[go: up one dir, main page]

CN107164629A - A kind of aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting - Google Patents

A kind of aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting Download PDF

Info

Publication number
CN107164629A
CN107164629A CN201710274802.5A CN201710274802A CN107164629A CN 107164629 A CN107164629 A CN 107164629A CN 201710274802 A CN201710274802 A CN 201710274802A CN 107164629 A CN107164629 A CN 107164629A
Authority
CN
China
Prior art keywords
tail gas
sulfuric acid
hydrogenation catalyst
sodium carbonate
microwave
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.)
Pending
Application number
CN201710274802.5A
Other languages
Chinese (zh)
Inventor
曲雯雯
张家麟
徐盛明
叶小磊
彭金辉
张利波
郭胜惠
王璐
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.)
Kunming University of Science and Technology
Original Assignee
Kunming University of Science and Technology
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 Kunming University of Science and Technology filed Critical Kunming University of Science and Technology
Priority to CN201710274802.5A priority Critical patent/CN107164629A/en
Publication of CN107164629A publication Critical patent/CN107164629A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B1/00Preliminary treatment of ores or scrap
    • C22B1/02Roasting processes
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00Sulfur; Compounds thereof
    • C01B17/69Sulfur trioxide; Sulfuric acid
    • C01B17/74Preparation
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D7/00Carbonates of sodium, potassium or alkali metals in general
    • C01D7/07Preparation from the hydroxides
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B21/00Obtaining aluminium
    • C22B21/0007Preliminary treatment of ores or scrap or any other metal source
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B21/00Obtaining aluminium
    • C22B21/0015Obtaining aluminium by wet processes
    • C22B21/0023Obtaining aluminium by wet processes from waste materials
    • C22B21/003Obtaining aluminium by wet processes from waste materials from spent catalysts
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0407Leaching processes
    • C22B23/0415Leaching processes with acids or salt solutions except ammonium salts solutions
    • C22B23/043Sulfurated acids or salts thereof
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B34/00Obtaining refractory metals
    • C22B34/30Obtaining chromium, molybdenum or tungsten
    • C22B34/34Obtaining molybdenum
    • C22B34/345Obtaining molybdenum from spent catalysts
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/006Wet processes
    • C22B7/007Wet processes by acid leaching
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/80Compositional purity
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Manufacturing & Machinery (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Inorganic Chemistry (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Processing Of Solid Wastes (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

本发明涉及一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,属于环境保护和资源综合回收再利用领域。本发明将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,细磨至粒径不大于400目,在氧气氛围条件下,微波焙烧得到焙砂和尾气,尾气依次经氧化性溶液、去离子水、饱和氢氧化钠溶液处理得到稀硫酸和碳酸钠溶液,焙砂主要为金属氧化物,稀硫酸和碳酸钠溶液可作为该金属氧化物的浸出剂;本发明的废铝基加氢催化剂能充分氧化脱硫脱碳,有害尾气的零排放,并获得后续回收金属所需的浸出剂,实现了废铝基稀贵金属催化剂高效清洁循环利用。

The invention relates to a method for treating waste aluminum-based hydrogenation catalysts based on microwave oxygen-enriched roasting, and belongs to the fields of environmental protection and resource comprehensive recovery and reuse. In the present invention, the waste aluminum-based hydrogenation catalyst is subjected to deoiling treatment to obtain an oil-free waste aluminum-based hydrogenation catalyst, which is finely ground to a particle size of not more than 400 meshes, and is roasted by microwave under oxygen atmosphere conditions to obtain calcined sand and tail gas, and the tail gas is sequentially passed through Oxidizing solution, deionized water, saturated sodium hydroxide solution are processed to obtain dilute sulfuric acid and sodium carbonate solution, and calcined sand is mainly metal oxide, and dilute sulfuric acid and sodium carbonate solution can be used as the leaching agent of this metal oxide; Waste of the present invention The aluminum-based hydrogenation catalyst can fully oxidize, desulfurize and decarburize, produce zero emission of harmful tail gas, and obtain the leaching agent required for subsequent metal recovery, which realizes the efficient and clean recycling of waste aluminum-based rare metal catalysts.

Description

一种基于微波富氧焙烧的废铝基加氢催化剂处理方法A method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting

技术领域technical field

本发明涉及一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,属于环境保护和资源综合回收再利用领域。The invention relates to a method for treating waste aluminum-based hydrogenation catalysts based on microwave oxygen-enriched roasting, and belongs to the fields of environmental protection and resource comprehensive recovery and reuse.

背景技术Background technique

铝基催化剂是一种以γ-Al2O3为载体,钼、镍、钒、钴、钨等有价金属或其氧化物为活性组分的催化剂,广泛应用于石油化工行业原油的加氢脱硫精炼过程,以提高油品质量。但催化剂在使用一定周期后,因钒等金属沉积和二硫化碳中毒而失去活性不可再生。失活后的废催化剂含有约15-25%的硫、6-10%的碳以及大量有价金属,并且有价金属主要以硫化物的形式存在不利于回收。若不经处理直接填埋不仅造成资源的浪费而且还会因其中的重金属元素对环境造成严重污染。Aluminum-based catalyst is a catalyst with γ-Al 2 O 3 as the carrier and molybdenum, nickel, vanadium, cobalt, tungsten and other valuable metals or their oxides as active components. It is widely used in the hydrogenation of crude oil in the petrochemical industry Desulfurization refining process to improve oil quality. However, after a certain period of use, the catalyst loses its activity due to metal deposition such as vanadium and carbon disulfide poisoning and cannot be regenerated. The deactivated spent catalyst contains about 15-25% sulfur, 6-10% carbon and a large amount of valuable metals, and the presence of valuable metals mainly in the form of sulfide is not conducive to recovery. If it is directly landfilled without treatment, it will not only cause a waste of resources, but also cause serious pollution to the environment due to the heavy metal elements therein.

目前,处理这类废催化剂的方法主要有两种:一是作为固废直接地下填埋;二是先经高温火法焙烧预处理,除油、脱硫脱碳得到金属氧化物,再用湿法回收有价金属。前者污染土壤和地下水源,同时还会造成钼、镍、钒、钴,和钨等稀贵金属资源的流失。后者虽未造成资源浪费,但是由于直接火法焙烧难以精确控制相关条件,不可避免的产生难处理的复合金属氧化物及有害气体。At present, there are two main ways to deal with this kind of spent catalyst: one is to directly landfill it as solid waste; the other is to pretreat it by high-temperature fire roasting, degreasing, desulfurization and decarburization to obtain metal oxides, and then use wet method Recovery of valuable metals. The former pollutes soil and groundwater sources, and also causes the loss of rare and precious metal resources such as molybdenum, nickel, vanadium, cobalt, and tungsten. Although the latter does not cause waste of resources, it is difficult to accurately control the relevant conditions due to the direct fire roasting method, which inevitably produces difficult-to-handle composite metal oxides and harmful gases.

专利CN102367520A公开了一种从废铝基催化剂中综合回收钒的方法。将废铝基催化剂与碳酸钠按一定比例混合,在800~1200℃的高温下焙烧30~60min。该方法温度过高,所生成的氧化钼已经升华,虽然是回收钒,但却造成了钼资源的浪费,而且钠盐会对设备造成腐蚀,缩短设备的使用寿命。Patent CN102367520A discloses a method for comprehensively recovering vanadium from waste aluminum-based catalysts. The waste aluminum-based catalyst is mixed with sodium carbonate in a certain proportion, and roasted at a high temperature of 800-1200°C for 30-60 minutes. The temperature of this method is too high, and the generated molybdenum oxide has been sublimated. Although vanadium is recovered, it causes a waste of molybdenum resources, and the sodium salt will cause corrosion to the equipment and shorten the service life of the equipment.

