CN115957793A - A kind of biochar-based catalyst and its synthesis method and application - Google Patents
A kind of biochar-based catalyst and its synthesis method and application Download PDFInfo
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Abstract
Description
技术领域technical field
本发明涉及大气污染控制技术领域,具体为一种生物炭基催化剂及其合成方法和应用。The invention relates to the technical field of air pollution control, in particular to a biochar-based catalyst and its synthesis method and application.
背景技术Background technique
羰基硫(COS)和二硫化碳(CS2)广泛存在于大气环境中,并且COS是对流层和平流层底的主要含硫气体,它们的来源可分为自然源和人为源。COS和CS2在工业生产和使用过程中排放到大气环境,会对环境和人体造成严重的污染和危害。在大气中,CS2也可以被催化氧化成COS。工业生产中微量的COS和CS2对催化剂有毒害作用,使其催化效果和使用寿命受到严重的影响。由于COS和CS2会通过缓慢的水解反应生成硫化氢(H2S),腐蚀生产设备,不仅给工业生产带来了很大的经济损失,而且增加了设备投资和产品成本。同时COS和CS2的吸入对人类身体健康存在较大的危害。黄磷尾气中COS和CS2是共存的典型有机硫气体,黄磷尾气的净化及资源化利用前提必须同时脱除COS和CS2。Carbonyl sulfide (COS) and carbon disulfide (CS2) widely exist in the atmosphere, and COS is the main sulfur-containing gas in the troposphere and bottom stratosphere. Their sources can be divided into natural sources and anthropogenic sources. COS and CS2 are discharged into the atmosphere during industrial production and use, which will cause serious pollution and harm to the environment and the human body. In the atmosphere, CS2 can also be catalytically oxidized to COS. Trace amounts of COS and CS2 in industrial production have a poisonous effect on the catalyst, which seriously affects its catalytic effect and service life. Because COS and CS2 will generate hydrogen sulfide (H2S) through slow hydrolysis reaction, which will corrode production equipment, which not only brings great economic losses to industrial production, but also increases equipment investment and product costs. At the same time, the inhalation of COS and CS2 has great harm to human health. COS and CS2 in yellow phosphorus tail gas are typical organic sulfur gases that coexist. The premise of purification and resource utilization of yellow phosphorus tail gas must be to remove COS and CS2 at the same time.
本发明提供了一种生物炭基催化剂及其合成方法和应用,其中用的生物炭基催化剂的原料采用秸秆进行碳化,并且采用盐酸洗涤对VOCs进行吸附与处理利用,不产生有害污染物,既能解决生物质废弃物的处置问题,也能有效防治大气污染。The invention provides a biochar-based catalyst and its synthesis method and application, wherein the raw material of the biochar-based catalyst is carbonized with straw, and the VOCs are adsorbed, treated and utilized by washing with hydrochloric acid, and no harmful pollutants are produced. It can solve the disposal problem of biomass waste and effectively prevent and control air pollution.
发明内容Contents of the invention
针对现有技术的不足,本发明提供了一种生物炭基催化剂及其合成方法和应用,解决了采用秸秆进行碳化,并且采用盐酸洗涤对VOCs进行吸附与处理利用,不产生有害污染物,既能解决生物质废弃物的处置问题,也能有效防治大气污染的问题。Aiming at the deficiencies of the prior art, the present invention provides a biochar-based catalyst and its synthesis method and application, which solves the problem of using straw for carbonization, and adopting hydrochloric acid washing for adsorption and treatment of VOCs, without producing harmful pollutants, both It can solve the disposal problem of biomass waste and effectively prevent and control the problem of air pollution.
为实现以上目的,本发明通过以下技术方案予以实现:一种生物炭基催化剂及其合成方法和应用,包括生物炭,所述生物炭基氧化还原反应催化剂的比表面积为360m/g~800m/g。In order to achieve the above object, the present invention is achieved through the following technical solutions: a biochar-based catalyst and its synthesis method and application, including biochar, the specific surface area of the biochar-based redox reaction catalyst is 360m/g~800m/g g.
