WO2025054876A1 - Lithium battery positive electrode processing wastewater recovery and treatment apparatus and method - Google Patents
Lithium battery positive electrode processing wastewater recovery and treatment apparatus and method Download PDFInfo
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- WO2025054876A1 WO2025054876A1 PCT/CN2023/118700 CN2023118700W WO2025054876A1 WO 2025054876 A1 WO2025054876 A1 WO 2025054876A1 CN 2023118700 W CN2023118700 W CN 2023118700W WO 2025054876 A1 WO2025054876 A1 WO 2025054876A1
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B25/00—Phosphorus; Compounds thereof
- C01B25/16—Oxyacids of phosphorus; Salts thereof
- C01B25/26—Phosphates
- C01B25/30—Alkali metal phosphates
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B25/00—Phosphorus; Compounds thereof
- C01B25/16—Oxyacids of phosphorus; Salts thereof
- C01B25/26—Phosphates
- C01B25/32—Phosphates of magnesium, calcium, strontium, or barium
- C01B25/34—Magnesium phosphates
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/84—Recycling of batteries or fuel cells
Definitions
- the present application relates to the technical field of lithium battery positive electrode processing wastewater recovery, and in particular to a lithium battery positive electrode processing wastewater recovery and treatment device and method.
- iron phosphate needs to be prepared during the processing of lithium battery positive electrodes.
- Iron phosphate is usually synthesized by liquid phase reaction of ferrous sulfate, hydrogen peroxide and phosphoric acid under certain conditions. During the reaction, wastewater with high phosphorus content will be produced, which needs to be treated in a sewage treatment plant before being discharged.
- lithium washing wastewater is produced during the processing of lithium battery positive electrodes. The wastewater needs to be adjusted by pH value and then treated by MVR evaporator to recover lithium resources. Therefore, in the current treatment method of lithium battery positive electrode processing wastewater, phosphorus-containing wastewater is not effectively utilized, resulting in high recycling costs.
- the purpose of this application is to provide a device and method for recycling and treating wastewater from lithium battery positive electrode processing, so as to make more effective use of residual substances in the wastewater and reduce the cost of wastewater recycling.
- the present application provides a recycling and treatment device for lithium battery positive electrode processing wastewater, comprising:
- a collecting unit comprising a first storage tank and a second storage tank, wherein the first storage tank is used to store phosphorus-containing wastewater, and the second storage tank is used to store lithium-containing wastewater;
- the reaction unit comprises a tank body and a filter press module;
- the tank body comprises a connected reaction chamber and a sedimentation chamber, the reaction chamber is provided with a stirring module, the sedimentation chamber is provided with a horizontally arranged packing layer and a vertically arranged partition, one side of the packing layer is connected to the partition, the partition and the packing layer separate the sedimentation chamber into an upper area and a lower area, when wastewater is input into the sedimentation chamber, the wastewater passes through the packing layer from the lower area, enters the upper area and is discharged;
- the filter press module comprises a diaphragm pump and a filter press, The lower area is connected to the filter press through the diaphragm pump;
- the reaction unit is provided with two groups, which are respectively recorded as the first reaction unit and the second reaction unit, the reaction chamber of the first reaction unit is respectively connected to the first storage tank and the second storage tank, and the precipitation chamber of the first reaction unit is connected to the reaction chamber of the second reaction unit;
- the detection unit comprises a pH meter, a flow meter and a turbidity meter.
- the pH meter is installed in the reaction chamber.
- Two flow meters are provided and are installed at the outlet of the first storage tank and the outlet of the second storage tank respectively.
- the turbidity meter is installed in the precipitation chamber.
- the collection unit further includes a first centrifugal pump and a second centrifugal pump, the first storage tank is connected to the reaction chamber through the first centrifugal pump, and the second storage tank is connected to the reaction chamber through the second centrifugal pump.
- the cell body further includes a first end cap and a second end cap, wherein the first end cap is sealed on the reaction chamber, and the second end cap is sealed on the precipitation chamber.
- the stirring module includes a motor, a helical gear reducer and a stirring paddle connected in sequence, the helical gear reducer is installed on the upper part of the first end cover, and the stirring paddle is arranged at the lower part of the first end cover.
- a baffle is installed on the inner wall of the reaction chamber, and the baffle is arranged around the outer circumference of the stirring paddle.
- the pool body further includes a sludge scraper and suction machine, and the sludge scraper and suction machine is disposed on the second end cover.
- the packing layer is a honeycomb oblique tube packing layer.
- the tank body further includes a drainage chamber, which is communicated with the upper area of the sedimentation chamber, and the detection unit further includes a liquid level gauge, which is disposed in the drainage chamber.
- the present application provides a method for recycling and treating lithium battery positive electrode processing wastewater, comprising:
- the first storage tank and the second storage tank are opened to transport the phosphorus-containing wastewater and the lithium-containing wastewater into the reaction chamber of the first reaction unit, and the stirring module is started to obtain mixed wastewater.
- the pH value of the mixed wastewater is adjusted. After reaching 8-10, it flows into the sedimentation chamber of the first reaction unit, is filtered through the packing layer in the sedimentation chamber, and is precipitated in the lower area of the sedimentation chamber to form magnesium phosphate, and forms filtered wastewater in the upper area of the sedimentation chamber;
- the upper area of the sedimentation chamber of the first reaction unit is opened to transport the filtered wastewater into the reaction chamber of the second reaction unit, and the stirring module is started to adjust the pH value of the filtered wastewater to 11-13, and then the filtered wastewater flows into the sedimentation chamber of the second reaction unit, and is filtered through the packing layer in the sedimentation chamber to precipitate in the lower area of the sedimentation chamber to form lithium phosphate, and is discharged in the upper area of the sedimentation chamber as clean water;
- the diaphragm pumps of the first reaction unit and the second reaction unit are started to transport the magnesium phosphate and the lithium phosphate to the filter press respectively, and the magnesium phosphate filter cake and the lithium phosphate filter cake are obtained by pressing.
