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CN103374658A - Ultrafine lead oxide prepared from desulfurated lead plaster by means of three-stage process and method thereof - Google Patents

Ultrafine lead oxide prepared from desulfurated lead plaster by means of three-stage process and method thereof Download PDF

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CN103374658A
CN103374658A CN2012101216659A CN201210121665A CN103374658A CN 103374658 A CN103374658 A CN 103374658A CN 2012101216659 A CN2012101216659 A CN 2012101216659A CN 201210121665 A CN201210121665 A CN 201210121665A CN 103374658 A CN103374658 A CN 103374658A
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lead
desulfurization
ultra
acid
lead oxide
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杨家宽
朱新锋
李富元
周锋
刘建文
江姝
杨丹妮
李磊
张伟
孙晓娟
王琴
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JINYANG METALLURGICAL CO Ltd HUBEI PROV
Huazhong University of Science and Technology
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JINYANG METALLURGICAL CO Ltd HUBEI PROV
Huazhong University of Science and Technology
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    • 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
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/84Recycling of batteries or fuel cells

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Abstract

一种利用脱硫铅膏三段法制备的超细氧化铅及其方法,包括工序脱硫铅膏酸浸出:脱硫铅膏与酸反应,同时添加还原剂,反应结束后,固液分离,得含铅酸溶液;工序碳酸铅的制备:含铅酸溶液与碳酸钠反应,固液分离、洗涤、干燥得到碳酸铅;工序焙烧:碳酸铅经过焙烧后,制得超细氧化铅;所述超细氧化铅可以是PbO,Pb3O4,或者两者混合物,其平均颗粒粒度小于2μm,纳米晶粒径小于500nm。与现有技术相比,本发明的有益效果是:可直接制备蓄电池企业生产用的活性物质超细氧化铅粉化合物、铅挥发量小、烟尘率低、铅直收率高、能耗低和不产生二氧化硫污染等。A kind of superfine lead oxide prepared by desulfurization lead paste three-stage method and its method, including process Acid leaching of desulfurized lead paste: desulfurized lead paste is reacted with acid, and a reducing agent is added at the same time. After the reaction, the solid and liquid are separated to obtain a lead-containing acid solution; process Preparation of lead carbonate: reaction of lead-containing acid solution with sodium carbonate, solid-liquid separation, washing and drying to obtain lead carbonate; process Roasting: After the lead carbonate is roasted, superfine lead oxide is obtained; the superfine lead oxide can be PbO, Pb 3 O 4 , or a mixture of the two, the average particle size is less than 2 μm, and the nanocrystalline particle size is less than 500 nm. Compared with the prior art, the beneficial effects of the present invention are: the active material superfine lead oxide powder compound used in the production of storage battery enterprises can be directly prepared, the lead volatilization amount is small, the smoke rate is low, the lead yield is high, the energy consumption is low and No sulfur dioxide pollution etc.

Description

利用脱硫铅膏三段法制备的超细氧化铅及其方法Ultrafine lead oxide prepared by desulfurization lead paste three-stage method and method thereof

技术领域 technical field

本发明涉及废铅酸蓄电池的回收利用领域,特别是将污染环境的废铅膏采用湿法浸出和低温焙烧工艺从废铅蓄电池中回收直接制备超细铅粉,属于再生铅生产技术领域。  The invention relates to the field of recycling of waste lead-acid batteries, in particular to reclaiming waste lead paste which pollutes the environment from waste lead batteries through wet leaching and low-temperature roasting processes to directly prepare superfine lead powder, which belongs to the technical field of recycled lead production. the

背景技术 Background technique

铅的用途非常广泛,其年产量在有色金属中位居第四位仅次于铝、铜、锌。随着汽车数量的增加,铅蓄电池工业得到迅速发展,每年产生的废铅蓄电池数量在不断增加。铅酸蓄电池是世界上各类电池中产量最大、用途最广的一种电池,它所消耗的铅占全球总耗铅量的82%。为了节约有限的矿物资源,避免废铅物料对环境的污染,国内外均十分重视废铅材料的回收利用。各国政府都大力支持从废铅蓄电池中回收铅的再生铅生产和再生铅生产新技术的研究。  Lead has a wide range of uses, and its annual output ranks fourth among nonferrous metals after aluminum, copper, and zinc. With the increase of the number of automobiles, the lead-acid battery industry has developed rapidly, and the amount of waste lead-acid batteries produced every year is constantly increasing. Lead-acid battery is the battery with the largest output and widest application among all kinds of batteries in the world, and its lead consumption accounts for 82% of the total lead consumption in the world. In order to save limited mineral resources and avoid environmental pollution caused by waste lead materials, the recycling and utilization of waste lead materials are attached great importance both at home and abroad. The governments of various countries strongly support the research on the production of secondary lead and the new technology of secondary lead production by recovering lead from waste lead-acid batteries. the

