[go: up one dir, main page]

CN1583229A - Treatment Methods of Cooking Fume Pollution - Google Patents

Treatment Methods of Cooking Fume Pollution Download PDF

Info

Publication number
CN1583229A
CN1583229A CN200410044883.2A CN200410044883A CN1583229A CN 1583229 A CN1583229 A CN 1583229A CN 200410044883 A CN200410044883 A CN 200410044883A CN 1583229 A CN1583229 A CN 1583229A
Authority
CN
China
Prior art keywords
parts
oil fume
water
cooking oil
cooking
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN200410044883.2A
Other languages
Chinese (zh)
Other versions
CN1240468C (en
Inventor
周政
刘红军
梁银春
张志炳
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nanjing University
Institute of Chemical Industry of Forest Products of CAF
Original Assignee
Nanjing University
Institute of Chemical Industry of Forest Products of CAF
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nanjing University, Institute of Chemical Industry of Forest Products of CAF filed Critical Nanjing University
Priority to CN200410044883.2A priority Critical patent/CN1240468C/en
Publication of CN1583229A publication Critical patent/CN1583229A/en
Application granted granted Critical
Publication of CN1240468C publication Critical patent/CN1240468C/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Landscapes

  • Catalysts (AREA)

Abstract

本发明公开了一种烹饪油烟污染的治理方法,使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将100~160份硫酸铜溶于500~1500份水中加入50~200份高岭土,在30℃~100℃下搅拌并加入10%~80%的氢氧化钠水溶液100~300份,反应10~40分钟后,将反应物倾入水中,待其分层后,取出沉降的生成物,干燥后,再于600℃~1000℃下焙烧4小时~8小时。本发明能够降低烹饪油烟对环境危害,使烹饪油烟转化成对环境友好燃烧的燃料。

Figure 200410044883

The invention discloses a method for treating cooking oil fume pollution. The collected cooking oil fume is degraded by a fume degradation catalyst heated to 100-200°C. The oil fume degradation catalyst is prepared by dissolving 100-160 parts of copper sulfate in 500 Add 50-200 parts of kaolin to 1500 parts of water, stir at 30°C-100°C and add 100-300 parts of 10%-80% sodium hydroxide aqueous solution, react for 10-40 minutes, then pour the reactant into water, After the layers are separated, the sedimented product is taken out, dried, and then calcined at 600° C. to 1000° C. for 4 hours to 8 hours. The invention can reduce the harm of cooking oil fume to the environment, and convert the cooking oil fume into environmentally friendly burning fuel.

Figure 200410044883

Description

烹饪油烟污染的治理方法Treatment Methods of Cooking Fume Pollution

                         技术领域Technical field

本发明涉及一种烹饪油烟的处理方法,尤其涉及一种烹饪油烟污染的治理方法。The invention relates to a cooking fume treatment method, in particular to a cooking fume pollution control method.