- the pH value of the mixed wastewater and the filtered wastewater is adjusted by injecting liquid alkali.
- the present application provides a lithium battery positive electrode processing wastewater recovery and treatment device, which has the following beneficial effects compared with the prior art:
- the first storage tank is used to store phosphorus-containing wastewater
- the second storage tank is used to store lithium-containing wastewater. Both wastewaters are generated during the processing of lithium battery positive electrodes.
- the reaction unit includes a cell body and a filter press module. The two wastewaters are mixed in the cell body to react and form precipitates, which are then squeezed through the filter press module to obtain magnesium phosphate filter cakes and lithium phosphate filter cakes, so that the materials in the wastewater can be effectively recovered, the residual substances in the wastewater can be more fully utilized, and the cost of wastewater recovery can be reduced.
- FIG1 is a schematic diagram of the overall structure of a device for recycling and treating lithium battery positive electrode processing wastewater provided in an embodiment of the present application.
- FIG. 2 is a schematic diagram of the enlarged structure of the cell body of the first reaction unit of the lithium battery positive electrode processing wastewater recovery and treatment device provided in an embodiment of the present application.
- FIG 3 is an enlarged structural schematic diagram of the filter press module of the lithium battery positive electrode processing wastewater recovery and treatment device provided in an embodiment of the present application.
- FIG. 4 is a schematic diagram of the enlarged structure of the stirring module of the lithium battery positive electrode processing wastewater recovery and treatment device provided in an embodiment of the present application.
- FIG. 5 shows the molar concentrations of lithium ions, magnesium ions and phosphate ions in the solution at different pH values.
- 100 recycling and processing device; 1, collecting unit; 11, first storage tank; 12, second storage tank; 2, reaction unit; 21, tank body; 210, drainage chamber; 211, reaction chamber; 212, sedimentation chamber; 212a, upper area; 212b, lower area; 213, stirring module; 2131, motor; 2132, helical gear reducer; 2133, stirring paddle; 214, packing layer; 215, partition; 216, first end cover; 217, second end cover; 218, baffle; 219, hanging suction machine; 23, filter press module; 231, diaphragm pump; 232, filter press; 3, detection unit; 31, pH meter; 32, flow meter; 33, turbidity meter; 34, liquid level meter.
- first and second are used for descriptive purposes only, and cannot be understood as indicating or implying relative importance or implicitly indicating the number of technical features indicated, that is, the features defined as “first” and “second” may explicitly or implicitly include one or more of the features.
- “multiple” means two or more.
- a lithium battery positive electrode processing wastewater recovery and treatment device 100 provided in an embodiment of the present application includes: a collection unit 1, including a first storage tank 11 and a second storage tank 12, the first storage tank 11 is used to store phosphorus-containing wastewater, and the second storage tank 12 is used to store lithium-containing wastewater; a reaction unit 2, which includes a cell body 21 and a filter press module 23; the cell body 21 includes a reaction chamber 211 and a sedimentation chamber 212 connected to each other, the reaction chamber 211 is equipped with a stirring module 213, and the sedimentation chamber 212 is equipped with a stirring module 213.
- a horizontally arranged packing layer 214 and a vertically arranged partition 215 are installed inside, one side of the packing layer 214 is connected to the partition 215, and the partition 215 and the packing layer 214 separate the sedimentation chamber 212 into an upper area 212a and a lower area 212b.
- the filter press module 23 includes a diaphragm pump 231 and a filter press 232, and the lower area 212b is connected to the filter press 232 through the diaphragm pump 231;
- the reaction unit 2 is provided with two groups, which are respectively recorded as the first reaction unit and the second reaction unit, and the reaction chamber 211 of the first reaction unit is respectively connected to the first storage tank 11 and the second storage tank 12, and the sedimentation chamber 212 of the first reaction unit is connected to the reaction chamber 211 of the second reaction unit;
- the detection unit 3 includes a pH meter 31, a flow meter 32 and a turbidity meter 33.
- the pH meter 31 is installed in the reaction chamber 211.
- Two flow meters 32 are provided and are installed at the outlet of the first storage tank 11 and the outlet of the second storage tank 11 respectively.
- the turbidity meter 33 is installed in the sedimentation chamber.
- the first storage tank 11 is used to store phosphorus-containing wastewater
- the second storage tank 12 is used to store lithium-containing wastewater.
- Both wastewaters are wastewater generated during the processing of lithium battery positive electrodes;
- the reaction unit 2 includes a cell body 21 and a filter press module 23.
- the two wastewaters are mixed in the cell body 21 for reaction, and the filter press module 23 is used to press to obtain magnesium phosphate filter cake and lithium phosphate filter cake, so that the materials in the wastewater can be effectively recovered, the residual substances in the wastewater can be more fully utilized, and the cost of wastewater recovery can be reduced.
- the collection unit 1 further includes a first centrifugal pump and a second centrifugal pump, the first storage tank 11 is connected to the reaction chamber 211 through the first centrifugal pump, and the second storage tank 12 is connected to the reaction chamber 211 through the second centrifugal pump.
- the first centrifugal pump and the second centrifugal pump can stably transport the wastewater in the first storage tank 11 and the second storage tank 12 to the reaction chamber 211 of the first reaction unit.
- the cell body 21 further includes a first end cap 216 and a second end cap 217.
- the first end cap 216 is sealed on the reaction chamber 211
- the second end cap 217 is sealed on the sedimentation chamber 212.
- the first end cap 216 and the second end cap 217 are provided so that the wastewater in the reaction chamber 211 and the sedimentation chamber 212 will not leak out during the reaction process.
