CN115820945A - Regulating agent for separating and enriching iron in iron and steel dust mud, method and application - Google Patents

Regulating agent for separating and enriching iron in iron and steel dust mud, method and application Download PDF

Info

Publication number
CN115820945A
CN115820945A CN202211181690.6A CN202211181690A CN115820945A CN 115820945 A CN115820945 A CN 115820945A CN 202211181690 A CN202211181690 A CN 202211181690A CN 115820945 A CN115820945 A CN 115820945A
Authority
CN
China
Prior art keywords
iron
reaction
separating
regulating agent
separation
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
CN202211181690.6A
Other languages
Chinese (zh)
Inventor
颜旭
曾烨婧
叶恒棣
林璋
李谦
柯勇
李云
杨本涛
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.)
Central South University
Zhongye Changtian International Engineering Co Ltd
Original Assignee
Central South University
Zhongye Changtian International Engineering Co Ltd
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 Central South University, Zhongye Changtian International Engineering Co Ltd filed Critical Central South University
Priority to CN202211181690.6A priority Critical patent/CN115820945A/en
Publication of CN115820945A publication Critical patent/CN115820945A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • 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

  • Manufacture And Refinement Of Metals (AREA)

Abstract

The invention provides a regulating agent for separating and enriching iron in iron and steel dust mud, a method and application thereof. The regulating agent comprises one or more of ferric chloride hexahydrate and ferric chloride trihydrate. The method for separating and enriching iron in the iron and steel dust comprises the following steps: mixing the iron and steel dust mud and a regulating agent to carry out hydrothermal reaction. Adding water into the reactant, centrifugally cleaning and separating to obtain an iron-enriched precipitate and a zinc-containing separation solution. Under the hydrothermal condition, crystal water in the regulating agent is separated and iron ions are hydrolyzed, hydrogen ions generated in the hydrolysis process can enable iron and steel dust mud to generate ore phase transformation to release internal zinc, nucleation and growth of hematite are accelerated by the existence of the regulating agent, iron elements are enriched in precipitates, other metal ions are retained in a solution, and separation and enrichment of the iron elements are realized. The regulating agent can realize effective separation of metal elements by a mineral phase hydrothermal method, thereby avoiding the problem of subsequent acid treatment and reducing pollution; and shortens the process flow.

Description

钢铁尘泥中的铁分离与富集的调控剂、方法及应用Regulating agent, method and application of iron separation and enrichment in iron and steel dust

技术领域technical field

本发明涉及钢铁尘泥分离回收技术领域,尤其涉及一种钢铁尘泥中的铁分离与富集的调控剂、方法及应用。The invention relates to the technical field of separation and recovery of iron and steel dust, in particular to a regulator, method and application of iron separation and enrichment in iron and steel dust.

背景技术Background technique

铁作为地壳中含量第二的金属,是目前最主要的一种金属材料。铁广泛应用于制药、农药、粉末冶金、热氢发生器、凝胶推进剂、燃烧活性剂、催化剂、水清洁吸附剂、烧结活性剂、粉末冶金制品、各种机械零部件制品、硬质合金材料制品等领域。纯铁用于制发电机和电动机的铁芯,还原铁粉用于粉末冶金,钢铁用于制造机器和工具。此外,铁及其化合物还用于制磁铁、药物、墨水、颜料、磨料等。铁元素还是人体所需的必要微量元素之一,由此可见铁的重要性。As the second most abundant metal in the earth's crust, iron is currently the most important metal material. Iron is widely used in pharmaceuticals, pesticides, powder metallurgy, thermal hydrogen generators, gel propellants, combustion activators, catalysts, water cleaning adsorbents, sintering activators, powder metallurgy products, various mechanical parts products, hard alloys Material products and other fields. Pure iron is used to make iron cores for generators and motors, reduced iron powder is used for powder metallurgy, and steel is used to make machines and tools. In addition, iron and its compounds are also used to make magnets, medicines, inks, pigments, abrasives, etc. Iron is also one of the essential trace elements needed by the human body, which shows the importance of iron.

钢铁是工业产品的基础,钢铁冶炼行业更是国民经济的重要基础工业,但钢铁冶炼行业在加工生产的过程中,不仅需要投入大量的物质资源和能量资源,还排放大量的废水、废气和固体废弃物。这些废弃物对环境造成危害、对人类健康形成威胁。其中钢铁冶炼都会产生大量的钢铁尘泥,是冶炼行业主要面临的固体废弃物之一。Iron and steel is the foundation of industrial products, and the iron and steel smelting industry is an important basic industry of the national economy. However, in the process of processing and production, the iron and steel smelting industry not only needs to invest a lot of material resources and energy resources, but also discharges a lot of waste water, waste gas and solid waste. These wastes are harmful to the environment and pose a threat to human health. Among them, iron and steel smelting will produce a large amount of iron and steel dust, which is one of the main solid wastes faced by the smelting industry.

钢铁尘泥主要来源于钢铁冶炼过程中的炼铁、炼钢、烧结、轧钢等环节,含有多种碱金属和重金属元素,回收利用率低。钢铁冶金尘泥产生量约为粗钢产量的10 %~12 %,以2020年我国粗钢产量为10.65亿吨计算,产生的钢铁冶炼尘泥达到了1.065~1.278亿吨。含锌尘泥是钢铁冶炼过程中产生的典型含铁废渣。含锌尘泥产生量约为粗钢产量的10%,中国含锌尘泥年产量达8000万吨以上。Iron and steel dust mainly comes from ironmaking, steelmaking, sintering, steel rolling and other links in the iron and steel smelting process. It contains a variety of alkali metals and heavy metal elements, and the recycling rate is low. The amount of iron and steel metallurgical dust generated is about 10% to 12% of the crude steel output. Assuming that my country's crude steel output in 2020 is 1.065 billion tons, the generated iron and steel smelting dust has reached 106.5 to 127.8 million tons. Zinc-containing dust is a typical iron-containing waste slag produced in the iron and steel smelting process. The production of zinc-containing dust is about 10% of crude steel production, and the annual output of zinc-containing dust in China is more than 80 million tons.

