CN103316585B - A kind of method of organic pollution in nanometer mineral material Purge gas - Google Patents
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Abstract
Description
一、技术领域 1. Technical field
本发明属于环保技术领域,具体涉及到挥发性有机污染物净化技术和材料。 The invention belongs to the technical field of environmental protection, and in particular relates to purification technology and materials of volatile organic pollutants.
二、背景技术 2. Background technology
挥发性有机物(VOCs)通常是指常压下沸点为50-260℃的有机化合物,如烷烃、烯烃、芳香烃、氯代芳烃以及饱和、不饱和的醛、酮等。VOCs主要来源于石油、化工、造纸、油漆涂料、采矿、金属电镀和纺织等行业排放的废气,以及众多交通工具所排放的废气。 Volatile organic compounds (VOCs) usually refer to organic compounds with a boiling point of 50-260°C under normal pressure, such as alkanes, alkenes, aromatic hydrocarbons, chlorinated aromatic hydrocarbons, saturated and unsaturated aldehydes, ketones, etc. VOCs mainly come from exhaust gases emitted by industries such as petroleum, chemical industry, papermaking, paint coatings, mining, metal electroplating, and textiles, as well as exhaust gases emitted by many vehicles.
据统计,2005-2010年间,我国VOCs排放总量约2650-3100万吨,而2010年我国仅涂料应用过程就向大气释放VOCs约388万吨,在挥发性有机废气总排放中占有很大比例。苯系物、醇、醋、醚、酮等五类化合物是当前涂料应用排放有机废气的主要成分,分别占到总量的29%、19%、13%、10%和11%,其中31%为有毒有害物质,以甲苯和二甲苯为主。随着社会发展和人们对环境质量要求的提高,世界各国对有机废气的排放制定了严格的环保法规,如美国、日本、德国等都制定了严格的有机废气排放标准,特别是对苯系物、多环芳烃、多氯联苯、二恶英等常见的和强毒性的工业有机废气,更是引起了人们和环保工作者的关注。美国清洁空气修正案(l990年)要求监测的189种优先控制的有毒空气污染物中,约有100种为挥发性有机污染物;我国1997年颁布并实施的《大气污染物综合排放标准》中共限定了33种污染物的排放限值,其中就包括苯系物(苯、甲苯和二甲苯)等多种VOCs。目前我国大气污染的控制和治理多集中于电厂和锅炉等大型固定源的烟气除尘、脱硫、脱硝等的技术研究和工业推广上,相比之下挥发性有机废气,如苯系物有机废气的排放未引起足够的重视。故开发经济、高效的有机废气处理技术,将对改善我国的大气质量,实现大气污染的控制和治理具有重要的环境、经济和社会意义。 According to statistics, from 2005 to 2010, the total emission of VOCs in my country was about 26.5-31 million tons. In 2010, only about 3.88 million tons of VOCs were released into the atmosphere during the coating application process in my country, accounting for a large proportion of the total emissions of volatile organic waste gases. . Five types of compounds, such as benzene series, alcohol, vinegar, ether, and ketone, are the main components of organic waste gas emitted by current coating applications, accounting for 29%, 19%, 13%, 10%, and 11% of the total, of which 31% It is a toxic and harmful substance, mainly toluene and xylene. With the development of society and the improvement of people's requirements for environmental quality, countries around the world have formulated strict environmental protection regulations on the discharge of organic waste gas, such as the United States, Japan, Germany, etc., have formulated strict organic waste gas emission standards, especially for benzene series , polycyclic aromatic hydrocarbons, polychlorinated biphenyls, dioxins and other common and highly toxic industrial organic waste gases have attracted the attention of people and environmental protection workers. Among the 189 priority toxic air pollutants that are required to be monitored in the United States Clean Air Amendment (1990), about 100 are volatile organic pollutants; the "Comprehensive Emission Standards for Atmospheric Pollutants" promulgated and implemented in my country in 1997 The emission limits of 33 kinds of pollutants are limited, including various VOCs such as benzene series (benzene, toluene and xylene). At present, the control and treatment of air pollution in my country are mostly focused on the technical research and industrial promotion of flue gas dust removal, desulfurization, and denitrification of large-scale fixed sources such as power plants and boilers. In contrast, volatile organic waste gases, such as benzene series organic waste gases emissions have not received enough attention. Therefore, the development of economical and efficient organic waste gas treatment technology will have important environmental, economic and social significance for improving my country's air quality and realizing the control and governance of air pollution.