专利CN 102042388B公开了一种含镍、钼废催化剂回收金属的方法,在空气中,300~550℃条件下焙烧1~10小时,去除废催化剂中油质物及硫和碳,该方法焙烧时间过长,能耗大,并且污染空气。专利CN 105274344A提及一种从废石油催化剂中回收钒和钼的方法,将废催化剂在空气中点燃,空烧温度为500~650℃,以达到去除废催化剂中硫和碳的目的,但由于废催化剂表面附着有大量原油,空气中点燃很难控制焙烧温度,会导致焙砂中生成难处理复合金属氧化物(CoMoO4、NiMoO4、NiAl2O4等),而影响后续金属的浸取回收。Patent CN 102042388B discloses a method for recovering metals from waste catalysts containing nickel and molybdenum. It is roasted in the air at 300-550°C for 1-10 hours to remove oily substances, sulfur and carbon in the spent catalysts. The roasting time of this method is too long. long, consumes a lot of energy, and pollutes the air. Patent CN 105274344A mentions a method for recovering vanadium and molybdenum from waste petroleum catalysts. The waste catalyst is ignited in the air at a temperature of 500-650°C to achieve the purpose of removing sulfur and carbon in the waste catalyst. However, due to There is a large amount of crude oil attached to the surface of the spent catalyst, and it is difficult to control the calcination temperature when it is ignited in the air, which will lead to the generation of refractory composite metal oxides (CoMoO 4 , NiMoO 4 , NiAl 2 O 4 , etc.) in the calcine, which will affect the leaching of subsequent metals Recycle.

专利CN 105274343A公开了一种从石油加氢废催化剂中提取钨和镍的方法,将磨细至一定粒度的废催化剂至于马弗炉中,在600~800℃的条件下氧化焙烧3~5小时,该方法焙烧时间长,能耗大,产生有害气体污染空气。Patent CN 105274343A discloses a method for extracting tungsten and nickel from spent petroleum hydrogenation catalysts. Put the spent catalysts that have been ground to a certain particle size in a muffle furnace, and oxidize and roast them at 600-800°C for 3-5 hours , This method takes a long time to roast, consumes a lot of energy, and produces harmful gases that pollute the air.

以上从废催化剂中去硫和碳的方法存在以下几个缺点:a. 处理时间长,焙烧温度高,能耗高;b. 处理温度难以控制,易生成难处理复合金属氧化物;c. 对焙烧设备的耐腐蚀性要求高;d.未对废气进行处理,污染环境。The above methods for removing sulfur and carbon from spent catalysts have the following disadvantages: a. The treatment time is long, the roasting temperature is high, and the energy consumption is high; b. The treatment temperature is difficult to control, and it is easy to generate complex metal oxides; Roasting equipment requires high corrosion resistance; d. Waste gas is not treated, polluting the environment.

发明内容Contents of the invention

针对现有技术的不足,本发明提供了一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,该方法具有能耗低、工艺设备简单、处理时间短的特点,避免了难处理复合金属氧化物的生成,实现了焙烧尾气的无害化综合利用。Aiming at the deficiencies of the prior art, the present invention provides a waste aluminum-based hydrogenation catalyst treatment method based on microwave oxygen-enriched roasting. The formation of metal oxides realizes the harmless comprehensive utilization of roasting tail gas.

本发明的技术方案是:在富氧氛围下,对废铝基加氢催化剂进行微波焙烧,去除废催化剂中的硫和碳,实现对废催化剂中有价金属的氧化脱硫,得到易于浸出的金属氧化物,金属氧化物可进行湿法浸出回收金属,焙烧尾气无害化综合处理得到硫酸和碳酸钠溶液,硫酸和碳酸钠溶液均可作为金属氧化物的浸出剂。The technical scheme of the present invention is: in an oxygen-enriched atmosphere, carry out microwave roasting on the waste aluminum-based hydrogenation catalyst to remove sulfur and carbon in the waste catalyst, realize oxidative desulfurization of valuable metals in the waste catalyst, and obtain easily leached metal Oxides and metal oxides can be recovered by wet leaching, and sulfuric acid and sodium carbonate solutions can be obtained through harmless comprehensive treatment of roasting tail gas. Both sulfuric acid and sodium carbonate solutions can be used as leaching agents for metal oxides.

一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:A method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst;

(2)将步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于400目;(2) finely grinding the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is not greater than 400 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到焙砂和尾气Ⅰ;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain calcined sand and tail gas I;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液处理得到稀硫酸Ⅰ和尾气Ⅱ;(4) Tail gas I obtained in step (3) is treated with an oxidative solution to obtain dilute sulfuric acid I and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ和步骤(5)所得稀硫酸Ⅱ合并,蒸馏得到浓硫酸;将步骤(6)所得碳酸钠溶液蒸发结晶得到碳酸钠晶体;(7) combining dilute sulfuric acid I obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distilling to obtain concentrated sulfuric acid; evaporating and crystallizing the sodium carbonate solution obtained in step (6) to obtain sodium carbonate crystals;

(8)将步骤(7)所得碳酸钠晶体加入到去离子水中配制成浓度0.5~2.5mol/L的碳酸钠溶液Ⅱ,将步骤(7)所得浓硫酸配制成浓度1~3mol/L的稀硫酸溶液Ⅲ;(8) Add the sodium carbonate crystals obtained in step (7) into deionized water to prepare sodium carbonate solution II with a concentration of 0.5~2.5mol/L, and prepare the concentrated sulfuric acid obtained in step (7) into a dilute solution with a concentration of 1~3mol/L. Sulfuric acid solution III;

(9)将步骤(3)所得焙砂加入到步骤(8)所得碳酸钠溶液Ⅱ或稀硫酸溶液Ⅲ中,在温度为75~95℃、搅拌条件下,反应2~5h得到金属浸出液;(9) Add the calcined sand obtained in step (3) to the sodium carbonate solution II or dilute sulfuric acid solution III obtained in step (8), and react for 2 to 5 hours at a temperature of 75-95°C under stirring conditions to obtain a metal leachate;

所述步骤(3)中微波频率为2450MHz,微波功率为700~2000W,微波焙烧温度为500~700℃,焙烧时间为15 ~75min;In the step (3), the microwave frequency is 2450MHz, the microwave power is 700-2000W, the microwave roasting temperature is 500-700°C, and the roasting time is 15-75min;

所述步骤(4)中氧化性溶液为过氧化氢或次氯酸钠溶液,氧化性溶液的质量浓度为10~30%;The oxidizing solution in the step (4) is hydrogen peroxide or sodium hypochlorite solution, and the mass concentration of the oxidizing solution is 10-30%;

所述步骤(9)中焙砂与碳酸钠溶液Ⅱ的固液比g:ml为1:(5~10),焙砂与稀硫酸溶液的固液比g:ml为1:(4~9);In the step (9), the solid-to-liquid ratio g:ml of calcined sand and sodium carbonate solution II is 1:(5~10), and the solid-liquid ratio g:ml of calcined sand and dilute sulfuric acid solution is 1:(4~9 );

所述脱油处理的方法按照申请号201710033821.9的专利“一种脱除废铝基加氢催化剂表面油质物的方法”进行脱油处理。The deoiling treatment method is carried out according to the patent application number 201710033821.9 "A method for removing oily substances on the surface of waste aluminum-based hydrogenation catalyst".