废铅蓄电池中含铅物料包括板栅和膏泥两部分。板栅的成份是铅合金,含铅高达90%-95%;铅膏成分复杂,主要由PbSO4、PbO2、PbO、Pb和少量杂质组成,含铅60%-80%。废铅膏火法熔炼的炉型主要有反射炉、回转短炉、鼓风炉等专业炉型。铅膏中PbSO4含量一般在50%以上,PbSO4熔点高,达到完全分解的温度要在1000 ℃以上,是熔炼过程中产生SO2的主要原因。同时高温下造成大量的铅挥发损失并形成污染性的铅尘。由于铅及其化合物的挥发而引起的操作人员铅中毒是很严重的,引起的烟尘量增大也必然导致炼铅直收率的降低和含铅烟尘对环境的污染。此外火法冶炼的能耗也较高,国内小再生铅厂生产1 t铅一般能耗500-600 kg标煤,国内专业再生铅企业的能耗在130-310 kg/t,而目前国外能耗的一般水平达到200 kg/t以下。  Lead-containing materials in waste lead-acid batteries include grids and paste. The composition of the grid is lead alloy, containing 90%-95% lead; the composition of lead paste is complex, mainly composed of PbSO 4 , PbO 2 , PbO, Pb and a small amount of impurities, containing 60%-80% lead. The furnace types for waste lead plaster pyromelting mainly include reverberatory furnaces, short rotary furnaces, blast furnaces and other professional furnace types. The content of PbSO 4 in lead paste is generally more than 50%. The melting point of PbSO 4 is high, and the temperature for complete decomposition should be above 1000 ℃, which is the main reason for the generation of SO 2 in the smelting process. At the same time, a large amount of lead volatilization loss is caused at high temperature and polluting lead dust is formed. The lead poisoning of operators caused by the volatilization of lead and its compounds is very serious, and the increase in the amount of smoke and dust caused will inevitably lead to the reduction of the direct yield of lead smelting and the pollution of the lead-containing smoke to the environment. In addition, the energy consumption of pyrometallurgy is also relatively high. The energy consumption of 1 ton of lead produced by small domestic secondary lead factories generally consumes 500-600 kg standard coal, and the energy consumption of domestic professional secondary lead enterprises is 130-310 kg/t. The general level of consumption is below 200 kg/t.

为了解决火法高温熔炼带来的环境问题,有些学者引入电解沉积法(简称电积法)研究了铅酸蓄电池的湿法冶金工艺。代表性的是Prengmann和McDonald发明的RSR工艺。RSR工艺根据脱硫转化-还原转化-电积法溶解浸出反应所用的典型试剂,可以归纳为(NH4)2CO3-Na2SO3-H2SiF4三段式湿法电积工艺。此外,还有其他类似的铅膏转化-浸出-电积湿法冶金工艺的研究。引入电积法的湿法冶金回收工艺,解决了铅膏火法冶炼工艺中的SO2排放以及高温下铅的挥发问题。然而,该工艺投资大,只适合于建造大规模的回收工厂,能耗较大,甚至比传统火法冶金工艺还要高。因此,高能耗的问题仍然有待解决。  In order to solve the environmental problems caused by pyrothermal smelting, some scholars introduced the electrolytic deposition method (referred to as the electrowinning method) to study the hydrometallurgical process of lead-acid batteries. Representative is the RSR process invented by Prengmann and McDonald. The RSR process can be summarized as (NH 4 ) 2 CO 3 -Na 2 SO 3 -H 2 SiF 4 three-stage wet electrodeposition process according to the typical reagents used in the desulfurization conversion-reduction conversion-electrowinning dissolution and leaching reaction. In addition, there are other similar paste conversion-leaching-electrodeposition hydrometallurgical processes. Introducing the electrowinning hydrometallurgical recovery process solves the problems of SO 2 emission and lead volatilization at high temperature in the lead paste pyrometallurgy process. However, this process requires a large investment and is only suitable for the construction of large-scale recycling plants. It consumes a lot of energy, even higher than the traditional pyrometallurgical process. Therefore, the problem of high energy consumption remains to be solved.

