CN116040752A - Preparation method and application of biochar electrode - Google Patents
Preparation method and application of biochar electrode Download PDFInfo
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Abstract
Description
技术领域technical field
本发明涉及一种电极材料技术领域,具体的是一种石墨化悬铃木果球负载金属的生物炭电极的制备方法及其应用。The invention relates to the technical field of electrode materials, in particular to a preparation method and application of a metal-loaded biochar electrode of graphitized sycamore fruit balls.
背景技术Background technique
硝态氮的去除是未来提高水环境质量的重要环节。世界范围内地下水硝态氮的污染也非常严重。美国许多地区地下水中硝态氮含量平均年增长0.8mg/L,德国农用井水中硝态氮浓度有过半的概率超60mg/L。由此可见,硝态氮的有效去除是我国乃至世界上一个长期且艰巨的环境修复任务。The removal of nitrate nitrogen is an important part of improving the quality of water environment in the future. The pollution of nitrate nitrogen in groundwater is also very serious in the world. The nitrate nitrogen content in groundwater in many areas of the United States has an average annual increase of 0.8mg/L, and the concentration of nitrate nitrogen in German agricultural well water has a probability of exceeding 60mg/L. It can be seen that the effective removal of nitrate nitrogen is a long-term and arduous environmental restoration task in my country and even in the world.
地表水本身具有一定的自我净化和自我修复功能,自己修复一轮周期大概是1400年,依靠自身完成净化修复几乎不可能。目前,国内外许多研究者对硝态氮还原去除技术进行了深入研究,主要可分为物理化学去除法、生物反硝化法及化学还原修复法。Surface water itself has certain self-purification and self-repair functions. The cycle of self-repair is about 1400 years, and it is almost impossible to complete the purification and repair by itself. At present, many researchers at home and abroad have conducted in-depth research on nitrate nitrogen reduction and removal technology, which can be mainly divided into physical and chemical removal methods, biological denitrification methods and chemical reduction repair methods.
现有电化学还原技术中,常常采用粉末状生物炭材料制作电极,这就需要用胶水将粉末材料涂覆到电极片上,一方面成本很高,另一方面这样制成的电极只有表面发生作用,传质效率低,涂覆在电极片上的炭化粉末会发生团聚,影响电极的稳定性,涂覆不能保证均一性,降低硝态氮的去除效率。In the existing electrochemical reduction technology, powdered biochar materials are often used to make electrodes, which requires glue to coat the powdered materials on the electrode sheet. On the one hand, the cost is very high, and on the other hand, the electrode made in this way only works on the surface. , The mass transfer efficiency is low, and the carbonized powder coated on the electrode sheet will agglomerate, which will affect the stability of the electrode. The uniformity of the coating cannot be guaranteed, and the removal efficiency of nitrate nitrogen will be reduced.
本发明属于电化学还原硝态氮的电极材料技术领域,石墨化悬铃木果球生物炭电极有利于提升电极对硝态氮的选择性吸附,同时负载的金属可增强活性物种生成以提高硝态氮的氮气选择性,最终达到高效去除硝态氮的目的。The invention belongs to the technical field of electrode materials for electrochemical reduction of nitrate nitrogen. The graphitized syringa fruit ball biochar electrode is conducive to improving the selective adsorption of the electrode to nitrate nitrogen, and at the same time, the loaded metal can enhance the generation of active species to increase the nitrate nitrogen. Nitrogen selectivity, and finally achieve the purpose of efficient removal of nitrate nitrogen.
发明内容Contents of the invention
为了克服现有技术中的少部分缺陷,本发明提供了石墨化悬铃木果球负载金属的生物炭电极的制备及其应用方法,不但原材料来源广泛,成本低廉,而且简化了工艺,降低了环境污染的风险。In order to overcome a small number of defects in the prior art, the present invention provides the preparation and application method of a metal-loaded biochar electrode from graphitized sycamore fruit balls, which not only has a wide range of raw materials and low cost, but also simplifies the process and reduces environmental pollution. risks of.