气体中有机污染物净化处理的方法主要有两类:一类是回收法,另一类是销毁法。回收法主要有炭吸附、变压吸附、冷凝法及膜分离技术,回收法是通过物理方法用压力、温度、选择性吸附剂和选择性渗透膜等方法来分离VOCs的。销毁法有高温燃烧法、催化低温燃烧法、催化氧化法、生物氧化及集成技术。销毁法主要是通过化学或生化反应,用催化剂、热或者微生物将挥发性有机物转变成为二氧化碳和水。在这些污染控制技术中,研究较多并且广泛采用的有热破坏法、吸附法、吸收法、冷凝法等,近年来形成的新控制技术有生物膜法、臭氧分解法、电晕法、等离子体分解法等。 There are two main methods for the purification and treatment of organic pollutants in gas: one is the recovery method, and the other is the destruction method. The recovery methods mainly include carbon adsorption, pressure swing adsorption, condensation method and membrane separation technology. The recovery method uses pressure, temperature, selective adsorbent and selective permeable membrane to separate VOCs through physical methods. Destruction methods include high-temperature combustion method, catalytic low-temperature combustion method, catalytic oxidation method, biological oxidation and integrated technology. The destruction method mainly uses catalysts, heat or microorganisms to convert volatile organic compounds into carbon dioxide and water through chemical or biochemical reactions. Among these pollution control technologies, thermal destruction method, adsorption method, absorption method, condensation method, etc. have been widely studied and widely used. New control technologies formed in recent years include biofilm method, ozonolysis method, corona method, plasma pollution method, etc. body decomposition, etc.
催化低温燃烧法产生的热量难以维持自热,还是需要对气体加热才能达到所需温度,能耗较高。吸附法具有去除效率高、净化彻底、能耗低、工艺成熟和易于推广的优点,具有较好的环境和经济效益,缺点是处理设备庞大且流程复杂,当废气中有胶粒物质或其它杂质时吸附剂很容易失效,而且材料再生时必须经过再处理容易造成二次污染,从而增加了处理的成本。吸收法是利用气态污染物在某些液态溶剂中具有很好的溶解性,以液体作为吸收剂,使废气中的有害成分被液体吸收,从而达到分离污染物净化气体的目的,但是仍然有吸收溶剂的挥发以及吸收剂的再生问题。生物降解法成本较低,但是很多有机污染物的可生物降解性不高,限制了生物法的运用。光催化氧化法得到了广泛的研究,但是这一方法在对VOCs的净化方面还存在着较多缺点,例如,在光催化氧化反应过程中会产生酮、醛、酸等有机中间产物,可能造成二次污染,另外,光催化氧化法只能针对浓度较低的VOCs来进行处理,催化剂也存在容易失活、难以固定等缺点。等离子体技术的特点是运行工艺简单,所用的设备维护比较方便,工作流程短而且可操作性好,但是这一方法存在一些弊端:能耗较高,能量利用率有待进一步的提高;放电的副产物可能会造成二次污染,例如会产生NOx、CO、O3等气体。 The heat generated by the catalytic low-temperature combustion method is difficult to maintain self-heating, and the gas still needs to be heated to reach the required temperature, and the energy consumption is high. The adsorption method has the advantages of high removal efficiency, thorough purification, low energy consumption, mature process and easy promotion, and has good environmental and economic benefits. The disadvantage is that the treatment equipment is huge and the process is complicated. When the adsorbent is easy to fail, and the material must be reprocessed when it is regenerated, it will easily cause secondary pollution, thereby increasing the cost of treatment. The absorption method is to use the gaseous pollutants to have good solubility in some liquid solvents, and use the liquid as an absorbent to make the harmful components in the exhaust gas absorbed by the liquid, so as to achieve the purpose of separating pollutants and purifying the gas, but there is still absorption Solvent volatilization and absorbent regeneration. The cost of biodegradation is low, but the biodegradability of many organic pollutants is not high, which limits the application of biological methods. Photocatalytic oxidation has been widely studied, but this method still has many shortcomings in the purification of VOCs. For example, organic intermediate products such as ketones, aldehydes, and acids will be produced during the photocatalytic oxidation reaction, which may cause Secondary pollution. In addition, the photocatalytic oxidation method can only be used to treat low-concentration VOCs, and the catalyst also has disadvantages such as easy deactivation and difficulty in fixing. The characteristics of plasma technology are simple operation process, convenient equipment maintenance, short work process and good operability, but this method has some disadvantages: high energy consumption, and the energy utilization rate needs to be further improved; the side effects of discharge The product may cause secondary pollution, such as NO x , CO, O 3 and other gases.