优选的,一种生物炭基催化剂的合成方法,包括以下步骤;Preferably, a synthetic method of a biochar-based catalyst, comprising the following steps;
步骤一、首先对小麦秸秆进行酸洗预处理:将小麦秸秆先用一定量浓度的硝酸溶液处理,再用去离子水清洗,得到酸洗预处理的小麦秸秆;Step 1. First, carry out pickling pretreatment on the wheat straw: first treat the wheat straw with a certain concentration of nitric acid solution, and then wash it with deionized water to obtain the pickling pretreated wheat straw;
步骤二、将小麦秸秆粉碎至粒径为40-200目得到小麦秸秆粉,再用温度为600-800℃、氮气氛围条件下,将步骤一所得小麦秸秆粉焙烧1—3h得到碳粉;Step 2, crushing the wheat straw to a particle size of 40-200 mesh to obtain wheat straw powder, and then roasting the wheat straw powder obtained in step 1 for 1-3 hours at a temperature of 600-800° C. under a nitrogen atmosphere to obtain carbon powder;
步骤三、进一步地加入生物炭与氯化亚砜、二甲基甲酰胺混合均匀,然后在温度为40-90℃、超声条件下浸渍反应1—3h,采用无水四氢呋喃洗涤,真空过滤即得甲酰氯茶梗基生物炭吸附催化剂。Step 3: Add biochar, thionyl chloride, and dimethylformamide to mix evenly, then impregnate at a temperature of 40-90°C under ultrasonic conditions for 1-3 hours, wash with anhydrous tetrahydrofuran, and vacuum filter to obtain Formyl chloride tea stem-based biochar adsorption catalyst.
优选的,所述步骤一包括以下步骤,将清洗完成的秸秆进行105℃干燥12小时,再通过研磨机粉碎后过40-200目筛;得到的1000g秸秆粉在600℃管式炉中热解3小时,升温速率5℃/min;残留物先用0.1mol/L盐酸洗涤,再取适量去离子水水洗三次至中性,产物于105℃下干燥12小时后取出备用。Preferably, the first step includes the steps of drying the cleaned straw at 105°C for 12 hours, crushing it through a grinder and passing it through a 40-200 mesh sieve; pyrolyzing the obtained 1000g straw powder in a tube furnace at 600°C For 3 hours, the heating rate was 5°C/min; the residue was first washed with 0.1mol/L hydrochloric acid, and then washed three times with appropriate amount of deionized water until neutral. The product was dried at 105°C for 12 hours and then taken out for use.
优选的,所述步骤二还包括以下步骤,将步骤二所得碳粉、炭和盐混合物加入到硝酸溶液中混合均匀,在温度为80℃条件下反应2h,过滤、洗涤、干燥即得生物炭。Preferably, the step 2 further includes the steps of adding the mixture of carbon powder, charcoal and salt obtained in step 2 into the nitric acid solution and mixing evenly, reacting at a temperature of 80°C for 2 hours, filtering, washing, and drying to obtain biochar .
优选的,所述步骤二还包括以下步骤,炭化中所用到的秸秆来源于小麦、水稻、玉米、薯类、油菜、棉花、甘蔗中的至少一种。Preferably, the second step further includes the step that the straw used in the carbonization is derived from at least one of wheat, rice, corn, potato, rapeseed, cotton, and sugar cane.
优选的,所述炭、盐混合物在惰性气体氛围下进行升温,经高温掺杂处理后停止加热,冷却至室温,并依次进行酸洗、水洗和干燥,得到氮、磷共掺杂的生物炭基氧化还原反应催化剂,高温掺杂处理的温度为700℃~900℃。Preferably, the charcoal and salt mixture are heated up under an inert gas atmosphere, stopped heating after high-temperature doping treatment, cooled to room temperature, and sequentially pickled, washed and dried to obtain biochar co-doped with nitrogen and phosphorus Based on redox reaction catalyst, the temperature of high temperature doping treatment is 700℃~900℃.
