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CN110548391A - Catalytic oxidation system for treating benzene organic matters by manganese-based catalyst prepared based on waste ternary electrode material - Google Patents

Catalytic oxidation system for treating benzene organic matters by manganese-based catalyst prepared based on waste ternary electrode material Download PDF

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CN110548391A
CN110548391A CN201910643681.6A CN201910643681A CN110548391A CN 110548391 A CN110548391 A CN 110548391A CN 201910643681 A CN201910643681 A CN 201910643681A CN 110548391 A CN110548391 A CN 110548391A
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benzene
catalytic oxidation
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air pump
organic matter
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CN110548391B (en
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郭耀广
张棋超
李思涵
关杰
吴鸿铖
刘志远
王璞
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Shanghai Polytechnic University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
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    • B01D53/8668Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
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    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
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    • B01J23/8892Manganese

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Abstract

本发明公开了一种基于废旧三元电极材料制备的锰基催化剂处理苯系有机物的催化氧化系统。该系统包括第一、第二气泵、配气系统、苯系有机物发生装置、缓冲装置、预热装置和催化反应装置;本系统通过第一气泵将苯系有机物发生装置中的有机物载出进入缓冲装置,调节第二气泵对载出的有机物进行稀释,稳定后进入预热装置,而后通过以蜂窝状堇青石为载体,负载有基于废旧三元电极材料制备的锰基催化剂的催化反应装置,使有机物得到催化降解。本发明的催化氧化系统通过基于废旧三元电极材料制备的锰基催化剂降低有机物氧化反应的反应活化能,进而降低反应温度,提高反应速率,使有机物降解为H2O和CO2,降低氧化系统处理有机废气所消耗能量的同时提高降解率。

The invention discloses a catalytic oxidation system for treating benzene series organic matter based on a manganese-based catalyst prepared from waste ternary electrode materials. The system includes the first and second air pumps, gas distribution system, benzene-based organic compound generator, buffer device, preheating device and catalytic reaction device; the system uses the first air pump to carry the organic matter in the benzene-based organic compound generator into the buffer device, adjust the second air pump to dilute the organic matter carried out, and enter the preheating device after stabilization, and then pass through the catalytic reaction device with the honeycomb cordierite as the carrier and the manganese-based catalyst prepared based on the waste ternary electrode material. Organic matter is catalytically degraded. The catalytic oxidation system of the present invention reduces the reaction activation energy of the oxidation reaction of organic matter through the manganese-based catalyst prepared based on waste ternary electrode materials, thereby reducing the reaction temperature, increasing the reaction rate, degrading the organic matter into H 2 O and CO 2 , and reducing the oxidation system Improve the degradation rate while treating the energy consumed by organic waste gas.

Description

一种基于废旧三元电极材料制备的锰基催化剂处理苯系有机 物的催化氧化系统A manganese-based catalyst based on waste ternary electrode materials for the treatment of benzene-based organic Catalytic Oxidation System

技术领域technical field

本发明属于废气治理技术领域,特别涉及一种基于废旧三元电极材料制备的锰基催化剂处理苯系有机物的催化氧化系统。The invention belongs to the technical field of waste gas treatment, and in particular relates to a catalytic oxidation system for treating benzene series organic matter with a manganese-based catalyst prepared from waste ternary electrode materials.