三、发明内容 3. Contents of the invention
本发明旨在提供一种挥发性有机污染物净化方法,所要解决的技术问题是设计合适的催化材料和工艺使其能通过催化双氧水化学氧化的方式去除气体中的挥发性有机污染物。 The present invention aims to provide a method for purifying volatile organic pollutants. The technical problem to be solved is to design suitable catalytic materials and processes to remove volatile organic pollutants in gas by catalyzing the chemical oxidation of hydrogen peroxide.
本发明解决技术问题采用如下技术方案: The present invention solves technical problem and adopts following technical scheme:
反应器外壳(1)、进气口(2)、穿孔布气板(3)、铁氧化物滤料层(4)、出气口(5)、双氧水储池(6)、双氧水加料口(7)。 Reactor shell (1), air inlet (2), perforated gas distribution plate (3), iron oxide filter material layer (4), gas outlet (5), hydrogen peroxide storage tank (6), hydrogen peroxide feed port (7 ).
净化气体中有机污染物的方法是: The method of purifying organic pollutants in gas is:
气体从进样口(2)进入,与双氧水储池(6)中的双氧水接触; The gas enters from the inlet (2) and contacts with the hydrogen peroxide in the hydrogen peroxide storage tank (6);
通过调节储存池中双氧水浓度、进气速度、进气与双氧水溶液接触方式调控双氧水的挥发速度,使气体中双氧水的量为氧化有机污染物所需双氧水理论量的100-110%; Regulate the volatilization rate of hydrogen peroxide by adjusting the concentration of hydrogen peroxide in the storage tank, the speed of intake air, and the contact mode between intake air and hydrogen peroxide solution, so that the amount of hydrogen peroxide in the gas is 100-110% of the theoretical amount of hydrogen peroxide required to oxidize organic pollutants;
挥发的双氧水与气体混合均匀一起通过穿孔布气板(3),气体穿过装有纳米化矿物材料颗粒的固定滤层,通过纳米化矿物材料的非均相芬顿反应氧化挥发性有机污染物。 The volatilized hydrogen peroxide is evenly mixed with the gas and passes through the perforated gas distribution plate (3), the gas passes through the fixed filter layer filled with nano-sized mineral material particles, and oxidizes volatile organic pollutants through the heterogeneous Fenton reaction of nano-sized mineral materials .
与已有技术相比,本发明有益效果体现在: Compared with the prior art, the beneficial effects of the present invention are reflected in:
1、发明人利用了双氧水有一定的挥发性这一特点,反应器下部设置双氧水储存池,进气气流与双氧水接触,部分挥发双氧水与气体混合,通过储存池中双氧水浓度、进气速度、进气与双氧水溶液接触方式调控双氧水的挥发速度,为有机污染物的氧化提供适合比例的氧化剂。双氧水与进气完全很合均匀,有利于提高反应速率。 1. The inventor took advantage of the fact that hydrogen peroxide has a certain volatility. The lower part of the reactor is equipped with a hydrogen peroxide storage tank. The intake air flow is in contact with the hydrogen peroxide, and part of the volatilized hydrogen peroxide is mixed with the gas. The method of contacting the gas with the hydrogen peroxide solution regulates the volatilization rate of the hydrogen peroxide and provides an appropriate proportion of oxidants for the oxidation of organic pollutants. Hydrogen peroxide is completely compatible with the intake air, which is beneficial to improve the reaction rate.
2、本发明的净化气体中有机污染物方法,关键是使用纳米化矿物材料作为催化剂催化双氧水氧化净化污染物。所用的纳米化矿物材料具有纳米晶和纳米孔,属于纳米结构材料,具有较大的比表面积和反应活性,表现出非常优异的催化活性,提高气固相芬顿氧化效果;所用的纳米化矿物材料制备方法简单,原料为储量丰富的矿物资源,如褐铁矿矿石、硫铁矿矿石,来源广泛,制备成本低。 2. The key to the method for purifying organic pollutants in gas of the present invention is to use nanometerized mineral materials as catalysts to catalyze hydrogen peroxide to oxidize and purify pollutants. The nano-mineral materials used have nanocrystals and nano-pores, belong to nano-structure materials, have a large specific surface area and reactivity, show very excellent catalytic activity, and improve the effect of gas-solid phase Fenton oxidation; the nano-minerals used The preparation method of the material is simple, the raw materials are mineral resources with abundant reserves, such as limonite ore and pyrite ore, the sources are extensive, and the preparation cost is low.