- the stirring module 213 includes a motor 2131, The helical gear reducer 2132 and the stirring paddle 2133, the helical gear reducer 2132 is installed on the upper part of the first end cover 216, and the stirring paddle 2133 is arranged on the lower part of the first end cover 216, so that the installation structure of the stirring module 213 is stable; when working, the starting motor 2131 is adjusted through the helical gear reducer 2132, and the available output torque is increased without increasing the power consumption of the motor 2131, so that the stirring paddle 2133 can stir and mix the wastewater in the reaction chamber 211.
- a baffle 218 is installed on the inner wall of the reaction chamber 211, and the baffle 218 is arranged around the outer periphery of the stirring paddle 2133.
- the baffle 218 has an anti-swirl effect, so that the wastewater is mixed more evenly.
- the tank body 21 further includes a sludge scraper 219, which is disposed on the second end cover 217.
- the sludge scraper 219 is used to maintain and clean the tank body 21 when the tank body 21 is not in use.
- the packing layer 214 is a honeycomb inclined tube packing layer.
- a swirling flow is formed, so that a large contact area is generated between the sediment and the liquid, thereby accelerating the sedimentation of the sediment.
- the pool body 21 also includes a drainage chamber 210, which is connected to the upper area 212a of the sedimentation chamber 212, wherein the liquid in the drainage chamber 210 of the first reaction unit flows into the reaction chamber 211 of the second reaction unit, and the detection unit 3 also includes a liquid level gauge 34, which is arranged in the drainage chamber 210, and the liquid level gauge 34 is used to detect the liquid level height of the drainage chamber 210; according to actual needs, the liquid level gauge 34 can also be installed in the first storage tank 11, the second storage tank 12 and the reaction chamber 211 to measure the liquid level height.
- Another embodiment of the application provides a method for recycling and treating lithium battery positive electrode processing wastewater, comprising:
- the phosphorus-containing wastewater is collected by the first storage tank 11, and the lithium-containing wastewater is collected by the second storage tank 12; it should be noted that the phosphorus-containing wastewater is generated in the process of preparing iron phosphate, which is usually synthesized by liquid phase reaction of ferrous sulfate, hydrogen peroxide and phosphoric acid under certain conditions, and wastewater with high phosphorus content is generated during the reaction.
- the lithium-containing wastewater is generated in the process of lithium washing, and the wastewater also contains magnesium ions.
- the stirring module 213 Open the first storage tank 11 and the second storage tank 12 to transport the phosphorus-containing wastewater and the lithium-containing wastewater to the In the reaction chamber 211 of a reaction unit, the stirring module 213 is started to obtain mixed wastewater, and the pH value of the mixed wastewater is adjusted to 8-10 and then flows into the sedimentation chamber 212 of the first reaction unit. After being filtered through the packing layer 214 in the sedimentation chamber 212, magnesium phosphate is precipitated in the lower area 212b of the sedimentation chamber 212, and filtered wastewater is formed in the upper area 212a of the sedimentation chamber 212.
- the upper area 212a of the sedimentation chamber 212 of the first reaction unit is opened to transport the filtered waste water to the reaction chamber 211 of the second reaction unit, and the stirring module 213 is started to adjust the pH value of the filtered waste water to 11-13 and then flow into the sedimentation chamber 212 of the second reaction unit.
- the waste water is precipitated in the lower area 212b of the sedimentation chamber 212 to form lithium phosphate, and clean water is formed in the upper area 212a of the sedimentation chamber 212 for discharge.
- the pH value of the clean water is adjusted to 6-9 (optionally 7) by injecting acidic substances before being discharged.
- the diaphragm pumps 231 of the first reaction unit and the second reaction unit are started to transport magnesium phosphate and lithium phosphate to the filter press 232 respectively, and the magnesium phosphate filter cake and the lithium phosphate filter cake are obtained by squeezing.
- the diaphragm pump 231 is a pneumatic diaphragm pump
- the filter press 232 is a diaphragm filter press; the wastewater generated by the diaphragm filter presses of the first reaction unit and the second reaction unit after the filtration operation is transported to the sedimentation chambers 212 of the first reaction unit and the second reaction unit for reuse.
- the pH value of the mixed wastewater and the filtered wastewater is adjusted by injecting liquid alkali.
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Abstract
Description
本申请涉及锂电池正极加工废水回收技术领域,特别是涉及一种锂电池正极加工废水的回收处理装置及方法。The present application relates to the technical field of lithium battery positive electrode processing wastewater recovery, and in particular to a lithium battery positive electrode processing wastewater recovery and treatment device and method.
一方面在锂电池正极加工过程中需要制备磷酸铁,磷酸铁通常由硫酸亚铁、双氧水与磷酸在一定条件下液相反应合成,在反应过程中会产生含磷较高的废水,该废水需要通过污水处理厂处理后再排放。另一方面在锂电池正极加工过程中会产生洗锂废水,该废水需经PH值调节,再通过MVR蒸发器处理实现对锂资源进行回收。因此,目前锂电池正极加工废水处理方式中,对含磷废水未能有效的利用,使回收成本高。On the one hand, iron phosphate needs to be prepared during the processing of lithium battery positive electrodes. Iron phosphate is usually synthesized by liquid phase reaction of ferrous sulfate, hydrogen peroxide and phosphoric acid under certain conditions. During the reaction, wastewater with high phosphorus content will be produced, which needs to be treated in a sewage treatment plant before being discharged. On the other hand, lithium washing wastewater is produced during the processing of lithium battery positive electrodes. The wastewater needs to be adjusted by pH value and then treated by MVR evaporator to recover lithium resources. Therefore, in the current treatment method of lithium battery positive electrode processing wastewater, phosphorus-containing wastewater is not effectively utilized, resulting in high recycling costs.