目前钢铁厂处理含锌尘泥的方法主要有火法、湿法以及联合方法。对于低锌的粉尘主要采用火法,其中转底炉和回转窑工艺使用最为广泛。回转窑工艺得到的焙烧矿经过磁选分离,可得到铁品位高、含锌量低的磁选精矿;转底炉工艺可得到铁品位为56.71 %,含Zn量为0.07 %的焙烧产品。但是回转窑易结圈,操作要求高,操作不当1个月就会结瘤,作业率低,且设备投资大,操作费用高、能耗大。转底炉工艺粉尘中元素较为复杂,后续处理回收较困难;且该工艺维护成本高、能耗高、效率低。除此之外,火法工艺还会造成二次污染,环保性差。湿法浸出过程中,钢铁尘泥中的铁酸锌尖晶石浸出率较低,且浸出需要用到大量酸或者碱,酸浸过程会产生大量酸泥,后续处理困难。At present, the methods for dealing with zinc-containing dust in iron and steel plants mainly include fire method, wet method and combined method. The fire method is mainly used for low-zinc dust, among which the rotary hearth furnace and rotary kiln process are the most widely used. The roasted ore obtained by the rotary kiln process can be separated by magnetic separation to obtain a magnetically separated concentrate with high iron grade and low zinc content; the rotary hearth furnace process can obtain a roasted product with an iron grade of 56.71% and a Zn content of 0.07%. However, the rotary kiln is easy to form rings, and the operation requirements are high. Improper operation will cause nodules in one month, the operation rate is low, and the equipment investment is large, the operation cost is high, and the energy consumption is large. The elements in the rotary hearth furnace process dust are relatively complex, and subsequent treatment and recovery are difficult; and the process has high maintenance costs, high energy consumption, and low efficiency. In addition, the pyrotechnic process will also cause secondary pollution, which is poor in environmental protection. In the wet leaching process, the leaching rate of zinc ferrite spinel in iron and steel dust sludge is low, and a large amount of acid or alkali is required for leaching. The acid leaching process will produce a large amount of acid sludge, which is difficult for subsequent treatment.

发明内容Contents of the invention

本发明的主要目的是提供一种钢铁尘泥中的铁分离与富集的调控剂、方法及应用,以解决钢铁尘泥处理工艺复杂、污染小、后处理简单的技术问题。The main purpose of the present invention is to provide a regulating agent, method and application of iron separation and enrichment in iron and steel dust to solve the technical problems of complicated iron and steel dust treatment process, less pollution and simple post-treatment.

为实现上述目的,本发明第一方面提供了一种用于钢铁尘泥中的铁分离与富集的调控剂,调控剂包括六水合氯化铁和三水合氯化铁中的一种或几种。To achieve the above object, the first aspect of the present invention provides a regulator for iron separation and enrichment in iron and steel dust, the regulator includes one or more of ferric chloride hexahydrate and ferric chloride trihydrate kind.

本发明第二方面提供了一种钢铁尘泥中的铁分离与富集的方法,包括以下步骤:The second aspect of the present invention provides a method for iron separation and enrichment in iron and steel dust, comprising the following steps:

将钢铁尘泥和调控剂混合,在密闭的容器中进行水热反应,调控剂包括六水合氯化铁和三水合氯化铁中的一种或几种。The iron and steel dust sludge is mixed with a regulating agent, and the hydrothermal reaction is carried out in a closed container, and the regulating agent includes one or more of ferric chloride hexahydrate and ferric chloride trihydrate.

将反应物加水清洗,分离沉淀物,得到铁富集沉淀物。The reactant was washed with water, and the precipitate was separated to obtain an iron-enriched precipitate.

根据本申请的实施方式,将反应物加水清洗,分离沉淀物,得到铁富集沉淀物的步骤包括:According to the embodiment of the present application, the steps of washing the reactant with water, separating the precipitate, and obtaining the iron-enriched precipitate include:

将反应物加水清洗,离心分离沉淀物,得到铁富集沉淀物。The reactant was washed with water, and the precipitate was centrifuged to obtain an iron-enriched precipitate.

根据本申请的实施方式,水热反应的反应温度为150℃~200℃。According to an embodiment of the present application, the reaction temperature of the hydrothermal reaction is 150°C to 200°C.

根据本申请的实施方式,水热反应的反应温度为180~200℃。According to an embodiment of the present application, the reaction temperature of the hydrothermal reaction is 180-200°C.

根据本申请的实施方式,水热反应的时长为2~20小时。According to the embodiment of the present application, the duration of the hydrothermal reaction is 2-20 hours.

根据本申请的实施方式,水热反应的时长为4~10小时。According to the embodiment of the present application, the duration of the hydrothermal reaction is 4-10 hours.

根据本申请的实施方式,调控剂与钢铁尘泥的质量比为(1~2):1。According to the embodiment of the present application, the mass ratio of the regulating agent to the iron and steel dust is (1~2):1.

根据本申请的实施方式,在将反应物加水清洗,分离沉淀物的步骤中,收集分离后的液相,得到含锌分离液。According to an embodiment of the present application, in the step of washing the reactant with water and separating the precipitate, the separated liquid phase is collected to obtain a zinc-containing separation liquid.

本发明第三方面提供了一种上述的钢铁尘泥中的铁分离与富集的方法在钢铁尘泥回收中的应用。The third aspect of the present invention provides an application of the above-mentioned iron separation and enrichment method in steel dust sludge recovery.