3、使用的纳米化矿物材料为粒径0.5-5mm颗粒物,装填成为固定滤层,滤层孔隙率大,气体阻力小。 3. The nanometerized mineral material used is particles with a particle size of 0.5-5mm, which is filled into a fixed filter layer with large porosity and low gas resistance.
4、使用低浓度盐酸、或硫酸、或硝酸对装填的纳米化矿物材料滤料进行处理,使纳米化矿物材料表面呈现酸性,提高了催化双氧水氧化有机污染物的效率,因为酸性条件下更有利于双氧水氧化有机污染物的反应。 4. Use low-concentration hydrochloric acid, sulfuric acid, or nitric acid to treat the filled nano-mineral material filter material, making the surface of the nano-mineral material acidic, and improving the efficiency of catalyzing hydrogen peroxide to oxidize organic pollutants, because it is more efficient under acidic conditions. It is beneficial to the reaction of hydrogen peroxide to oxidize organic pollutants.
四、附图说明 4. Description of drawings
图1纳米化矿物材料净化挥发性气态污染物的反应器结构示意图:1-外壳;2-进气口;3-穿孔布气板;4-纳米化矿物材料填料层;5-出气口;6-双氧水储池;7-双氧水补加口。 Figure 1 Schematic diagram of the reactor structure for purifying volatile gaseous pollutants with nano-sized mineral materials: 1-housing; 2-inlet; 3-perforated gas distribution plate; - Hydrogen peroxide storage tank; 7 - Hydrogen peroxide filling port.
图2 纳米铁矿物材料的X射线衍射图谱,显示所用纳米矿物材料的组成和结构特征。 Figure 2 X-ray diffraction pattern of nano-iron mineral materials, showing the composition and structural characteristics of the nano-mineral materials used.
图3 几种纳米铁矿物材料催化双氧水氧化甲烷效率(气体中甲烷体积分数为5%) Figure 3 Catalytic efficiency of hydrogen peroxide oxidation methane by several nano-iron mineral materials (the volume fraction of methane in the gas is 5%)
图4几种纳米铁矿物材料催化双氧水氧化甲苯效率(气体中甲苯浓度为2.43g/Nm3) Figure 4 Catalytic efficiency of hydrogen peroxide oxidation of toluene by several nano-iron mineral materials (the concentration of toluene in the gas is 2.43g/Nm 3 )
五、具体实施方式 5. Specific implementation
实施例1: Example 1:
把褐铁矿矿石破碎、筛分获得粒径为0.5~1mm颗粒物(图2)。 The limonite ore is crushed and sieved to obtain particles with a particle size of 0.5-1mm (Figure 2).
把制备的颗粒用2%硝酸浸渍,沥干,装填入反应器上部。 The prepared granules were impregnated with 2% nitric acid, drained, and loaded into the upper part of the reactor.
净化气体中有机污染物的装置如图1所示,1-外壳;2-进气口;3-穿孔布气板;4-纳米化矿物材料滤层;5-出气口;6-双氧水储池;7-双氧水加料口。 The device for purifying organic pollutants in the gas is shown in Figure 1, 1-housing; 2-inlet; 3-perforated gas distribution plate; 4-nanometer mineral material filter layer; 5-gas outlet; 6-hydrogen peroxide storage tank ; 7-hydrogen peroxide feed port.
用空气泵把空气通过0.1%的甲醛水溶液,用质量流量计调节气体流量,获得含甲醛334mg/m3的模拟气体。 Use an air pump to pass the air through 0.1% formaldehyde aqueous solution, and use a mass flow meter to adjust the gas flow to obtain a simulated gas containing 334mg/ m3 of formaldehyde.