背景技术Background technique

近年来,雾霾频发,已经严重影响到周围环境和人类健康,引起人们广泛关注,雾霾频发的一大诱因就是有毒有害气体的释放,其中VOCs的产生占据着重要比例,生态环境部颁发了各种法规条例和标准来限制污染气体的排放。在VOCs的排放中,化工行业产生的废气所占比例最大,而且化工行业产生的废气具有成分复杂、浓度大、不稳定等特点,针对化工行业产生的废气最有效,应用最广泛的技术是直接热力燃烧和热力催化氧化,直接热力燃烧需要额外添加燃料,由于其燃烧的温度比较高,对设备材质的要求也比较高,造成其运行成本大大增加,另外高温下的直接燃烧会产生热力型氮氧化物造成二次污染,此外还存在不完全燃烧现象。相比而言,热力催化氧化的催化氧化温度比较低,不需要额外添加燃料,不存在二次污染问题,运行成本相对比较低,而且化工行业产生的有机废气不需要进行浓缩处理,可以直接用来催化燃烧,热力催化选用贵金属将会增加其运行费用,相比贵金属,一般过渡金属氧化物也具有良好的催化降解效果,而且一般过渡金属通过复合获得的催化剂,其性能可以和贵金属相媲美,催化剂的选择对于整个技术至为关键。目前废旧锂电池应用广泛,面临着大量报废的问题,而其中的正极材料中含有大量的有价金属元素,将废旧三元电极材料应用在催化氧化催化剂的制备中,既简化了电池正极材料的回收程序,又降低了催化氧化降解的成本,达到以废治废的目的,可以使催化氧化技术在工业废气治理中发挥更重要的作用,更具优势。In recent years, the frequent occurrence of smog has seriously affected the surrounding environment and human health, and has aroused widespread concern. One of the major causes of frequent smog is the release of toxic and harmful gases, of which the generation of VOCs occupies an important proportion. The Ministry of Ecology and Environment Various regulations and standards are issued to limit the emission of polluting gases. In the emission of VOCs, the waste gas produced by the chemical industry accounts for the largest proportion, and the waste gas produced by the chemical industry has the characteristics of complex composition, high concentration, and instability. The most effective and widely used technology for the waste gas produced by the chemical industry is direct Thermal combustion and thermal catalytic oxidation, direct thermal combustion requires additional fuel, because the combustion temperature is relatively high, and the requirements for equipment materials are also relatively high, resulting in a significant increase in operating costs. In addition, direct combustion at high temperatures will produce thermal nitrogen Oxides cause secondary pollution, and incomplete combustion also exists. In contrast, the catalytic oxidation temperature of thermodynamic catalytic oxidation is relatively low, no additional fuel is required, there is no secondary pollution problem, and the operating cost is relatively low, and the organic waste gas generated in the chemical industry does not need to be concentrated and can be used directly For catalytic combustion, the selection of noble metals for thermodynamic catalysis will increase its operating costs. Compared with noble metals, general transition metal oxides also have good catalytic degradation effects, and the performance of catalysts obtained by compounding transition metals can be comparable to that of noble metals. Catalyst selection is critical to the overall technology. At present, waste lithium batteries are widely used and are facing the problem of a large number of scrapping, and the positive electrode materials contain a large amount of valuable metal elements. The application of waste ternary electrode materials in the preparation of catalytic oxidation catalysts not only simplifies the preparation of battery positive electrode materials The recovery procedure also reduces the cost of catalytic oxidation degradation and achieves the purpose of treating waste with waste, which can make catalytic oxidation technology play a more important role and have more advantages in industrial waste gas treatment.

发明内容Contents of the invention

有鉴于此,本发明的目的在于提供一种基于废旧三元电极材料制备的锰基催化剂处理苯系有机物的催化氧化系统。该系统能通过高效催化剂降低有机物氧化反应的反应活化能,进而降低反应温度,提高反应速率,使有机物降解为H2O和CO2,降低氧化系统处理有机废气所消耗能量的同时提高降解率。In view of this, the object of the present invention is to provide a catalytic oxidation system for treating benzene-based organics based on a manganese-based catalyst prepared from waste ternary electrode materials. The system can reduce the reaction activation energy of the oxidation reaction of organic matter through high-efficiency catalysts, thereby reducing the reaction temperature, increasing the reaction rate, degrading organic matter into H 2 O and CO 2 , reducing the energy consumed by the oxidation system to treat organic waste gas and improving the degradation rate.

本发明的技术方案具体介绍如下。The technical solution of the present invention is specifically introduced as follows.

