CN115353238A - Treatment method of battery-grade lithium nitrate production wastewater - Google Patents
Treatment method of battery-grade lithium nitrate production wastewater Download PDFInfo
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Abstract
Description
技术领域technical field
本发明属于废水处理技术领域,具体涉及一种电池级硝酸锂生产废水的处理方法。The invention belongs to the technical field of waste water treatment, and in particular relates to a treatment method for battery-grade lithium nitrate production waste water.
背景技术Background technique
硝酸锂(LiNO3)是一种在锂离子电池生产中不可或缺的电极材料,不论是磷酸铁锂电池还是三元锂电池,都离不开硝酸锂的使用。随着新能源产业特别是新能源汽车的兴起,锂离子电池需求量大增,从而带来硝酸锂的需求量逐年增高。硝酸锂生产废水的处理及废水中高价值物料的回收成为一个新的课题。Lithium nitrate (LiNO 3 ) is an indispensable electrode material in the production of lithium-ion batteries. Whether it is a lithium iron phosphate battery or a ternary lithium battery, the use of lithium nitrate is inseparable. With the rise of the new energy industry, especially new energy vehicles, the demand for lithium-ion batteries has increased significantly, which has led to an increase in the demand for lithium nitrate year by year. The treatment of lithium nitrate production wastewater and the recovery of high-value materials in wastewater have become a new topic.
硝酸锂生产过程一般会使用碳酸锂或氢氧化锂与硝酸反应,并对反应生成的硝酸锂进行蒸发、干燥得到,因此在此过程中会产生蒸发、干燥产生的冷凝水,水中含有系统带出的硝酸锂等生成原料。The production process of lithium nitrate generally uses lithium carbonate or lithium hydroxide to react with nitric acid, and the lithium nitrate produced by the reaction is evaporated and dried. Therefore, condensed water generated by evaporation and drying will be produced in this process, and the water contains system. Lithium nitrate and other raw materials.
由于硝酸锂废水中硝酸锂浓度较低,在通常的处理工艺中,通常会将硝酸锂废水经物化混凝沉淀后排放或并入厂区生活污水等其他废水一同处理达标后排放。造成水资源与硝酸锂原料的浪费。Due to the low concentration of lithium nitrate in lithium nitrate wastewater, in the usual treatment process, lithium nitrate wastewater is usually discharged after physical and chemical coagulation and sedimentation or merged into other wastewater such as domestic sewage in the factory area for treatment and discharge after reaching the standard. Cause the waste of water resource and lithium nitrate raw material.
发明内容Contents of the invention
本发明旨在解决上述问题,提供了一种电池级硝酸锂生产废水的处理方法,能够实现水资源、锂资源的综合回收利用。The present invention aims to solve the above problems, and provides a treatment method for battery-grade lithium nitrate production wastewater, which can realize the comprehensive recovery and utilization of water resources and lithium resources.
按照本发明的技术方案,所述电池级硝酸锂生产废水的处理方法,包括以下步骤,According to the technical scheme of the present invention, the treatment method of said battery-grade lithium nitrate production wastewater comprises the following steps,
S1:电池级硝酸锂生产废水进入换热单元进行降温;S1: The battery-grade lithium nitrate production wastewater enters the heat exchange unit for cooling;
S2:降温后的电池级硝酸锂生产废水进入超滤单元进行过滤,过滤所得浓水直接排放,过滤所得产水进入进入一级软化器,去除钙镁离子;S2: The battery-grade lithium nitrate production wastewater after cooling enters the ultrafiltration unit for filtration, the concentrated water obtained from the filtration is directly discharged, and the product water obtained from the filtration enters the primary softener to remove calcium and magnesium ions;
S3:一级软化器产水进入一级反渗透单元进行浓缩分离,一级反渗透单元浓缩分离所得产水作为循环冷却水排出,一级反渗透单元浓缩分离所得浓水进入二级软化器,去除钙镁离子;S3: The water produced by the first-stage softener enters the first-stage reverse osmosis unit for concentration and separation. The product water obtained by the concentration and separation of the first-stage reverse osmosis unit is discharged as circulating cooling water, and the concentrated water obtained by the concentration and separation of the first-stage reverse osmosis unit enters the second-stage softener. Remove calcium and magnesium ions;
S4:二级软化器产水进入二级反渗透单元进行浓缩分离,二级反渗透单元浓缩分离所得产水作为循环冷却水排出;S4: The water produced by the secondary softener enters the secondary reverse osmosis unit for concentration and separation, and the product water obtained from the concentration and separation of the secondary reverse osmosis unit is discharged as circulating cooling water;
S5:二级反渗透单元浓缩分离所得浓水进入电渗析单元进行盐水分离,盐水分离所得产水回流至一级反渗透单元继续处理或直接排放,盐水分离所得浓水作为生产原料提锂回用,完成电池级硝酸锂生产废水的处理。S5: The concentrated water obtained from the concentration and separation of the secondary reverse osmosis unit enters the electrodialysis unit for brine separation, and the product water obtained from the brine separation is returned to the primary reverse osmosis unit for further treatment or directly discharged, and the concentrated water obtained from the brine separation is used as a production raw material to extract lithium for reuse , Complete the treatment of battery-grade lithium nitrate production wastewater.