上述的用于钢铁尘泥中的铁分离与富集的调控剂,包括六水合氯化铁和三水合氯化铁中的一种或几种。在进行水热反应的情形下,调控剂中的结晶水脱离并使铁离子发生水解,水解过程产生的氢离子可以使得钢铁尘泥发生矿相转变释放内部的锌,同时调控剂的存在加速赤铁矿的形核与生长,使铁元素富集在沉淀中,而其他金属离子存留在溶液中,实现铁元素分离和富集。该调控剂可以通过矿相水热法来实现金属元素的有效分离,避免了后续酸处理的问题、减少了污染;并且缩短工艺流程。The aforementioned regulating agent for iron separation and enrichment in iron and steel dust sludge includes one or more of ferric chloride hexahydrate and ferric chloride trihydrate. In the case of hydrothermal reaction, the crystal water in the regulating agent is detached and the iron ions are hydrolyzed, and the hydrogen ions generated in the hydrolysis process can make the steel dust sludge undergo mineral phase transformation and release the internal zinc, and the presence of the regulating agent accelerates redox. The nucleation and growth of iron ore enriches the iron element in the precipitate, while other metal ions remain in the solution, realizing the separation and enrichment of iron element. The regulating agent can realize the effective separation of metal elements through mineral phase hydrothermal method, avoid the problem of subsequent acid treatment, reduce pollution; and shorten the process flow.

附图说明Description of drawings

为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图示出的结构获得其他的附图。In order to more clearly illustrate the technical solutions in the embodiments of the present invention or the prior art, the following will briefly introduce the drawings that need to be used in the description of the embodiments or the prior art. Obviously, the accompanying drawings in the following description are only These are some embodiments of the present invention. For those skilled in the art, other drawings can also be obtained according to the structures shown in these drawings without creative effort.

图1为本申请一实施方式的矿相水热调控法实现钢铁尘泥中铁分离与富集的方法的流程示意图;Fig. 1 is a schematic flow diagram of a method for iron separation and enrichment in iron and steel dust sludge realized by mineral phase hydrothermal control method according to an embodiment of the present application;

图2为实施例1中反应前电炉尘泥和反应后铁富集沉淀物的XRD图,其中:图2(a)为反应前电炉尘泥XRD图,图2(b)为反应后的铁富集沉淀物的XRD图;Fig. 2 is the XRD pattern of the electric furnace dust sludge before the reaction and the iron-enriched precipitate after the reaction in Example 1, wherein: Fig. 2 (a) is the XRD pattern of the electric furnace dust sludge before the reaction, and Fig. 2 (b) is the iron after the reaction XRD pattern of enriched precipitate;

图3为实施例1中反应前电炉尘泥和反应后铁富集沉淀物的扫描电镜图,其中:图3(a)为反应前电炉尘泥扫描电镜图,图3(b)为反应后的铁富集沉淀物的扫描电镜图;Fig. 3 is the scanning electron micrograph of the electric furnace dust sludge before the reaction and the iron-enriched precipitate after the reaction in Example 1, wherein: Fig. 3 (a) is the scanning electron micrograph of the electric furnace dust sludge before the reaction, and Fig. 3 (b) is after the reaction Scanning electron micrographs of iron-enriched precipitates;

图4为实施1中反应前后电炉尘泥和铁富集沉淀物中铁、锌元素含量变化图;Fig. 4 is the change diagram of iron and zinc element content in the electric furnace dust sludge and iron-enriched sediment before and after the reaction in the implementation 1;

图5为对比例1中反应前转炉尘泥和反应后铁富集沉淀物的XRD图;Fig. 5 is the XRD pattern of the converter dust sludge before the reaction and the iron-enriched precipitate after the reaction in Comparative Example 1;

图6为对比例2中反应前转炉尘泥和反应后铁富集沉淀物的XRD图。Fig. 6 is the XRD pattern of the converter dust sludge before the reaction and the iron-enriched precipitate after the reaction in Comparative Example 2.

本发明目的的实现、功能特点及优点将结合实施方式,参照附图做进一步说明。The realization of the purpose of the present invention, functional characteristics and advantages will be further described with reference to the accompanying drawings in combination with the implementation modes.

具体实施方式Detailed ways

下面将结合本发明实施方式中的附图,对本发明实施方式中的技术方案进行清楚、完整地描述,显然,所描述的实施方式仅仅是本发明的一部分实施方式,而不是全部的实施方式。基于本发明中的实施方式,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施方式,都属于本发明保护的范围。The following will clearly and completely describe the technical solutions in the embodiments of the present invention in conjunction with the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, not all of them. Based on the implementation manners in the present invention, all other implementation manners obtained by persons of ordinary skill in the art without making creative efforts belong to the scope of protection of the present invention.

需要说明,本发明实施方式中所有方向性指示(诸如上、下……)仅用于解释在某一特定姿态(如附图所示)下各部件之间的相对位置关系、运动情况等,如果该特定姿态发生改变时,则该方向性指示也相应地随之改变。It should be noted that all directional indications (such as up, down, etc.) in the embodiments of the present invention are only used to explain the relative positional relationship, movement, etc. between the components in a certain posture (as shown in the drawings), If the specific posture changes, the directional indication also changes accordingly.

另外,在本发明中如涉及“第一”、“第二”等的描述仅用于描述目的,而不能理解为指示或暗示其相对重要性或者隐含指明所指示的技术特征的数量。由此,限定有“第一”、“第二”的特征可以明示或者隐含地包括至少一个该特征。In addition, in the present invention, descriptions such as "first", "second" and so on are used for description purposes only, and should not be understood as indicating or implying their relative importance or implicitly indicating the quantity of indicated technical features. Thus, the features defined as "first" and "second" may explicitly or implicitly include at least one of these features.

并且,本发明各个实施方式之间的技术方案可以相互结合,但是必须是以本领域普通技术人员能够实现为基础,当技术方案的结合出现相互矛盾或无法实现时应当认为这种技术方案的结合不存在,也不在本发明要求的保护范围之内。Moreover, the technical solutions of the various embodiments of the present invention can be combined with each other, but it must be based on the realization of those skilled in the art. When the combination of technical solutions is contradictory or cannot be realized, it should be considered as a combination of technical solutions. Does not exist, nor is it within the scope of protection required by the present invention.

本发明提供了一种用于钢铁尘泥中的铁分离与富集的调控剂,调控剂包括六水合氯化铁和三水合氯化铁中的一种或几种。The invention provides a regulating agent for iron separation and enrichment in iron and steel dust sludge. The regulating agent includes one or more of ferric chloride hexahydrate and ferric chloride trihydrate.