目前的湿法过程以及先进的活法过程都需要先对铅膏脱硫,然后再进行电沉积或者火法熔炼。最终的产物是金属铅锭。而大部分金属铅还要被做成铅粉用于新电池的制作。  Both the current wet process and the advanced live process require desulfurization of the lead paste before electrodeposition or pyromelting. The final product is metallic lead ingots. And most of the metal lead is also made into lead powder for the production of new batteries. the

CN1920065A采用方铅矿为原料,通过浸出结晶得到PbCl2,氯化铅溶液中加入硫酸制备硫酸铅,硫酸铅通过化学合成得到前躯体碳酸铅,最后制备得到β-PbO。CN101573461A采用柠檬酸与柠檬酸钠混合溶液处理铅膏制备超细氧化铅,同时消耗的柠檬酸较多,价格较高,回收硫酸钠困难。CN101514395A采用草酸还原、过滤,沉淀与硝酸反应,沉淀在与碳酸铵反应,过滤,沉淀也加入到硝酸溶液中,溶液与氨水反应,过滤,沉淀热分解得到氧化铅。工艺相对复杂,同时在反应用硝酸、氨水等挥发性较大的药剂。  CN1920065A adopts galena as raw material, obtains PbCl 2 through leaching and crystallization, adds sulfuric acid to lead chloride solution to prepare lead sulfate, and obtains precursor lead carbonate through chemical synthesis of lead sulfate, and finally prepares β-PbO. CN101573461A uses a mixed solution of citric acid and sodium citrate to process lead plaster to prepare superfine lead oxide. At the same time, more citric acid is consumed, the price is higher, and it is difficult to recover sodium sulfate. CN101514395A adopts oxalic acid reduction, filtration, precipitation reacts with nitric acid, precipitation reacts with ammonium carbonate, filtration, precipitation is also added to nitric acid solution, solution reacts with ammonia water, filtration, precipitation thermal decomposition to obtain lead oxide. The process is relatively complicated, and at the same time, volatile agents such as nitric acid and ammonia water are used in the reaction.

综上所述,如何提供一种过程完善、工艺简单、节约资源、能源且不会对环境造成二次污染的铅酸度电池铅膏处理方法,已经是该领域内技术人员研究的重要课题。  To sum up, how to provide a lead-acid battery lead paste treatment method with perfect process, simple process, resource saving, energy saving and no secondary pollution to the environment has become an important research topic for technicians in this field. the

发明内容 Contents of the invention

本发明的目的在于提供一种利用脱硫铅膏三段法制备的超细氧化铅,该超细氧化铅,其平均颗粒粒度小于2 μm,纳米晶粒径小于500 nm。所述超细氧化铅可以是PbO,Pb3O4,或者两者混合物。  The object of the present invention is to provide an ultra-fine lead oxide prepared by a three-stage desulfurization lead paste method. The ultra-fine lead oxide has an average particle size of less than 2 μm and a nanocrystalline particle size of less than 500 nm. The ultrafine lead oxide can be PbO, Pb 3 O 4 , or a mixture of both.

本发明的目的还在于提供利用脱硫铅膏三段法制备超细氧化铅的方法,该方法由废旧铅酸电池脱硫后的铅膏制备超细氧化铅粉、其铅粉纯度高,同时它的生产流程简单、无环境污染或环境污染极低、铅回收率高、降低能耗和减少环境污染效果显著。  The object of the present invention is also to provide the method that utilizes desulfurization lead paste three-stage method to prepare superfine lead oxide, and this method prepares superfine lead oxide powder by the lead paste after the desulfurization of waste lead-acid battery, and its lead powder purity is high, simultaneously its The production process is simple, there is no or very low environmental pollution, the lead recovery rate is high, and the effect of reducing energy consumption and environmental pollution is remarkable. the

本发明的技术方案分为几个部分:脱硫铅膏的制备、铅膏的浸出、超细碳酸铅的制备、超细铅粉的制备和副产品回收。包括工序 

Figure 829622DEST_PATH_IMAGE001
脱硫铅膏酸浸出:脱硫铅膏与酸反应,同时添加还原剂,反应结束后,固液分离,得含铅酸溶液;工序
Figure 19295DEST_PATH_IMAGE002
碳酸铅的制备:含铅酸溶液与碳酸钠反应,反应结束后,固液分离、洗涤、干燥得到碳酸铅;工序
Figure 794484DEST_PATH_IMAGE003
焙烧:碳酸铅经过焙烧后,制得超细氧化铅;本发明所述工序
Figure 360594DEST_PATH_IMAGE001
的还原剂为可溶性无机氧化剂。  The technical solution of the invention is divided into several parts: preparation of desulfurized lead paste, leaching of lead paste, preparation of ultrafine lead carbonate, preparation of ultrafine lead powder and recovery of by-products. Including process
Figure 829622DEST_PATH_IMAGE001
Acid leaching of desulfurized lead paste: desulfurized lead paste is reacted with acid, and a reducing agent is added at the same time. After the reaction, the solid and liquid are separated to obtain a lead-containing acid solution; process
Figure 19295DEST_PATH_IMAGE002
Preparation of lead carbonate: react with lead-containing acid solution and sodium carbonate, after the reaction, separate solid and liquid, wash and dry to obtain lead carbonate; process
Figure 794484DEST_PATH_IMAGE003
Roasting: After the lead carbonate is roasted, superfine lead oxide is obtained; the process described in the present invention
Figure 360594DEST_PATH_IMAGE001
The reducing agent is a soluble inorganic oxidizing agent.