一种基于废旧三元电极材料制备的锰基催化剂处理苯系有机物的催化氧化系统,其包括第一气泵、第二气泵、配气系统、苯系有机物发生装置、第一缓冲装置、预热装置、催化反应装置和第二缓冲装置;第一气泵通过配气系统依次和苯系有机物发生装置和第一缓冲装置相连,用于将苯系有机物载出进入第一缓冲装置,第二气泵通过配气系统和第一缓冲装置相连,用于对载出的苯系有机物进行稀释;第一缓冲装置依次通过管路和预热装置、催化反应装置相连,用于将苯系有机物经由预热装置加热后进入催化反应装置进行催化氧化反应,对苯系有机物进行降解;所述预热装置中设置陶瓷蓄热体,陶瓷蓄热体采用第一热电偶进行加热,第一热电偶与第一控温仪连接,所述催化反应装置采用管式反应器,采用第二热电偶对管式反应器进行加热,第二热电偶与第二控温仪连接,管式反应器中设有基于废旧三元电极材料制备的负载型锰基催化剂;降解后的苯系有机物经过第二缓冲装置后从排口排出。A catalytic oxidation system for treating benzene-series organics with a manganese-based catalyst prepared from waste ternary electrode materials, which includes a first air pump, a second air pump, a gas distribution system, a benzene-series organics generating device, a first buffer device, and a preheating device , a catalytic reaction device and a second buffer device; the first air pump is sequentially connected with the benzene-based organic matter generating device and the first buffer device through the gas distribution system, and is used to carry out the benzene-based organic matter into the first buffer device, and the second air pump passes through the distribution system The gas system is connected to the first buffer device, which is used to dilute the benzene-series organic matter carried out; the first buffer device is connected to the preheating device and the catalytic reaction device in turn through pipelines, and is used to heat the benzene-series organic matter through the preheating device Then enter the catalytic reaction device to carry out catalytic oxidation reaction, and degrade the benzene series organic matter; the ceramic regenerator is set in the preheating device, and the ceramic regenerator is heated by the first thermocouple, and the first thermocouple and the first temperature control The catalytic reaction device uses a tubular reactor, and the second thermocouple is used to heat the tubular reactor. The second thermocouple is connected to the second temperature controller. The tubular reactor is equipped with a waste ternary The supported manganese-based catalyst prepared by the electrode material; the degraded benzene series organic matter is discharged from the discharge port after passing through the second buffer device.

本发明中,进入预热装置的苯系有机物的浓度为300-2500mg/m3;进一步的,苯系有机物的浓度为1200~2500 mg/m3In the present invention, the concentration of the benzene-series organics entering the preheating device is 300-2500 mg/m 3 ; further, the concentration of the benzene-series organics is 1200-2500 mg/m 3 .

本发明中,苯系有机物包括苯和甲苯。In the present invention, the benzene series organic substances include benzene and toluene.

本发明中,基于废旧三元电极材料制备的负载型锰基催化剂以蜂窝状堇青石为载体,以;其制备方法如下:In the present invention, the supported manganese-based catalyst prepared based on the waste ternary electrode material takes honeycomb cordierite as a carrier, and its preparation method is as follows:

(1)将蜂窝状堇青石放置于干燥箱中100-110℃的温度下干燥10-12小时;(1) Place the honeycomb cordierite in a drying oven at a temperature of 100-110°C for 10-12 hours;

(2)用30~50ml王水溶解0.5~1g废旧锂电池三元正极材料LiNi1−xy Co x Mn y O2配制所需浸渍液;(2) Dissolve 0.5~1g LiNi 1− xy Co x Mn y O 2 ternary cathode material of waste lithium battery with 30~50ml aqua regia to prepare the required impregnation solution;

(3)将步骤(1)干燥处理后的载体置于步骤(2)所配制的浸渍液中浸渍3-4小时;(3) Immerse the dried carrier in step (1) in the impregnation solution prepared in step (2) for 3-4 hours;

(4)将浸渍处理过的样品在烘箱中100-110℃的温度下处理10-12小时;(4) Treat the impregnated sample in an oven at a temperature of 100-110°C for 10-12 hours;

(5)在马弗炉中在1150~1250℃条件下处理活化制成催化氧化催化剂。(5) Treat and activate in a muffle furnace at 1150~1250°C to make a catalytic oxidation catalyst.

