black calcined product, which is ground and washed in 0.5M sulfuric acid for 10 hours, and then further washed with
<实施例2><Example 2>
本实施例制备一种锰氮共掺杂碳纳米片,氯化锰四水合物、氯化锌、三聚氰胺、葡萄糖质量分别为0.394g、0.136g、5g、2g,具体操作为:In this example, a manganese-nitrogen co-doped carbon nanosheet is prepared. The masses of manganese chloride tetrahydrate, zinc chloride, melamine, and glucose are 0.394g, 0.136g, 5g, and 2g respectively. The specific operations are as follows:
步骤1,将0.394g氯化锰四水合物及0.136g氯化锌溶于5ml超纯水溶液中,混合均匀得到A液;
步骤2,将5g三聚氰胺及2g葡萄糖溶于25ml超纯水溶液中,混合均匀得到B液;
步骤3,将A液缓慢滴加入B液中,滴加过程中持续搅拌,滴加完毕后继续搅拌一段时间,搅拌时间为4h,得到乳白色沉淀;
步骤4,将乳白色沉淀缓慢滴入液氮中急速冷冻,以每秒一滴的速度滴入液氮中进行急速冷冻,得到冷冻产物;
步骤5,将冷冻产物放入冷冻干燥器中在-45℃~-55℃条件下冷冻干燥,研磨真空干燥得到白色粉末;
步骤6,将白色粉末在氮气气氛下以4℃~6℃的升温速率升温至800℃~900℃高温煅烧,得到黑色煅烧产物,研磨并在0.5M硫酸中洗涤10h,再进一步用去离子水清洗2~4次,洗涤干燥得到锰氮共掺杂碳纳米片,标记为Mn-N@C-2。Step 6: Calcining the white powder in a nitrogen atmosphere at a heating rate of 4°C to 6°C to 800°C to 900°C to obtain a black calcined product, which is ground and washed in 0.5M sulfuric acid for 10 hours, and then further washed with
<对比例1><Comparative example 1>
本对比例制备一种锰氮共掺杂碳纳米片,氯化锰四水合物、氯化锌、三聚氰胺、葡萄糖质量分别为0g、0.136、5g、2g,其余操作与实施例2中相同,得到对比样氮掺杂碳纳米片,标记为N@C。In this comparative example, a manganese-nitrogen co-doped carbon nanosheet is prepared. The masses of manganese chloride tetrahydrate, zinc chloride, melamine, and glucose are respectively 0g, 0.136, 5g, and 2g. The rest of the operations are the same as in Example 2, and the obtained The comparison sample nitrogen-doped carbon nanosheets, marked as N@C.
<对比例2><Comparative example 2>
本对比例制备一种锰氮共掺杂碳纳米片,氯化锰四水合物、氯化锌、三聚氰胺、葡萄糖质量分别为0.197g、0.136、0g、2g,其余操作与实施例2中相同,得到对比样氮掺杂碳纳米片,标记为Mn@C。In this comparative example, a manganese-nitrogen co-doped carbon nanosheet was prepared, and the masses of manganese chloride tetrahydrate, zinc chloride, melamine, and glucose were respectively 0.197g, 0.136, 0g, and 2g, and the rest of the operations were the same as in Example 2. A comparison sample of nitrogen-doped carbon nanosheets was obtained, labeled as Mn@C.
<测试例><test case>
对实施例1制备的锰氮共掺杂碳纳米片进行扫描电镜检测及透射电镜检测,检测结果见图1与图2。Scanning electron microscopy and transmission electron microscopy were performed on the manganese nitrogen co-doped carbon nanosheets prepared in Example 1, and the detection results are shown in FIGS. 1 and 2 .
图1是本发明的实施例1中的锰氮共掺杂碳纳米片的扫描电镜示意图,图2是本发明的实施例1中的锰氮共掺杂碳纳米片的透射电镜示意图。FIG. 1 is a schematic diagram of a scanning electron microscope of manganese nitrogen co-doped carbon nanosheets in Example 1 of the present invention, and FIG. 2 is a schematic diagram of a transmission electron microscope of manganese nitrogen co-doped carbon nanosheets in Example 1 of the present invention.
如图1、2所示,可以看出明显看出,Mn-N@C-1的SEM图和TEM图主要以层状和片状结构为主,且表面出现丰富的褶皱,表明金属锰的成功掺杂,此外层状结构提供了更大的比表面积(98.94m2/g),以及更多的活性位点,提高了材料的催化效果。As shown in Figures 1 and 2, it can be clearly seen that the SEM and TEM images of Mn-N@C-1 are mainly layered and sheet-like structures, and there are abundant wrinkles on the surface, indicating that the metal manganese Successful doping, in addition, the layered structure provides a larger specific surface area (98.94m 2 /g) and more active sites, which improves the catalytic effect of the material.