本发明的有益效果是:The beneficial effects of the present invention are:

(1)本发明采用微波富氧焙烧废催化剂,能充分氧化脱硫脱碳,有害尾气的零排放,并获得后续回收金属所需的浸出剂,实现了废铝基稀贵金属催化剂高效清洁循环利用;(1) The present invention adopts microwave oxygen-enriched roasting of spent catalysts, which can fully oxidize, desulfurize and decarburize, eliminate harmful exhaust gas, and obtain the leaching agent required for subsequent metal recovery, realizing the efficient, clean and recyclable utilization of waste aluminum-based rare and precious metal catalysts;

(2)本发明的工艺无毒无害、能耗低、工艺简单,对设备依赖度低,一台可通气氛微波反应装置及相应的尾气回收处理装置即可完成;(2) The process of the present invention is non-toxic and harmless, low energy consumption, simple process, and low dependence on equipment, and can be completed by a microwave reaction device that can pass through the atmosphere and a corresponding tail gas recovery and treatment device;

(3)本方法的焙烧物料先期经过脱油处理,焙烧温度易于控制,有效地避免了因温度过高或温度上下波动而生成难分解多金属复合氧化物,进而有效促进了后续稀贵金属的浸取回收;(3) The roasted material of this method has been deoiled in advance, and the roasting temperature is easy to control, which effectively avoids the formation of refractory multi-metal composite oxides due to excessive temperature or fluctuations in temperature, and effectively promotes the subsequent leaching of rare and precious metals. Take back;

(4)本发明方法同时实现了焙烧尾气的综合回收利用,降低了成本,保护环境。(4) The method of the present invention realizes the comprehensive recovery and utilization of the roasting tail gas at the same time, reduces the cost and protects the environment.

附图说明Description of drawings

图1为本发明的工艺流程图。Fig. 1 is a process flow diagram of the present invention.

具体实施方式detailed description

下面结合具体实施方式对本发明作进一步详细说明,但本发明的保护范围并不限于所述内容。The present invention will be described in further detail below in conjunction with specific embodiments, but the protection scope of the present invention is not limited to the content described.

实施例1:如图1所示,一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:Embodiment 1: As shown in Figure 1, a method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,其中无油废铝基加氢催化剂的含碳率为15.6%,含硫率为6.5%;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst, wherein the oil-free waste aluminum-based hydrogenation catalyst has a carbon content of 15.6% and a sulfur content of 6.5%;

(2)将20g步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于400目;(2) Finely grind 20 g of the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is no greater than 400 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到金属氧化物和尾气Ⅰ,其中微波频率为2450MHz,微波功率为700W,焙烧温度为500℃,焙烧时间为15min;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain metal oxide and tail gas I, wherein the microwave frequency is 2450MHz, the microwave power is 700W, the roasting temperature is 500°C, and the roasting time is 15min;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液(氧化性溶液为过氧化氢溶液,过氧化氢溶液的质量浓度为30%)处理得到稀硫酸Ⅰ和尾气Ⅱ;(4) Tail gas I obtained in step (3) is treated with an oxidizing solution (the oxidizing solution is a hydrogen peroxide solution, and the mass concentration of the hydrogen peroxide solution is 30%) to obtain dilute sulfuric acid I and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液Ⅰ和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution I and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ和步骤(5)所得稀硫酸Ⅱ合并,蒸馏浓缩得到质量浓度为65%的浓硫酸;将步骤(6)所得碳酸钠溶液Ⅰ蒸发结晶得到碳酸钠晶体;(7) Combine dilute sulfuric acid I obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distill and concentrate to obtain concentrated sulfuric acid with a mass concentration of 65%; evaporate and crystallize sodium carbonate solution I obtained in step (6) to obtain sodium carbonate crystal;

(8)将步骤(7)所得碳酸钠晶体加入到去离子水中配制成浓度0.5mol/L的碳酸钠溶液Ⅱ;(8) adding sodium carbonate crystals obtained in step (7) into deionized water to prepare sodium carbonate solution II with a concentration of 0.5mol/L;

(9)将步骤(3)所得焙砂加入到步骤(8)所得碳酸钠溶液Ⅱ中,其中焙砂与碳酸钠溶液Ⅱ的固液比g:ml为1: 5,在温度为75 ℃、搅拌速度为200r/min的条件下,反应2 h,得到金属Mo的浸出液;(9) Add the calcined sand obtained in step (3) to the sodium carbonate solution II obtained in step (8), wherein the solid-to-liquid ratio g:ml of the calcined sand to the sodium carbonate solution II is 1: 5, at a temperature of 75 °C, Under the condition of stirring speed of 200r/min, react for 2 h to obtain the leaching solution of metal Mo;

本实施例中焙砂的质量为15.248g,焙砂的含碳率为1.23%,含硫率1.63%,经计算去油废铝基催化剂的脱碳率为93.9%,脱硫率为83.4%,可得到质量浓度为65%的硫酸,纯度为97.8%的碳酸钠晶体,金属Mo的浸出率为96.3%。The quality of calcined sand in the present embodiment is 15.248g, and the carbon content rate of calcined sand is 1.23%, and sulfur content rate is 1.63%, and the decarburization rate of oil-removing waste aluminum-based catalyst is calculated as 93.9%, and the desulfurization rate is 83.4%. Sulfuric acid with a mass concentration of 65% and sodium carbonate crystals with a purity of 97.8% can be obtained, and the leaching rate of metal Mo is 96.3%.

实施例2:如图1所示,一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:Embodiment 2: As shown in Figure 1, a method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,其中无油废铝基加氢催化剂的含碳率为15.6%,含硫率为8.3%;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst, wherein the oil-free waste aluminum-based hydrogenation catalyst has a carbon content of 15.6% and a sulfur content of 8.3%;

(2)将20g步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于200目;(2) Finely grind 20 g of the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is not greater than 200 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到金属氧化物和尾气Ⅰ,其中微波频率为2450MHz,微波功率为1200W,焙烧温度为550℃,焙烧时间为30min;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain metal oxide and tail gas I, wherein the microwave frequency is 2450MHz, the microwave power is 1200W, the roasting temperature is 550°C, and the roasting time is 30min;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液(氧化性溶液为次氯酸钠溶液,次氯酸钠溶液的质量浓度为10%)处理得到稀硫酸Ⅰ、稀盐酸和尾气Ⅱ;(4) Tail gas I obtained in step (3) is treated with an oxidizing solution (the oxidizing solution is sodium hypochlorite solution, and the mass concentration of sodium hypochlorite solution is 10%) to obtain dilute sulfuric acid I, dilute hydrochloric acid and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液Ⅰ和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution I and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ、稀盐酸和步骤(5)所得稀硫酸Ⅱ合并,蒸馏得到质量浓度为68%的浓硫酸;将步骤(6)所得碳酸钠溶液Ⅰ蒸发结晶得到碳酸钠晶体;(7) Combine dilute sulfuric acid I, dilute hydrochloric acid obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distill to obtain concentrated sulfuric acid with a mass concentration of 68%; evaporate and crystallize sodium carbonate solution I obtained in step (6) to obtain sodium carbonate crystals;

(8)将步骤(7)所得浓硫酸加入到去离子水中配制成浓度1 mol/L的稀硫酸溶液Ⅲ;(8) Add the concentrated sulfuric acid obtained in step (7) to deionized water to prepare dilute sulfuric acid solution III with a concentration of 1 mol/L;