把含甲醛的模拟气体从进气口(2)进入,与双氧水储池(6)中的双氧水接触,储池中双氧水浓度设定为15%进行试验;挥发的双氧水与气体混合均匀一起通过穿孔布气板(3)再穿过纳米化矿物材料滤层,催化双氧水氧化气体中的有机污染污物。 Enter the simulated gas containing formaldehyde from the air inlet (2), contact with the hydrogen peroxide in the hydrogen peroxide storage tank (6), and set the concentration of hydrogen peroxide in the storage tank to 15% for the test; the volatilized hydrogen peroxide and the gas are mixed evenly and pass through the perforation The gas distribution plate (3) passes through the filter layer of nano-sized mineral materials to catalyze the organic pollutants in the hydrogen peroxide oxidation gas.
从净化装置出气口(5)排出的气体用蒸馏水吸收,用乙酰丙酮分光光度法测定溶液中甲醛的量,根据气体流量及溶液中甲醛浓度计算出气中甲醛浓度,甲醛去除率大于90%。 The gas discharged from the gas outlet (5) of the purification device is absorbed with distilled water, the amount of formaldehyde in the solution is measured by acetylacetone spectrophotometry, and the formaldehyde concentration in the gas is calculated according to the gas flow rate and the formaldehyde concentration in the solution. The formaldehyde removal rate is greater than 90%.
实施例2: Example 2:
把褐铁矿矿石破碎、筛分获得粒径为1.0~5mm颗粒物,取样50g放入马弗炉在300℃煅烧1小时得到由纳晶赤铁矿构成的纳米孔、高比表面积的纳米化矿物材料(图2)。 The limonite ore is crushed and sieved to obtain particles with a particle size of 1.0~5mm, and 50g of the sample is put into a muffle furnace for calcination at 300°C for 1 hour to obtain a nano-sized mineral with nanopores and a high specific surface area composed of nanocrystalline hematite Materials (Figure 2).
把制备的纳米化矿物材料颗粒用5%硝酸浸渍,沥干,装填入反应器上部。 The prepared nanometerized mineral material particles are impregnated with 5% nitric acid, drained, and loaded into the upper part of the reactor.
用空气泵把空气通过0.1%的甲醛水溶液,用质量流量计调节气体流量,获得含甲醛334mg/m3的模拟气体。 Use an air pump to pass the air through 0.1% formaldehyde aqueous solution, and use a mass flow meter to adjust the gas flow to obtain a simulated gas containing 334mg/ m3 of formaldehyde.
把含甲醛的模拟气体从进气口(2)进入,与双氧水储池(6)中的双氧水接触,储池中双氧水浓度设定为30%进行试验;挥发的双氧水与气体混合均匀一起通过穿孔布气板(3)再穿过纳米化矿物材料滤层,催化双氧水氧化气体中的有机污染污物。 Enter the simulated gas containing formaldehyde from the air inlet (2), contact with the hydrogen peroxide in the hydrogen peroxide storage tank (6), and set the concentration of hydrogen peroxide in the storage tank to 30% for the test; the volatilized hydrogen peroxide and the gas are mixed evenly and pass through the perforation The gas distribution plate (3) passes through the filter layer of nano-sized mineral materials to catalyze the organic pollutants in the hydrogen peroxide oxidation gas.
从净化装置出气口(5)排出的气体用蒸馏水吸收,用乙酰丙酮分光光度法测定溶液中甲醛的量,根据气体流量及溶液中甲醛浓度计算出气中甲醛浓度,甲醛去除率大于95%。 The gas discharged from the gas outlet (5) of the purification device is absorbed with distilled water, the amount of formaldehyde in the solution is measured by acetylacetone spectrophotometry, and the formaldehyde concentration in the gas is calculated according to the gas flow rate and the formaldehyde concentration in the solution. The formaldehyde removal rate is greater than 95%.
实施例3: Example 3:
把褐铁矿矿石破碎、筛分获得粒径为0.5~1mm颗粒物,取样50g放入管式炉中,通入氢气300℃煅烧2小时,得到由纳晶磁铁矿和纳米铁构成的纳米孔、高比表面积的纳米化矿物材料。 Limonite ore is crushed and sieved to obtain particles with a particle size of 0.5~1mm, 50g of the sample is put into a tube furnace, and hydrogen gas is introduced into it for calcination at 300°C for 2 hours to obtain nanopores composed of nanocrystalline magnetite and nano-iron , Nano-sized mineral materials with high specific surface area.
把制备的纳米化矿物材料颗粒用5%硫酸浸渍,沥干,装填入反应器上部; The prepared nano mineral material particles are impregnated with 5% sulfuric acid, drained, and loaded into the upper part of the reactor;
用空气泵把空气通过0.1%的甲醛水溶液,用质量流量计调节气体流量,获得含甲醛的模拟气体。 Use an air pump to pass air through 0.1% formaldehyde aqueous solution, and use a mass flow meter to adjust the gas flow to obtain a simulated gas containing formaldehyde.