本发明所述工序

Figure 662263DEST_PATH_IMAGE001
的酸为乙酸或者硝酸;所述含铅酸溶液为乙酸铅或者硝酸铅溶液。  Process of the present invention
Figure 662263DEST_PATH_IMAGE001
The acid is acetic acid or nitric acid; the lead-containing acid solution is lead acetate or lead nitrate solution.

所述工序

Figure 22837DEST_PATH_IMAGE001
中, 脱硫铅膏与酸的投料比例是脱硫铅膏中的铅与酸的摩尔比例为l:2-5, 优选的是1:2.5;脱硫铅膏与含有酸水溶液的质量比例为1:3-30;优选的是1:10;反应温度为室温-50 ℃;反应时间为0.5-3 h,反应时间优选的是1 h。  The process
Figure 22837DEST_PATH_IMAGE001
Among them, the feeding ratio of desulfurized lead paste and acid is that the molar ratio of lead and acid in the desulfurized lead paste is 1:2-5, preferably 1:2.5; the mass ratio of desulfurized lead paste to acid-containing aqueous solution is 1:3 -30; preferably 1:10; the reaction temperature is room temperature-50°C; the reaction time is 0.5-3 h, and the reaction time is preferably 1 h.

本发明工序

Figure 721540DEST_PATH_IMAGE001
中可溶性无机氧化剂为双氧水,脱硫铅膏中的PbO2与过氧化氢的摩尔比例为1:1-8,优先1:1.5。  Process of the present invention
Figure 721540DEST_PATH_IMAGE001
The medium-soluble inorganic oxidant is hydrogen peroxide, and the molar ratio of PbO2 and hydrogen peroxide in the desulfurization lead paste is 1:1-8, preferably 1:1.5.

本发明工序中的含铅酸溶液,加入碳酸钠反应,含铅酸溶液与碳酸钠的摩尔比例为1:1.5-3,含铅酸溶液与碳酸钠反应时间为0.1-2 h,优选0.5 h,反应温度为室温-50℃,同时保证溶液的pH小于10。  Process of the present invention In the lead-containing acid solution, add sodium carbonate to react, the molar ratio of lead-containing acid solution and sodium carbonate is 1:1.5-3, the reaction time of lead-containing acid solution and sodium carbonate is 0.1-2 h, preferably 0.5 h, the reaction temperature Room temperature -50°C, while ensuring that the pH of the solution is less than 10.

本发明工序

Figure 981937DEST_PATH_IMAGE002
中的含铅酸溶液,加入碳酸钠反应,可以同时加入含铅酸溶液中的铅重量1-5%的结构导向剂聚乙二醇。  Process of the present invention
Figure 981937DEST_PATH_IMAGE002
The lead-containing acid solution in the solution is added with sodium carbonate to react, and the structure-directing agent polyethylene glycol of 1-5% of the lead weight in the lead-containing acid solution can be added at the same time.

工序

Figure 778992DEST_PATH_IMAGE003
中碳酸铅的焙烧温度为250-500 ℃,焙烧时间为0.5-6 h,最后产物为超细氧化铅。  process
Figure 778992DEST_PATH_IMAGE003
The calcination temperature of medium lead carbonate is 250-500 ℃, the calcination time is 0.5-6 h, and the final product is ultrafine lead oxide.

 本发明的使用的脱硫铅膏产物可以是PbCO3、Pb(CO3)2(OH)、Pb10O(CO3)6(OH)6、NaPb2(CO3)2OH、Pb(OH)2以及没有反应Pb、PbO、PbO2,可能没有少量完全反应的硫酸铅以及它们的混合物。  The desulfurized lead paste products used in the present invention can be PbCO 3 , Pb 3 (CO 3 ) 2 (OH), Pb 10 O(CO 3 ) 6 (OH) 6 , NaPb 2 (CO 3 ) 2 OH, Pb(OH ) 2 and unreacted Pb, PbO, PbO 2 , and possibly a small amount of fully reacted lead sulfate and mixtures thereof.