发明内容Summary of the invention
本申请的目的是提供一种锂电池正极加工废水的回收处理装置及方法,更为充分的利用废水残留物质,降低废水回收成本。The purpose of this application is to provide a device and method for recycling and treating wastewater from lithium battery positive electrode processing, so as to make more effective use of residual substances in the wastewater and reduce the cost of wastewater recycling.
为了实现上述目的,一方面本申请提供了一种锂电池正极加工废水的回收处理装置,包括:In order to achieve the above-mentioned purpose, on the one hand, the present application provides a recycling and treatment device for lithium battery positive electrode processing wastewater, comprising:
收集单元,包括第一储槽和第二储槽,所述第一储槽用于存储含磷废水,所述第二储槽用于存储含锂废水;A collecting unit, comprising a first storage tank and a second storage tank, wherein the first storage tank is used to store phosphorus-containing wastewater, and the second storage tank is used to store lithium-containing wastewater;
反应单元,其包括池体和压滤模块;所述池体包括相连通的反应室和沉淀室,所述反应室内安装有搅拌模块,所述沉淀室内安装有水平布置的填料层和竖直布置的隔板,所述填料层的一侧与所述隔板连接,所述隔板与所述填料层将所述沉淀室分隔为上部区域和下部区域,当所述沉淀室输入废水时,该废水从所述下部区域通过所述填料层,再进入所述上部区域后排出;所述压滤模块包括隔膜泵和压滤机,所 述下部区域通过所述隔膜泵与所述压滤机连通;所述反应单元设有两组,分别记为第一反应单元和第二反应单元,所述第一反应单元的所述反应室分别与所述第一储槽及所述第二储槽连通,所述第一反应单元的所述沉淀室与所述第二反应单元的所述反应室连通;The reaction unit comprises a tank body and a filter press module; the tank body comprises a connected reaction chamber and a sedimentation chamber, the reaction chamber is provided with a stirring module, the sedimentation chamber is provided with a horizontally arranged packing layer and a vertically arranged partition, one side of the packing layer is connected to the partition, the partition and the packing layer separate the sedimentation chamber into an upper area and a lower area, when wastewater is input into the sedimentation chamber, the wastewater passes through the packing layer from the lower area, enters the upper area and is discharged; the filter press module comprises a diaphragm pump and a filter press, The lower area is connected to the filter press through the diaphragm pump; the reaction unit is provided with two groups, which are respectively recorded as the first reaction unit and the second reaction unit, the reaction chamber of the first reaction unit is respectively connected to the first storage tank and the second storage tank, and the precipitation chamber of the first reaction unit is connected to the reaction chamber of the second reaction unit;
检测单元,其包括PH计、流量计和浊度计,所述PH计安装于所述反应室内,所述流量计设有两个,且分别安装于所述第一储槽的出口及所述第二储槽的出口,所述浊度计安装于所述沉淀室内。The detection unit comprises a pH meter, a flow meter and a turbidity meter. The pH meter is installed in the reaction chamber. Two flow meters are provided and are installed at the outlet of the first storage tank and the outlet of the second storage tank respectively. The turbidity meter is installed in the precipitation chamber.
在一些实施例中,所述收集单元还包括第一离心泵和第二离心泵,所述第一储槽通过第一离心泵与所述反应室连通,所述第二储槽通过第二离心泵与所述反应室连通。In some embodiments, the collection unit further includes a first centrifugal pump and a second centrifugal pump, the first storage tank is connected to the reaction chamber through the first centrifugal pump, and the second storage tank is connected to the reaction chamber through the second centrifugal pump.
在一些实施例中,所述池体还包括第一端盖和第二端盖,所述第一端盖封盖于所述反应室上,所述第二端盖封盖于所述沉淀室上。In some embodiments, the cell body further includes a first end cap and a second end cap, wherein the first end cap is sealed on the reaction chamber, and the second end cap is sealed on the precipitation chamber.
在一些实施例中,所述搅拌模块包括依次连接的电机、斜齿轮减速机和搅拌桨,所述斜齿轮减速机安装于所述第一端盖的上部,所述搅拌桨设于所述第一端盖的下部。In some embodiments, the stirring module includes a motor, a helical gear reducer and a stirring paddle connected in sequence, the helical gear reducer is installed on the upper part of the first end cover, and the stirring paddle is arranged at the lower part of the first end cover.
在一些实施例中,所述反应室的内壁安装有挡板,所述挡板环绕设于所述搅拌桨的外周。In some embodiments, a baffle is installed on the inner wall of the reaction chamber, and the baffle is arranged around the outer circumference of the stirring paddle.
在一些实施例中,所述池体还包括刮吸泥机,所述刮吸泥机设于所述第二端盖上。In some embodiments, the pool body further includes a sludge scraper and suction machine, and the sludge scraper and suction machine is disposed on the second end cover.
在一些实施例中,所述填料层为蜂窝斜管填料层。In some embodiments, the packing layer is a honeycomb oblique tube packing layer.
在一些实施例中,所述池体还包括排液室,所述排液室与所述沉淀室的所述上部区域连通,所述检测单元还包括液位计,所述液位计设于所述排液室内。In some embodiments, the tank body further includes a drainage chamber, which is communicated with the upper area of the sedimentation chamber, and the detection unit further includes a liquid level gauge, which is disposed in the drainage chamber.