本发明涉及的石墨化悬铃木果球负载金属的生物炭电极的制备方法,包括以下步骤:The preparation method of the metal-loaded biochar electrode of the graphitized syringa fruit balls involved in the present invention comprises the following steps:
S1、将清洗干净并烘干的悬铃木果球置入具有聚四氟乙烯内衬和不锈钢外套的高压釜中,同时向高压釜中加入一定浓度的金属盐溶液,使溶液浸没悬铃木果球;S1. Put the cleaned and dried sycamore fruit balls into an autoclave with a polytetrafluoroethylene lining and a stainless steel jacket, and add a certain concentration of metal salt solution to the autoclave at the same time, so that the solution is immersed in the sycamore fruit balls;
S2、将高压釜放入烘箱中在一定温度下保持一定时间,使悬铃木果球炭化,同时将金属负载于水热炭化悬铃木果球表面,通过负载金属,能够增加电极表面上电催化活性位点的数量,增强电极对水中硝态氮的高容量吸附和高选择性去除能力;S2. Put the autoclave in an oven and keep it at a certain temperature for a certain period of time to carbonize the syringa fruit balls. At the same time, load the metal on the surface of the syringa fruit balls for hydrothermal carbonization. By loading the metals, the electrocatalytic active sites on the electrode surface can be increased. The quantity of the electrode can enhance the high-capacity adsorption and high-selectivity removal capacity of nitrate nitrogen in water;
S3、将水热反应后的悬铃木果球在高压釜中自然冷却,随后取出果球,然后用去离子水清洗,清洗结束的果球在80℃真空环境中干燥,得到有金属负载的水热炭化悬铃木果球;S3. Naturally cool the sycamore fruit balls after the hydrothermal reaction in an autoclave, then take out the fruit balls, and then wash them with deionized water. The cleaned fruit balls are dried in a vacuum environment at 80°C to obtain metal-loaded hydrothermal Carbonized sycamore fruit balls;
S4、将有金属负载的水热炭化悬铃木果球浸入一定浓度的高铁酸钾溶液浸泡8h后,转移到管式炉中,并向管式炉通入非氧化性气体,在一定温度下处理一定时间,高铁酸钾作为活化剂和催化剂有利于同步实现炭化悬铃木果球的进一步活化和石墨化;S4. After immersing the hydrothermally carbonized Platanus fruit balls with metal loading in a certain concentration of potassium ferrate solution for 8 hours, transfer them to a tube furnace, and feed a non-oxidizing gas into the tube furnace, and treat them at a certain temperature for a certain period of time. Time, potassium ferrate as an activator and catalyst is conducive to the simultaneous realization of further activation and graphitization of carbonized sycamore fruit balls;
S5、处理结束后,在管式炉中对石墨化果球自然冷却,石墨化后的悬铃木果球质地坚硬且导电性能更好,之后用去离子水对石墨化果球进行清洗至无杂质,在干燥箱内烘干后,得到石墨化悬铃木果球负载金属的生物炭电极。S5, after finishing the treatment, the graphitized fruit balls are naturally cooled in a tube furnace. The graphitized plane tree fruit balls are hard and have better electrical conductivity, and then the graphitized fruit balls are cleaned to no impurities with deionized water. After drying in a drying oven, a metal-loaded biochar electrode of the graphitized Platanus fruit balls was obtained.
进一步地,S2所述烘箱的温度设置为100℃~350℃,水热时间为8h~18h。Further, the temperature of the oven in S2 is set at 100°C-350°C, and the water heating time is 8h-18h.
进一步地,所述金属盐溶液为铜盐溶液或镍盐溶液。Further, the metal salt solution is a copper salt solution or a nickel salt solution.
进一步地,所述金属盐溶液为硫酸盐、硝酸盐、氯化盐中的一种且所述金属盐溶液的浓度在0.5~50mmol/L。Further, the metal salt solution is one of sulfate, nitrate, and chloride salt, and the concentration of the metal salt solution is 0.5˜50 mmol/L.
进一步地,所述高铁酸钾溶液浓度在0.02~0.5mol/LFurther, the concentration of the potassium ferrate solution is 0.02~0.5mol/L
进一步地,所述非氧化性气体为氢气、氩气、氦气、氮气、二氧化碳、一氧化碳中的一种。Further, the non-oxidizing gas is one of hydrogen, argon, helium, nitrogen, carbon dioxide, and carbon monoxide.