采用本发明方法制备的超细氧化铅粉(PbO),其平均颗粒粒度小于2 μm,纳米晶粒径小于500 nm,纯度大于99.8%,整个工艺过程铅的回收率超过97%。  The ultrafine lead oxide powder (PbO) prepared by the method of the present invention has an average particle size of less than 2 μm, a nanocrystalline particle size of less than 500 nm, a purity of greater than 99.8%, and a lead recovery rate of more than 97% in the entire process. the

本发明的脱硫铅膏中的铅化合物均能与乙酸或者硝酸快速的反应。在工艺过程中步骤(1)和(2)浸出转化过程中滤液可以连续回用,当乙酸钠达到一定程度时,可以回收乙酸钠。  All the lead compounds in the desulfurized lead paste of the present invention can react rapidly with acetic acid or nitric acid. During the process of step (1) and (2) leaching and conversion in the process, the filtrate can be continuously reused, and when the sodium acetate reaches a certain level, the sodium acetate can be recovered. the

与现有技术相比,本发明的有益效果是:具有直接制备蓄电池企业生产用的活性物质超细氧化铅粉化合物、铅挥发量小、烟尘率低、铅直收率高、能耗低和不产生二氧化硫污染等特点。  Compared with the prior art, the beneficial effects of the present invention are: it has the advantages of directly preparing the active material superfine lead oxide powder compound used in the production of storage battery enterprises, the lead volatilization is small, the smoke rate is low, the lead yield is high, the energy consumption is low and No sulfur dioxide pollution and other characteristics. the

附图说明 Description of drawings

图1为本发明碳酸铅产品的XRD图。  Fig. 1 is the XRD figure of lead carbonate product of the present invention. the

图2为本发明碳酸铅产品的SEM图。  Fig. 2 is the SEM figure of lead carbonate product of the present invention. the

图3为本发明的320 ℃超细氧化铅的XRD图。  Fig. 3 is the XRD pattern of 320 ℃ ultrafine lead oxide of the present invention. the

图4为本发明的320 ℃超细氧化铅的SEM图(放大倍数5000倍)。  Fig. 4 is the SEM image (magnification 5000 times) of 320 ℃ ultrafine lead oxide of the present invention. the

图5为本发明的320 ℃超细氧化铅的SEM图(放大倍数20000倍)。  Fig. 5 is the SEM image (magnification 20000 times) of 320 ℃ ultrafine lead oxide of the present invention. the

图6为本发明的450 ℃的超细氧化铅的XRD图。  Fig. 6 is the XRD figure of the ultrafine lead oxide of 450 ℃ of the present invention. the

图7为本发明的450 ℃超细氧化铅的SEM图(放大倍数5000倍)。  Figure 7 is a SEM image of the 450°C ultrafine lead oxide of the present invention (magnification 5000 times). the

图8为本发明的450 ℃超细氧化铅的SEM图(放大倍数20000倍)。  Figure 8 is a SEM image of the 450°C ultrafine lead oxide of the present invention (magnification 20,000 times). the

具体实施方式 Detailed ways

下面对本发明做进一步说明。  The present invention will be further described below. the

实施例1:Example 1:

(1)脱硫铅膏的制备 (1) Preparation of desulfurized lead paste

废铅蓄电池倒酸处理后,经过破碎分选处理,筛分得到废铅膏;将预处理后废铅膏加到有脱硫剂的溶液中,常用的脱硫剂碳酸钠、碳酸氢钠、碳酸铵等,脱硫结束后进行固液分离。 After the waste lead-acid batteries are deacidified, they are crushed, sorted, and sieved to obtain the waste lead plaster; the pretreated waste lead plaster is added to the solution with a desulfurizing agent, and the commonly used desulfurizing agents are sodium carbonate, sodium bicarbonate, and ammonium carbonate. After the desulfurization is completed, solid-liquid separation is carried out.