                         背景技术 Background technique

近年来,随着我国经济水平的不断提高,各种餐馆、饭店等饮食单位的数量急剧增加。其烹饪油烟污染源已成为仅次于工业污染源和交通污染源后的第三大空气污染源。研究表明,烹调油烟成分复杂,具有一定的吸入毒性、免疫毒性和致突变性,对人体健康存在一定的危害。为此国家环保总局于2000年颁布实施《饮食业油烟排放标准(试行)》(GWPB5-2000)。目前,解决的主要方法是排除和净化法。例如:机械式油烟净化设备,主要优点是设备简单、压降较小、弊端在于对小粒径的颗粒去除率低,总去除率亦较低。过滤式油烟净化设备,优点是净化率高,运行稳定可靠,可同时去除大部分油烟的气味,但由于吸附材料捕集的颗粒物粘度较高,清洗比较困难。如果采用一次吸附材料、费用又会过高。另外,还有静电式、湿式和复合式。这些治理方法和装置都是从排除和净化设计思想出发,属于物理处理方法,存在有不彻底性,有二次污染和设备中污渍的清除以及机械噪音等问题。这些弊端和问题难以彻底解决。In recent years, with the continuous improvement of my country's economic level, the number of various restaurants, restaurants and other catering units has increased dramatically. Its cooking oil fume pollution source has become the third largest air pollution source after industrial pollution sources and traffic pollution sources. Studies have shown that cooking fume has complex components, has certain inhalation toxicity, immunotoxicity and mutagenicity, and has certain hazards to human health. For this reason, the State Environmental Protection Administration promulgated and implemented "The Cooking Fume Emission Standard (Trial)" (GWPB5-2000) in 2000. At present, the main method to solve is to exclude and purify. For example: mechanical oil fume purification equipment, the main advantages are simple equipment, small pressure drop, and the disadvantage is that the removal rate of small particle size particles is low, and the total removal rate is also low. Filter-type oil fume purification equipment has the advantages of high purification rate, stable and reliable operation, and can remove most of the smell of oil fume at the same time. However, due to the high viscosity of the particles captured by the adsorption material, cleaning is more difficult. If a primary adsorption material is used, the cost will be too high. In addition, there are electrostatic, wet and composite. These treatment methods and devices are all based on the design idea of exclusion and purification, which belong to physical treatment methods, and there are problems such as incompleteness, secondary pollution, removal of stains in equipment, and mechanical noise. These drawbacks and problems are difficult to completely solve.

                          技术内容Technical content

本发明提供一种能够降低烹饪油烟对环境危害的烹饪油烟污染的治理方法。The invention provides a treatment method for cooking oil fume pollution which can reduce the environmental harm of cooking oil fume.

本发明采用以下技术方案:The present invention adopts following technical scheme:

本发明是一种烹饪油烟污染的治理方法,使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将100~160份硫酸铜溶于500~1500份水中加入50~200份高岭土,在30~100℃下搅拌并加入10%~80%的氢氧化钠水溶液100~300份,反应10~40分钟后,将反应物倾入水中,待其分层后,取出沉降的生成物,干燥后,再于600℃~1000℃下焙烧4小时~8小时。The invention relates to a treatment method for cooking oil fume pollution. The collected cooking oil fume is degraded by a fume degradation catalyst heated to 100-200 °C. The preparation of the oil fume degradation catalyst is to dissolve 100-160 parts of copper sulfate in 500- Add 50-200 parts of kaolin to 1500 parts of water, stir at 30-100°C and add 100-300 parts of 10%-80% sodium hydroxide aqueous solution, react for 10-40 minutes, pour the reactant into water, wait After layering, take out the sedimented product, dry it, and then bake it at 600°C to 1000°C for 4 hours to 8 hours.

与现有技术相比,本发明具有如下有益效果:Compared with the prior art, the present invention has the following beneficial effects:

①本发明所述的降解催化剂是将高岭土同硫酸铜和氢氧化钠在反应生成氧化铜时,在一起共混制成氧化铜与高岭土中的组分形成了分子结合物,该结合物对烹饪油烟有很好的降解效果,由于通过高温烧结,具有象瓷器一样的强度,有很好的耐水性、耐蚀性,本发明的制备方法,能在高温烧结前制成各种成状,以利于提高油烟的通过速度和降解反应效果。本发明使烹饪时产生的油烟用催化降解催化剂进行氧化反应,使其中不易燃烧的高沸点、大分子化合物,不饱和多烃结构化合物和水气一起凝聚的细小颗粒,被氧化生成饱和的小分子低沸点化合物,该类化合物能用于环境友好燃烧的燃料。验证实验:取烹饪时产生的油烟,通过冷凝得到黑褐色粘稠状液体100g,加热蒸镏,收集到了100~220℃的馏份50g、未蒸出残渣48g;制样测紫外光谱,其谱图显示有不饱和烃存在;取样在酒精灯上燃烧,有未能燃烧完全而产生的黑烟。将烹饪时产生的油烟通过被加热到100℃~200℃的催化降解催化剂,而后冷凝得到冷凝液100g,其被降解后的液体呈黄色,有微量水,半透明状,测沸程为90~130℃,此间馏份为98g,瓶底有少量未成渣的流动态度黄色液体,制样测紫外光谱,其谱图显示为饱和烃类化合物;取样在酒精灯上燃烧,未见黑烟出现,燃烧完全;称重降解催化剂为100g,没有增加重量,说明反应过程中没有油烟滞留。②本发明由于使用了催化降解催化剂,把烹饪油烟进行了化学氧化处理。使灶具燃烧加热→烹饪→产生油烟→油烟氧化降解→灶具燃烧这一个烹饪制做食物的过程,成为自循环体系的过程,在这一过程中无中间排放物。它优于其它物理的处理方法。③本发明在处理油烟的同时又为烹饪加热提供了能源,使烹饪油烟得到了综合利用。④本发明制备的降解催化剂因为添加了高岭土,在600℃以上高温焙烧成型,所以能耐水、耐腐蚀。油烟气在接触催化剂过程阻力小,不会滞留。1. the degradation catalyst of the present invention is that when kaolin is reacted with copper sulfate and sodium hydroxide to generate copper oxide, the components in the kaolin are blended together to form a molecular bond, and the bond is harmful to cooking. The oil fume has a good degradation effect. Because it has the same strength as porcelain through high-temperature sintering, it has good water resistance and corrosion resistance. The preparation method of the present invention can be made into various shapes before high-temperature sintering. It is beneficial to improve the passing speed of oil fume and the effect of degradation reaction. In the present invention, the soot produced during cooking is oxidized with a catalytic degradation catalyst, so that the non-combustible high-boiling point, macromolecular compounds, unsaturated multi-hydrocarbon structural compounds and fine particles condensed together with water vapor are oxidized to form saturated small molecules Low boiling point compounds, which can be used as fuels for environmentally friendly combustion. Verification experiment: take the cooking fumes, condense to obtain 100g of dark brown viscous liquid, heat and distill, collect 50g of distillate at 100-220℃, and 48g of undistilled residue; sample preparation and UV spectrum measurement, the spectrum The picture shows the presence of unsaturated hydrocarbons; the sample is burned on an alcohol lamp, and there is black smoke produced by incomplete combustion. The cooking fume is passed through the catalytic degradation catalyst heated to 100℃~200℃, and then condensed to obtain 100g of condensate. The degraded liquid is yellow, with a trace of water, translucent, and the measured boiling range is 90~ 130°C, the distillate here is 98g, and there is a small amount of yellow liquid with no slagging at the bottom of the bottle. The ultraviolet spectrum of the sample is measured, and the spectrum shows saturated hydrocarbon compounds; the sample is burned on an alcohol lamp, and no black smoke appears. Combustion was complete; the degradation catalyst was weighed to be 100g, and the weight did not increase, indicating that there was no soot retention in the reaction process. ② The present invention has carried out chemical oxidation treatment on the cooking fume due to the use of the catalytic degradation catalyst. The process of cooking and making food by making the stove burn → cook → produce oil fume → oxidize and degrade oil fume → burn the stove becomes a process of self-circulation system, and there is no intermediate emission in this process. It is superior to other physical processing methods. ③The present invention provides energy for cooking and heating while processing oily fumes, so that cooking oily fumes are comprehensively utilized. ④ The degradation catalyst prepared by the present invention is water-resistant and corrosion-resistant because kaolin is added and baked at a high temperature above 600°C. The oily fume has low resistance and will not stay in the process of contacting the catalyst.

                         附图说明Description of drawings

图1是油烟降解前的紫外吸收光谱。Figure 1 is the UV absorption spectrum before the oil fume is degraded.

图2是油烟降解后的紫外吸收光谱。Figure 2 is the UV absorption spectrum after the oil fume is degraded.