(9)将步骤(3)所得焙砂加入到步骤(8)所得稀硫酸溶液Ⅲ中,其中焙砂与稀硫酸溶液Ⅲ的固液比g:ml为1: 4,在温度为80℃、搅拌速度为200 r/min的条件下,反应3 h,得到金属Mo、Ni、Co、Al的浸出液;(9) Add the calcined sand obtained in step (3) to the dilute sulfuric acid solution III obtained in step (8), wherein the solid-to-liquid ratio g:ml of the calcined sand to the dilute sulfuric acid solution III is 1: 4, and when the temperature is 80°C, Under the condition of stirring speed of 200 r/min, react for 3 h to obtain the leaching solution of metal Mo, Ni, Co, Al;

本实施例中焙砂的质量为14.762g,焙砂的含碳率为1.13%,含硫率1.55%,经计算去油废铝基催化剂的脱碳率为94.7%,脱硫率为86.2%,可得到质量浓度为68%的硫酸,纯度为95.5%的碳酸钠晶体,金属Mo、Ni、Co、Al的浸出率分别为95.7%、97.1%,97.4%和93.0%。The quality of calcined sand in the present embodiment is 14.762g, and the carbon content rate of calcined sand is 1.13%, and sulfur content rate is 1.55%, after calculation, the decarburization rate of deoiled waste aluminum-based catalyst is 94.7%, and the desulfurization rate is 86.2%, Sulfuric acid with a mass concentration of 68% and sodium carbonate crystals with a purity of 95.5% can be obtained. The leaching rates of metals Mo, Ni, Co, and Al are 95.7%, 97.1%, 97.4% and 93.0%, respectively.

实施例3:如图1所示,一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:Embodiment 3: As shown in Figure 1, a method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,其中无油废铝基加氢催化剂的含碳率为18.2%,含硫率为10.0%;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst, wherein the oil-free waste aluminum-based hydrogenation catalyst has a carbon content of 18.2% and a sulfur content of 10.0%;

(2)将20g步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于80目;(2) Finely grind 20 g of the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is no greater than 80 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到金属氧化物和尾气Ⅰ,其中微波频率为2450MHz,微波功率为1700W,焙烧温度为700℃,焙烧时间为45min;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain metal oxide and tail gas I, wherein the microwave frequency is 2450MHz, the microwave power is 1700W, the roasting temperature is 700°C, and the roasting time is 45min;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液(氧化性溶液为次氯酸钠溶液,次氯酸钠溶液的质量浓度为10%)处理得到稀硫酸Ⅰ、稀盐酸和尾气Ⅱ;(4) Tail gas I obtained in step (3) is treated with an oxidizing solution (the oxidizing solution is sodium hypochlorite solution, and the mass concentration of sodium hypochlorite solution is 10%) to obtain dilute sulfuric acid I, dilute hydrochloric acid and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液Ⅰ和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution I and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ、稀盐酸和步骤(5)所得稀硫酸Ⅱ合并,蒸馏得到质量浓度为66%的浓硫酸;将步骤(6)所得稀硫酸溶液Ⅰ蒸发结晶得到碳酸钠晶体;(7) Combine dilute sulfuric acid I, dilute hydrochloric acid obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distill to obtain concentrated sulfuric acid with a mass concentration of 66%; evaporate and crystallize dilute sulfuric acid solution I obtained in step (6) to obtain sodium carbonate crystals;

(8)将步骤(7)所得浓硫酸加入到去离子水中配制成浓度2 mol/L的稀硫酸溶液Ⅲ;(8) Add the concentrated sulfuric acid obtained in step (7) to deionized water to prepare dilute sulfuric acid solution III with a concentration of 2 mol/L;

(9)将步骤(3)所得焙砂加入到步骤(8)所得稀硫酸溶液Ⅲ中,其中焙砂与稀硫酸溶液Ⅲ的固液比g:ml为1: 7,在温度为95 ℃、搅拌速度为200 r/min的条件下,反应4 h,得到金属Mo、Ni、Co、Al的浸出液;(9) Add the calcined sand obtained in step (3) to the dilute sulfuric acid solution III obtained in step (8), wherein the solid-to-liquid ratio g:ml of the calcined sand to the dilute sulfuric acid solution III is 1: 7, at a temperature of 95 °C, Under the condition of stirring speed of 200 r/min, react for 4 h to obtain the leaching solution of metal Mo, Ni, Co, Al;

本实施例中焙砂的质量为14.436g,焙砂的含碳率为1.07%,含硫率1.42%,经计算去油废铝基催化剂的脱碳率为95.8%,脱硫率为89.8%,可得到质量浓度为66%的硫酸,纯度为98.2%的碳酸钠晶体,金属Mo、Ni、Co、Al的浸出率分别为96.9%、98.7%,99.1%和94.6%。The quality of calcined sand in the present embodiment is 14.436g, and the carbon content rate of calcined sand is 1.07%, and the sulfur content rate is 1.42%. After calculation, the decarburization rate of deoiled waste aluminum-based catalyst is 95.8%, and the desulfurization rate is 89.8%. Sulfuric acid with a mass concentration of 66% can be obtained, sodium carbonate crystals with a purity of 98.2% can be obtained, and the leaching rates of metal Mo, Ni, Co, and Al are 96.9%, 98.7%, 99.1% and 94.6%, respectively.

实施例4:如图1所示,一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:Embodiment 4: As shown in Figure 1, a method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,其中无油废铝基加氢催化剂的含碳率为20.0%,含硫率为8.3%;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst, wherein the oil-free waste aluminum-based hydrogenation catalyst has a carbon content of 20.0% and a sulfur content of 8.3%;

(2)将20g步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于150目;(2) Finely grind 20 g of the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is no greater than 150 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到金属氧化物和尾气Ⅰ,其中微波频率为2450MHz,微波功率为1200W,焙烧温度为650℃,焙烧时间为60min;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain metal oxide and tail gas I, wherein the microwave frequency is 2450MHz, the microwave power is 1200W, the roasting temperature is 650°C, and the roasting time is 60min;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液(氧化性溶液为过氧化氢溶液,过氧化氢溶液的质量浓度为25%)处理得到稀硫酸Ⅰ和尾气Ⅱ;(4) Tail gas I obtained in step (3) is treated with an oxidizing solution (the oxidizing solution is a hydrogen peroxide solution, and the mass concentration of the hydrogen peroxide solution is 25%) to obtain dilute sulfuric acid I and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液Ⅰ和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution I and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ和步骤(5)所得稀硫酸Ⅱ合并,蒸馏得到质量浓度为68%的浓硫酸;将步骤(6)所得碳酸钠溶液Ⅰ蒸发结晶得到碳酸钠晶体;(7) Combine dilute sulfuric acid I obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distill to obtain concentrated sulfuric acid with a mass concentration of 68%; evaporate and crystallize sodium carbonate solution I obtained in step (6) to obtain sodium carbonate crystals ;

(8)将步骤(7)所得碳酸钠晶体加入到去离子水中配制成浓度1.5 mol/L的碳酸钠溶液Ⅱ;(8) Add the sodium carbonate crystals obtained in step (7) into deionized water to prepare sodium carbonate solution II with a concentration of 1.5 mol/L;

(9)将步骤(3)所得焙砂加入到步骤(8)所得碳酸钠溶液Ⅱ中,其中焙砂与碳酸钠溶液Ⅱ的固液比g:ml为1: 6,在温度为80℃、搅拌速度为200 r/min的条件下,反应5 h,得到金属Mo的浸出液;(9) Add the calcined sand obtained in step (3) to the sodium carbonate solution II obtained in step (8), wherein the solid-to-liquid ratio g:ml of the calcined sand to the sodium carbonate solution II is 1: 6, at a temperature of 80°C, Under the condition of a stirring speed of 200 r/min, react for 5 h to obtain a leaching solution of metal Mo;

本实施例中焙砂的质量为14.538g,焙砂的含碳率为0.83%,含硫率1.14%,经计算去油废铝基催化剂的脱碳率为97.0%,脱硫率为90.0%,可得到质量浓度为68%的硫酸,纯度为97.6%的碳酸钠晶体,金属 Mo的浸出率为97.2 %。The quality of calcined sand in the present embodiment is 14.538g, and the carbon content rate of calcined sand is 0.83%, and the sulfur content rate is 1.14%, after calculation, the decarburization rate of deoiled waste aluminum-based catalyst is 97.0%, and the desulfurization rate is 90.0%, Can obtain the sulfuric acid that mass concentration is 68%, the sodium carbonate crystal that purity is 97.6%, the leaching rate of metal Mo is 97.2%.