钢铁尘泥可以为含锌尘泥,例如可以是电炉尘泥、转炉尘泥中的一种或几种。六水合氯化铁和三水合氯化铁在使用过程中均为粉末状。The iron and steel dust can be zinc-containing dust, for example, it can be one or more of electric furnace dust and converter dust. Both ferric chloride hexahydrate and ferric chloride trihydrate are in powder form during use.

上述的用于钢铁尘泥中的铁分离与富集的调控剂,包括六水合氯化铁和三水合氯化铁中的一种或几种。在水热条件下,调控剂中的结晶水脱离并使铁离子发生水解,水解过程产生的氢离子可以使得钢铁尘泥发生矿相转变释放内部的锌,同时调控剂的存在加速赤铁矿的形核与生长,使铁元素富集在沉淀中,其他金属离子存留在溶液中,实现铁元素分离和富集。The aforementioned regulating agent for iron separation and enrichment in iron and steel dust sludge includes one or more of ferric chloride hexahydrate and ferric chloride trihydrate. Under hydrothermal conditions, the crystallization water in the regulator is detached and the iron ions are hydrolyzed, and the hydrogen ions generated during the hydrolysis process can cause the steel dust to undergo a mineral phase transformation and release the internal zinc. At the same time, the presence of the regulator accelerates the hematite Nucleation and growth enrich the iron element in the precipitate, and other metal ions remain in the solution to realize the separation and enrichment of iron element.

为了完成对钢铁尘泥中金属离子的分离富集,本发明提供了一种矿相水热调控实现钢铁尘泥中铁、锌分离和铁元素富集的方法,包括以下步骤:In order to complete the separation and enrichment of metal ions in iron and steel dust, the present invention provides a method for iron and zinc separation and iron element enrichment in iron and steel dust by hydrothermal control of ore phase, comprising the following steps:

S100:将钢铁尘泥和调控剂混合,在密闭的容器中进行水热反应,调控剂包括六水合氯化铁和三水合氯化铁中的一种或几种。S100: mixing iron and steel dust with a regulator, and performing a hydrothermal reaction in an airtight container, where the regulator includes one or more of ferric chloride hexahydrate and ferric chloride trihydrate.

在该步骤将钢铁尘泥与调控剂混合,得反应前驱体。钢铁尘泥与调控剂混合的混合时间可以为10-30 min。如此将钢铁尘泥与调控剂混合均匀。In this step, steel dust and regulator are mixed to obtain a reaction precursor. The mixing time for mixing steel dust and regulator can be 10-30 min. In this way, the iron and steel dust and the regulator are mixed evenly.

密闭的容器可以开启,当反应前驱体装入后封闭,例如可以为水热反应釜。水热反应釜加热进行水热反应。在该过程中,密闭的容器内的气体受热膨胀,会为反应前驱体提供一个具有一定压力的反应环境。The airtight container can be opened and closed after the reaction precursor is loaded, for example, it can be a hydrothermal reactor. The hydrothermal reaction kettle is heated for hydrothermal reaction. In this process, the gas in the airtight container is heated and expanded, which will provide a reaction environment with a certain pressure for the reaction precursor.

水热反应是指在一定的温度和压力下,在水、水溶液或蒸汽等流体中所进行有关化学反应的总称。Hydrothermal reaction refers to the general term for related chemical reactions in fluids such as water, aqueous solution or steam at a certain temperature and pressure.

关于水热反应,在本申请的一种实施方式中,在加热反应过程中,六水合氯化铁和三水合氯化铁中的结晶水,会形成少量游离状态的水(为了便于称呼,可以称为生成水)。故而该反应过程也可以称为水热反应。Regarding the hydrothermal reaction, in one embodiment of the present application, during the heating reaction, the crystallization water in ferric chloride hexahydrate and ferric chloride trihydrate will form a small amount of free water (for ease of reference, it can be called produced water). Therefore, the reaction process can also be called hydrothermal reaction.

具体地,参见上述关于调控剂在水热条件下的分析,基于金属离子水解产酸的原理,氯化铁水解生成的氯化氢(HCl)会溶解在生成水中,从而形成具有高浓度氢离子(H+)的溶液,该溶液可以与ZnFe2O4反应,同时,形成的Fe3+也会在密封体系中水解,如下面的方程式所示。Specifically, referring to the above-mentioned analysis on regulators under hydrothermal conditions, based on the principle of hydrolysis of metal ions to produce acid, the hydrogen chloride (HCl) generated by the hydrolysis of ferric chloride will be dissolved in the generated water, thereby forming a high concentration of hydrogen ions (HCl) + ), the solution can react with ZnFe 2 O 4 , and at the same time, the formed Fe 3+ will also be hydrolyzed in the sealed system, as shown in the following equation.

2FeCl3 + 3H2O = Fe2O3 + 6HCl 2FeCl3 + 3H2O = Fe2O3 + 6HCl

ZnFe2O4 + 8H+ = Zn2+ + 2Fe3+ + 4H2OZnFe 2 O 4 + 8H + = Zn 2+ + 2Fe 3+ + 4H 2 O

2Fe3+ + 3H2O = Fe2O3 + 6H+ 2Fe 3+ + 3H 2 O = Fe 2 O 3 + 6H +

关于水热反应,在本申请的一种实施方式中,也可以在反应前驱体中再加入少量的水,以进行水热反应。Regarding the hydrothermal reaction, in one embodiment of the present application, a small amount of water can also be added to the reaction precursor to carry out the hydrothermal reaction.

S200:将反应物加水清洗,分离沉淀物,得到铁富集沉淀物。S200: washing the reactant with water, separating the precipitate, and obtaining an iron-enriched precipitate.

钢铁尘泥和调控剂经过水热反应之后,反应物呈一定的湿润状态。在水热条件下使得调控剂水解促使钢铁尘泥的矿相发生变化,实现金属离子的有效脱出,并且通过调控剂调节金属离子的形核生长行为,使铁大部分转化为Fe2O3,其他金属离子仍是离子状态。在反应物中加入水,Fe2O3形成沉淀物,其他金属离子仍是离子状态,存留在溶液中。After the steel dust and regulator undergo hydrothermal reaction, the reactants are in a certain wet state. Under hydrothermal conditions, the regulator is hydrolyzed to promote the mineral phase change of iron and steel dust, to realize the effective extraction of metal ions, and through the regulator to regulate the nucleation and growth behavior of metal ions, most of the iron is converted into Fe 2 O 3 , Other metal ions are still in ionic state. When water is added to the reactant, Fe 2 O 3 forms a precipitate, and other metal ions remain in the ionic state and remain in the solution.