另一方面本申请提供了一种锂电池正极加工废水的回收处理方法,包括:On the other hand, the present application provides a method for recycling and treating lithium battery positive electrode processing wastewater, comprising:
通过第一储槽收集含磷废水,通过第二储槽收集含锂废水;collecting phosphorus-containing wastewater through a first storage tank and collecting lithium-containing wastewater through a second storage tank;
开启第一储槽和第二储槽将含磷废水及含锂废水输送到第一反应单元的反应室内,启动搅拌模块得到混合废水,将混合废水的PH值调 节至8~10后流入到第一反应单元的沉淀室中,经过沉淀室内的填料层过滤在沉淀室的下部区域沉淀形成磷酸镁,在沉淀室的上部区域形成过滤废水;The first storage tank and the second storage tank are opened to transport the phosphorus-containing wastewater and the lithium-containing wastewater into the reaction chamber of the first reaction unit, and the stirring module is started to obtain mixed wastewater. The pH value of the mixed wastewater is adjusted. After reaching 8-10, it flows into the sedimentation chamber of the first reaction unit, is filtered through the packing layer in the sedimentation chamber, and is precipitated in the lower area of the sedimentation chamber to form magnesium phosphate, and forms filtered wastewater in the upper area of the sedimentation chamber;
开启第一反应单元的沉淀室的上部区域将过滤废水输送到第二反应单元的反应室内,启动搅拌模块将过滤废水PH值调节至11~13后流入到第二反应单元的沉淀室中,经过沉淀室内的填料层过滤在沉淀室的下部区域沉淀形成磷酸锂,在沉淀室的上部区域形成清水排出;The upper area of the sedimentation chamber of the first reaction unit is opened to transport the filtered wastewater into the reaction chamber of the second reaction unit, and the stirring module is started to adjust the pH value of the filtered wastewater to 11-13, and then the filtered wastewater flows into the sedimentation chamber of the second reaction unit, and is filtered through the packing layer in the sedimentation chamber to precipitate in the lower area of the sedimentation chamber to form lithium phosphate, and is discharged in the upper area of the sedimentation chamber as clean water;
启动第一反应单元和第二反应单元的隔膜泵分别将磷酸镁和磷酸锂输送到压滤机内,压榨得到磷酸镁滤饼和磷酸锂滤饼。The diaphragm pumps of the first reaction unit and the second reaction unit are started to transport the magnesium phosphate and the lithium phosphate to the filter press respectively, and the magnesium phosphate filter cake and the lithium phosphate filter cake are obtained by pressing.
在一些实施例中,对所述混合废水及所述过滤废水的PH值调节时,通过注入液碱的方式进行。In some embodiments, the pH value of the mixed wastewater and the filtered wastewater is adjusted by injecting liquid alkali.
本申请提供一种锂电池正极加工废水的回收处理装置,与现有技术相比,其有益效果在于:The present application provides a lithium battery positive electrode processing wastewater recovery and treatment device, which has the following beneficial effects compared with the prior art:
设置的第一储槽用于存储含磷废水,第二储槽用于存储含锂废水,两种废水均为锂电池正极加工过程中产生的废水;设置的反应单元包括池体和压滤模块,两种废水混合在池体反应形成沉淀,通过压滤模块压榨得到磷酸镁滤饼和磷酸锂滤饼,使得废水中的材料能够有效的回收,更为充分的利用废水残留物质,降低废水回收成本。The first storage tank is used to store phosphorus-containing wastewater, and the second storage tank is used to store lithium-containing wastewater. Both wastewaters are generated during the processing of lithium battery positive electrodes. The reaction unit includes a cell body and a filter press module. The two wastewaters are mixed in the cell body to react and form precipitates, which are then squeezed through the filter press module to obtain magnesium phosphate filter cakes and lithium phosphate filter cakes, so that the materials in the wastewater can be effectively recovered, the residual substances in the wastewater can be more fully utilized, and the cost of wastewater recovery can be reduced.
图1为本申请实施例提供的锂电池正极加工废水的回收处理装置的整体结构示意图。FIG1 is a schematic diagram of the overall structure of a device for recycling and treating lithium battery positive electrode processing wastewater provided in an embodiment of the present application.
图2为本申请实施例提供的锂电池正极加工废水的回收处理装置的第一反应单元的池体放大结构示意图。2 is a schematic diagram of the enlarged structure of the cell body of the first reaction unit of the lithium battery positive electrode processing wastewater recovery and treatment device provided in an embodiment of the present application.
图3为本申请实施例提供的锂电池正极加工废水的回收处理装置的压滤模块放大结构示意图。3 is an enlarged structural schematic diagram of the filter press module of the lithium battery positive electrode processing wastewater recovery and treatment device provided in an embodiment of the present application.
图4为本申请实施例提供的锂电池正极加工废水的回收处理装置的搅拌模块放大结构示意图。 4 is a schematic diagram of the enlarged structure of the stirring module of the lithium battery positive electrode processing wastewater recovery and treatment device provided in an embodiment of the present application.
图5为在不同的PH值状态下锂离子、镁离子及磷酸根离子在溶液中物质的量浓度。FIG. 5 shows the molar concentrations of lithium ions, magnesium ions and phosphate ions in the solution at different pH values.
图中:100、回收处理装置;1、收集单元;11、第一储槽;12、第二储槽;2、反应单元;21、池体;210、排液室;211、反应室;212、沉淀室;212a、上部区域;212b、下部区域;213、搅拌模块;2131、电机;2132、斜齿轮减速机;2133、搅拌桨;214、填料层;215、隔板;216、第一端盖;217、第二端盖;218、挡板;219、挂吸泥机;23、压滤模块;231、隔膜泵;232、压滤机;3、检测单元;31、PH计;32、流量计;33、浊度计;34、液位计。In the figure: 100, recycling and processing device; 1, collecting unit; 11, first storage tank; 12, second storage tank; 2, reaction unit; 21, tank body; 210, drainage chamber; 211, reaction chamber; 212, sedimentation chamber; 212a, upper area; 212b, lower area; 213, stirring module; 2131, motor; 2132, helical gear reducer; 2133, stirring paddle; 214, packing layer; 215, partition; 216, first end cover; 217, second end cover; 218, baffle; 219, hanging suction machine; 23, filter press module; 231, diaphragm pump; 232, filter press; 3, detection unit; 31, pH meter; 32, flow meter; 33, turbidity meter; 34, liquid level meter.