(2)制备醋酸铅溶液  (2) Preparation of lead acetate solution

将(1)的脱硫铅膏加入乙酸溶液中,脱硫铅膏与乙酸的投料比例为脱硫铅膏中的铅与乙酸的摩尔比例为1:2.5,同时加入还原剂双氧水,脱硫铅膏中的PbO2与过氧化氢的摩尔比例为1:1.5反应,反应0.5 h后的后过滤分离,得到乙酸铅溶液。脱硫铅膏与乙酸溶液可能发生的反应方程式可能是: Add the desulfurized lead paste of (1) into the acetic acid solution, and the feeding ratio of the desulfurized lead paste to acetic acid is 1:2.5 in the molar ratio of lead in the desulfurized lead paste to acetic acid. 2 reacted with hydrogen peroxide in a molar ratio of 1:1.5, and after reacting for 0.5 h, filtered and separated to obtain lead acetate solution. The possible reaction equation between desulfurized lead paste and acetic acid solution may be:

PbCO3+2CH3COOH→Pb(CH3COO)2+H2O+ CO2                    (1) PbCO 3 +2CH 3 COOH→Pb(CH 3 COO) 2 +H 2 O+ CO 2 (1)

PbO+2CH3COOH→Pb(CH3COO)2+H2O                           (2) PbO+2CH 3 COOH→Pb(CH 3 COO) 2 +H 2 O (2)

PbO2+2CH3COOH +H2O2→Pb(CH3COO)2+2H2O+ O2                 (3) PbO 2 +2CH 3 COOH +H 2 O 2 →Pb(CH 3 COO) 2 +2H 2 O+ O 2 (3)

Pb3(CO3)2(OH)2+6CH3COOH→3Pb(CH3COO)2+4H2O+2CO2       (4) Pb 3 (CO 3 ) 2 (OH) 2 +6CH 3 COOH→3Pb(CH 3 COO) 2 +4H 2 O+2CO 2 (4)

Pb10O(CO3)6(OH)6+20CH3COOH→10Pb(CH3COO)2+13H2O+6CO2    (5) Pb 10 O(CO 3 ) 6 (OH) 6 +20CH 3 COOH→10Pb(CH 3 COO) 2 +13H 2 O+6CO 2 (5)

NaPb2(CO3)2OH+5CH3COOH→2Pb(CH3COO)2+H2O+2CO2+Na(CH3COO) (6) NaPb 2 (CO 3 ) 2 OH+5CH 3 COOH→2Pb(CH 3 COO) 2 +H 2 O+2CO 2 +Na(CH 3 COO) (6)

Pb(OH)2+2CH3COOH→Pb(CH3COO)2+2H2O                      (7) Pb(OH) 2 +2CH 3 COOH→Pb(CH 3 COO) 2 +2H 2 O (7)

(3)碳酸铅的制备 (3) Preparation of lead carbonate

将(2)的乙酸铅溶液中加入的碳酸钠,铅与碳酸钠摩尔比为1:1.5,反应时间为0.5h,固液分离,得到的碳酸铅,碳酸铅的XRD的见图1,SEM图见图2。 The sodium carbonate added to the lead acetate solution of (2), the molar ratio of lead and sodium carbonate is 1:1.5, the reaction time is 0.5h, the solid-liquid separation, the obtained lead carbonate, the XRD of lead carbonate is shown in Figure 1, SEM See Figure 2 for the picture.

Pb(CH3COO)2+Na2CO3 →PbCO3+2Na(CH3COO)                (8)  Pb(CH 3 COO) 2 +Na 2 CO 3 →PbCO 3 +2Na(CH 3 COO) (8)

(4)焙烧制备超细铅粉 (4) Preparation of superfine lead powder by roasting

将(3)中的烘干后的产物碳酸铅放入焙烧炉中,在320 ℃焙烧1 h,得到超细氧化铅化合物产品,其XRD的见图3,SEM图见图4,图5。 Put the dried lead carbonate in (3) into a roasting furnace and roast at 320 °C for 1 h to obtain an ultrafine lead oxide compound product. See Figure 3 for XRD and Figure 4 and Figure 5 for SEM images.

采用本发明方法制备的超细氧化铅粉(PbO),其平均颗粒粒度小于2 μm,纳米晶粒径小于500 nm,纯度大于99.8%,整个工艺过程铅的回收率超过97%。  The ultrafine lead oxide powder (PbO) prepared by the method of the present invention has an average particle size of less than 2 μm, a nanocrystalline particle size of less than 500 nm, a purity of greater than 99.8%, and a lead recovery rate of more than 97% in the entire process. the

实施例2:Example 2:

与实施例1不同之处在于:浸出剂为硝酸,脱硫铅膏与硝酸的投料比例为脱硫铅膏中的铅与硝酸的摩尔比例为1:2.5,同时加入还原剂双氧水,脱硫铅膏中的PbO2与过氧化氢的摩尔比例为1:1.5反应,反应0.5 h后的后过滤分离,得到硝酸铅溶液。脱硫铅膏与硝酸溶液可能发生的反应方程式可能是: Difference with embodiment 1 is: leaching agent is nitric acid, and the molar ratio of the lead in the desulfurization lead paste and nitric acid is that the molar ratio of the lead in the desulfurization lead paste and nitric acid is 1:2.5, add reducing agent hydrogen peroxide simultaneously, the lead in the desulfurization lead paste The molar ratio of PbO 2 and hydrogen peroxide is 1:1.5 to react, after reacting for 0.5 h, filter and separate to obtain lead nitrate solution. The possible reaction equation between desulfurization lead paste and nitric acid solution may be:

PbCO3+2HNO3→Pb(NO3)2+H2O+ CO2                    (9) PbCO 3 +2HNO 3 →Pb(NO 3 ) 2 +H 2 O+ CO 2 (9)

PbO+2HNO3→Pb(NO3)2+H2O                           (10) PbO+2HNO 3 →Pb(NO 3 ) 2 +H 2 O (10)

PbO2+2HNO3 +H2O2→Pb(NO3)2+2H2O+ O2                      (11) PbO 2 +2HNO 3 +H 2 O 2 →Pb(NO 3 ) 2 +2H 2 O+ O 2 (11)

Pb3(CO3)2(OH)2+6HNO3→3Pb(NO3)2+4H2O+2CO2              (12) Pb 3 (CO 3 ) 2 (OH) 2 +6HNO 3 →3Pb(NO 3 ) 2 +4H 2 O+2CO 2 (12)

Pb10O(CO3)6(OH)6+20HNO3→10Pb(NO3)2+13H2O+6CO2          (13) Pb 10 O(CO 3 ) 6 (OH) 6 +20HNO 3 →10Pb(NO 3 ) 2 +13H 2 O+6CO 2 (13)

NaPb2(CO3)2OH+5HNO3→2Pb(NO3)2+3H2O+2CO2 + NaNO3          (14) NaPb 2 (CO 3 ) 2 OH+5HNO 3 →2Pb(NO 3 ) 2 +3H 2 O+2CO 2 + NaNO 3 (14)

Pb(OH)2+2HNO3→Pb(NO3)2+2H2O                 (15) Pb(OH) 2 +2HNO 3 →Pb(NO 3 ) 2 +2H 2 O (15)

硝酸铅溶液中加入的碳酸钠,铅与碳酸钠摩尔比为1:1.5,反应时间为0.5h,固液分离,得到的碳酸铅。反应方程为16 Sodium carbonate added to the lead nitrate solution, the molar ratio of lead to sodium carbonate is 1:1.5, the reaction time is 0.5h, and solid-liquid separation is performed to obtain lead carbonate. The reaction equation is 16

Pb(NO3)2+Na2CO3 →PbCO3+2NaNO3                     (16)  Pb(NO 3 ) 2 +Na 2 CO 3 →PbCO 3 +2NaNO 3 (16)

 其它物质的最终得到超细氧化铅粉产品,原料利用率98.3%,收率为99.0%。其它与实施例1相同,工艺主要参数见表1。 The final product of other substances is ultrafine lead oxide powder, the utilization rate of raw materials is 98.3%, and the yield is 99.0%. Others are the same as in Example 1, and the main process parameters are shown in Table 1.

 实施例3: Example 3:

与实施例1不同之处在于:焙烧温度为450 ℃,最终得到红色的超细氧化铅化合物产品,XRD见图6,SEM见图7、图8,原料利用率98.0%,收率为99.2%。其它与实施例1相同,工艺主要参数见表1。 The difference from Example 1 is that the calcination temperature is 450°C, and finally a red ultrafine lead oxide compound product is obtained. XRD is shown in Figure 6, SEM is shown in Figure 7 and Figure 8, the utilization rate of raw materials is 98.0%, and the yield is 99.2%. . Others are the same as in Example 1, and the main process parameters are shown in Table 1.

[0036] 实施例4: Embodiment 4:

与实施例1不同之处在于:酸浸出时乙酸的投加量为脱硫铅膏中的铅与乙酸的摩尔比例1:3,脱硫时固液比为1:15,最终得到超细氧化铅粉产品,原料利用率98.1%,收率95.6%。其它与实施例2相同,工艺主要参数见表1。 The difference from Example 1 is that the dosage of acetic acid during acid leaching is the molar ratio of lead and acetic acid in the desulfurization lead paste is 1:3, the solid-liquid ratio is 1:15 during desulfurization, and finally superfine lead oxide powder is obtained The product has a raw material utilization rate of 98.1%, and a yield of 95.6%. Others are the same as in Example 2, and the main process parameters are shown in Table 1.