实施例5:如图1所示,一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:Embodiment 5: As shown in Figure 1, a method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,其中无油废铝基加氢催化剂的含碳率为20.0%,含硫率为6.5%;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst, wherein the oil-free waste aluminum-based hydrogenation catalyst has a carbon content of 20.0% and a sulfur content of 6.5%;

(2)将20g步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于300目;(2) Finely grind 20 g of the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is not greater than 300 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到金属氧化物和尾气Ⅰ,其中微波频率为2450MHz,微波功率为700W,焙烧温度为700℃,焙烧时间为75min;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain metal oxide and tail gas I, wherein the microwave frequency is 2450MHz, the microwave power is 700W, the roasting temperature is 700°C, and the roasting time is 75min;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液(氧化性溶液为次氯酸钠溶液,次氯酸钠溶液的质量浓度为10%)处理得到稀硫酸Ⅰ,稀盐酸和尾气Ⅱ;(4) The tail gas I obtained in step (3) is treated with an oxidizing solution (the oxidizing solution is a sodium hypochlorite solution, and the mass concentration of the sodium hypochlorite solution is 10%) to obtain dilute sulfuric acid I, dilute hydrochloric acid and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液Ⅰ和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution I and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ、稀盐酸和步骤(5)所得稀硫酸Ⅱ合并,蒸馏得到质量浓度为68%的浓硫酸;将步骤(6)所得碳酸钠溶液Ⅰ蒸发结晶得到碳酸钠晶体;(7) Combine dilute sulfuric acid I, dilute hydrochloric acid obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distill to obtain concentrated sulfuric acid with a mass concentration of 68%; evaporate and crystallize sodium carbonate solution I obtained in step (6) to obtain sodium carbonate crystals;

(8)将步骤(7)所得碳酸钠晶体加入到去离子水中配制成浓度2.0mol/L的碳酸钠溶液Ⅱ;(8) Add the sodium carbonate crystals obtained in step (7) into deionized water to prepare sodium carbonate solution II with a concentration of 2.0mol/L;

(9)将步骤(3)所得焙砂加入到步骤(8)所得碳酸钠溶液Ⅱ中,其中焙砂与碳酸钠溶液Ⅱ的固液比g:ml为1: 8,在温度为85 ℃、搅拌速度为200 r/min的条件下,反应3h,得到金属Mo的浸出液;(9) Add the calcined sand obtained in step (3) to the sodium carbonate solution II obtained in step (8), wherein the solid-to-liquid ratio g:ml of the calcined sand to the sodium carbonate solution II is 1: 8, at a temperature of 85 °C, Under the condition that the stirring speed is 200 r/min, react for 3 hours to obtain the leaching solution of metal Mo;

本实施例中焙砂的质量为14.579g,焙砂的含碳率为1.10%,含硫率1.38%,经计算去油废铝基催化剂的脱碳率为96.0%,脱硫率为84.5%,可得到质量浓度为68%的硫酸,纯度为97.9%的碳酸钠晶体,金属Mo的浸出率为98.4%。The quality of calcined sand in the present embodiment is 14.579g, and the carbon content rate of calcined sand is 1.10%, and sulfur content rate is 1.38%. After calculation, the decarburization rate of deoiled waste aluminum-based catalyst is 96.0%, and the desulfurization rate is 84.5%. Sulfuric acid with a mass concentration of 68%, sodium carbonate crystals with a purity of 97.9%, and a leaching rate of metal Mo of 98.4% can be obtained.

实施例6:如图1所示,一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:Embodiment 6: As shown in Figure 1, a method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,其中无油废铝基加氢催化剂的含碳率为18.2%,含硫率为8.3%;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst, wherein the oil-free waste aluminum-based hydrogenation catalyst has a carbon content of 18.2% and a sulfur content of 8.3%;

(2)将20g步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于250目;(2) Finely grind 20 g of the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is no greater than 250 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到金属氧化物和尾气Ⅰ,其中微波频率为2450MHz,微波功率为1500W,焙烧温度为650℃,焙烧时间为30min;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain metal oxide and tail gas I, wherein the microwave frequency is 2450MHz, the microwave power is 1500W, the roasting temperature is 650°C, and the roasting time is 30min;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液(氧化性溶液为过氧化氢溶液,过氧化氢溶液的质量浓度为25%)处理得到稀硫酸Ⅰ和尾气Ⅱ;(4) Tail gas I obtained in step (3) is treated with an oxidizing solution (the oxidizing solution is a hydrogen peroxide solution, and the mass concentration of the hydrogen peroxide solution is 25%) to obtain dilute sulfuric acid I and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液Ⅰ和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution I and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ和步骤(5)所得稀硫酸Ⅱ合并,蒸馏得到质量浓度为69%的浓硫酸;将步骤(6)所得碳酸钠溶液Ⅰ蒸发结晶得到碳酸钠晶体;(7) Combine dilute sulfuric acid I obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distill to obtain concentrated sulfuric acid with a mass concentration of 69%; evaporate and crystallize sodium carbonate solution I obtained in step (6) to obtain sodium carbonate crystals ;

(8)将步骤(7)所得碳酸钠晶体加入到去离子水中配制成浓度1.8mol/L的碳酸钠溶液Ⅱ;(8) Add the sodium carbonate crystals obtained in step (7) into deionized water to prepare sodium carbonate solution II with a concentration of 1.8mol/L;

(9)将步骤(3)所得焙砂加入到步骤(8)所得碳酸钠溶液Ⅱ中,其中焙砂与碳酸钠溶液Ⅱ的固液比g:ml为1: 10,在温度为95℃、搅拌速度为200 r/min的条件下,反应4 h,得到金属Mo的浸出液;(9) Add the calcined sand obtained in step (3) to the sodium carbonate solution II obtained in step (8), wherein the solid-to-liquid ratio g:ml of the calcined sand to the sodium carbonate solution II is 1: 10, and the temperature is 95°C, Under the condition of stirring speed of 200 r/min, react for 4 h to obtain the leaching solution of metal Mo;

本实施例中焙砂的质量为14.245g,焙砂的含碳率为0.73%,含硫率1.16%,经计算去油废铝基催化剂的脱碳率为97.1%,脱硫率为90.0%,可得到质量浓度为69%的硫酸,纯度为98.4%的碳酸钠晶体,金属Mo的浸出率为93.9%。The quality of calcined sand in the present embodiment is 14.245g, and the carbon content rate of calcined sand is 0.73%, and the sulfur content rate is 1.16%, after calculation, the decarburization rate of deoiled waste aluminum-based catalyst is 97.1%, and the desulfurization rate is 90.0%, Sulfuric acid with a mass concentration of 69%, sodium carbonate crystals with a purity of 98.4%, and a leaching rate of metal Mo of 93.9% can be obtained.