                         具体实施方案Specific implementation plan

实施例1:本发明是一种烹饪油烟污染的治理方法,使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将100~160份硫酸铜溶于500~1500份水中加入50~200份高岭土,在30~100℃下搅拌并加入10%~80%的氢氧化钠水溶液100~300份,反应10~40分钟后,将反应物倾入水中,待其分层后,取出沉降的生成物,干燥后,再于600℃~1000℃下焙烧4小时~8小时,在本实施例中,生成物应被干燥至可以被捏合状态,干燥办法可以采用风干措施,即:将生成物风干、捏合并使其成型后,再将其置于100℃~120℃下烘干,捏合所形成的形状球形、方形、环形或其他不规则形状。Embodiment 1: The present invention is a treatment method for cooking oil fume pollution. The collected cooking oil fume is degraded by a soot degradation catalyst heated to 100°C to 200°C. The oil fume degradation catalyst is prepared by adding 100 to 160 parts of copper sulfate Dissolve 500-1500 parts of water, add 50-200 parts of kaolin, stir at 30-100°C and add 100-300 parts of 10%-80% sodium hydroxide aqueous solution, react for 10-40 minutes, pour the reactant into In water, after the layers are separated, take out the sedimented product, dry it, and then bake it at 600°C to 1000°C for 4 hours to 8 hours. In this example, the product should be dried until it can be kneaded. The method can be air-dried, that is: air-dry, knead and shape the product, then dry it at 100°C to 120°C, and knead to form a spherical, square, ring or other irregular shape.

实施例2:本发明是一种烹饪油烟污染的治理方法,使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将100份硫酸铜溶于500~1500份水中加入50份高岭土,在30℃下搅拌并加入10%(重量百分比)的氢氧化钠水溶液100份,反应10分钟后,将反应物倾入500ml水中,待其分层后,取出所得沉降的生成物,干燥后,再于600℃下熔烧4小时后,即得烹饪油烟降解催化剂118g,堆比重:~0.78g/cm3Embodiment 2: The present invention is a treatment method for cooking oil fume pollution. The collected cooking oil fume is degraded by a soot degradation catalyst heated to 100°C to 200°C. The oil fume degradation catalyst is prepared by dissolving 100 parts of copper sulfate in Add 50 parts of kaolin to 500-1500 parts of water, stir at 30°C and add 100 parts of 10% (percentage by weight) sodium hydroxide aqueous solution, react for 10 minutes, pour the reactant into 500ml of water, and after layering, The precipitated product was taken out, dried, and then sintered at 600° C. for 4 hours to obtain 118 g of a cooking oil fume degradation catalyst with a bulk specific gravity of ~0.78 g/cm 3 .

实施例3:本发明是一种烹饪油烟污染的治理方法,使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将115份硫酸铜溶于700份水中加入156份高岭土,在38℃下搅拌并加入22%氢氧化钠水溶液150份,反应17分钟后,将反应物倾入1000ml水中,待其分层后,取出所得沉降的生成物,干燥后,再于680℃下熔烧4.8小时。Embodiment 3: The present invention is a treatment method for cooking oil fume pollution. The collected cooking oil fume is degraded by a soot degradation catalyst heated to 100°C to 200°C. The oil fume degradation catalyst is prepared by dissolving 115 parts of copper sulfate in Add 156 parts of kaolin to 700 parts of water, stir at 38° C. and add 150 parts of 22% aqueous sodium hydroxide solution. After reacting for 17 minutes, pour the reactant into 1000 ml of water. After drying, it was further calcined at 680°C for 4.8 hours.

实施例4:本发明是一种烹饪油烟污染的治理方法,使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将123份硫酸铜溶于800份水中加入87份高岭土,在57℃下搅拌并加入30%氢氧化钠水溶液170份,反应25分钟后,将反应物倾入1500ml水中,待其分层后,取出所得沉降的生成物,干燥后,再于765℃下熔烧6.2小时。Embodiment 4: The present invention is a treatment method for cooking oil fume pollution. The collected cooking oil fume is degraded by a soot degradation catalyst heated to 100°C to 200°C. The oil fume degradation catalyst is prepared by dissolving 123 parts of copper sulfate in Add 87 parts of kaolin to 800 parts of water, stir at 57° C. and add 170 parts of 30% aqueous sodium hydroxide solution. After reacting for 25 minutes, pour the reactant into 1500 ml of water. After drying, it was further calcined at 765°C for 6.2 hours.