把含甲醛的模拟气体从进气口(2)进入,与双氧水储池(6)中的双氧水接触,储池中双氧水浓度分别设定为5、10、15%不同的浓度进行试验;挥发的双氧水与气体混合均匀一起通过穿孔布气板(3)再穿过纳米化矿物材料滤层,催化双氧水氧化气体中的有机污染污物。 Enter the simulated gas containing formaldehyde from the air inlet (2) and contact with the hydrogen peroxide in the hydrogen peroxide storage tank (6). The hydrogen peroxide and the gas are evenly mixed and passed through the perforated air distribution plate (3) and then through the nano-sized mineral material filter layer to catalyze the hydrogen peroxide to oxidize the organic pollutants in the gas.
从净化装置出气口(5)排出的气体用蒸馏水吸收,用乙酰丙酮分光光度法测定溶液中甲醛的量,根据气体流量及溶液中甲醛浓度计算出气中甲醛浓度,甲醛去除率大于95%。 The gas discharged from the gas outlet (5) of the purification device is absorbed with distilled water, the amount of formaldehyde in the solution is measured by acetylacetone spectrophotometry, and the formaldehyde concentration in the gas is calculated according to the gas flow rate and the formaldehyde concentration in the solution. The formaldehyde removal rate is greater than 95%.
实施例4: Example 4:
把黄铁矿矿石破碎、筛分获得粒径为0.5~1mm颗粒物,取样50g放入管式炉,通入氮气,550℃煅烧1小时,得到由纳晶磁黄铁矿构成的纳米孔、高比表面积的纳米化矿物材料(图2)。 The pyrite ore is crushed and sieved to obtain particles with a particle size of 0.5~1mm, and 50g of the sample is put into a tube furnace, fed with nitrogen, and calcined at 550°C for 1 hour to obtain nanopore, high Nanosized mineral materials with specific surface area (Figure 2).
把制备的纳米化矿物材料颗粒用0.5%硫酸浸渍,沥干,装填入反应器上部; The prepared nano mineral material particles are impregnated with 0.5% sulfuric acid, drained, and loaded into the upper part of the reactor;
用空气泵把空气通过0.1%的甲醛水溶液,用质量流量计调节气体流量,获得含甲醛的模拟气体。 Use an air pump to pass air through 0.1% formaldehyde aqueous solution, and use a mass flow meter to adjust the gas flow to obtain a simulated gas containing formaldehyde.
把含甲醛的模拟气体从进气口(2)进入,与双氧水储池(6)中的双氧水接触,储池中双氧水浓度分别设定为5、10、15%不同的浓度进行试验;挥发的双氧水与气体混合均匀一起通过穿孔布气板(3)再穿过纳米化矿物材料滤层,催化双氧水氧化气体中的有机污染污物。 Enter the simulated gas containing formaldehyde from the air inlet (2) and contact with the hydrogen peroxide in the hydrogen peroxide storage tank (6). The hydrogen peroxide and the gas are evenly mixed and passed through the perforated air distribution plate (3) and then through the nano-sized mineral material filter layer to catalyze the hydrogen peroxide to oxidize the organic pollutants in the gas.
从净化装置出气口(5)排出的气体用蒸馏水吸收,用乙酰丙酮分光光度法测定溶液中甲醛的量,根据气体流量及溶液中甲醛浓度计算出气中甲醛浓度,甲醛去除率大于95%。 The gas discharged from the gas outlet (5) of the purification device is absorbed with distilled water, the amount of formaldehyde in the solution is measured by acetylacetone spectrophotometry, and the formaldehyde concentration in the gas is calculated according to the gas flow rate and the formaldehyde concentration in the solution. The formaldehyde removal rate is greater than 95%.
实施例5: Example 5:
把黄铁矿矿石破碎、筛分获得粒径为0.5~1mm颗粒物,取样50g放入管式炉,通入氮气,550℃煅烧1小时,得到由纳晶磁黄铁矿构成的纳米孔、高比表面积的纳米化矿物材料(图2)。 The pyrite ore is crushed and sieved to obtain particles with a particle size of 0.5~1mm, and 50g of the sample is put into a tube furnace, fed with nitrogen, and calcined at 550°C for 1 hour to obtain nanopore, high Nanosized mineral materials with specific surface area (Figure 2).