将沉淀物分离(例如离心)后,即为铁富集沉淀物。分离后的液相可以称为含锌分离液。该过程可实现钢铁尘泥中铁、锌元素的有效分离,解决了钢铁尘泥资源化难度大及重金属难以高效分离再利用的技术问题。铁富集沉淀物可以多进行几次加水清洗和分离的过程。如此铁富集沉淀物表面吸附的反应液中的金属离子被洗去。在清洗后还可以进行烘干处理。When the precipitate is separated (eg centrifuged), it is an iron-rich precipitate. The separated liquid phase can be called zinc-containing separation liquid. This process can realize the effective separation of iron and zinc elements in iron and steel dust, and solve the technical problems that the resource utilization of iron and steel dust is difficult and heavy metals are difficult to efficiently separate and reuse. The iron-enriched precipitate can be washed and separated by adding water several times. The metal ions in the reaction solution adsorbed on the surface of the iron-rich precipitate are washed away. It can also be dried after cleaning.

与现有技术相比,本发明具有以下优点:Compared with the prior art, the present invention has the following advantages:

本发明可以实现从钢铁尘泥中进行铁、锌元素的有效分离,危废的二次利用,提高资源的利用率。本发明通过采用矿相水热法实现钢铁尘泥中金属离子有效脱出同时,调控剂的引入成功实现赤铁矿的有效成核和生长。相比于酸浸处理,减少了酸的使用,避免了后续酸处理的问题;通过一步矿相水热法来实现金属元素的有效分离,缩短工艺流程,进一步地保证了分离的有效性和产率,在不需要二次烧结的情况下,在水热条件和调控剂的共同作用下使得含铁沉淀物晶型生长,得到晶格排列整齐的含铁沉淀物,即铁富集沉淀物。铁富集沉淀物为铁含量高的沉淀物,具体为赤铁矿,可以进行二次利用。The invention can realize effective separation of iron and zinc elements from iron and steel dust, secondary utilization of hazardous waste, and improvement of utilization rate of resources. In the present invention, metal ions in iron and steel dust are effectively removed by adopting mineral phase hydrothermal method, and at the same time, effective nucleation and growth of hematite are successfully realized by the introduction of regulators. Compared with acid leaching treatment, the use of acid is reduced, and the problem of subsequent acid treatment is avoided; the effective separation of metal elements is realized by one-step mineral phase hydrothermal method, the process flow is shortened, and the effectiveness of separation and production are further ensured. In the absence of secondary sintering, under the joint action of hydrothermal conditions and regulators, the iron-containing precipitates grow in crystal form, and iron-containing precipitates with well-arranged crystal lattices are obtained, that is, iron-rich precipitates. The iron-enriched sediment is a sediment with high iron content, specifically hematite, which can be used for secondary use.

在一些实施例中,水热反应的反应温度为150℃~200℃。优选180-200℃。温度过低会导致钢铁尘泥中的铁酸锌难以分解。In some embodiments, the reaction temperature of the hydrothermal reaction is 150°C-200°C. Preferably 180-200°C. If the temperature is too low, it will be difficult to decompose the zinc ferrite in the steel dust.

在一些实施例中,水热反应的时长为2~20小时。优选4-10h。时长过短会导致铁酸锌分解不完全,不能完全转化为赤铁矿。In some embodiments, the duration of the hydrothermal reaction is 2-20 hours. Preferably 4-10h. If the time is too short, the zinc ferrite will not be completely decomposed and cannot be completely converted into hematite.

在一些实施例中,调控剂与钢铁尘泥的质量比为(1~2):1。调控剂用量不足会导致铁酸锌分解不完全。In some embodiments, the mass ratio of the regulating agent to the steel dust is (1~2):1. Insufficient dosage of regulator will lead to incomplete decomposition of zinc ferrite.

在前面的分析过程中,已经提及锌和其他的金属离子主要在溶液中,也可以对这部分金属离子进行二次利用。因此,在一些实施例中,还包括:在将反应物加水清洗,分离沉淀物的步骤中,收集分离后的液相,得到含锌分离液。In the previous analysis process, it has been mentioned that zinc and other metal ions are mainly in solution, and this part of metal ions can also be used for secondary use. Therefore, in some embodiments, it also includes: in the step of washing the reactant with water and separating the precipitate, collecting the separated liquid phase to obtain a zinc-containing separation liquid.

含锌分离液中含其他金属分离液,通过处理实现金属离子的再回收,进而实现资源的二次利用。The zinc-containing separation liquid contains other metal separation liquids, and metal ions can be recovered through treatment, thereby realizing the secondary utilization of resources.

本发明还提供了一种上述的钢铁尘泥中的铁分离与富集的方法在钢铁尘泥回收中的应用。The present invention also provides an application of the above iron separation and enrichment method in steel dust and sludge recycling.

为了便于对上述实施方式做进一步理解,现举例说明:In order to facilitate the further understanding of the above implementation, an example is given to illustrate:

实施例1Example 1

1、将电炉尘泥(Fe52.4 %,Zn7.96 %)与六水合氯化铁以2:3的比例充分混合30min,得反应前驱体。1. Fully mix electric furnace dust sludge (Fe52.4%, Zn7.96%) and ferric chloride hexahydrate at a ratio of 2:3 for 30 minutes to obtain a reaction precursor.