下面将结合本申请实施例中的附图,对本申请实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本申请的一部分实施例,而不是全部的实施例。The technical solutions in the embodiments of the present application will be clearly and completely described below in conjunction with the drawings in the embodiments of the present application. Obviously, the described embodiments are only part of the embodiments of the present application, rather than all the embodiments.
需要理解的是,在本申请的描述中,术语“上”、“下”、“竖直”、“水平”、“顶”、“底”、“内”、“外”等指示的方位或位置关系为基于附图所示的方位或位置关系,仅是为了便于描述本申请和简化描述,而不是指示或暗示所指的装置或元件必须具有特定的方位、以特定的方位构造和操作,因此不能理解为对本申请的限制。术语“第一”、“第二”仅用于描述目的,而不能理解为指示或暗示相对重要性或者隐含指明所指示的技术特征的数量,也即,限定有“第一”、“第二”的特征可以明示或者隐含地包括一个或者更多个该特征。此外,除非另有说明,“多个”的含义是两个或两个以上。It should be understood that, in the description of the present application, the terms "upper", "lower", "vertical", "horizontal", "top", "bottom", "inside", "outside", etc., indicating the orientation or positional relationship are based on the orientation or positional relationship shown in the drawings, and are only for the convenience of describing the present application and simplifying the description, rather than indicating or implying that the device or element referred to must have a specific orientation, be constructed and operated in a specific orientation, and therefore cannot be understood as a limitation on the present application. The terms "first" and "second" are used for descriptive purposes only, and cannot be understood as indicating or implying relative importance or implicitly indicating the number of technical features indicated, that is, the features defined as "first" and "second" may explicitly or implicitly include one or more of the features. In addition, unless otherwise specified, "multiple" means two or more.
如图1-4所示,本申请一个实施例提供的锂电池正极加工废水的回收处理装置100,包括:收集单元1,包括第一储槽11和第二储槽12,第一储槽11用于存储含磷废水,第二储槽12用于存储含锂废水;反应单元2,其包括池体21和压滤模块23;池体21包括相连通的反应室211和沉淀室212,反应室211内安装有搅拌模块213,沉淀室212 内安装有水平布置的填料层214和竖直布置的隔板215,填料层214的一侧与隔板215连接,隔板215与填料层214将沉淀室212分隔为上部区域212a和下部区域212b,当沉淀室212输入废水时,该废水从下部区域212a通过填料层214,再进入上部区域212b后排出;压滤模块23包括隔膜泵231和压滤机232,下部区域212b通过隔膜泵231与压滤机232连通;反应单元2设有两组,分别记为第一反应单元和第二反应单元,第一反应单元的反应室211分别与第一储槽11及第二储槽12连通,第一反应单元的沉淀室212与第二反应单元的反应室211连通;As shown in Figures 1-4, a lithium battery positive electrode processing wastewater recovery and treatment device 100 provided in an embodiment of the present application includes: a collection unit 1, including a first storage tank 11 and a second storage tank 12, the first storage tank 11 is used to store phosphorus-containing wastewater, and the second storage tank 12 is used to store lithium-containing wastewater; a reaction unit 2, which includes a cell body 21 and a filter press module 23; the cell body 21 includes a reaction chamber 211 and a sedimentation chamber 212 connected to each other, the reaction chamber 211 is equipped with a stirring module 213, and the sedimentation chamber 212 is equipped with a stirring module 213. A horizontally arranged packing layer 214 and a vertically arranged partition 215 are installed inside, one side of the packing layer 214 is connected to the partition 215, and the partition 215 and the packing layer 214 separate the sedimentation chamber 212 into an upper area 212a and a lower area 212b. When wastewater is input into the sedimentation chamber 212, the wastewater passes through the packing layer 214 from the lower area 212a, enters the upper area 212b and is discharged; the filter press module 23 includes a diaphragm pump 231 and a filter press 232, and the lower area 212b is connected to the filter press 232 through the diaphragm pump 231; the reaction unit 2 is provided with two groups, which are respectively recorded as the first reaction unit and the second reaction unit, and the reaction chamber 211 of the first reaction unit is respectively connected to the first storage tank 11 and the second storage tank 12, and the sedimentation chamber 212 of the first reaction unit is connected to the reaction chamber 211 of the second reaction unit;
检测单元3,其包括PH计31、流量计32和浊度计33,PH计31安装于反应室211内,流量计32设有两个,且分别安装于第一储槽11的出口及第二储槽11的出口,浊度计33安装于沉淀室内。The detection unit 3 includes a pH meter 31, a flow meter 32 and a turbidity meter 33. The pH meter 31 is installed in the reaction chamber 211. Two flow meters 32 are provided and are installed at the outlet of the first storage tank 11 and the outlet of the second storage tank 11 respectively. The turbidity meter 33 is installed in the sedimentation chamber.
基于上述的设置,通过第一储槽11用于存储含磷废水,第二储槽12用于存储含锂废水,两种废水均为锂电池正极加工过程中产生的废水;反应单元2包括池体21和压滤模块23,两种废水混合在池体21反应,通过压滤模块压23榨得到磷酸镁滤饼和磷酸锂滤饼,使得废水中的材料能够有效的回收,更为充分的利用废水残留物质,降低废水回收成本。Based on the above-mentioned configuration, the first storage tank 11 is used to store phosphorus-containing wastewater, and the second storage tank 12 is used to store lithium-containing wastewater. Both wastewaters are wastewater generated during the processing of lithium battery positive electrodes; the reaction unit 2 includes a cell body 21 and a filter press module 23. The two wastewaters are mixed in the cell body 21 for reaction, and the filter press module 23 is used to press to obtain magnesium phosphate filter cake and lithium phosphate filter cake, so that the materials in the wastewater can be effectively recovered, the residual substances in the wastewater can be more fully utilized, and the cost of wastewater recovery can be reduced.