本发明通过膜系统、电渗析系统的联合使用将水资源、锂资源得到综合回收利用。The invention comprehensively recycles water resources and lithium resources through the joint use of membrane system and electrodialysis system.
进一步的,所述步骤S1中,电池级硝酸锂生产废水进入换热单元前储存于调节池,调节池用于电池级硝酸锂生产废水的缓冲储存。Further, in the step S1, the battery-grade lithium nitrate production wastewater is stored in a regulating tank before entering the heat exchange unit, and the regulating pond is used for buffer storage of the battery-grade lithium nitrate production wastewater.
进一步的,所述步骤S1中,降温至30-40℃,优选为35℃,用于保护后续处理中的膜材料。Further, in the step S1, the temperature is lowered to 30-40° C., preferably 35° C., to protect the membrane material in subsequent processing.
进一步的,所述超滤单元中的超滤膜平均孔径30-70nm。Further, the average pore size of the ultrafiltration membrane in the ultrafiltration unit is 30-70 nm.
进一步的,所述步骤S2中,采用外压式过滤。Further, in the step S2, external pressure filtration is adopted.
进一步的,所述步骤S2中,超滤单元的产水率90-95%,优选为93%,其进水流速为28-32m3/h,产水流速为26-29m3/h(进入一级软化器),浓水流速为1.5-2.5m3/h排放;在一个实施例中,进水流速为29m3/h,产水流速为27m3/h(进入一级软化器),浓水流速为2m3/h排放Further, in the step S2, the water production rate of the ultrafiltration unit is 90-95%, preferably 93%, the feed water flow rate is 28-32m 3 /h, and the water production flow rate is 26-29m 3 /h (into primary softener), the flow rate of concentrated water is 1.5-2.5m 3 /h; in one embodiment, the flow rate of incoming water is 29m 3 /h, and the flow rate of product water is 27m 3 /h (entering the primary softener), Concentrated water flow rate is 2m 3 /h discharge
进一步的,所述步骤S3中,一级反渗透单元中浓缩分离的平均操作压力为0.7-1.0mpa。Further, in the step S3, the average operating pressure of concentration and separation in the primary reverse osmosis unit is 0.7-1.0 mpa.
进一步的,所述步骤S3中,一级反渗透单元中浓缩分离的产水回收率为70-80%,优选为75%;其进水流速为26-29m3/h,浓水流速为6.5-7.5m3/h。Further, in the step S3, the recovery rate of the concentrated and separated product water in the primary reverse osmosis unit is 70-80%, preferably 75%; -7.5m 3 /h.
进一步的,所述步骤S4中,二级反渗透单元中浓缩分离的平均操作压力为1.2-2.0mpa。Further, in the step S4, the average operating pressure of concentration and separation in the secondary reverse osmosis unit is 1.2-2.0 mpa.