优选的,所述惰性气体氛围为氮气氛围或氩气氛围,升温的速率为5℃/min~10℃/min,并且保温时间为6h~10h。Preferably, the inert gas atmosphere is a nitrogen atmosphere or an argon atmosphere, the heating rate is 5°C/min˜10°C/min, and the holding time is 6h˜10h.
优选的,一种生物炭基催化剂的应用,所述生物炭基催化剂主要用于VOCs为处理条件,保持反应器的转鼓转数为0.2~2r/min,pH为6.5~7.5,温度为25~30℃,处理的VOCs的浓度值为350-1000mg/m的应用。Preferably, the application of a biochar-based catalyst, the biochar-based catalyst is mainly used for VOCs as the treatment conditions, the drum rotation speed of the reactor is kept at 0.2-2r/min, the pH is 6.5-7.5, and the temperature is 25 ~30°C, the concentration of VOCs treated is 350-1000mg/m2.
本发明提供了一种生物炭基催化剂及其合成方法和应用。具备以下有益效果:The invention provides a biochar-based catalyst as well as its synthesis method and application. Has the following beneficial effects:
本发明通过高活性生物炭基催化剂具备多元金属的催化特性,炭、盐混合物在惰性气体氧化技术体系,呈现出对VOCs同步去除的高效性能,农业废弃物秸秆为生物炭原料,秸秆盐酸洗涤为还原剂多种金属离子转化为高活性的零价金属催化剂颗粒。In the present invention, the high-activity biochar-based catalyst has the catalytic characteristics of multiple metals, and the mixture of carbon and salt in the inert gas oxidation technology system presents a high-efficiency performance for synchronous removal of VOCs. The agricultural waste straw is the raw material of biochar, and the straw is washed with hydrochloric acid. The reducing agent converts various metal ions into highly active zero-valent metal catalyst particles.
具体实施方式Detailed ways
下面将结合本发明实施例,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 technical solutions in the embodiments of the present invention will be clearly and completely described below in conjunction with the embodiments of the present invention. Apparently, the described embodiments are only some of the embodiments of the present invention, not all of them. 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.
实施例一:Embodiment one:
本发明实施例提供一种生物炭基催化剂及其合成方法和应用,包括生物炭,生物炭基氧化还原反应催化剂的比表面积为700m/g。The embodiment of the present invention provides a biochar-based catalyst and its synthesis method and application, including biochar, and the specific surface area of the biochar-based redox reaction catalyst is 700m/g.
步骤一、首先对小麦秸秆进行酸洗预处理:将小麦秸秆先用一定量浓度的硝酸溶液处理,再用去离子水清洗,得到酸洗预处理的小麦秸秆;Step 1. First, carry out pickling pretreatment on the wheat straw: first treat the wheat straw with a certain concentration of nitric acid solution, and then wash it with deionized water to obtain the pickling pretreated wheat straw;
步骤二、将小麦秸秆粉碎至粒径为50目得到小麦秸秆粉,再用温度为700℃、氮气氛围条件下,将步骤一所得小麦秸秆粉焙烧2h得到碳粉;Step 2, crushing the wheat straw to a particle size of 50 mesh to obtain wheat straw powder, and then roasting the wheat straw powder obtained in Step 1 for 2 hours at a temperature of 700° C. under a nitrogen atmosphere to obtain carbon powder;
步骤三、进一步地加入生物炭与氯化亚砜、二甲基甲酰胺混合均匀,然后在温度为80℃、超声条件下浸渍反应1.5h,采用无水四氢呋喃洗涤,真空过滤即得甲酰氯茶梗基生物炭吸附催化剂,通过高活性生物炭基催化剂具备多元金属的催化特性,炭、盐混合物在惰性气体氧化技术体系,呈现出对VOCs同步去除的高效性能,农业废弃物秸秆为生物炭原料,秸秆盐酸洗涤为还原剂多种金属离子转化为高活性的零价金属催化剂颗粒。Step 3: Add biochar, thionyl chloride, and dimethylformamide to mix evenly, then impregnate and react for 1.5 hours under ultrasonic conditions at a temperature of 80°C, wash with anhydrous tetrahydrofuran, and vacuum filter to obtain formyl chloride tea The stalk-based biochar adsorption catalyst has the catalytic characteristics of multiple metals through the high-activity biochar-based catalyst. The carbon and salt mixture in the inert gas oxidation technology system shows high efficiency for the simultaneous removal of VOCs. The agricultural waste straw is used as a raw material for biochar , the straw was washed with hydrochloric acid as a reducing agent to convert various metal ions into highly active zero-valent metal catalyst particles.