<应用例1><Application example 1>
将实施例1、2和对比例1、2制备得到的锰氮共掺杂碳纳米片作为催化剂,活化过硫酸盐(PMS)来降解苯酚。该苯酚降解实验的具体实验过程如下:The manganese nitrogen co-doped carbon nanosheets prepared in Examples 1 and 2 and Comparative Examples 1 and 2 were used as catalysts to activate persulfate (PMS) to degrade phenol. The concrete experimental process of this phenol degradation experiment is as follows:
在含有100mL超纯水的250mL烧杯中进行,在室温下进行磁性搅拌。在一个典型的实验中,在100mL苯酚溶液(20mgL-1)中加入20mg催化剂和20mg氧化剂PMS。pH值用磷酸盐缓冲盐水(PBS,20mM)稳定。Carried out in a 250 mL beaker containing 100 mL of ultrapure water with magnetic stirring at room temperature. In a typical experiment, 20 mg catalyst and 20 mg oxidant PMS were added to 100 mL phenol solution (20 mgL −1 ). The pH was stabilized with phosphate buffered saline (PBS, 20 mM).
在给定的时间内每1分钟,取0.9mL样品,通过0.22μm膜过滤器过滤,然后用0.1ml甲醇溶液在玻璃瓶中淬灭,进行高效液相色谱分析(HPLC)。得到对应的污染物浓度,5分钟后停止降解,结束实验,对5分钟内的测定数据进行处理分析,实验结果见图3。Every 1 min for a given time, 0.9 mL samples were taken, filtered through a 0.22 μm membrane filter, and then quenched with 0.1 ml of methanol solution in a glass vial for high-performance liquid chromatography (HPLC). Get the corresponding pollutant concentration, stop the degradation after 5 minutes, end the experiment, and process and analyze the measurement data within 5 minutes. The experimental results are shown in Figure 3.
图3是本发明中的不同种类催化剂对苯酚去除效果的影响。其中,横坐标均表示降解反应时间,单位为min,纵坐标均表示降解比,(即溶液中存在的苯酚浓度/苯酚的初始浓度)单位为%。Fig. 3 is the influence of different types of catalysts on the removal effect of phenol in the present invention. Wherein, the abscissas all represent the degradation reaction time in min, and the ordinates all represent the degradation ratio, (that is, the concentration of phenol present in the solution/the initial concentration of phenol) in %.
从图3可知,加入Mn-N@C-1后,催化性能显著,降解进行地很快,在5min内苯酚的降解率约为100%,降解效果最好。其次是Mn-N@C-2,降解率为70.1%。N@C和Mn@C的降解最慢,5分钟后停止降解时,降解效果分别为46.7%和23.6%。Mn-N@C-1中苯酚降解的增强进一步表明了引入Mn/N共掺杂的重要作用。碳基材料中Mn-Nx键的形成已被证明可以调节碳基材料的电子结构,进一步提高了催化剂活化PMS的性能。It can be seen from Figure 3 that after adding Mn-N@C-1, the catalytic performance is remarkable, and the degradation proceeds very quickly. The degradation rate of phenol is about 100% within 5 minutes, and the degradation effect is the best. It is followed by Mn-N@C-2 with a degradation rate of 70.1%. The degradation of N@C and Mn@C was the slowest, and when the degradation stopped after 5 min, the degradation effects were 46.7% and 23.6%, respectively. The enhanced phenol degradation in Mn-N@C-1 further indicates the important role of introducing Mn/N co-doping. The formation of Mn–Nx bonds in carbon-based materials has been shown to tune the electronic structure of carbon-based materials, further enhancing the performance of catalysts for activating PMS.
<应用例2><Application example 2>
将实施例1制备得到的Mn-N@C-1作为催化剂,对比催化剂不同投加量对于苯酚降解实验的影响,四个平行试验的催化剂投加量分别为5mg、10mg、20mg、30mg。除了催化剂投加量不同外,降解实验过程的其他步骤与应用例1中相同。不同投加量催化剂的降解对比结果见图4。The Mn-N@C-1 prepared in Example 1 was used as a catalyst to compare the effects of different catalyst dosages on the phenol degradation experiment. The catalyst dosages of the four parallel experiments were 5 mg, 10 mg, 20 mg, and 30 mg, respectively. Except that the dosage of the catalyst is different, other steps of the degradation experiment process are the same as those in Application Example 1. The degradation comparison results of catalysts with different dosages are shown in Fig. 4.