2、将反应前驱体置于反应釜中进行水热反应,反应温度为200 ℃、反应时间10 h。反应结束后多次清洗得到得铁富集沉淀物和含锌分离液。反应前的电炉尘泥和反应后的铁富集沉淀物的XRD谱如附图2所示,可以看出,水热反应后电炉尘泥转化为赤铁矿,铁酸锌尖晶石的衍射峰消失。反应前的电炉尘泥和反应后的铁富集沉淀物的扫描电镜图如附图3所示,可以看出,水热反应后产物为圆球状赤铁矿,颗粒分布更均匀。2. Put the reaction precursor in the reactor for hydrothermal reaction, the reaction temperature is 200 °C, and the reaction time is 10 h. After the reaction is finished, the iron-enriched precipitate and the zinc-containing separation liquid are obtained by washing several times. The XRD spectrum of the electric furnace dust sludge before the reaction and the iron-enriched precipitate after the reaction is shown in Figure 2. It can be seen that the electric furnace dust sludge is converted into hematite after the hydrothermal reaction, and the diffraction of zinc ferrite spinel The peak disappears. The scanning electron microscope images of the electric furnace dust sludge before the reaction and the iron-enriched precipitate after the reaction are shown in Figure 3. It can be seen that the product after the hydrothermal reaction is spherical hematite, and the particle distribution is more uniform.

3、将反应前的电炉尘泥和反应后的铁富集沉淀物进行消解,使用ICP-OES对样品中铁、锌元素进行定量测试。元素含量变化如附图4所示,可以看出反应前的电炉尘泥含铁52.4 %,含锌7.96 %;反应后的铁富集沉淀物含铁66.63 %,含锌0.11 %。水热后固相中Fe含量接近赤铁矿理论含铁值,锌的分离率达98 %。3. Digest the electric furnace dust sludge before the reaction and the iron-enriched sediment after the reaction, and use ICP-OES to quantitatively test the iron and zinc elements in the sample. Changes in element content are shown in Figure 4. It can be seen that the electric furnace dust sludge before the reaction contains 52.4% iron and 7.96% zinc; the iron-enriched precipitate after the reaction contains 66.63% iron and 0.11% zinc. After hydrothermal treatment, the Fe content in the solid phase is close to the theoretical iron content value of hematite, and the separation rate of zinc reaches 98%.

实施例2Example 2

1、将实施例1的电炉尘泥与六水合氯化铁以1:2的比例充分混合10 min,得反应前驱体。1. Fully mix the electric furnace dust and ferric chloride hexahydrate at a ratio of 1:2 for 10 minutes to obtain a reaction precursor.

2、将反应前驱体置于反应釜中进行水热反应,反应温度为200 ℃、反应时间8 h。反应结束后多次清洗得到得铁富集沉淀物和含锌分离液。2. Put the reaction precursor in the reactor for hydrothermal reaction, the reaction temperature is 200 °C, and the reaction time is 8 h. After the reaction is finished, the iron-enriched precipitate and the zinc-containing separation liquid are obtained by washing several times.

3、在本实施例中,反应前的电炉尘泥含铁52.4 %,含锌7.96 %;反应后的铁富集沉淀物含铁66.75 %,含锌0.06 %。3. In this embodiment, the electric furnace dust sludge before the reaction contains 52.4% iron and 7.96% zinc; the iron-enriched precipitate after the reaction contains 66.75% iron and 0.06% zinc.

实施例3Example 3

1、将转炉尘泥(Fe49.7 %,Zn10.15 %)与六水合氯化铁以2:3的比例充分混合30min,得反应前驱体。1. Fully mix converter dust (Fe49.7%, Zn10.15%) and ferric chloride hexahydrate at a ratio of 2:3 for 30 minutes to obtain a reaction precursor.

2、将反应前驱体置于反应釜中进行水热反应,反应温度为180 ℃、反应时间10 h。反应结束后多次清洗得到得铁富集沉淀物和含锌分离液。2. Put the reaction precursor in the reactor for hydrothermal reaction, the reaction temperature is 180 °C, and the reaction time is 10 h. After the reaction is finished, the iron-enriched precipitate and the zinc-containing separation liquid are obtained by washing several times.

3、在本实施例中,反应前的转炉尘泥含铁49.7 %,含锌10.15 %;反应后的铁富集沉淀物含铁65.33 %,含锌1.18 %。3. In this example, the converter dust before the reaction contains 49.7% iron and 10.15% zinc; the iron-enriched precipitate after the reaction contains 65.33% iron and 1.18% zinc.

实施例4Example 4

1、将实施例1的电炉尘泥与三水合氯化铁以1:1的比例充分混合20 min,得反应前驱体。1. Fully mix the electric furnace dust and ferric chloride trihydrate in a ratio of 1:1 for 20 min to obtain a reaction precursor.

2、将反应前驱体置于反应釜中进行水热反应,反应温度为180 ℃、反应时间4 h。反应结束后多次清洗得到得铁富集沉淀物和含锌分离液。2. Put the reaction precursor in the reactor for hydrothermal reaction, the reaction temperature is 180 °C, and the reaction time is 4 h. After the reaction is finished, the iron-enriched precipitate and the zinc-containing separation liquid are obtained by washing several times.

3、在本实施例中,反应前的电炉尘泥含铁52.4 %,含锌7.96 %;反应后的铁富集沉淀物含铁65.77 %,含锌0.13 %。3. In this embodiment, the electric furnace dust sludge before the reaction contains 52.4% iron and 7.96% zinc; the iron-enriched precipitate after the reaction contains 65.77% iron and 0.13% zinc.

实施例5Example 5

1、将实施例3的转炉尘泥与六水合氯化铁以2:3的比例充分混合20 min,得反应前驱体。1. Fully mix the converter dust sludge of Example 3 with ferric chloride hexahydrate at a ratio of 2:3 for 20 min to obtain a reaction precursor.

2、将反应前驱体置于反应釜中进行水热反应,反应温度为200 ℃、反应时间2 h。反应结束后多次清洗得到得铁富集沉淀物和含锌分离液。2. Put the reaction precursor in the reactor for hydrothermal reaction, the reaction temperature is 200 °C, and the reaction time is 2 h. After the reaction is finished, the iron-enriched precipitate and the zinc-containing separation liquid are obtained by washing several times.

3、在本实施例中,反应前的转炉尘泥含铁49.7 %,含锌10.15 %;反应后的铁富集沉淀物含铁62.43 %,含锌2.01 %。3. In this example, the converter dust before the reaction contains 49.7% iron and 10.15% zinc; the iron-enriched precipitate after the reaction contains 62.43% iron and 2.01% zinc.