实施例7:如图1所示,一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:Embodiment 7: As shown in Figure 1, a method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,其中无油废铝基加氢催化剂的含碳率为18.2%,含硫率为8.3%;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst, wherein the oil-free waste aluminum-based hydrogenation catalyst has a carbon content of 18.2% and a sulfur content of 8.3%;

(2)将20g步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于100目;(2) Finely grind 20 g of the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is not greater than 100 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到金属氧化物和尾气Ⅰ,其中微波频率为2450MHz,微波功率为1500W,焙烧温度为650℃,焙烧时间为75min;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain metal oxide and tail gas I, wherein the microwave frequency is 2450MHz, the microwave power is 1500W, the roasting temperature is 650°C, and the roasting time is 75min;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液(氧化性溶液为次氯酸钠溶液,次氯酸钠溶液的质量浓度为10%)处理得到稀硫酸Ⅰ,稀盐酸和尾气Ⅱ;(4) The tail gas I obtained in step (3) is treated with an oxidizing solution (the oxidizing solution is a sodium hypochlorite solution, and the mass concentration of the sodium hypochlorite solution is 10%) to obtain dilute sulfuric acid I, dilute hydrochloric acid and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液Ⅰ和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution I and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ、稀盐酸和步骤(5)所得稀硫酸Ⅱ合并,蒸馏得到质量浓度为70%的浓硫酸;将步骤(6)所得碳酸钠溶液Ⅰ蒸发结晶得到碳酸钠晶体;(7) Combine dilute sulfuric acid I, dilute hydrochloric acid obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distill to obtain concentrated sulfuric acid with a mass concentration of 70%; evaporate and crystallize sodium carbonate solution I obtained in step (6) to obtain sodium carbonate crystals;

(8)将步骤(7)所得浓硫酸加入到去离子水中配制成浓度2.5mol/L的稀硫酸溶液Ⅲ;(8) Add the concentrated sulfuric acid obtained in step (7) into deionized water to prepare dilute sulfuric acid solution III with a concentration of 2.5mol/L;

(9)将步骤(3)所得焙砂加入到步骤(8)所得稀硫酸溶液Ⅲ中,其中焙砂与稀硫酸溶液Ⅲ的固液比g:ml为1:8,在温度为80℃、搅拌速度为200r/min的条件下,反应3.5h,得到金属Mo、Ni、Co、Al的浸出液;(9) Add the calcined sand obtained in step (3) to the dilute sulfuric acid solution III obtained in step (8), wherein the solid-to-liquid ratio g:ml of the calcined sand to the dilute sulfuric acid solution III is 1:8, at a temperature of 80°C, Under the condition of stirring speed of 200r/min, react for 3.5h to obtain the leaching solution of metal Mo, Ni, Co, Al;

本实施例中焙砂的质量为13.726g,焙砂的含碳率为0.52%,含硫率0.78%,经计算去油废铝基催化剂的脱碳率为98.0%,脱硫率为91.7%,可得到质量浓度为70%的硫酸,纯度为97.8%的碳酸钠晶体,Mo的浸出率为98.6%,Al的浸出率为97.4%,Co的浸出率为99.2%,Ni的浸出率为99.1%。The quality of calcined sand in the present embodiment is 13.726g, and the carbon content rate of calcined sand is 0.52%, and sulfur content rate is 0.78%, after calculation, the decarburization rate of deoiled waste aluminum-based catalyst is 98.0%, and the desulfurization rate is 91.7%, Sulfuric acid with a mass concentration of 70% can be obtained, and sodium carbonate crystals with a purity of 97.8% can be obtained. The leaching rate of Mo is 98.6%, the leaching rate of Al is 97.4%, the leaching rate of Co is 99.2%, and the leaching rate of Ni is 99.1%. .

实施例8:如图1所示,一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:Embodiment 8: As shown in Figure 1, a method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,其中无油废铝基加氢催化剂的含碳率为18.2%,含硫率为6.5%;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst, wherein the oil-free waste aluminum-based hydrogenation catalyst has a carbon content of 18.2% and a sulfur content of 6.5%;

(2)将20g步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于150目;(2) Finely grind 20 g of the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is no greater than 150 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到焙砂和尾气Ⅰ,其中微波频率为2450MHz,微波功率为2000W,焙烧温度为600℃,焙烧时间为45min;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain calcined sand and tail gas I, wherein the microwave frequency is 2450MHz, the microwave power is 2000W, the roasting temperature is 600°C, and the roasting time is 45min;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液(氧化性溶液为次氯酸钠溶液,次氯酸钠溶液的质量浓度为10%)处理得到稀硫酸Ⅰ,稀盐酸和尾气Ⅱ;(4) The tail gas I obtained in step (3) is treated with an oxidizing solution (the oxidizing solution is a sodium hypochlorite solution, and the mass concentration of the sodium hypochlorite solution is 10%) to obtain dilute sulfuric acid I, dilute hydrochloric acid and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液Ⅰ和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution I and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ、稀盐酸和步骤(5)所得稀硫酸Ⅱ合并,蒸馏得到质量浓度为69%的浓硫酸;将步骤(6)所得碳酸钠溶液Ⅰ蒸发结晶得到碳酸钠晶体;(7) Combine dilute sulfuric acid I, dilute hydrochloric acid obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distill to obtain concentrated sulfuric acid with a mass concentration of 69%; evaporate and crystallize sodium carbonate solution I obtained in step (6) to obtain sodium carbonate crystals;

(8)将步骤(7)所得碳酸钠晶体加入到去离子水中配制成浓度2.5mol/L的碳酸钠溶液Ⅱ;(8) adding sodium carbonate crystals obtained in step (7) into deionized water to prepare sodium carbonate solution II with a concentration of 2.5mol/L;

(9)将步骤(3)所得焙砂加入到步骤(8)所得碳酸钠溶液Ⅱ中,其中焙砂与碳酸钠溶液Ⅱ的固液比g:ml为1:9,在温度为90℃、搅拌速度为200r/min的条件下,反应3.5h,得到金属Mo的浸出液;(9) Add the calcined sand obtained in step (3) to the sodium carbonate solution II obtained in step (8), wherein the solid-to-liquid ratio g:ml of the calcined sand to the sodium carbonate solution II is 1:9, at a temperature of 90°C, Under the condition of stirring speed of 200r/min, react for 3.5h to obtain the leaching solution of metal Mo;

本实施例中焙砂的质量为13.838g,焙砂的含碳率为0.66%,含硫率0.98%,经计算去油废铝基催化剂的脱碳率为97.7%,脱硫率为93.2%,可得到质量浓度为69%的硫酸,纯度为98.1%的碳酸钠晶体;金属Mo的浸出率为92.3%。The quality of calcined sand in the present embodiment is 13.838g, and the carbon content rate of calcined sand is 0.66%, and sulfur content rate is 0.98%, after calculation, the decarburization rate of deoiled waste aluminum-based catalyst is 97.7%, and the desulfurization rate is 93.2%, Sulfuric acid with a mass concentration of 69% and sodium carbonate crystals with a purity of 98.1% can be obtained; the leaching rate of metal Mo is 92.3%.