图4是本发明中的催化剂不同投加量对苯酚去除效果的影响。其中,横坐标均表示降解反应时间,单位为min,纵坐标均表示降解比,(即溶液中存在的苯酚浓度/苯酚的初始浓度)单位为%。Fig. 4 is the effect of different dosages of catalysts in the present invention on the removal effect of phenol. Wherein, the abscissas all represent the degradation reaction time in min, and the ordinates all represent the degradation ratio, (that is, the concentration of phenol present in the solution/the initial concentration of phenol) in %.
如图4所示,当材料的添加量为0.2g/L时,苯酚的被去除率在5分钟内约为100%,之后随着催化剂Mn-N@C-1投加量的增加,苯酚的被去除率均呈现上升趋势。当投加量为0.3g/L时,苯酚的被去除率几乎达到最大值。表明苯酚降解速率与催化剂的含量成正比。随着催化剂含量的增加,为PMS活化提供了更多活性位点,从而产生丰富的活性氧去除苯酚。As shown in Figure 4, when the amount of material added is 0.2 g/L, the removal rate of phenol is about 100% within 5 minutes, and then with the increase of the amount of catalyst Mn-N@C-1, the removal rate of phenol The removal rate showed an upward trend. When the dosage was 0.3g/L, the removal rate of phenol almost reached the maximum value. It shows that the degradation rate of phenol is directly proportional to the content of catalyst. As the catalyst content increased, more active sites were provided for PMS activation, resulting in abundant active oxygen for phenol removal.
<应用例3><Application example 3>
本应用例为实施例1中的锰氮共掺杂碳纳米片的循环性能实验,将作为实施例1中的锰氮共掺杂碳纳米片Mn-N@C-1作为催化剂,进行5次循环实验。实验中所用装置及测试仪器与应用例1相同,时间过程除物质的添加量与取样时间外,其余没有叙述部分与应用例1相同。This application example is the cycle performance experiment of the manganese-nitrogen co-doped carbon nanosheets in Example 1, using the manganese-nitrogen co-doped carbon nanosheets Mn-N@C-1 as the catalyst in Example 1, and carried out 5 times Loop experiment. The devices and testing instruments used in the experiment are the same as those in Application Example 1, and the time course is the same as Application Example 1 except for the amount of substances added and the sampling time.
实验过程具体如下:The experimental process is as follows:
在25℃条件下用实施例1做出的材料50mg,过硫酸盐20mg,加入到100ml浓度为20mg/l的苯酚溶液中形成降解液,5分钟内每隔1分钟,取0.9mL样品,通过0.22μm膜过滤器过滤,然后用0.1ml甲醇溶液在玻璃瓶中淬灭,进行高效液相色谱分析(HPLC)。5分钟后通过抽滤装置抽滤、洗涤、在60℃真空干燥箱中干燥12小时,回收催化剂。第二次循环,将干燥完全的样品重新以第一次循环的实验条件进行,循环往复,直到第五次循环结束。结果见图5。At 25°C, use 50 mg of the material made in Example 1, 20 mg of persulfate, and add it to 100 ml of phenol solution with a concentration of 20 mg/l to form a degradation solution. Take 0.9 mL of sample every 1 minute within 5 minutes, and pass Filter through a 0.22 μm membrane filter, then quench with 0.1 ml of methanol solution in a glass vial, and perform high-performance liquid chromatography (HPLC). After 5 minutes, the catalyst was filtered through a suction filtration device, washed, and dried in a vacuum oven at 60° C. for 12 hours to recover the catalyst. In the second cycle, the completely dried samples were re-run under the experimental conditions of the first cycle, and the cycle was repeated until the fifth cycle ended. The results are shown in Figure 5.
图5是本发明的应用例3中的循环降解效果图。Fig. 5 is a cycle degradation effect diagram in application example 3 of the present invention.
由图5可知,经过5次循环实验,实施例1制备的锰氮共掺杂碳纳米片仍然具有良好的催化降解性能,五分钟内降解效果分别为100%、99.5%、99.0%、95.4%、89.5%,说明Mn-N@C-1具有良好的循环性。It can be seen from Figure 5 that after 5 cycles of experiments, the manganese-nitrogen co-doped carbon nanosheets prepared in Example 1 still have good catalytic degradation performance, and the degradation effects within five minutes are 100%, 99.5%, 99.0%, and 95.4%, respectively. , 89.5%, indicating that Mn-N@C-1 has a good cycle.