Figure DEST_PATH_1
Figure DEST_PATH_1

Claims (8)

1. a ultra-fine lead oxide that utilizes the preparation of desulfurization lead plaster three-stage process is characterized in that described ultra-fine lead oxide can be PbO, Pb 3O 4, perhaps both mixtures, its average grain granularity is less than 2 μ m, and nanocrystalline particle diameter is less than 500 nm.
2. one kind is utilized the desulfurization lead plaster three-stage process to prepare the ultra-fine lead oxide method, it is characterized in that: comprise operation
Figure 2012101216659100001DEST_PATH_IMAGE001
The desulfurization lead plaster Ore Leaching: desulfurization lead plaster and acid-respons, add simultaneously reductive agent, after reaction finished, solid-liquid separation got leaded acid solution; Operation The preparation of lead carbonate: leaded acid solution and yellow soda ash reaction, solid-liquid separation, washing, drying obtain lead carbonate; Operation Roasting: lead carbonate makes ultra-fine lead oxide through after the roasting; Described operation Reductive agent be solubility inorganic oxidizer.
3. utilize as claimed in claim 2 the desulfurization lead plaster three-stage process to prepare the method for ultra-fine lead oxide, it is characterized in that: described operation
Figure 968822DEST_PATH_IMAGE001
Acid be acetic acid or nitric acid; Described operation
Figure 39546DEST_PATH_IMAGE001
Leaded acid solution be lead acetate or lead nitrate solution.
4. as described in claim 2 or 3, utilize the desulfurization lead plaster three-stage process to prepare the method for ultra-fine lead oxide, it is characterized in that: described operation In, desulfurization lead plaster with acid ingredient proportion be in the desulfurization lead plaster lead with acid molar ratio be l:2-5; Desulfurization lead plaster is 1:3-30 with the mass ratio that contains aqueous acid; Temperature of reaction is room temperature-50 ℃; Reaction times is 0.5-3 h, and the reaction times is 1 h preferably.
5. as described in claim 2 or 3, utilize the desulfurization lead plaster three-stage process to prepare the method for ultra-fine lead oxide, it is characterized in that: operation
Figure 258965DEST_PATH_IMAGE001
Middle solubility inorganic oxidizer is hydrogen peroxide, the PbO in the desulfurization lead plaster 2With the molar ratio of hydrogen peroxide be 1:1-8, preferential 1:1.5.
6. as described in claim 2 or 3, utilize the desulfurization lead plaster three-stage process to prepare the method for ultra-fine lead oxide, it is characterized in that: operation
Figure 739625DEST_PATH_IMAGE002
In leaded acid solution, add the yellow soda ash reaction, the molar ratio of leaded acid solution and yellow soda ash is 1:1.5-3, leaded acid solution and yellow soda ash reaction times are 0.1-2 h, preferred 0.5 h, temperature of reaction is room temperature-50 ℃.
7. as described in claim 2 or 3, utilize the desulfurization lead plaster three-stage process to prepare the method for ultra-fine lead oxide, it is characterized in that: operation
Figure 32066DEST_PATH_IMAGE002
In leaded acid solution, add the yellow soda ash reaction, add simultaneously the structure directing agent polyoxyethylene glycol of the plumbous weight 1-5% in the leaded acid solution.
8. as described in claim 2 or 3, utilize the desulfurization lead plaster three-stage process to prepare the method for ultra-fine lead oxide, it is characterized in that: operation The maturing temperature of middle lead carbonate is 250-500 ℃, and roasting time is 0.5-6 h, and final product is ultra-fine lead oxide.
CN2012101216659A 2012-04-24 2012-04-24 Ultrafine lead oxide prepared from desulfurated lead plaster by means of three-stage process and method thereof Pending CN103374658A (en)

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US9828654B2 (en) 2014-02-21 2017-11-28 Chilwee Power Co. Ltd & Beijing University Of Chemical Technology Method for directly recovering lead oxide used for a lead-acid battery cathode from waste lead paste
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CN110137452A (en) * 2019-04-26 2019-08-16 浙江工业大学 A kind of preparation method and application of Nanometer sized lead oxide/carbon composite
CN110127753A (en) * 2019-05-23 2019-08-16 昆明理工大学 A method for recycling lead oxide from waste lead-acid batteries
CN112939067A (en) * 2021-01-20 2021-06-11 生态环境部华南环境科学研究所 Method for producing nano high-purity lead oxide by resource treatment of waste lead paste
CN113136492A (en) * 2021-03-30 2021-07-20 广西大学 Method for recovering lead from waste lead paste
CN113277550A (en) * 2021-05-24 2021-08-20 湖北华德莱节能减排科技有限公司 Lead-containing solid waste treatment method, and preparation method and application of lead dioxide powder

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