实施例9:如图1所示,一种基于微波富氧焙烧的废铝基加氢催化剂处理方法,具体步骤如下:Embodiment 9: As shown in Figure 1, a method for treating waste aluminum-based hydrogenation catalyst based on microwave oxygen-enriched roasting, the specific steps are as follows:

(1)将废铝基加氢催化剂进行脱油处理得到无油废铝基加氢催化剂,其中无油废铝基加氢催化剂的含碳率为15.6%,含硫率为10.0%;(1) Deoiling the waste aluminum-based hydrogenation catalyst to obtain an oil-free waste aluminum-based hydrogenation catalyst, wherein the oil-free waste aluminum-based hydrogenation catalyst has a carbon content of 15.6% and a sulfur content of 10.0%;

(2)将20g步骤(1)所得无油废铝基加氢催化剂细磨至粒径不大于200目;(2) Finely grind 20 g of the oil-free waste aluminum-based hydrogenation catalyst obtained in step (1) until the particle size is not greater than 200 mesh;

(3)在氧气氛围条件下,将步骤(2)所得产物进行微波焙烧得到金属氧化物和尾气Ⅰ,其中微波频率为2450MHz,微波功率为1200W,焙烧温度为700℃,焙烧时间为60min;(3) Under the condition of oxygen atmosphere, the product obtained in step (2) is subjected to microwave roasting to obtain metal oxide and tail gas I, wherein the microwave frequency is 2450MHz, the microwave power is 1200W, the roasting temperature is 700°C, and the roasting time is 60min;

(4)步骤(3)所得尾气Ⅰ经氧化性溶液(氧化性溶液为过氧化氢溶液,过氧化氢溶液的质量浓度为20%)处理得到稀硫酸Ⅰ和尾气Ⅱ;(4) Tail gas I obtained in step (3) is treated with an oxidizing solution (the oxidizing solution is a hydrogen peroxide solution, and the mass concentration of the hydrogen peroxide solution is 20%) to obtain dilute sulfuric acid I and tail gas II;

(5)步骤(4)所得尾气Ⅱ经去离子水处理得到稀硫酸Ⅱ和尾气Ⅲ;(5) Tail gas II obtained in step (4) is treated with deionized water to obtain dilute sulfuric acid II and tail gas III;

(6)步骤(5)所得尾气Ⅲ经饱和氢氧化钠溶液处理得到碳酸钠溶液Ⅰ和尾气Ⅳ,尾气Ⅳ直接排出;(6) Tail gas III obtained in step (5) is treated with saturated sodium hydroxide solution to obtain sodium carbonate solution I and tail gas IV, and tail gas IV is directly discharged;

(7)将步骤(4)所得稀硫酸Ⅰ和步骤(5)所得稀硫酸Ⅱ合并,蒸馏得到质量浓度为70%的浓硫酸;将步骤(6)所得碳酸钠溶液Ⅰ蒸发结晶得到碳酸钠晶体;(7) Combine dilute sulfuric acid I obtained in step (4) and dilute sulfuric acid II obtained in step (5), and distill to obtain concentrated sulfuric acid with a mass concentration of 70%; evaporate and crystallize sodium carbonate solution I obtained in step (6) to obtain sodium carbonate crystals ;

(8)将步骤(7)所得浓硫酸加入到去离子水中配制成浓度3.0 mol/L的稀硫酸溶液Ⅲ;(8) Add the concentrated sulfuric acid obtained in step (7) to deionized water to prepare dilute sulfuric acid solution III with a concentration of 3.0 mol/L;

(9)将步骤(3)所得焙砂加入到步骤(8)所得稀硫酸溶液Ⅲ中,其中焙砂与稀硫酸溶液Ⅲ的固液比g:ml为1:9,在温度为85 ℃、搅拌速度为200 r/min的条件下,反应2 h,得到金属Mo、Ni、Co、Al的浸出液;(9) Add the calcined sand obtained in step (3) to the dilute sulfuric acid solution III obtained in step (8), wherein the solid-to-liquid ratio g:ml of the calcined sand to the dilute sulfuric acid solution III is 1:9, at a temperature of 85 °C, Under the condition of stirring speed of 200 r/min, react for 2 h to obtain the leaching solution of metal Mo, Ni, Co, Al;

本实施例中焙砂的质量为13.838g,焙砂的含碳率为0.66%,含硫率0.98%,经计算去油废铝基催化剂的脱碳率为97.7%,脱硫率为93.2%,可得到质量浓度为70%的硫酸,纯度为98.1%的碳酸钠晶体,金属Mo、Ni、Co、Al的浸出率分别为95.3%、97.6%,98.1%和94.5%。The quality of calcined sand in the present embodiment is 13.838g, and the carbon content rate of calcined sand is 0.66%, and sulfur content rate is 0.98%, after calculation, the decarburization rate of deoiled waste aluminum-based catalyst is 97.7%, and the desulfurization rate is 93.2%, Sulfuric acid with a mass concentration of 70%, sodium carbonate crystals with a purity of 98.1% can be obtained, and the leaching rates of metals Mo, Ni, Co, and Al are 95.3%, 97.6%, 98.1% and 94.5%, respectively.

Claims (4)

1. a kind of aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting, it is characterised in that comprise the following steps that:
(1)Aluminium scrap base hydrogenation catalyst progress deoiling treatment is obtained into oil-free aluminium scrap base hydrogenation catalyst;
(2)By step(1)Gained oil-free aluminium scrap base hydrogenation catalyst is finely ground to particle diameter and is not more than 400 mesh;
(3)Under oxygen ambient conditions, by step(2)Products therefrom carries out microwave calcining and obtains calcining and tail gas I;
(4)Step(3)The oxidized property solution processing of gained tail gas I obtains dilute sulfuric acid I and tail gas II;
(5)Step(4)Gained tail gas II handles through deionized water and obtains dilute sulfuric acid II and tail gas III;
(6)Step(5)Gained tail gas III handles through saturation sodium hydroxide solution and obtains sodium carbonate liquor I and tail gas IV, tail gas IV It is expelled directly out;
(7)By step(4)Gained dilute sulfuric acid I and step(5)Gained dilute sulfuric acid II merges, and distillation obtains the concentrated sulfuric acid;By step(6) The evaporative crystallization of gained sodium carbonate liquor I obtains crystals of sodium carbonate;
(8)By step(7)Gained crystals of sodium carbonate is added to the sodium carbonate that 0.5 ~ 2.5mol/L of concentration is configured in deionized water Solution II, by step(7)The gained concentrated sulfuric acid is configured to 1 ~ 3mol/L of concentration dilution heat of sulfuric acid III;
(9)By step(3)Gained calcining is added to step(8)In gained sodium carbonate liquor II or dilution heat of sulfuric acid III, in temperature For under 75 ~ 95 DEG C, stirring condition, 2 ~ 5h of reaction obtains metal leachate.
2. the aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting according to claim 1, it is characterised in that: Step(3)Middle microwave frequency is 2450MHz, and microwave power is 700 ~ 2000W, and microwave calcining temperature is 500 ~ 700 DEG C, during roasting Between be 15 ~ 75min.
3. the aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting according to claim 1, it is characterised in that: Step(4)Middle oxidizing solution is hydrogen peroxide or liquor natrii hypochloritis, and the mass concentration of oxidizing solution is 10 ~ 30%.
4. the aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting according to claim 1, it is characterised in that: Step(9)The solid-to-liquid ratio g of middle calcining and sodium carbonate liquor II:Ml is 1:(5 ~ 10), the solid-to-liquid ratio of calcining and dilution heat of sulfuric acid III g:Ml is 1: (4~9).
CN201710274802.5A 2017-04-25 2017-04-25 A kind of aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting Pending CN107164629A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710274802.5A CN107164629A (en) 2017-04-25 2017-04-25 A kind of aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710274802.5A CN107164629A (en) 2017-04-25 2017-04-25 A kind of aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting

Publications (1)

Publication Number Publication Date
CN107164629A true CN107164629A (en) 2017-09-15

Family

ID=59812752

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710274802.5A Pending CN107164629A (en) 2017-04-25 2017-04-25 A kind of aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting

Country Status (1)