实施例的作用与效果Function and effect of embodiment
根据本发明的实施例所提供的一种锰氮共掺杂碳纳米片、制备方法及应用,该方法通过冷冻干燥和碳化过程的两步合成过程,将过渡金属锰成功地锚定在掺杂N的多孔碳上。该材料以三聚氰胺为氮源,葡萄糖为碳源,氯化锰为金属前驱体,一步碳化形成。三聚氰胺在热解过程中形成了g-C3N4,葡萄糖生成的初级碳中间体通过供体-受体相互作用与层状g-C3N4结合,g-C3N4作为模板引导碳层沿平面形成碳纳米片结构;其次,三聚氰胺提供丰富的氮原子环境,捕获过渡金属锰,形成高度分散的Mn-Nx配位键,将氮物种固定在碳纳米片上,提供多种活性氮组分。A manganese-nitrogen co-doped carbon nanosheet, preparation method and application provided according to the embodiments of the present invention, the method successfully anchors the transition metal manganese in the doped N on porous carbon. The material uses melamine as a nitrogen source, glucose as a carbon source, and manganese chloride as a metal precursor, and is formed by one-step carbonization. Melamine forms gC3N4 during pyrolysis, and the primary carbon intermediate produced by glucose binds to layered gC3N4 through donor-acceptor interactions, and gC3N4 acts as a template to guide the carbon layer along the plane to form carbon Nanosheet structure; secondly, melamine provides a rich nitrogen atom environment, captures transition metal manganese, forms highly dispersed Mn-Nx coordination bonds, immobilizes nitrogen species on carbon nanosheets, and provides a variety of active nitrogen components.
该方法以葡萄糖作为碳底物固定氮原子,以防止在高温加热过程中氮原子的损失率过高,有助于在碳基材料中形成了Mn-Nx配位键的高密度和均匀分布。随着温度升高,g-C3N4进一步热解产生大量含氮气体,导致碳纳米片卷曲出现介孔碳骨架结构,不仅有效避免了碳层的重叠,而且增加了氮位点固定在碳骨架上的可能性。This method uses glucose as a carbon substrate to fix nitrogen atoms to prevent the loss rate of nitrogen atoms from being too high during high-temperature heating, which contributes to the formation of high density and uniform distribution of Mn-Nx coordination bonds in carbon-based materials. As the temperature increases, gC 3 N 4 is further pyrolyzed to produce a large amount of nitrogen-containing gas, which leads to the curling of carbon nanosheets and the mesoporous carbon skeleton structure, which not only effectively avoids the overlapping of carbon layers, but also increases the number of nitrogen sites fixed on the carbon skeleton. on possibility.
过渡金属和氮共掺杂的碳基材料可以有效调节原始碳材料的电子结构,提高催化活性;此外掺杂的过渡金属以M-Nx配位键的形式存在于材料内部,被外层的碳壳所保护使得金属浸出的浓度减少,有效提高碳基材料在催化反应中的耐久性。Carbon-based materials co-doped with transition metals and nitrogen can effectively adjust the electronic structure of the original carbon materials and improve the catalytic activity; in addition, the doped transition metals exist in the material in the form of M-Nx coordination bonds, and the outer layer of carbon The protection of the shell reduces the concentration of metal leaching, effectively improving the durability of carbon-based materials in catalytic reactions.
因此本发明的实施例通过锰氮共掺杂改性的碳基材料,提高了催化剂降解有机污染物苯酚速率且具有良好的循环性,降低了金属浸出浓度,不会对环境造成二次污染。例如,应用例1中,降解进行5min时,降解比即达到了约100%;应用例2中,不同投加量的锰氮共掺杂碳纳米片的降解效果依然优异;应用例3中,循环使用5次,仍能达到较好的催化效果。Therefore, the embodiment of the present invention uses manganese-nitrogen co-doped modified carbon-based materials to increase the rate of catalyst degradation of organic pollutant phenol and has good circulation, reduces metal leaching concentration, and will not cause secondary pollution to the environment. For example, in application example 1, when the degradation is performed for 5 minutes, the degradation ratio reaches about 100%; in application example 2, the degradation effect of manganese-nitrogen co-doped carbon nanosheets with different dosages is still excellent; in application example 3, It can still achieve a good catalytic effect after being recycled 5 times.
上述实施方式为本发明的优选案例,并不用来限制本发明的保护范围。凡是利用本发明说明书所作的等效结构或等效流程变换,或直接或间接运用在其他相关的技术领均同理包括在本发明的专利保护范围内。The above embodiments are preferred examples of the present invention, and are not intended to limit the protection scope of the present invention. Any equivalent structure or equivalent process conversion made by using the description of the present invention, or direct or indirect application in other related technical fields are also included in the scope of patent protection of the present invention.
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CN119318731A (en) * | 2024-10-25 | 2025-01-17 | 深地科学与工程云龙湖实验室 | Sprayable hydrogel for healing bacterial infection wound and preparation method thereof |
CN119318731B (en) * | 2024-10-25 | 2025-04-01 | 深地科学与工程云龙湖实验室 | A sprayable hydrogel for healing bacterial infection wounds and preparation method thereof |
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