本发明中,预热装置中的温度为100-200℃;催化反应装置中温度为175-375℃。In the present invention, the temperature in the preheating device is 100-200°C; the temperature in the catalytic reaction device is 175-375°C.

本发明中,第一气泵的配气量在0-10 L/min之间,第二气泵的配气量在0-50 L/min之间;催化反应装置中的空速为5000-12000h-1In the present invention, the air distribution volume of the first air pump is between 0-10 L/min, the air distribution volume of the second air pump is between 0-50 L/min; the space velocity in the catalytic reaction device is 5000-12000h -1 .

与现有技术相比,本发明的有益效果在于:Compared with prior art, the beneficial effect of the present invention is:

本发明能降低苯系有机物的降解温度,与传统的燃烧工艺相比,反应系统更节能。The invention can reduce the degradation temperature of benzene series organic matter, and compared with the traditional combustion process, the reaction system is more energy-saving.

本发明所采用的催化剂的活性成分为基于废旧锂电池三元正极材料NCM制备的复合的金属氧化物,比传统的贵金属催化剂价格低,具有可再生的特点,并且具有较高的苯系有机物降解率。The active component of the catalyst used in the present invention is a composite metal oxide prepared based on NCM, the ternary positive electrode material of waste lithium batteries, which is lower in price than traditional noble metal catalysts, has the characteristics of regeneration, and has higher degradation of benzene-based organics Rate.

本发明选用蜂窝状堇青石作为载体进行活性测试,与传统载体相比,具有机械强度高、压降小、耐热性好等特点。The invention selects the honeycomb cordierite as the carrier for the activity test, and compared with the traditional carrier, it has the characteristics of high mechanical strength, small pressure drop, good heat resistance and the like.

附图说明Description of drawings

图1为有机废气处理催化氧化系统的结构示意图。Figure 1 is a schematic structural diagram of a catalytic oxidation system for organic waste gas treatment.

图2为蜂窝状堇青石载体的截面图。Fig. 2 is a cross-sectional view of a honeycomb cordierite carrier.

图中标号:1-第一气泵,2-第二气泵,3-配气系统,4-苯系有机物发生装置,5-第一缓冲装置,6-陶瓷蓄热体,7-第一控温仪,8-第二控温仪,9-管式反应器,10-第二缓冲装置,11-管式炉,12-排口,13-采样口,14-蜂窝状堇青石载体,15-第一热电偶,16-第二热电偶。Labels in the figure: 1-first air pump, 2-second air pump, 3-gas distribution system, 4-benzene-based organic matter generator, 5-first buffer device, 6-ceramic heat storage body, 7-first temperature control instrument, 8-second temperature controller, 9-tubular reactor, 10-second buffer device, 11-tube furnace, 12-outlet, 13-sampling port, 14-honeycomb cordierite carrier, 15- 1st thermocouple, 16 - 2nd thermocouple.

具体实施方式Detailed ways

下面结合附图和实施例对本发明的技术方案进行详细阐述。The technical solutions of the present invention will be described in detail below in conjunction with the drawings and embodiments.

本发明提供一种能够高效处理苯系有机物的催化氧化系统(图1),其包括:The present invention provides a catalytic oxidation system capable of efficiently treating benzene series organics (Figure 1), which includes:

第一气泵1、第二气泵2、配气系统3、苯系有机物发生装置4和第一缓冲装置5;苯系有机物发生装置4中包含温控系统,其通过温控系统保持低温,例如1℃,以保证苯系有机物发生装置4中的苯系有机物保持液体状态。同时仅通过空气(第一气泵1)的流载出苯系有机物不能满足实验要求,特用另一支气流(第二气泵2)对载出的苯系有机物进行稀释来调节其浓度。其通过电脑智能控制气泵流量,以调节第一缓冲装置5中苯系有机物浓度。The first air pump 1, the second air pump 2, the gas distribution system 3, the benzene series organic matter generating device 4 and the first buffer device 5; the benzene series organic matter generating device 4 includes a temperature control system, which keeps a low temperature through the temperature control system, such as 1 ℃, to ensure that the benzene-series organics in the benzene-series organics generator 4 remain in a liquid state. At the same time, only the flow of air (first air pump 1) to carry out the benzene-series organics cannot meet the experimental requirements. Another air flow (second air pump 2) is specially used to dilute the carried-out benzene-series organics to adjust its concentration. It intelligently controls the flow rate of the air pump through the computer to adjust the concentration of benzene series organic matter in the first buffer device 5 .

实施例中,控制气体浓度的鼓吹液态甲苯3的第一气泵1(0-10 L/min)和鼓吹空气的第二气泵2(0-50 L/min),通过调节第一气泵1将温控系统中苯系有机物发生装置4中的甲苯载出进入到第一缓冲装置,调节第二气泵2对载出的甲苯进行稀释,控制目标降解物甲苯的浓度,气体的总流量为12 L/min,甲苯气体浓度维持在1500 mg/m3In the embodiment, the first air pump 1 (0-10 L/min) for blowing liquid toluene 3 and the second air pump 2 (0-50 L/min) for blowing air are used to control the gas concentration. By adjusting the first air pump 1, the temperature The toluene in the benzene series organic matter generating device 4 in the control system is carried out into the first buffer device, and the second air pump 2 is adjusted to dilute the carried out toluene to control the concentration of the target degradation product toluene. The total flow rate of the gas is 12 L/ min, the toluene gas concentration was maintained at 1500 mg/m 3 .

待气体稳定后,通过配气系统3后的甲苯进入预热装置中的陶瓷蓄热体6中,通过第一控温仪7连接的第一热电偶15对目标污染物甲苯进行升温,所选用陶瓷蓄热体6为圆柱体,横截面直径为20 cm,蓄热体中蜂窝孔的孔径为0.5 cm;系统中选用的陶瓷蓄热体6具有高强度、耐高温、耐腐蚀、耐磨等特性。预热装置中的温度在100-200℃之间。After the gas is stabilized, the toluene passing through the gas distribution system 3 enters the ceramic regenerator 6 in the preheating device, and the first thermocouple 15 connected to the first temperature controller 7 heats up the temperature of the target pollutant toluene. The ceramic regenerator 6 is a cylinder with a cross-sectional diameter of 20 cm, and the diameter of the honeycomb holes in the regenerator is 0.5 cm; the ceramic regenerator 6 selected in the system has high strength, high temperature resistance, corrosion resistance, wear resistance, etc. characteristic. The temperature in the preheating device is between 100-200°C.

预热后的气体进入催化反应装置,该装置选用管式反应器9作为催化反应装置,该管式反应器9为一石英管,管的长度为450 mm,内径为22 mm,外径为25 mm,体积为168 mL,石英管内部放置催化剂,用管式炉对其进行加热,用第二热电偶16测试其床层温度,热电偶16连接第二控温仪8控制管式炉对床层的加热温度;The preheated gas enters the catalytic reaction device, and the device selects a tubular reactor 9 as the catalytic reaction device. The tubular reactor 9 is a quartz tube with a length of 450 mm, an inner diameter of 22 mm, and an outer diameter of 25 mm. mm, the volume is 168 mL, the catalyst is placed inside the quartz tube, heated by a tube furnace, and the bed temperature is tested by the second thermocouple 16, which is connected to the second temperature controller 8 to control the tube furnace to the bed. Layer heating temperature;

实施例中,管式反应器9中放置的催化剂为通过废旧三元电极材料制备的锰基催化剂的具体制备方法如下:In the embodiment, the catalyst placed in the tubular reactor 9 is a manganese-based catalyst prepared from waste ternary electrode materials. The specific preparation method is as follows:

将堇青石放置于干燥箱中110℃的温度下干燥10小时,用50 ml王水溶解1 g废旧锂电池三元正极材料LiNi1−xy Co x Mn y O2配制所需浸渍液,将干燥处理后的载体置于所配制的浸渍液中浸渍3小时,然后将浸渍处理过的催化剂在烘箱中100℃下处理10小时,最后在马弗炉中在1200 ℃条件下处理活化制成催化氧化催化剂,该催化剂能有效降低有机污染物的降解温度,减少能源浪费,提高反应活性。Place cordierite in a drying oven at 110°C and dry for 10 hours, then dissolve 1 g of waste lithium battery ternary cathode material LiNi 1− xy Co x Mn y O 2 with 50 ml of aqua regia to prepare the required impregnation solution. The dried carrier is immersed in the prepared impregnation solution for 3 hours, then the impregnated catalyst is treated in an oven at 100°C for 10 hours, and finally activated in a muffle furnace at 1200°C to obtain Catalytic oxidation catalyst, which can effectively reduce the degradation temperature of organic pollutants, reduce energy waste, and improve reaction activity.

实施例中,将取用的1 g电废旧锂电池三元正极材料LiNi1−xy Co x Mn y O2于电炉中,经煅烧后置于50 ml王水中,后经微波消解处理后通过ICP-AES测其金属元素含量,锰占66.49%,镍占16.11%,钴占7.94%,锂占7.69%,并含有少量1.78%铝。In the example, 1 g of waste lithium battery ternary positive electrode material LiNi 1− xy Co x Mn y O 2 was taken in an electric furnace, calcined, placed in 50 ml of aqua regia, and then digested by microwave The content of metal elements measured by ICP-AES shows that manganese accounts for 66.49%, nickel accounts for 16.11%, cobalt accounts for 7.94%, lithium accounts for 7.69%, and contains a small amount of 1.78% aluminum.

降解后的甲苯气体通过放置有活性炭的第二缓冲装置10对尾气中残留的有机气体进The toluene gas after the degradation is carried out to the residual organic gas in the tail gas by the second buffer device 10 that is placed with gac.

行吸附去除。Remove by adsorption.

待系统稳定后,分别对进出口气体进行采样,入口浓度通过采样口13进行采样,出口浓度通过排口12进行采样;用取样针进行采样后,通过气相色谱仪来测定气体浓度,以此来评价该有机废气催化氧化系统的性能。After the system is stabilized, the inlet and outlet gases are sampled respectively, the inlet concentration is sampled through the sampling port 13, and the outlet concentration is sampled through the outlet 12; after sampling with a sampling needle, the gas concentration is measured by a gas chromatograph to The performance of the organic waste gas catalytic oxidation system was evaluated.

环境工况影响因素测试Environmental working condition influencing factor test

本发明预热装置中的温度设定为150℃,待催化降解反应装置稳定运行10 min后进行测定。改变两路气泵的调节阀控制气体浓度维持稳定。The temperature in the preheating device of the present invention is set at 150° C., and the measurement is performed after the catalytic degradation reaction device has run stably for 10 minutes. Change the regulating valves of the two air pumps to control the gas concentration to maintain stability.

本发明控制催化反应装置中的温度为375℃和进气的浓度1500mg/m3在不变条件下,分别设置具有一定间隔的空速,反应系统稳定运行10min后分别在反应器的前端和后端进行采样分析,分别在空速为5372.5、5732.5、7643.3、9554.1、12420.4 h-1的情况下,测定甲苯转化效率,结果显示随着空速在5732.5h-1时甲苯的转化率最高,能达到85%以上,而随着空速的升高,所制催化剂对甲苯的降解率会有一定程度的降低。The present invention controls the temperature in the catalytic reaction device to be 375°C and the concentration of the intake air to be 1500mg/m 3 under constant conditions, respectively set the space velocity with a certain interval, and after the reaction system runs stably for 10 minutes, the reaction system is respectively at the front end and the rear of the reactor. Sampling analysis was carried out at the end, and the conversion efficiency of toluene was measured under the conditions of space velocity of 5372.5, 5732.5 , 7643.3, 9554.1, and 12420.4 h -1 respectively. It can reach more than 85%, and with the increase of space velocity, the degradation rate of toluene of the prepared catalyst will decrease to a certain extent.