进一步地,在所述步骤S5中所述管式炉的温度设置为在600℃~1500℃,复合生物碳材料的恒温处理时间为1.5h~5h。Further, in the step S5, the temperature of the tube furnace is set at 600° C. to 1500° C., and the constant temperature treatment time of the composite biochar material is 1.5 h to 5 h.
一种石墨化悬铃木果球负载金属的生物炭电极,由上述水热法与煅烧法结合制备而成。其中水热法指步骤S1-S3,煅烧法指步骤S4和S5。A metal-loaded biochar electrode of graphitized syringa fruit balls is prepared by combining the above-mentioned hydrothermal method with a calcination method. Wherein the hydrothermal method refers to steps S1-S3, and the calcination method refers to steps S4 and S5.
一种石墨化悬铃木果球负载金属的生物炭电极在硝态氮去除过程中的应用,采用钌铱钛涂层电极作为对电极,尺寸为30mm×30mm×1mm,制备的生物炭电极作为工作电极,以硝酸钠为电解质溶液,对硝酸盐进行降解,降解过程中电压控制在-0.8V~-1.5V。Application of a metal-loaded biochar electrode of graphitized syringa fruit balls in the process of removing nitrate nitrogen. A ruthenium-iridium-titanium-coated electrode is used as a counter electrode with a size of 30mm×30mm×1mm, and the prepared biochar electrode is used as a working electrode , using sodium nitrate as electrolyte solution to degrade nitrate, and the voltage is controlled at -0.8V~-1.5V during the degradation process.
本发明的有益之处在于:利用自然界中存在的天然中空管结构的悬铃木果球制备生物炭电极,经过两步加热使其水热炭化负载金属、石墨化,并将其用于电催化去除水中硝态氮污染物,使之高选择性地转化为氮气。The benefit of the present invention lies in that: the biochar electrode is prepared by using the natural hollow tube structure of the plane tree fruit ball existing in nature, and after two-step heating, it is hydrothermally carbonized and graphitized to support the metal, and it is used for electrocatalytic removal Nitrate nitrogen pollutants in water, so that it is converted into nitrogen gas with high selectivity.
同时,此方法将悬铃木果球投入使用,也可以解决这种植物的成熟果球季节性干扰人们日常生活的问题。At the same time, this method puts the sycamore fruit balls into use, which can also solve the problem that the mature fruit balls of this plant interfere with people's daily life seasonally.
提供了一种利用悬铃木果球制备生物质电极,同时在形成的石墨化生物炭表面负载金属化合物的方法,并将其用于转化水中硝态氮为氮气的电催化过程。Provided is a method for preparing a biomass electrode by using sycamore fruit balls, and simultaneously loading metal compounds on the surface of the formed graphitized biochar, and using it for an electrocatalytic process of converting nitrate nitrogen into nitrogen in water.
相对于现有技术中将悬铃木粉碎成电极的方式,本发明通过利用悬铃木本身的结构(悬铃木果毛质地坚硬,呈节状,每节为中空管状结构,节间端部有褐色环状凸起,具有吸附性能),不仅能够简化电极的制备流程,并且悬铃木作为整体结构便于布置,克服现有技术中电极加工过程繁琐的缺陷。With respect to the mode that plane tree is crushed into electrodes in the prior art, the present invention utilizes the structure of plane tree itself (plane tree fruit hairs are hard and nodal, each joint is a hollow tubular structure, and there are brown ring-shaped protrusions at the end of the joint. , has adsorption performance), not only can simplify the preparation process of the electrode, but also the plane tree as an overall structure is convenient to arrange, and overcomes the cumbersome defect of the electrode processing process in the prior art.
为让本发明的上述和其他目的、特征和优点能更明显易懂,下文特举较佳实施例,并配合所附图式,作详细说明如下。In order to make the above and other objects, features and advantages of the present invention more comprehensible, preferred embodiments will be described in detail below together with the accompanying drawings.
附图说明Description of drawings
为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其他的附图。In order to more clearly illustrate the technical solutions in the embodiments of the present invention or the prior art, the following will briefly introduce the drawings that need to be used in the description of the embodiments or the prior art. Obviously, the accompanying drawings in the following description are only These are some embodiments of the present invention. Those skilled in the art can also obtain other drawings based on these drawings without creative work.