把制备的纳米化矿物材料颗粒用0.5%硫酸浸渍,沥干,装填入反应器上部; The prepared nano mineral material particles are impregnated with 0.5% sulfuric acid, drained, and loaded into the upper part of the reactor;
把纯甲烷标准气、空气分别通过质量流量计控制配置成为体积分数为1%、2%、3%、4%、5%的混合气体,把含甲烷的模拟气体从进样口(2)进入,与双氧水储池(6)中的双氧水接触,储池中双氧水浓度为5%,挥发的双氧水与气体混合均匀一起通过穿孔布气板(3)再穿过纳米化矿物材料滤层,催化双氧水氧化气体中的甲烷。 The pure methane standard gas and air are respectively controlled and configured by the mass flow meter to form a mixed gas with a volume fraction of 1%, 2%, 3%, 4%, and 5%, and the simulated gas containing methane enters from the injection port (2) , in contact with the hydrogen peroxide in the hydrogen peroxide storage tank (6), the concentration of hydrogen peroxide in the storage tank is 5%, the volatilized hydrogen peroxide is mixed with the gas evenly and passes through the perforated gas distribution plate (3) and then passes through the nanometerized mineral material filter layer to catalyze the hydrogen peroxide Oxidizes methane in the gas.
从净化装置出口(5)排出的气体用气相色谱仪分析,在甲烷体积分数小于5%时,甲烷去除率大于95%(图3)。 The gas discharged from the outlet (5) of the purification device is analyzed by a gas chromatograph. When the methane volume fraction is less than 5%, the methane removal rate is greater than 95% (Figure 3).
实施例6: Embodiment 6:
把黄铁矿矿石破碎、筛分获得粒径为0.5~1mm颗粒物,取样50g放入管式炉,通入氮气,550℃煅烧1小时,得到由纳晶磁黄铁矿构成的纳米孔、高比表面积的纳米化矿物材料。 The pyrite ore is crushed and sieved to obtain particles with a particle size of 0.5~1mm, and 50g of the sample is put into a tube furnace, fed with nitrogen, and calcined at 550°C for 1 hour to obtain nanopore, high Nano-sized mineral materials with specific surface area.
把制备的纳米化矿物材料颗粒用0.1%硫酸浸渍,沥干,装填入反应器上部。用空气泵把10mL/min的空气通过纯液体甲苯获得含高浓度甲苯的气体,把该气体通过质量流量计控制与另一路空气在混合瓶中混合,获得10mg/m3、100mg/m3、500mg/m3、1000mg/m3、5000mg/m3不同甲醛浓度的模拟气体,把含甲苯的模拟气体从进样口(2)进入反应器,与双氧水储池(6)中的双氧水接触,储池中双氧水浓度为5%,挥发的双氧水与气体混合均匀一起通过穿孔布气板(3)再穿过纳米化矿物材料滤层,通过芬顿反应催化双氧水氧化甲苯。 The prepared nanometerized mineral material particles are impregnated with 0.1% sulfuric acid, drained, and loaded into the upper part of the reactor. Use an air pump to pass 10mL/min of air through pure liquid toluene to obtain a gas containing high concentration of toluene, and control the gas through a mass flow meter and mix it with another air in a mixing bottle to obtain 10mg/m 3 , 100mg/m 3 , 500mg/m 3 , 1000mg/m 3 , and 5000mg/m 3 simulated gas with different formaldehyde concentrations, the simulated gas containing toluene enters the reactor from the injection port (2), and contacts with the hydrogen peroxide in the hydrogen peroxide storage tank (6), The concentration of hydrogen peroxide in the storage tank is 5%, and the volatilized hydrogen peroxide and gas are evenly mixed and pass through the perforated gas distribution plate (3) and then through the filter layer of nano-sized mineral materials, and catalyze the oxidation of toluene by hydrogen peroxide through the Fenton reaction.
从净化装置出口(7)排出的气体用活性炭吸附后用二硫化碳解析,然后用气相色谱分析,计算处理后甲苯浓度和去除效率,甲苯去除率95%(图4)。 The gas discharged from the outlet (7) of the purification device is adsorbed by activated carbon, analyzed by carbon disulfide, and then analyzed by gas chromatography to calculate the toluene concentration and removal efficiency after treatment. The removal rate of toluene is 95% (Figure 4).
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