在一个实施例中,收集单元1还包括第一离心泵和第二离心泵,第一储槽11通过第一离心泵与反应室211连通,第二储槽12通过第二离心泵与反应室211连通。通过第一离心泵和第二离心泵能够将第一储槽11和第二储槽12内的废水稳定输送到第一反应单元的反应室211中。In one embodiment, the collection unit 1 further includes a first centrifugal pump and a second centrifugal pump, the first storage tank 11 is connected to the reaction chamber 211 through the first centrifugal pump, and the second storage tank 12 is connected to the reaction chamber 211 through the second centrifugal pump. The first centrifugal pump and the second centrifugal pump can stably transport the wastewater in the first storage tank 11 and the second storage tank 12 to the reaction chamber 211 of the first reaction unit.
如图2所示,池体21还包括第一端盖216和第二端盖217,第一端盖216封盖于反应室211上,第二端盖217封盖于沉淀室212上。通过设置第一端盖216和第二端盖217使得反应室211和沉淀室212内的废水在反应过程中不会泄漏出来。As shown in Fig. 2, the cell body 21 further includes a first end cap 216 and a second end cap 217. The first end cap 216 is sealed on the reaction chamber 211, and the second end cap 217 is sealed on the sedimentation chamber 212. The first end cap 216 and the second end cap 217 are provided so that the wastewater in the reaction chamber 211 and the sedimentation chamber 212 will not leak out during the reaction process.
具体的,如图4所示,搅拌模块213包括依次连接的电机2131、 斜齿轮减速机2132和搅拌桨2133,斜齿轮减速机2132安装于第一端盖216的上部,搅拌桨2133设于第一端盖216的下部,使得搅拌模块213安装结构稳定;在工作时,启动电机2131通过斜齿轮减速机2132进行调节,在不增加电机2131功耗的情况下增加可用的输出扭矩,使得搅拌桨2133能够在反应室211内对废水进行搅拌混合。Specifically, as shown in FIG. 4 , the stirring module 213 includes a motor 2131, The helical gear reducer 2132 and the stirring paddle 2133, the helical gear reducer 2132 is installed on the upper part of the first end cover 216, and the stirring paddle 2133 is arranged on the lower part of the first end cover 216, so that the installation structure of the stirring module 213 is stable; when working, the starting motor 2131 is adjusted through the helical gear reducer 2132, and the available output torque is increased without increasing the power consumption of the motor 2131, so that the stirring paddle 2133 can stir and mix the wastewater in the reaction chamber 211.
可选的,反应室211的内壁安装有挡板218,挡板218环绕设于搅拌桨2133的外周。挡板218具有防旋流的效果,使得废水的混合更加均匀。Optionally, a baffle 218 is installed on the inner wall of the reaction chamber 211, and the baffle 218 is arranged around the outer periphery of the stirring paddle 2133. The baffle 218 has an anti-swirl effect, so that the wastewater is mixed more evenly.
在一个实施例中,池体21还包括刮吸泥机219,刮吸泥机219设于第二端盖217上。刮吸泥机219的作用是在池体21不使用时对池体21进行维护清理。In one embodiment, the tank body 21 further includes a sludge scraper 219, which is disposed on the second end cover 217. The sludge scraper 219 is used to maintain and clean the tank body 21 when the tank body 21 is not in use.
具体的,填料层214为蜂窝斜管填料层。废水在经过蜂窝斜管填料层的过程中会形成旋流状的流动,使沉淀物与液体之间产生大量的接触面积,从而较快地加速沉淀物的沉淀。Specifically, the packing layer 214 is a honeycomb inclined tube packing layer. When the wastewater passes through the honeycomb inclined tube packing layer, a swirling flow is formed, so that a large contact area is generated between the sediment and the liquid, thereby accelerating the sedimentation of the sediment.
在一个实施例中,池体21还包括排液室210,排液室210与沉淀室212的上部区域212a连通,其中,第一反应单元的排液室210中的液体流入到第二反应单元的反应室211内,检测单元3还包括液位计34,液位计34设于排液室210内,液位计34用于检测排液室210的液面高度;根据实际需要液位计34还可以安装在第一储槽11、第二储槽12以及反应室211内,对液面高度进行测量。In one embodiment, the pool body 21 also includes a drainage chamber 210, which is connected to the upper area 212a of the sedimentation chamber 212, wherein the liquid in the drainage chamber 210 of the first reaction unit flows into the reaction chamber 211 of the second reaction unit, and the detection unit 3 also includes a liquid level gauge 34, which is arranged in the drainage chamber 210, and the liquid level gauge 34 is used to detect the liquid level height of the drainage chamber 210; according to actual needs, the liquid level gauge 34 can also be installed in the first storage tank 11, the second storage tank 12 and the reaction chamber 211 to measure the liquid level height.
申请另一个实施例提供了锂电池正极加工废水的回收处理方法,包括:Another embodiment of the application provides a method for recycling and treating lithium battery positive electrode processing wastewater, comprising:
通过第一储槽11收集含磷废水,通过第二储槽12收集含锂废水;需要说明的是,含磷废水是在制备磷酸铁的过程中产生的,磷酸铁通常由硫酸亚铁、双氧水与磷酸在一定条件下液相反应合成,在反应过程中会产生含磷较高的废水。含锂废水是在洗锂加工过程中产生的,并且废水中还含有镁离子。The phosphorus-containing wastewater is collected by the first storage tank 11, and the lithium-containing wastewater is collected by the second storage tank 12; it should be noted that the phosphorus-containing wastewater is generated in the process of preparing iron phosphate, which is usually synthesized by liquid phase reaction of ferrous sulfate, hydrogen peroxide and phosphoric acid under certain conditions, and wastewater with high phosphorus content is generated during the reaction. The lithium-containing wastewater is generated in the process of lithium washing, and the wastewater also contains magnesium ions.