实施例5Example 5

1、将实施例3的转炉尘泥与六水合氯化铁以2:3的比例充分混合20 min,得反应前驱体。1. Fully mix the converter dust sludge of Example 3 with ferric chloride hexahydrate at a ratio of 2:3 for 20 min to obtain a reaction precursor.

2、将反应前驱体置于反应釜中进行水热反应,反应温度为150 ℃、反应时间20 h。反应结束后多次清洗得到得铁富集沉淀物和含锌分离液。2. Put the reaction precursor in the reactor for hydrothermal reaction, the reaction temperature is 150 °C, and the reaction time is 20 h. After the reaction is finished, the iron-enriched precipitate and the zinc-containing separation liquid are obtained by washing several times.

3、在本实施例中,反应前的转炉尘泥含铁49.7 %,含锌10.15 %;反应后的铁富集沉淀物含铁64.25 %,含锌1.84 %。3. In this example, the converter dust before the reaction contains 49.7% iron and 10.15% zinc; the iron-enriched precipitate after the reaction contains 64.25% iron and 1.84% zinc.

对比例1Comparative example 1

1、将2g实施例3的转炉尘泥(Fe49.7 %,Zn10.15 %)置于反应釜中进行水热反应,反应温度为200 ℃、反应时间10 h。反应结束后固液分离得到得铁富集沉淀物和含锌分离液。1. Put 2 g of the converter dust sludge (Fe49.7 %, Zn10.15 %) of Example 3 in a reactor for hydrothermal reaction at a reaction temperature of 200 °C and a reaction time of 10 h. After the reaction is completed, solid-liquid separation is performed to obtain an iron-rich precipitate and a zinc-containing separation liquid.

2、反应前的转炉尘泥和反应后的铁富集沉淀物的XRD谱如附图5所示,水热前后物相未发生变化。2. The XRD spectra of the converter dust sludge before the reaction and the iron-enriched precipitate after the reaction are shown in Figure 5, and the phase of the substance remains unchanged before and after hydrothermal treatment.

和实施例3相比可以看出,不加调控剂的条件下无法实现矿相转化铁锌分离。Compared with Example 3, it can be seen that the iron-zinc separation of mineral phase transformation cannot be realized without adding a regulator.

对比例2Comparative example 2

1、将2g实施例1的电炉尘泥(Fe52.4 %,Zn7.96 %)与六水合氯化铁以2:3的比例充分混合30 min,得反应前驱体。1. Fully mix 2g of the electric furnace dust sludge (Fe52.4%, Zn7.96%) of Example 1 with ferric chloride hexahydrate at a ratio of 2:3 for 30 minutes to obtain a reaction precursor.

2、将反应前驱体置于反应釜中进行水热反应,反应温度为100 ℃、反应时间10 h。反应结束后多次清洗得到得铁富集沉淀物和含锌分离液。反应后的铁富集沉淀物的XRD谱如附图6所示,水热后物相变化不大。2. Put the reaction precursor in the reactor for hydrothermal reaction, the reaction temperature is 100 °C, and the reaction time is 10 h. After the reaction is finished, the iron-enriched precipitate and the zinc-containing separation liquid are obtained by washing several times. The XRD spectrum of the iron-enriched precipitate after the reaction is shown in Figure 6, and the phase changes little after hydrothermal treatment.

和实施例1相比可以看出,100 ℃条件下铁酸锌不分解,无法实现矿相转化铁锌分离。Compared with Example 1, it can be seen that zinc ferrite does not decompose under the condition of 100 °C, and the iron-zinc separation of mineral phase transformation cannot be realized.

本发明的上述技术方案中,以上仅为本发明的优选实施例,并非因此限制本发明的专利范围,凡是在本发明的技术构思下,利用本发明说明书及附图内容所作的等效结构变换,或直接/间接运用在其他相关的技术领域均包括在本发明的专利保护范围。Among the above-mentioned technical solutions of the present invention, the above are only preferred embodiments of the present invention, and therefore do not limit the patent scope of the present invention. Under the technical conception of the present invention, the equivalent structural transformations made by utilizing the description of the present invention and the contents of the accompanying drawings , or directly/indirectly used in other related technical fields are included in the patent protection scope of the present invention.

Claims (10)

1. A regulating agent for separating and enriching iron in iron and steel dust mud is characterized in that the regulating agent comprises one or more of ferric chloride hexahydrate and ferric chloride trihydrate.
2. A method for separating and enriching iron in iron and steel dust mud is characterized by comprising the following steps:
mixing the iron and steel dust mud with a regulating agent, and carrying out hydrothermal reaction in a closed container, wherein the regulating agent comprises one or more of ferric chloride hexahydrate and ferric chloride trihydrate;
and adding water to the reactant for washing, and separating the precipitate to obtain the iron-enriched precipitate.
3. The method for separating and enriching iron according to claim 2, wherein the step of washing the reactant with water and separating the precipitate to obtain the iron-enriched precipitate comprises:
and adding water to the reaction product for washing, and centrifugally separating the precipitate to obtain the iron-enriched precipitate.
4. The method for separating and enriching iron of claim 2, wherein the reaction temperature of the hydrothermal reaction is 150 ℃ to 200 ℃.
5. The method for iron separation and enrichment according to claim 4, wherein the reaction temperature of the hydrothermal reaction is 180 to 200 ℃.
6. The method for iron separation and enrichment according to claim 4, wherein the hydrothermal reaction is carried out for a period of 2 to 20 hours.
7. The method for iron separation and enrichment according to claim 6, wherein the hydrothermal reaction is carried out for a period of 4 to 10 hours.
8. The method for iron separation and enrichment according to claim 2, wherein the mass ratio of the control agent to the steel dust mud is (1 to 2): 1.
9. The method for separating and enriching iron according to any one of claims 2 to 8, wherein in the step of adding water to wash the reactant and separating the precipitate, the separated liquid phase is collected to obtain a zinc-containing separation solution.
10. Use of the method of any one of claims 2 to 9 for iron separation and enrichment in iron and steel sludge recovery.
CN202211181690.6A 2022-09-27 2022-09-27 Regulating agent for separating and enriching iron in iron and steel dust mud, method and application Pending CN115820945A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202211181690.6A CN115820945A (en) 2022-09-27 2022-09-27 Regulating agent for separating and enriching iron in iron and steel dust mud, method and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202211181690.6A CN115820945A (en) 2022-09-27 2022-09-27 Regulating agent for separating and enriching iron in iron and steel dust mud, method and application