图1是电解池示意图。Figure 1 is a schematic diagram of an electrolytic cell.
图2为实施例1中负载镍的生物炭电极电催化降解水中硝酸盐的实验结果图。FIG. 2 is a graph showing the experimental results of the electrocatalytic degradation of nitrate in water by the nickel-loaded biochar electrode in Example 1. FIG.
图3为实施例2中的负载铜的生物炭电极通过电催化降解水中硝酸盐实验结果图。FIG. 3 is a graph showing the experimental results of the electrocatalytic degradation of nitrate in water by the copper-loaded biochar electrode in Example 2. FIG.
图4为石墨化悬铃木果球负载金属的生物炭电极的制备方法的示意图。Fig. 4 is a schematic diagram of the preparation method of the metal-loaded biochar electrode of graphitized Platanus fruit balls.
具体实施方式Detailed ways
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The following will clearly and completely describe the technical solutions in the embodiments of the present invention with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only some, not all, embodiments of the present invention. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present invention.
实施例1,负载镍生物炭电极的制备方法及通过电催化降解水中硝酸盐的去除效果Example 1, the preparation method of nickel-loaded biochar electrode and the removal effect of nitrate in water by electrocatalytic degradation
在本发明一较佳实施例中的一种石墨化悬铃木果球负载镍金属的生物炭电极的制备方法,包括以下步骤:In a preferred embodiment of the present invention, a method for preparing a biochar electrode of graphitized sycamore fruit balls loaded with nickel metal comprises the following steps:
S1、将清洗干净并烘干的悬铃木果球置入具有聚四氟乙烯内衬和不锈钢外套的高压釜中,同时向高压釜中加入5mmol/L的硫酸镍溶液,使溶液浸没悬铃木果球;S1, put the cleaned and dried syringa fruit balls into an autoclave with a polytetrafluoroethylene lining and a stainless steel jacket, and add 5mmol/L nickel sulfate solution to the autoclave at the same time, so that the solution is immersed in the syringa fruit balls;
S2、将高压釜放入烘箱中在120℃下保持8h,使悬铃木果球炭化,同时将金属镍负载于水热炭化悬铃木果球表面,通过负载金属镍,能够有效增加电极表面上电催化活性位点的数量,增强电极对水中硝态氮的高容量吸附和高选择性去除能力;S2. Put the autoclave in an oven and keep it at 120°C for 8 hours to carbonize the syringa fruit balls. At the same time, metal nickel is loaded on the surface of the syringa fruit balls for hydrothermal carbonization. By loading metal nickel, the electrocatalytic activity on the electrode surface can be effectively increased. The number of sites enhances the electrode's high-capacity adsorption and high-selectivity removal capacity for nitrate nitrogen in water;
S3、将水热反应后的金属镍负载悬铃木果球在高压釜中自然冷却,随后取出果球,然后用去离子水清洗,清洗结束的果球在80℃真空环境中干燥,得到有金属镍负载的水热炭化悬铃木果球;S3. Naturally cool the metal nickel-loaded sycamore fruit balls after the hydrothermal reaction in an autoclave, then take out the fruit balls, and then wash them with deionized water. The cleaned fruit balls are dried in a vacuum environment at 80°C to obtain metal nickel Loaded hydrothermal carbonization of plane tree fruit balls;
S4、将有金属镍负载的水热炭化悬铃木果球浸入0.1mol/L的高铁酸钾溶液浸泡8h后,转移到管式炉中,并向管式炉通入非氧化性气体,在一定温度下处理一定时间,高铁酸钾作为活化剂和催化剂有利于同步实现炭化悬铃木果球的进一步活化和石墨化;S4. After immersing the hydrothermally carbonized Platanus fruit balls loaded with metallic nickel in 0.1mol/L potassium ferrate solution for 8 hours, transfer them to a tube furnace, and feed non-oxidizing gas into the tube furnace, at a certain temperature Under treatment for a certain period of time, potassium ferrate as an activator and catalyst is conducive to the simultaneous realization of further activation and graphitization of carbonized sycamore fruit balls;
S5、处理结束后,在管式炉中石墨化果球自然冷却,之后用去离子水对石墨化果球进行清洗至无杂质,在干燥箱内烘干后,得到石墨化悬铃木果球负载镍的生物炭电极。S5. After the treatment, the graphitized fruit balls are cooled naturally in a tube furnace, and then the graphitized fruit balls are cleaned with deionized water until there are no impurities. After drying in a drying oven, the graphitized Platanus fruit balls are loaded with nickel biochar electrode.