进一步的,所述步骤S5中,二级反渗透单元中浓缩分离的产水回收率为55-65%,优选为75%;其进水流速为6.5-7.5m3/h,浓水流速为2.5-3.0m3/h;。Further, in the step S5, the recovery rate of the concentrated and separated product water in the secondary reverse osmosis unit is 55-65%, preferably 75%; the influent flow rate is 6.5-7.5m 3 /h, and the concentrated water flow rate is 2.5-3.0m 3 /h;.
具体的,上述处理方法所采用的处理系统包括依次连通的换热单元、超滤单元、一级软化器、一级反渗透单元、一级软化器、二级反渗透单元和电渗析单元,其中一级反渗透单元和二级反渗透单元的产水出口连接氧化池,电渗析单元的产水出口连接一级反渗透单元和/或排水池,电渗析单元的浓水出口设有回用水池。Specifically, the treatment system adopted in the above treatment method includes a heat exchange unit, an ultrafiltration unit, a primary softener, a primary reverse osmosis unit, a primary softener, a secondary reverse osmosis unit, and an electrodialysis unit connected in sequence, wherein The water outlet of the first-stage reverse osmosis unit and the second-stage reverse osmosis unit are connected to the oxidation tank, the water outlet of the electrodialysis unit is connected to the first-stage reverse osmosis unit and/or the drainage pond, and the concentrated water outlet of the electrodialysis unit is provided with a reuse pool .
进一步的,换热单元为板式换热器,其换热材质可以为SUS304(304不锈钢),换热单元的进水口端设有调节池;超滤单元包括超滤进水箱、超滤进水泵、超滤反洗泵、超滤膜组,超滤管路、仪表等;一级软化器、二级软化器括软化进水箱、软化器罐体、树脂、再生系统,软化器管路、软化器仪表。Further, the heat exchange unit is a plate heat exchanger, and its heat exchange material can be SUS304 (304 stainless steel), and the water inlet end of the heat exchange unit is provided with a regulating pool; the ultrafiltration unit includes an ultrafiltration water inlet tank, an ultrafiltration water inlet pump , ultrafiltration backwash pump, ultrafiltration membrane group, ultrafiltration pipeline, instrument, etc.; primary softener, secondary softener including softening water inlet tank, softener tank, resin, regeneration system, softener pipeline, Softener meter.
本发明的技术方案相比现有技术具有以下优点:Compared with the prior art, the technical solution of the present invention has the following advantages:
(1)本发明利用反渗透膜高效盐水分离作用及电渗析离子交换膜选择性透过性能的,实现盐类物质与有机物从溶液中脱除或富集浓缩,产生高浓度硝酸锂溶液;(1) The present invention utilizes the high-efficiency brine separation effect of the reverse osmosis membrane and the selective permeation performance of the electrodialysis ion-exchange membrane to realize the removal or enrichment and concentration of salts and organic matter from the solution to produce a high-concentration lithium nitrate solution;
(2)本发明有效解决了常规技术在对电池级硝酸锂生产废水进行处理时,存在的水资源与硝酸锂原料的浪费的问题,实现了水资源、锂资源的综合回收利用。(2) The present invention effectively solves the problem of waste of water resources and lithium nitrate raw materials that exist when the conventional technology is processing battery-grade lithium nitrate production wastewater, and realizes comprehensive recycling of water resources and lithium resources.
附图说明Description of drawings
图1为实施例1中的处理系统的结构示意图。FIG. 1 is a schematic structural view of the processing system in Example 1.
图2为实施例2中的处理方法的流程示意图。Figure 2 is a schematic flow chart of the processing method in Example 2.
附图标记说明:1-调节池、2-换热单元、3-超滤单元、4-一级软化器、5-一级反渗透单元、6-一级软化器、7-二级反渗透单元、8-电渗析单元、9-氧化池、10-排水池、11-回用水池。Explanation of reference signs: 1-regulating tank, 2-heat exchange unit, 3-ultrafiltration unit, 4-first-stage softener, 5-first-stage reverse osmosis unit, 6-first-stage softener, 7-second-stage reverse osmosis unit, 8-electrodialysis unit, 9-oxidation tank, 10-drainage tank, 11-reuse water tank.