Publications (1)

Publication Number Publication Date
CN115820945A true CN115820945A (en) 2023-03-21

Family

ID=85524003

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202211181690.6A Pending CN115820945A (en) 2022-09-27 2022-09-27 Regulating agent for separating and enriching iron in iron and steel dust mud, method and application

Country Status (1)

Country Link
CN (1) CN115820945A (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2018081856A1 (en) * 2016-11-01 2018-05-11 Austpac Resources N.L. Processing of zinc-containing waste materials
CN108315559A (en) * 2018-01-23 2018-07-24 昆明理工大学 A kind of method of steel plant's Zinc-Bearing Wastes separation of Zinc
CN109850952A (en) * 2019-04-03 2019-06-07 东北师范大学 High-purity separation method of iron ion in a kind of water containing heavy metal ion solution
CN111647754A (en) * 2020-06-14 2020-09-11 吴坤 Comprehensive utilization method of zinc-containing dust and sludge in steel plant
CN113201651A (en) * 2021-04-30 2021-08-03 湖南青涟环保科技有限公司 Synergistic treatment method of iron-containing dust and mud
CN115094240A (en) * 2022-07-25 2022-09-23 中南大学 Method for separating iron and lead and enriching iron element in iron-containing waste residue

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2018081856A1 (en) * 2016-11-01 2018-05-11 Austpac Resources N.L. Processing of zinc-containing waste materials
CN108315559A (en) * 2018-01-23 2018-07-24 昆明理工大学 A kind of method of steel plant's Zinc-Bearing Wastes separation of Zinc
CN109850952A (en) * 2019-04-03 2019-06-07 东北师范大学 High-purity separation method of iron ion in a kind of water containing heavy metal ion solution
CN111647754A (en) * 2020-06-14 2020-09-11 吴坤 Comprehensive utilization method of zinc-containing dust and sludge in steel plant
CN113201651A (en) * 2021-04-30 2021-08-03 湖南青涟环保科技有限公司 Synergistic treatment method of iron-containing dust and mud
CN115094240A (en) * 2022-07-25 2022-09-23 中南大学 Method for separating iron and lead and enriching iron element in iron-containing waste residue

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
HUI-GANG WANG 等: "A novel hydrothermal method for zinc extraction and separation from zinc ferrite and electric arc furnace dust", INTERNATIONAL JOURNAL OF MINERALS, METALLURGY AND MATERIALS, vol. 23, no. 2, pages 148 *
何志军 等: "钢铁冶金过程环保新技术", 冶金工业出版社, pages: 198 *

Similar Documents

Publication Publication Date Title
Liang et al. A review of metallurgical processes and purification techniques for recovering Mo, V, Ni, Co, Al from spent catalysts
Zhu et al. Near-complete recycling of real mix electroplating sludge as valuable metals via Fe/Cr co-crystallization and stepwise extraction route
Qu et al. Stepwise extraction of Fe, Al, Ca, and Zn: A green route to recycle raw electroplating sludge
Wen et al. An efficient utilization of chromium–containing vanadium tailings: Extraction of chromium by soda roasting–water leaching and preparation of chromium oxide
Sinha et al. Recovery of manganese from ferruginous manganese ore using ascorbic acid as reducing agent
Liu et al. Leaching and kinetic modeling of calcareous bornite in ammonia ammonium sulfate solution with sodium persulfate
Agrawal et al. A comprehensive review on the hydro metallurgical process for the production of nickel and copper powders by hydrogen reduction
Liu et al. A novel, clean, closed-loop process for directional recovery of rare earth elements, fluorine, and phosphorus from mixed rare earth concentrate
Yu et al. Vanadium extraction from water-cooled vanadium converter slag via salt-free roasting and acid leaching
Yao et al. Clean process for vanadium extraction from vanadium-bearing converter slag
CN115094240B (en) A method for iron-lead separation and iron element enrichment in iron-containing waste slag
Gao et al. A comparative study of extracting vanadium from vanadium titano-magnetite ores: calcium salt roasting vs sodium salt roasting
CN101717858A (en) Method for extracting molybdenum, nickel, vanadium and ferrum from polymetallic black-shale paragentic minerals
Han et al. Efficient extraction of nickel from sintered alloy by stepwise leaching: Thermodynamic and kinetic studies
Bakkar et al. Recovery of vanadium and nickel from heavy oil fly ash (HOFA): a critical review
Yan et al. Kinetics and mechanism of manganese reductive leaching from electrolytic manganese anode slag with elemental sulfur in sulfuric acid solution
Tian et al. Process and kinetics of the selective extraction of cobalt from high-silicon low-grade cobalt ores using ammonia leaching
Wang et al. Selective sulfuric acid cyclic leaching of vanadium from the calcification roasting pellets of vanadium titanomagnetite
Wang et al. Recovery of Ni matte from Ni-bearing electroplating sludge
Song et al. A novel ammonium-free vanadium precipitation process for the integrated actions of ascorbic acid reduction and enhanced hydrolysis under hydrothermal influence
Qiao et al. Recovery of high-quality iron phosphate from acid-leaching tailings of laterite nickel ore
Zhang et al. A cleaner and sustainable method for recovering rare earth and cobalt from NdFeB leaching residues
Chen et al. Hydrothermal precipitation of V3+ ions in V-bearing oxalic acid leachate to prepare V2O3
Tang et al. A clean process for recovering antimony from arsenic-bearing crystals and immobilizing arsenic as scorodite
Zhu et al. Gallium extraction from red mud via leaching with a weak acid

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: 20230321

RJ01 Rejection of invention patent application after publication