在上述实施例中,所述非氧化性气体为氢气、氩气、氦气、氮气、二氧化碳、一氧化碳中的一种。在实际实施过程中,通入管式炉的气体为氩气,氩气碳的稳定性更好。在其它实施例中,也可以根据成本及获取的难度选择其它非氧化性气体。In the above embodiment, the non-oxidizing gas is one of hydrogen, argon, helium, nitrogen, carbon dioxide, and carbon monoxide. In the actual implementation process, the gas fed into the tube furnace is argon, and the stability of carbon in argon is better. In other embodiments, other non-oxidizing gases may also be selected according to cost and difficulty of obtaining.
一种石墨化悬铃木果球负载金属的生物炭电极,由上述水热法与煅烧法相结合制备方法制备而成。其中水热法指步骤S1-S3,煅烧法指步骤S4和S5。The invention discloses a metal-loaded biochar electrode of graphitized sycamore fruit balls, which is prepared by combining the above-mentioned hydrothermal method and calcination method. Wherein the hydrothermal method refers to steps S1-S3, and the calcination method refers to steps S4 and S5.
一种石墨化悬铃木果球负载金属的生物炭电极在硝酸盐降解过程中的应用,采用钌铱钛涂层电极作为对电极,尺寸为30mm×30mm×1mm,制备的生物炭电极作为工作电极,以硝酸钠为电解质溶液,对硝态氮进行降解,降解过程中电压控制在-1.2V。The application of a metal-loaded biochar electrode of graphitized Platanus fruit balls in the process of nitrate degradation, using a ruthenium iridium titanium coating electrode as the counter electrode, the size is 30mm × 30mm × 1mm, the prepared biochar electrode is used as the working electrode, Sodium nitrate was used as the electrolyte solution to degrade nitrate nitrogen, and the voltage was controlled at -1.2V during the degradation process.
为了验证本发明以石墨化悬铃木果球负载金属的生物炭电极的制备方法制备而成的生物炭电极在硝酸盐降解过程中的应用效果,进行了以下实验:In order to verify the application effect of the biochar electrode prepared in the process of nitrate degradation by the preparation method of the biochar electrode of graphitized sycamore fruit balls loaded with metals in the present invention, the following experiments were carried out:
参照图1,实验器材包括稳压电源、所制备生物炭电极为工作电极、钌铱钛涂层电极为对电极和甘汞电极作为参比电极,电解实验在150mL烧杯中进行。用磁力搅拌器搅拌,以保持电解质溶液均一。Referring to Figure 1, the experimental equipment includes a regulated power supply, the prepared biochar electrode is the working electrode, the ruthenium iridium titanium coating electrode is the counter electrode, and the calomel electrode is the reference electrode. The electrolysis experiment is carried out in a 150mL beaker. Stir with a magnetic stirrer to keep the electrolyte solution homogeneous.
制备完成的负载镍的生物炭电极实验前,将制备的生物炭电极浸泡在100mg/L的硝酸钠5h,排除吸附的影响。在150mL的烧杯中加入100mg/L的硝酸钠溶液100mL,将所制备的负载镍生物炭石墨化电极用作工作电极,钌铱钛涂层电极用作对电极,甘汞电极作为参比电极,电压保持在-1.2V。每间隔一段时间取出1mL溶液对其中的硝态氮、亚硝态氮和铵态氮进行检测,检测结果如图2所示,由图可以明显看出该负载镍生物炭石墨化电极对硝酸根去除可以达到85%以上,其中氮气选择性可达到78.6%,实现了对硝酸盐的去除,并将其转化为N2。Before the experiment on the prepared nickel-loaded biochar electrode, soak the prepared biochar electrode in 100mg/L sodium nitrate for 5h to eliminate the influence of adsorption. Add 100mL of 100mg/L sodium nitrate solution in a 150mL beaker, the prepared nickel-loaded biochar graphitized electrode is used as a working electrode, the ruthenium-iridium-titanium coated electrode is used as a counter electrode, and the calomel electrode is used as a reference electrode. remain at -1.2V. Take out 1mL solution at intervals to detect the nitrate nitrogen, nitrite nitrogen and ammonium nitrogen. The detection results are shown in Figure 2. The removal can reach more than 85%, and the nitrogen selectivity can reach 78.6%, realizing the removal of nitrate and converting it into N 2 .