本发明通过调节气泵流量的大小获得所需的进气浓度,催化反应装置温度控制375℃,空速控制5732.5h-1,待催化反应装置运行稳定后在反应装置的进出口分别采样,本发明的进气浓度梯度为319.9、982.4、1622.7、2311.2 mg/m3的情况下,采样后通过气相色谱进行分析发现,浓度最高和浓度最低时甲苯的转化率差值在4%以下,相差不大,甲苯的降解率都能达到80%。In the present invention, the required intake air concentration is obtained by adjusting the flow rate of the air pump. The temperature of the catalytic reaction device is controlled at 375°C, and the air velocity is controlled at 5732.5h -1 . When the concentration gradient of the intake air is 319.9, 982.4, 1622.7, 2311.2 mg/m 3 , the analysis by gas chromatography after sampling shows that the difference between the conversion rate of toluene at the highest concentration and the lowest concentration is less than 4%, which is not much different. , the degradation rate of toluene can reach 80%.

在本发明的一个实例中,控制配气量12 L/min,空速5732.5 h-1,甲苯气体浓度为1500 mg/m3,对以蜂窝状堇青石为载体,负载物为从废旧三元电极材料中制备的锰基催化剂行有机物的降解实验,催化反应装置中的温度设置在175-375 ℃之间,温度的梯度设置为25 ℃,在温度从250-375 ℃上升的过程中,甲苯的转化率从30 %开始上升,350 ℃时趋于稳定,降解效率最高可以达到85 %以上。In an example of the present invention, the gas distribution volume is controlled to 12 L/min, the space velocity is 5732.5 h -1 , the toluene gas concentration is 1500 mg/m 3 , the honeycomb cordierite is used as the carrier, and the load is from waste ternary electrodes The manganese-based catalyst prepared in the material was used for the degradation experiment of organic matter. The temperature in the catalytic reaction device was set between 175-375 °C, and the temperature gradient was set at 25 °C. During the temperature rise from 250-375 °C, the toluene The conversion rate starts to increase from 30%, and tends to be stable at 350 ℃, and the highest degradation efficiency can reach more than 85%.

在本发明的一个实例中,控制配气量12 L/min,空速5732.5 h-1,甲苯气体浓度为1500 mg/m3,对没有负载从废旧三元电极材料中制备的锰基催化剂的蜂窝状堇青石进行有机物的降解实验,随着温度在200-350 ℃范围内不断上升,其对甲苯的去除几乎没有变化,无负载的堇青石载体对甲苯最高去除率不超过5 %。In an example of the present invention, the gas distribution volume is controlled at 12 L/min, the space velocity is 5732.5 h -1 , and the toluene gas concentration is 1500 mg/m 3 . The degradation experiment of organic matter with cordierite was carried out. As the temperature continued to rise in the range of 200-350 ℃, the removal of toluene was almost unchanged, and the highest removal rate of toluene on the unloaded cordierite carrier was no more than 5%.

综上所述,本发明提供的有机污染物催化氧化系统,以苯系有机物甲苯等作为降解对象,利用蜂窝状陶瓷蓄热体对有机污染物进行预加热,温度控制在100-200 ℃,利用以蜂窝状堇青石为载体,负载物为从废旧三元电极材料中制备的锰基催化剂降低有机污染物的降解温度,提高反应活性,以较低的温度达到使有机物降解的目的,避免浪费多余的能量,同时所制备的锰基复合金属氧化物催化剂能从废旧的三元电池中获取,所选用的复合金属氧化物催化剂具有和贵金属催化剂相似的性能,能够有效降低催化剂费用,节约成本,达到以废治废的目的。因此本发明具有环保,经济和高效率等优点。To sum up, the organic pollutant catalytic oxidation system provided by the present invention takes benzene-based organic matter toluene as the degradation object, uses honeycomb ceramic regenerator to preheat organic pollutants, and controls the temperature at 100-200 ° C. Honeycomb cordierite is used as the carrier, and the load is manganese-based catalyst prepared from waste ternary electrode materials to reduce the degradation temperature of organic pollutants, improve the reactivity, and achieve the purpose of degrading organic matter at a lower temperature, avoiding waste of excess At the same time, the prepared manganese-based composite metal oxide catalyst can be obtained from waste ternary batteries. The selected composite metal oxide catalyst has similar performance to the noble metal catalyst, which can effectively reduce the cost of the catalyst, save costs, and achieve The purpose of treating waste with waste. Therefore, the present invention has the advantages of environmental protection, economy and high efficiency.