实施例5:本发明是一种烹饪油烟污染的治理方法,使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将148份硫酸铜溶于900份水中加入125份高岭土,在83℃下搅拌并加入35%氢氧化钠水溶液210份,反应31分钟后,将反应物倾入1800ml水中,待其分层后,取出所得沉降的生成物,干燥后,再于890℃下燃烧6.9小时。Example 5: The present invention is a treatment method for cooking oil fume pollution. The collected cooking oil fume is degraded by a cooking fume degradation catalyst heated to 100°C to 200°C. The oil fume degradation catalyst is prepared by dissolving 148 parts of copper sulfate in Add 125 parts of kaolin to 900 parts of water, stir at 83° C. and add 210 parts of 35% aqueous sodium hydroxide solution. After reacting for 31 minutes, pour the reactant into 1800 ml of water. After drying, it was burned at 890°C for 6.9 hours.

实施例6:本发明是一种烹饪油烟污染的治理方法,使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将155份硫酸铜溶于1400份水中加入183份高岭土,在95℃下搅拌并加入45%氢氧化钠水溶液,反应37分钟后,将反应物倾入2000ml水中,待其分层后,取出所得沉降的生成物,干燥后,再于930℃下熔烧7.5小时。Embodiment 6: The present invention is a treatment method for cooking oil fume pollution. The collected cooking oil fume is degraded by a soot degradation catalyst heated to 100°C to 200°C. The oil fume degradation catalyst is prepared by dissolving 155 parts of copper sulfate in Add 183 parts of kaolin to 1400 parts of water, stir at 95°C and add 45% aqueous sodium hydroxide solution. After reacting for 37 minutes, pour the reactant into 2000ml of water. , and then sintered at 930 ° C for 7.5 hours.

实施例7:本发明是一种烹饪油烟污染的治理方法,使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将160份硫酸铜溶于1500份水中加入200份高岭土,在100℃下搅拌并加入60%氢氧化钠水溶液300份,反应40分钟后,将反应物倾入2500ml水中,待其分层后,取出所得沉降的生成物,干燥后,再于1000℃下熔烧8小时。Embodiment 7: The present invention is a treatment method for cooking oil fume pollution. The collected cooking oil fume is degraded by a soot degradation catalyst heated to 100°C to 200°C. The oil fume degradation catalyst is prepared by dissolving 160 parts of copper sulfate in Add 200 parts of kaolin to 1500 parts of water, stir at 100° C. and add 300 parts of 60% aqueous sodium hydroxide solution. After reacting for 40 minutes, pour the reactant into 2500 ml of water. After drying, it was melted at 1000°C for 8 hours.

Claims (2)

1、一种烹饪油烟污染的治理方法,其特征在于使收集到的烹饪油烟通过加热至100℃~200℃的油烟降解催化剂降解,该油烟降解催化剂的制备是将100~160份硫酸铜溶于500~1500份水中加入50~200份高岭土,在30~100℃下搅拌并加入10%~80%氢氧化钠水溶液100~300份,反应10~40分钟后,将反应物倾入水中,待其分层后,取出沉降的生成物,干燥后,再于600℃~1000℃下焙烧4小时~8小时。1. A treatment method for cooking oil fume pollution, characterized in that the collected cooking oil fume is degraded by a soot degradation catalyst heated to 100°C to 200°C, and the oil fume degradation catalyst is prepared by dissolving 100 to 160 parts of copper sulfate in Add 50-200 parts of kaolin to 500-1500 parts of water, stir at 30-100°C and add 100-300 parts of 10%-80% sodium hydroxide aqueous solution, react for 10-40 minutes, pour the reactant into water, wait After the layers are separated, the sedimented product is taken out, dried, and calcined at 600° C. to 1000° C. for 4 hours to 8 hours. 2、根据权利要求1所述的烹饪油烟污染的治理方法,其特征在于将生成物风干、捏合并使其成型后,再将其置于100℃~120℃下烘干。2. The cooking fume pollution control method according to claim 1, characterized in that the product is air-dried, kneaded and molded, and then dried at 100°C to 120°C.
CN200410044883.2A 2004-05-26 2004-05-26 Method for treating oily cooking pollution Expired - Fee Related CN1240468C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN200410044883.2A CN1240468C (en) 2004-05-26 2004-05-26 Method for treating oily cooking pollution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN200410044883.2A CN1240468C (en) 2004-05-26 2004-05-26 Method for treating oily cooking pollution