实施例2:负载铜生物炭电极的制备方法及通过电催化去除水中硝酸盐效果Example 2: Preparation method of copper-loaded biochar electrode and effect of removing nitrate in water by electrocatalysis
实施例2主要步骤与实施例1相同,不同之处在于,所述步骤S1,包括高压釜中加入5mmol/L的硫酸铜。The main steps of Example 2 are the same as those of Example 1, except that the step S1 includes adding 5 mmol/L copper sulfate to the autoclave.
实验前将制备的生物炭电极浸泡在100mg/L的硝酸钠5h,以排除吸附的影响,在150mL的烧杯中加入100mg/L的硝酸钠溶液100mL,将所制备的负载铜生物炭石墨化电极用作工作电极,钌铱钛涂层电极用作对电极,甘汞电极作为参比电极,电压保持在-1.2V。每间隔一段时间取出1mL溶液对其中的硝态氮、亚硝态氮和铵态氮进行检测,实验结果见图3,由图可以明显看出该负载铜生物炭石墨化电极对硝酸根去除可以达到90%以上,其中氮气选择性可达到81.2%。Before the experiment, soak the prepared biochar electrode in 100mg/L sodium nitrate for 5h to eliminate the influence of adsorption, add 100mL of 100mg/L sodium nitrate solution into a 150mL beaker, and prepare the prepared copper-loaded biochar graphitized electrode Used as a working electrode, a ruthenium-iridium-titanium-coated electrode was used as a counter electrode, and a calomel electrode was used as a reference electrode, and the voltage was maintained at -1.2V. Take out 1mL solution at intervals to detect nitrate nitrogen, nitrite nitrogen and ammonium nitrogen. The experimental results are shown in Figure 3. It can be clearly seen from the figure that the copper-loaded biochar graphitized electrode can remove nitrate. Reach more than 90%, and nitrogen selectivity can reach 81.2%.
由图2和图3可以明显看出,采用本发明制备而成的负载镍的生物炭电极和负载铜的生物炭电极,均能实现对硝酸盐的持续有效去除,并且持续时间长,由于本发明利用悬铃木果球本身的结构(悬铃木果毛质地坚硬,呈节状,每节为中空管状结构,节间端部有褐色环状凸起,具有吸附性能),不仅能够简化电极的制备流程,并且悬铃木果球作为整体结构便于布置,克服现有技术中电极加工过程繁琐的缺陷,在保证对硝酸盐的去除效果的同时,能够有效降低去除成本。It can be clearly seen from Figures 2 and 3 that the nickel-loaded biochar electrode and the copper-loaded biochar electrode prepared by the present invention can achieve continuous and effective removal of nitrate, and the duration is long. The invention utilizes the structure of the sycamore fruit ball itself (the sycamore fruit hair is hard and nodular, each section is a hollow tubular structure, and there are brown ring-shaped protrusions at the end of the internode, which has adsorption properties), not only can simplify the preparation process of the electrode, In addition, the planar tree fruit ball is easy to arrange as an overall structure, overcomes the cumbersome defect of the electrode processing process in the prior art, and can effectively reduce the removal cost while ensuring the removal effect on nitrate.
本发明中应用了具体实施例对本发明的原理及实施方式进行了阐述,以上实施例的说明只是用于帮助理解本发明的方法及其核心思想;同时,对于本领域的一般技术人员,依据本发明的思想,在具体实施方式及应用范围上均会有改变之处,综上所述,本说明书内容不应理解为对本发明的限制。In the present invention, specific examples have been applied to explain the principles and implementation methods of the present invention, and the descriptions of the above examples are only used to help understand the method of the present invention and its core idea; meanwhile, for those of ordinary skill in the art, according to this The idea of the invention will have changes in the specific implementation and scope of application. To sum up, the contents of this specification should not be construed as limiting the present invention.