尽管本发明已经给出了具体实施办法及案例,但上述实施例是示例性的,本发明的范围不局限于此。本发明所在的技术领域的技术人员可以根据本发明的内容范围内对上述案例进行变型。Although the present invention has provided specific implementation methods and cases, the above-mentioned embodiments are illustrative, and the scope of the present invention is not limited thereto. Those skilled in the technical field of the present invention can modify the above cases within the scope of the present invention.

Claims (7)

1. Catalytic oxidation system for treating benzene organic matters by using manganese-based catalyst prepared based on waste ternary electrode material
characterized in that the device comprises a first air pump, a second air pump, an air distribution system, a benzene series organic matter generating device, a first buffer device, a preheating device, a catalytic reaction device and a second buffer device; the first air pump is sequentially connected with the benzene system organic matter generating device and the first buffer device through the air distribution system and used for loading the benzene system organic matters into the first buffer device, and the second air pump is connected with the first buffer device through the air distribution system and used for diluting the loaded benzene system organic matters; the first buffer device is connected with the preheating device and the catalytic reaction device sequentially through a pipeline and is used for heating benzene organic matters through the preheating device and then enabling the benzene organic matters to enter the catalytic reaction device for catalytic oxidation reaction, and degrading the benzene organic matters; the catalytic reaction device adopts a tubular reactor, the tubular reactor is heated by a second thermocouple, the second thermocouple is connected with the second temperature controller, and a supported manganese-based catalyst prepared based on waste ternary electrode materials is arranged in the tubular reactor; and the degraded benzene organic matters are discharged from the discharge port after passing through the second buffer device.
2. The catalytic oxidation system according to claim 1, wherein the concentration of the benzene-based organic compound entering the preheating device is 300-2500mg/m 3.
3. The catalytic oxidation system according to claim 1, wherein the concentration of the benzene-based organic compound entering the preheating device is 1200-2500mg/m 3.
4. The catalytic oxidation system of claim 1, wherein the benzene-based organic comprises benzene and toluene.
5. The catalytic oxidation system of claim 1, wherein the supported manganese-based catalyst prepared based on the waste ternary electrode material is prepared by using honeycomb cordierite as a carrier; the preparation method comprises the following steps:
(1) Placing the honeycomb cordierite into a drying box to be dried for 10-12 hours at the temperature of 100-110 ℃;
(2) Dissolving 0.5 ~ 1g of waste lithium battery ternary positive electrode material LiNi 1- x - y Co x Mn y O 2 by using 30 ~ 50ml of aqua regia to prepare required impregnation liquid;
(3) Placing the carrier dried in the step (1) into the impregnation liquid prepared in the step (2) for impregnation for 3-4 hours;
(4) Treating the impregnated sample in an oven at a temperature of 100-110 ℃ for 10-12 hours;
(5) The catalyst is treated and activated in a muffle furnace at 1150 ~ 1250 ℃ to prepare the catalytic oxidation catalyst.
6. The catalytic oxidation system of claim 1, wherein the temperature in the preheating device is 100-200 ℃; the temperature in the catalytic reaction device is 175-375 ℃.
-17. The catalytic oxidation system of claim 1, wherein the air distribution amount of the first air pump is 0-10L/min, the air distribution amount of the second air pump is 0-50L/min, and the space velocity in the catalytic reaction device is 5000-.
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