Publications (2)

Publication Number Publication Date
CN1583229A true CN1583229A (en) 2005-02-23
CN1240468C CN1240468C (en) 2006-02-08

Family

ID=34601802

Family Applications (1)

Application Number Title Priority Date Filing Date
CN200410044883.2A Expired - Fee Related CN1240468C (en) 2004-05-26 2004-05-26 Method for treating oily cooking pollution

Country Status (1)

Country Link
CN (1) CN1240468C (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109595624A (en) * 2017-09-30 2019-04-09 江苏瑞丰科技实业有限公司 A kind of separation of oil smoke and gas cleaning processing technique
US12138614B1 (en) 2024-02-05 2024-11-12 King Faisal University Kaolin based zeolite a for rapid reduction of poultry litter odor

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109595624A (en) * 2017-09-30 2019-04-09 江苏瑞丰科技实业有限公司 A kind of separation of oil smoke and gas cleaning processing technique
US12138614B1 (en) 2024-02-05 2024-11-12 King Faisal University Kaolin based zeolite a for rapid reduction of poultry litter odor

Also Published As

Publication number Publication date
CN1240468C (en) 2006-02-08

Similar Documents

Publication Publication Date Title
CN103949153B (en) A kind of method and device utilizing light to help Fenton's reaction purifying smoke
CN108870492B (en) Central oil fume purification device
CN105731451A (en) A modification method of petroleum coke-based activated carbon and its application
CN203298370U (en) High temperature lampblack purification device
CN204447666U (en) A kind of smoke condensation device with dust-removal and desulfurizing denitration function
CN1240468C (en) Method for treating oily cooking pollution
CN101530743B (en) Oil smoke purifier applicable to downdraft kitchen ventilator
CN102000548A (en) Method for preparing modified active carbon adsorbent of low-concentration organic waste gas
CN116428599B (en) A pollution reduction and carbon reduction system for high-concentration VOCs waste gas at the open liquid surface of oily wastewater
CN207362144U (en) A kind of device for handling waste tire
Chen et al. Cytotoxicity and epithelial barrier toxicity of fine particles from residential biomass pellet burning
CN113398738A (en) Electronic industry waste gas treatment method
CN1140343C (en) Catalyst for purifying oil fume and its preparation method and application
CN115646999A (en) Method for converting calcium hydroxide pyrolysis waste circuit board into organic bromine
CN104707619B (en) Graphene/Cu-Mn-Ti composite catalyst, and preparation method and application thereof
CN109579016A (en) A kind of small rural consumer waste incineration purifying and dedusting device
CN105664603B (en) Desulfidation tail gas efficient pollution-free purification method in secondary lead smelting
CN107970921A (en) A kind of catalyst with catalysis organic exhaust gas combustion function and its preparation method and application and the method for catalysis organic exhaust gas burning
CN204710081U (en) A kind of chemical emission cyclic processing device
CN209519525U (en) A waste gas purification treatment device for asphalt processing
CN112480976B (en) A method for dry deep purification of blast furnace gas
CN100509118C (en) Cooking oil smoke degradation conversion device
CN206315627U (en) A kind of high-frequency induction heating technology exhaust treatment system
CN217698555U (en) Tail gas processing apparatus of high softening point pitch production
CN215027596U (en) Fire-proof material detects laboratory combustion exhaust gas treatment system

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20060208

Termination date: 20180526

CF01 Termination of patent right due to non-payment of annual fee