步骤一包括以下步骤,将清洗完成的秸秆进行105℃干燥12小时,再通过研磨机粉碎后过50目筛;得到的1000g秸秆粉在600℃管式炉中热解3小时,升温速率5℃/min;残留物先用0.1mol/L盐酸洗涤,再取适量去离子水水洗三次至中性,产物于105℃下干燥12小时后取出备用。Step 1 includes the following steps: dry the cleaned straw at 105°C for 12 hours, then pass it through a grinder and pass through a 50-mesh sieve; pyrolyze 1000g of the obtained straw powder in a tube furnace at 600°C for 3 hours, with a heating rate of 5°C /min; the residue was first washed with 0.1mol/L hydrochloric acid, and then washed three times with an appropriate amount of deionized water until neutral. The product was dried at 105°C for 12 hours and then taken out for use.
步骤二还包括以下步骤,将步骤二所得碳粉、炭和盐混合物加入到硝酸溶液中混合均匀,在温度为80℃条件下反应1.4h,过滤、洗涤、干燥即得生物炭。The second step also includes the steps of adding the mixture of carbon powder, charcoal and salt obtained in the second step into the nitric acid solution, mixing evenly, reacting at 80° C. for 1.4 hours, filtering, washing and drying to obtain biochar.
步骤二还包括以下步骤,炭化中所用到的秸秆来源于小麦。The second step also includes the following steps, the straw used in the carbonization is derived from wheat.
炭、盐混合物在惰性气体氛围下进行升温,经高温掺杂处理后停止加热,冷却至室温,并依次进行酸洗、水洗和干燥,得到氮、磷共掺杂的生物炭基氧化还原反应催化剂,高温掺杂处理的温度为750℃。The mixture of charcoal and salt is heated up in an inert gas atmosphere, after high-temperature doping treatment, the heating is stopped, cooled to room temperature, and then acid-washed, washed with water and dried in sequence to obtain a nitrogen-phosphorous co-doped biochar-based redox reaction catalyst , the temperature of the high temperature doping treatment is 750°C.
惰性气体氛围为氮气氛围或氩气氛围,升温的速率为7℃/min,并且保温时间为8h。The inert gas atmosphere is a nitrogen atmosphere or an argon atmosphere, the heating rate is 7°C/min, and the holding time is 8h.
生物炭基催化剂主要用于VOCs为处理条件,保持反应器的转鼓转数为1.5r/min,pH为7,温度为25℃,处理的VOCs的浓度值为900mg/m的应用。Biochar-based catalysts are mainly used for VOCs as treatment conditions, keep the drum rotation speed of the reactor at 1.5r/min, pH at 7, temperature at 25°C, and the concentration of VOCs to be treated is 900mg/m3.
实施例二:Embodiment two:
本发明实施例提供一种生物炭基催化剂及其合成方法和应用,包括生物炭,生物炭基氧化还原反应催化剂的比表面积为700m/g。The embodiment of the present invention provides a biochar-based catalyst and its synthesis method and application, including biochar, and the specific surface area of the biochar-based redox reaction catalyst is 700m/g.