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Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2005277240A (en) * | 2004-03-26 | 2005-10-06 | Toyoda Gosei Co Ltd | Ohmic electrode of silicon-carbide semiconductor, and manufacturing method thereof |
CN105609327A (en) * | 2015-12-19 | 2016-05-25 | 湘潭大学 | Porous active carbon/copper ion super-capacitor preparation method |
CN106040239A (en) * | 2016-05-27 | 2016-10-26 | 同济大学 | Controllable high-dispersion nano simple-substance metal/carbon composite material preparation method and electrical catalytic application thereof |
CN108889300A (en) * | 2018-06-04 | 2018-11-27 | 中国科学院生态环境研究中心 | A kind of preparation method and applications of novel hydro-thermal charcoal carried nanometer bi-metal catalyst |
CN109336225A (en) * | 2018-12-03 | 2019-02-15 | 北京林业大学 | Particle electrode for removing nitrate nitrogen from tail water of sewage treatment plant and preparation method thereof |
CN110270304A (en) * | 2019-05-08 | 2019-09-24 | 深圳市北林苑景观及建筑规划设计院有限公司 | Load Nanometer Copper watermifoil charcoal and its preparation method and application |
CN111266086A (en) * | 2020-01-22 | 2020-06-12 | 青岛农业大学 | A method for producing magnetic biochar from kitchen waste |
CN112520818A (en) * | 2020-11-13 | 2021-03-19 | 华南理工大学 | Preparation method and application of metal electrode for reducing nitrate nitrogen in wastewater |
CN112625712A (en) * | 2020-12-15 | 2021-04-09 | 青岛理工大学 | Process and method for catalyzing hydrothermal carbonization by using metal ions in copper slag |
CN114613611A (en) * | 2022-03-23 | 2022-06-10 | 黄山学院 | Preparation method and application of oxygen-enriched hollow tubular porous carbon |
-
2022
- 2022-10-18 CN CN202211274480.1A patent/CN116040752B/en active Active
Patent Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2005277240A (en) * | 2004-03-26 | 2005-10-06 | Toyoda Gosei Co Ltd | Ohmic electrode of silicon-carbide semiconductor, and manufacturing method thereof |
CN105609327A (en) * | 2015-12-19 | 2016-05-25 | 湘潭大学 | Porous active carbon/copper ion super-capacitor preparation method |
CN106040239A (en) * | 2016-05-27 | 2016-10-26 | 同济大学 | Controllable high-dispersion nano simple-substance metal/carbon composite material preparation method and electrical catalytic application thereof |
CN108889300A (en) * | 2018-06-04 | 2018-11-27 | 中国科学院生态环境研究中心 | A kind of preparation method and applications of novel hydro-thermal charcoal carried nanometer bi-metal catalyst |
CN109336225A (en) * | 2018-12-03 | 2019-02-15 | 北京林业大学 | Particle electrode for removing nitrate nitrogen from tail water of sewage treatment plant and preparation method thereof |
CN110270304A (en) * | 2019-05-08 | 2019-09-24 | 深圳市北林苑景观及建筑规划设计院有限公司 | Load Nanometer Copper watermifoil charcoal and its preparation method and application |
CN111266086A (en) * | 2020-01-22 | 2020-06-12 | 青岛农业大学 | A method for producing magnetic biochar from kitchen waste |
CN112520818A (en) * | 2020-11-13 | 2021-03-19 | 华南理工大学 | Preparation method and application of metal electrode for reducing nitrate nitrogen in wastewater |
CN112625712A (en) * | 2020-12-15 | 2021-04-09 | 青岛理工大学 | Process and method for catalyzing hydrothermal carbonization by using metal ions in copper slag |
CN114613611A (en) * | 2022-03-23 | 2022-06-10 | 黄山学院 | Preparation method and application of oxygen-enriched hollow tubular porous carbon |
Non-Patent Citations (1)
Title |
---|
李进平: "固废综合处置与协同利用实验指导教程", 31 March 2022, 华中科技大学出版社, pages: 224 - 226 * |
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