开启第一储槽11和第二储槽12将含磷废水及含锂废水输送到第 一反应单元的反应室211内,启动搅拌模块213得到混合废水,将混合废水的PH值调节至8~10后流入到第一反应单元的沉淀室212中,经过沉淀室212内的填料层214过滤在沉淀室212的下部区域212b沉淀形成磷酸镁,在沉淀室212的上部区域212a形成过滤废水。Open the first storage tank 11 and the second storage tank 12 to transport the phosphorus-containing wastewater and the lithium-containing wastewater to the In the reaction chamber 211 of a reaction unit, the stirring module 213 is started to obtain mixed wastewater, and the pH value of the mixed wastewater is adjusted to 8-10 and then flows into the sedimentation chamber 212 of the first reaction unit. After being filtered through the packing layer 214 in the sedimentation chamber 212, magnesium phosphate is precipitated in the lower area 212b of the sedimentation chamber 212, and filtered wastewater is formed in the upper area 212a of the sedimentation chamber 212.
开启第一反应单元的沉淀室212的上部区域212a将过滤废水输送到第二反应单元的反应室211内,启动搅拌模块213将过滤废水PH值调节至11~13后流入到第二反应单元的沉淀室212中,经过沉淀室212内的填料层214过滤在沉淀室212的下部区域212b沉淀形成磷酸锂,在沉淀室212的上部区域212a形成清水排出,其中,当清水排出到排液室210后,通过注入酸性物质将清水的PH值调节为6~9(可选为7)后再进行外排。The upper area 212a of the sedimentation chamber 212 of the first reaction unit is opened to transport the filtered waste water to the reaction chamber 211 of the second reaction unit, and the stirring module 213 is started to adjust the pH value of the filtered waste water to 11-13 and then flow into the sedimentation chamber 212 of the second reaction unit. After being filtered through the filler layer 214 in the sedimentation chamber 212, the waste water is precipitated in the lower area 212b of the sedimentation chamber 212 to form lithium phosphate, and clean water is formed in the upper area 212a of the sedimentation chamber 212 for discharge. After the clean water is discharged into the drainage chamber 210, the pH value of the clean water is adjusted to 6-9 (optionally 7) by injecting acidic substances before being discharged.
根据图5所示,比较不同的PH值状态下锂离子、镁离子及磷酸根离子在溶液中物质的量浓度(物质的量浓度越低表示溶液中沉淀物越多)可知,当沉淀形成磷酸镁时,PH值可选的调节至9;当沉淀形成磷酸锂时,PH值可选的调节至12。通过上述步骤,在第一反应单元和第二反应单元的沉淀室212内分别沉淀得到磷酸镁和磷酸锂。As shown in FIG5 , by comparing the molar concentrations of lithium ions, magnesium ions and phosphate ions in the solution under different pH values (the lower the molar concentration, the more precipitates in the solution), it can be seen that when magnesium phosphate is precipitated, the pH value can be optionally adjusted to 9; when lithium phosphate is precipitated, the pH value can be optionally adjusted to 12. Through the above steps, magnesium phosphate and lithium phosphate are precipitated in the precipitation chambers 212 of the first reaction unit and the second reaction unit, respectively.
在另一个实施例中,启动第一反应单元和第二反应单元的隔膜泵231分别将磷酸镁和磷酸锂输送到压滤机232内,压榨得到磷酸镁滤饼和磷酸锂滤饼。其中隔膜泵231为气动隔膜泵,压滤机232为隔膜压滤机;第一反应单元和第二反应单元的隔膜压滤机进过压滤作业后形成的废水对应输送到第一反应单元和第二反应单元的沉淀室212中再次利用。In another embodiment, the diaphragm pumps 231 of the first reaction unit and the second reaction unit are started to transport magnesium phosphate and lithium phosphate to the filter press 232 respectively, and the magnesium phosphate filter cake and the lithium phosphate filter cake are obtained by squeezing. The diaphragm pump 231 is a pneumatic diaphragm pump, and the filter press 232 is a diaphragm filter press; the wastewater generated by the diaphragm filter presses of the first reaction unit and the second reaction unit after the filtration operation is transported to the sedimentation chambers 212 of the first reaction unit and the second reaction unit for reuse.
在另一个实施例中,对混合废水及过滤废水的PH值调节时,通过注入液碱的方式进行。In another embodiment, the pH value of the mixed wastewater and the filtered wastewater is adjusted by injecting liquid alkali.
以上所述仅是本申请的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本申请技术原理的前提下,还可以做出若干改进和替换,这些改进和替换也应视为本申请的保护范围。 The above is only a preferred implementation of the present application. It should be pointed out that for ordinary technicians in this technical field, several improvements and substitutions can be made without departing from the technical principles of the present application. These improvements and substitutions should also be regarded as the scope of protection of the present application.
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| CN202380010739.8A CN117480128B (en) | 2023-09-14 | 2023-09-14 | A device and method for recycling wastewater from lithium battery positive electrode processing |
| PCT/CN2023/118700 WO2025054876A1 (en) | 2023-09-14 | 2023-09-14 | Lithium battery positive electrode processing wastewater recovery and treatment apparatus and method |
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| PCT/CN2023/118700 WO2025054876A1 (en) | 2023-09-14 | 2023-09-14 | Lithium battery positive electrode processing wastewater recovery and treatment apparatus and method |
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| CN117480128B (en) | 2025-09-30 |
| CN117480128A (en) | 2024-01-30 |
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