步骤一、首先对小麦秸秆进行酸洗预处理:将小麦秸秆先用一定量浓度的硝酸溶液处理,再用去离子水清洗,得到酸洗预处理的小麦秸秆;Step 1. First, carry out pickling pretreatment on the wheat straw: first treat the wheat straw with a certain concentration of nitric acid solution, and then wash it with deionized water to obtain the pickling pretreated wheat straw;
步骤二、将小麦秸秆粉碎至粒径为50目得到小麦秸秆粉,再用温度为700℃、氮气氛围条件下,将步骤一所得小麦秸秆粉焙烧2h得到碳粉;Step 2, crushing the wheat straw to a particle size of 50 mesh to obtain wheat straw powder, and then roasting the wheat straw powder obtained in Step 1 for 2 hours at a temperature of 700° C. under a nitrogen atmosphere to obtain carbon powder;
步骤三、进一步地加入生物炭与氯化亚砜、二甲基甲酰胺混合均匀,然后在温度为90℃、超声条件下浸渍反应1.5h,采用无水四氢呋喃洗涤,真空过滤即得甲酰氯茶梗基生物炭吸附催化剂,通过高活性生物炭基催化剂具备多元金属的催化特性,炭、盐混合物在惰性气体氧化技术体系,呈现出对VOCs同步去除的高效性能,农业废弃物秸秆为生物炭原料,秸秆盐酸洗涤为还原剂多种金属离子转化为高活性的零价金属催化剂颗粒。Step 3, further add biochar, thionyl chloride, and dimethylformamide and mix evenly, then impregnate and react for 1.5 hours under ultrasonic conditions at a temperature of 90°C, wash with anhydrous tetrahydrofuran, and vacuum filter to obtain formyl chloride tea The stalk-based biochar adsorption catalyst has the catalytic characteristics of multiple metals through the high-activity biochar-based catalyst. The carbon and salt mixture in the inert gas oxidation technology system shows high efficiency for the simultaneous removal of VOCs. The agricultural waste straw is used as a raw material for biochar , the straw was washed with hydrochloric acid as a reducing agent to convert various metal ions into highly active zero-valent metal catalyst particles.
步骤一包括以下步骤,将清洗完成的秸秆进行105℃干燥12小时,再通过研磨机粉碎后过50目筛;得到的1000g秸秆粉在600℃管式炉中热解3小时,升温速率5℃/min;残留物先用0.1mol/L盐酸洗涤,再取适量去离子水水洗三次至中性,产物于105℃下干燥12小时后取出备用。Step 1 includes the following steps: dry the cleaned straw at 105°C for 12 hours, then pass it through a grinder and pass through a 50-mesh sieve; pyrolyze 1000g of the obtained straw powder in a tube furnace at 600°C for 3 hours, with a heating rate of 5°C /min; the residue was first washed with 0.1mol/L hydrochloric acid, and then washed three times with an appropriate amount of deionized water until neutral. The product was dried at 105°C for 12 hours and then taken out for use.
步骤二还包括以下步骤,将步骤二所得碳粉、炭和盐混合物加入到硝酸溶液中混合均匀,在温度为100℃条件下反应2h,过滤、洗涤、干燥即得生物炭。The second step also includes the steps of adding the carbon powder, charcoal and salt mixture obtained in the second step into the nitric acid solution and mixing evenly, reacting at a temperature of 100° C. for 2 hours, filtering, washing and drying to obtain biochar.
步骤二还包括以下步骤,炭化中所用到的秸秆来源于小麦。The second step also includes the following steps, the straw used in the carbonization is derived from wheat.