Country Link
CN (1) CN107164629A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108531733A (en) * 2018-03-27 2018-09-14 昆明理工大学 A kind of method that useless aluminium-based catalyst of microwave sodium roasting consolidates sulphur decarburization
CN108893594A (en) * 2018-06-12 2018-11-27 昆明冶金高等专科学校 A kind of method of carbon distribution and sulphur in quick abjection failure platinum-rhenium catalyst
CN111945007A (en) * 2020-08-27 2020-11-17 中国科学院过程工程研究所 A kind of method for recovering vanadium and molybdenum from waste catalyst containing vanadium and molybdenum
CN113005301A (en) * 2021-02-26 2021-06-22 中南大学 A method for recovering precious metals from waste petrochemical catalysts
CN114606385A (en) * 2022-01-26 2022-06-10 中南大学 A kind of selective leaching method of molybdenum and vanadium in waste catalyst containing molybdenum and vanadium
CN115780480A (en) * 2022-09-26 2023-03-14 山东大学 Pyrolysis method of oil-containing waste catalyst
CN116060140A (en) * 2021-10-29 2023-05-05 中国石油化工股份有限公司 Method for recycling waste hydrogenation catalyst

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05156375A (en) * 1991-12-05 1993-06-22 Taiyo Koukou Kk Method for leaching valuable metal from waste catalyst
CN1305537A (en) * 1998-05-08 2001-07-25 壳牌石油公司 Process to recover molybdenum and vanadium metal from spent catalyst by alkaline leaching
CN1807253A (en) * 2006-01-18 2006-07-26 朴钟殷 Method for treating tail gas and waste water from rare earth finished ore acid method burning process
CN1872667A (en) * 2006-06-23 2006-12-06 李开春 Method for preparing vitriol from flue gas
CN101139102A (en) * 2006-09-05 2008-03-12 新疆天业(集团)有限公司 Method for preparing sodium carbonate liquor through stack gas carbonation
CN101417200A (en) * 2007-10-22 2009-04-29 辽河石油勘探局 Carbon dioxide, nitrogen gas recovering method in boiler flue gas
CN103203174A (en) * 2013-03-27 2013-07-17 华北电力大学(保定) A method for capturing SO2 and CO2 in the flue gas of a coal-fired power plant and producing chemical products
CN105274344A (en) * 2015-11-23 2016-01-27 刘楚玲 Method for recycling vanadium and molybdenum from waste petroleum catalyst

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05156375A (en) * 1991-12-05 1993-06-22 Taiyo Koukou Kk Method for leaching valuable metal from waste catalyst
CN1305537A (en) * 1998-05-08 2001-07-25 壳牌石油公司 Process to recover molybdenum and vanadium metal from spent catalyst by alkaline leaching
CN1807253A (en) * 2006-01-18 2006-07-26 朴钟殷 Method for treating tail gas and waste water from rare earth finished ore acid method burning process
CN1872667A (en) * 2006-06-23 2006-12-06 李开春 Method for preparing vitriol from flue gas
CN101139102A (en) * 2006-09-05 2008-03-12 新疆天业(集团)有限公司 Method for preparing sodium carbonate liquor through stack gas carbonation
CN101417200A (en) * 2007-10-22 2009-04-29 辽河石油勘探局 Carbon dioxide, nitrogen gas recovering method in boiler flue gas
CN103203174A (en) * 2013-03-27 2013-07-17 华北电力大学(保定) A method for capturing SO2 and CO2 in the flue gas of a coal-fired power plant and producing chemical products
CN105274344A (en) * 2015-11-23 2016-01-27 刘楚玲 Method for recycling vanadium and molybdenum from waste petroleum catalyst

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108531733A (en) * 2018-03-27 2018-09-14 昆明理工大学 A kind of method that useless aluminium-based catalyst of microwave sodium roasting consolidates sulphur decarburization
CN108893594A (en) * 2018-06-12 2018-11-27 昆明冶金高等专科学校 A kind of method of carbon distribution and sulphur in quick abjection failure platinum-rhenium catalyst
CN111945007A (en) * 2020-08-27 2020-11-17 中国科学院过程工程研究所 A kind of method for recovering vanadium and molybdenum from waste catalyst containing vanadium and molybdenum
CN113005301A (en) * 2021-02-26 2021-06-22 中南大学 A method for recovering precious metals from waste petrochemical catalysts
CN116060140A (en) * 2021-10-29 2023-05-05 中国石油化工股份有限公司 Method for recycling waste hydrogenation catalyst
CN116060140B (en) * 2021-10-29 2024-10-01 中国石油化工股份有限公司 Method for recycling waste hydrogenation catalyst
CN114606385A (en) * 2022-01-26 2022-06-10 中南大学 A kind of selective leaching method of molybdenum and vanadium in waste catalyst containing molybdenum and vanadium
CN115780480A (en) * 2022-09-26 2023-03-14 山东大学 Pyrolysis method of oil-containing waste catalyst
CN115780480B (en) * 2022-09-26 2024-05-28 山东大学 A method for pyrolysis of waste catalyst containing oil

Similar Documents

Publication Publication Date Title
CN107164629A (en) A kind of aluminium scrap base hydrogenation catalyst processing method based on microwave oxygen-enriched air roasting
CN105648241B (en) Valuable metal tungsten, vanadium, the method for titanium synthetical recovery in useless vanadium tungsten titanium denitrating catalyst
CN110482511B (en) Method for recovering anode material of waste lithium iron phosphate battery
CN114606386B (en) Process for recovering cobalt and lithium by grinding and leaching waste lithium battery
CN109576498B (en) Method for recovering graphite negative electrode material of lithium battery
CN111304441A (en) Method for removing impurities from waste battery leachate
CN104828864B (en) The technique that a kind of ilmenite salt Ore Leaching prepares synthetic rutile
WO2020233526A1 (en) Method for preparing carbon black from pyrolysis coke of waste tire by means of molten salt heat treatment and product thereof
CN108531733A (en) A kind of method that useless aluminium-based catalyst of microwave sodium roasting consolidates sulphur decarburization
CN113415813A (en) Method for recovering lithium nickel cobalt manganese from waste ternary battery material
CN112646977A (en) Method for recovering vanadium, molybdenum, nickel and aluminum from petroleum refining waste catalyst
CN109346741B (en) Method for recycling waste positive electrode material of lithium battery
CN110385044A (en) A kind of method of useless SCR catalyst dearsenification desiliconization
CN111778398A (en) Method for extracting vanadium and tungsten from waste SCR denitration catalyst
CN108160109A (en) A kind of microwave-assisted regeneration FCC dead catalyst methods
CN109593965B (en) A method for recovering valuable elements from aluminum-based petroleum refining waste catalysts
CN111940460A (en) A low-temperature catalytic denitrification method for aluminum ash final ash
CN110863219B (en) A method for resource utilization of zinc-containing converter dust and sludge
CN116282000A (en) A method for recycling graphite carbon slag from waste batteries and co-producing regenerated graphite active materials
CN102181650A (en) Process for reclaiming and preparing palladium chloride from waste palladium/calcium catalyst
CN118207419B (en) Methods for recycling valuable metals from waste batteries
CN114381604A (en) A method of composite biomass powder-assisted step-by-step mechanical activation for recycling cathode waste of lithium ion batteries
CN109487075B (en) Method for comprehensively recovering valuable elements in aluminum-based petroleum refining catalyst by utilizing reducing gas
CN107435101A (en) A kind of method for reclaiming palladium in useless palladium carbon catalyst
Cheng et al. Classification and progress of extraction technologies for nonferrous metal resources

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20170915

RJ01 Rejection of invention patent application after publication