炭、盐混合物在惰性气体氛围下进行升温,经高温掺杂处理后停止加热,冷却至室温,并依次进行酸洗、水洗和干燥,得到氮、磷共掺杂的生物炭基氧化还原反应催化剂,高温掺杂处理的温度为1000℃。The mixture of charcoal and salt is heated up in an inert gas atmosphere, after high-temperature doping treatment, the heating is stopped, cooled to room temperature, and then acid-washed, washed with water and dried in sequence to obtain a nitrogen-phosphorous co-doped biochar-based redox reaction catalyst , the temperature of the high-temperature doping treatment is 1000°C.
惰性气体氛围为氮气氛围或氩气氛围,升温的速率为7℃/min,并且保温时间为8h。The inert gas atmosphere is a nitrogen atmosphere or an argon atmosphere, the heating rate is 7°C/min, and the holding time is 8h.
生物炭基催化剂主要用于VOCs为处理条件,保持反应器的转鼓转数为1.5r/min,pH为7,温度为25℃,处理的VOCs的浓度值为900mg/m的应用。Biochar-based catalysts are mainly used for VOCs as treatment conditions, keep the drum rotation speed of the reactor at 1.5r/min, pH at 7, temperature at 25°C, and the concentration of VOCs to be treated is 900mg/m3.
实施例三:Embodiment three:
本发明实施例提供一种生物炭基催化剂及其合成方法和应用,包括生物炭,生物炭基氧化还原反应催化剂的比表面积为700m/g。The embodiment of the present invention provides a biochar-based catalyst and its synthesis method and application, including biochar, and the specific surface area of the biochar-based redox reaction catalyst is 700m/g.
步骤一、首先对小麦秸秆进行酸洗预处理:将小麦秸秆先用一定量浓度的硝酸溶液处理,再用去离子水清洗,得到酸洗预处理的小麦秸秆;Step 1. First, carry out pickling pretreatment on the wheat straw: first treat the wheat straw with a certain concentration of nitric acid solution, and then wash it with deionized water to obtain the pickling pretreated wheat straw;
步骤二、将小麦秸秆粉碎至粒径为50目得到小麦秸秆粉,再用温度为700℃、氮气氛围条件下,将步骤一所得小麦秸秆粉焙烧4h得到碳粉;Step 2, crushing the wheat straw to a particle size of 50 mesh to obtain wheat straw powder, and then roasting the wheat straw powder obtained in step 1 for 4 hours at a temperature of 700°C under a nitrogen atmosphere to obtain carbon powder;
步骤三、进一步地加入生物炭与氯化亚砜、二甲基甲酰胺混合均匀,然后在温度为80℃、超声条件下浸渍反应5h,采用无水四氢呋喃洗涤,真空过滤即得甲酰氯茶梗基生物炭吸附催化剂,通过高活性生物炭基催化剂具备多元金属的催化特性,炭、盐混合物在惰性气体氧化技术体系,呈现出对VOCs同步去除的高效性能,农业废弃物秸秆为生物炭原料,秸秆盐酸洗涤为还原剂多种金属离子转化为高活性的零价金属催化剂颗粒。Step 3, further adding biochar, thionyl chloride, and dimethylformamide to mix evenly, then immersing and reacting for 5 hours under ultrasonic conditions at a temperature of 80°C, washing with anhydrous tetrahydrofuran, and vacuum filtering to obtain formyl chloride tea stems The biochar-based adsorption catalyst has the catalytic characteristics of multiple metals through the high-activity biochar-based catalyst. The mixture of carbon and salt in the inert gas oxidation technology system presents a high-efficiency performance for the simultaneous removal of VOCs. Agricultural waste straw is the raw material for biochar. Straw hydrochloric acid washing is used as a reducing agent to convert various metal ions into highly active zero-valent metal catalyst particles.
步骤一包括以下步骤,将清洗完成的秸秆进行105℃干燥12小时,再通过研磨机粉碎后过50目筛;得到的1000g秸秆粉在600℃管式炉中热解3小时,升温速率5℃/min;残留物先用0.1mol/L盐酸洗涤,再取适量去离子水水洗三次至中性,产物于105℃下干燥12小时后取出备用。Step 1 includes the following steps: dry the cleaned straw at 105°C for 12 hours, then pass it through a grinder and pass through a 50-mesh sieve; pyrolyze 1000g of the obtained straw powder in a tube furnace at 600°C for 3 hours, with a heating rate of 5°C /min; the residue was first washed with 0.1mol/L hydrochloric acid, and then washed three times with an appropriate amount of deionized water until neutral. The product was dried at 105°C for 12 hours and then taken out for use.
步骤二还包括以下步骤,将步骤二所得碳粉、炭和盐混合物加入到硝酸溶液中混合均匀,在温度为80℃条件下反应6h,过滤、洗涤、干燥即得生物炭。The second step also includes the steps of adding the carbon powder, charcoal and salt mixture obtained in the second step into the nitric acid solution, mixing evenly, reacting at 80° C. for 6 hours, filtering, washing and drying to obtain biochar.
步骤二还包括以下步骤,炭化中所用到的秸秆来源于小麦。The second step also includes the following steps, the straw used in the carbonization is derived from wheat.
炭、盐混合物在惰性气体氛围下进行升温,经高温掺杂处理后停止加热,冷却至室温,并依次进行酸洗、水洗和干燥,得到氮、磷共掺杂的生物炭基氧化还原反应催化剂,高温掺杂处理的温度为750℃。The mixture of charcoal and salt is heated up in an inert gas atmosphere, after high-temperature doping treatment, the heating is stopped, cooled to room temperature, and then acid-washed, washed with water and dried in sequence to obtain a nitrogen-phosphorous co-doped biochar-based redox reaction catalyst , the temperature of the high temperature doping treatment is 750°C.
惰性气体氛围为氮气氛围或氩气氛围,升温的速率为7℃/min,并且保温时间为8h。The inert gas atmosphere is a nitrogen atmosphere or an argon atmosphere, the heating rate is 7°C/min, and the holding time is 8h.
生物炭基催化剂主要用于VOCs为处理条件,保持反应器的转鼓转数为1.5r/min,pH为7,温度为25℃,处理的VOCs的浓度值为900mg/m的应用。Biochar-based catalysts are mainly used for VOCs as treatment conditions, keep the drum rotation speed of the reactor at 1.5r/min, pH at 7, temperature at 25°C, and the concentration of VOCs to be treated is 900mg/m3.
具体参数表1Specific parameter table 1
由此可知本发明中的生物炭基催化剂的吸附效果最好。It can be seen that the adsorption effect of the biochar-based catalyst in the present invention is the best.
尽管已经示出和描述了本发明的实施例,对于本领域的普通技术人员而言,可以理解在不脱离本发明的原理和精神的情况下可以对这些实施例进行多种变化、修改、替换和变型,本发明的范围由所附权利要求及其等同物限定。Although the embodiments of the present invention have been shown and described, those skilled in the art can understand that various changes, modifications and substitutions can be made to these embodiments without departing from the principle and spirit of the present invention. and modifications, the scope of the invention is defined by the appended claims and their equivalents.
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CN110339812A (en) * | 2019-07-09 | 2019-10-18 | 四川大学 | Modified biochar and its application in adsorption of VOCs |
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CN107486237A (en) * | 2017-08-30 | 2017-12-19 | 昆明理工大学 | A kind of formyl chloride tea stalk base charcoal adsorption catalyst and preparation method thereof |
US20200298202A1 (en) * | 2017-12-12 | 2020-09-24 | Jiangsu Academy Of Agricultural Sciences | Preparation Method for Combined Modified Straw Active Particulate Carbon Adsorption Material and Use of Same |
CN109841858A (en) * | 2019-03-27 | 2019-06-04 | 华中科技大学 | The method and product of charcoal base oxygen reduction reaction catalyst are prepared using bean dregs |
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