具体实施方式Detailed ways
下面结合附图和具体实施例对本发明作进一步说明,以使本领域的技术人员可以更好地理解本发明并能予以实施,但所举实施例不作为对本发明的限定。The present invention will be further described below in conjunction with the accompanying drawings and specific embodiments, so that those skilled in the art can better understand the present invention and implement it, but the examples given are not intended to limit the present invention.
实施例1Example 1
如图1所示,电池级硝酸锂生产废水的处理系统,包括依次连通的调节池1、换热单元2、超滤单元3、一级软化器4、一级反渗透单元5、一级软化器6、二级反渗透单元7和电渗析单元8。其中,超滤单元3的浓水出口连接排水池10;一级反渗透单元5和二级反渗透单元7的产水出口连接氧化池9;电渗析单8的产水出口连接一级反渗透单元5和/或排水池10,电渗析单元的浓水出口连接回用水池11。As shown in Figure 1, the treatment system for battery-grade lithium nitrate production wastewater includes a regulating tank 1, a heat exchange unit 2, an ultrafiltration unit 3, a
实施例2Example 2
如图2所示,电池级硝酸锂生产废水的处理方法,采用实施例1中的处理系统,包括以下步骤:As shown in Figure 2, the treatment method of battery-grade lithium nitrate production waste water adopts the treatment system in embodiment 1, comprises the following steps:
S1:使用增压泵将存储于调节池中的电池级硝酸锂生产废水(废水)泵入换热单元(板式换热器)在冷却水的作用下进行降温,废水温度从50℃降低至35℃;S1: Use a booster pump to pump the battery-grade lithium nitrate production wastewater (wastewater) stored in the regulating tank into the heat exchange unit (plate heat exchanger) to cool down under the action of cooling water, and the temperature of the wastewater is reduced from 50°C to 35°C ℃;
调节池的废水总盐分为1000mg/L,废水通入调节池的流速为29m3/h;换热单元的进水流速为29m3/h;The total salt content of the wastewater in the regulating tank is 1000mg/L, and the flow rate of the wastewater entering the regulating tank is 29m 3 /h; the flow rate of the water entering the heat exchange unit is 29m 3 /h;
S2:降温后的电池级硝酸锂生产废水进入超滤单元进行过滤,去除其中的悬浮物;超滤单元过滤所得浓水直接排放,过滤所得产水进入进入一级软化器,去除钙镁离子;S2: The battery-grade lithium nitrate production wastewater after cooling enters the ultrafiltration unit for filtration to remove suspended solids; the concentrated water filtered by the ultrafiltration unit is directly discharged, and the filtered product water enters the primary softener to remove calcium and magnesium ions;
超滤单元包括超滤进水箱、超滤进水泵、超滤反洗泵、超滤膜组,管路、仪表等;超滤单元设计产水率93%,进水流速29m3/h,产水以流速27m3/h进入一级软化器,浓水以流速2m3/h排放(排入排水池10);The ultrafiltration unit includes an ultrafiltration water inlet tank, an ultrafiltration water inlet pump, an ultrafiltration backwash pump, an ultrafiltration membrane group, pipelines, instruments, etc.; the designed water production rate of the ultrafiltration unit is 93%, and the influent flow rate is 29m3 /h. The produced water enters the primary softener at a flow rate of 27m 3 /h, and the concentrated water is discharged at a flow rate of 2m 3 /h (into the drainage tank 10);
S3:一级软化器产水进入一级反渗透单元进行浓缩(将硝酸锂进行浓缩)分离,一级反渗透单元浓缩分离所得产水作为循环冷却水(用于厂区循环)排出,一级反渗透单元浓缩分离所得浓水进入二级软化器,去除钙镁离子;S3: The water produced by the primary softener enters the primary reverse osmosis unit for concentration (concentrating lithium nitrate) and separation. Concentrated water obtained from the concentration and separation of the osmosis unit enters the secondary softener to remove calcium and magnesium ions;
一级反渗透单元设计产水回收率75%,进水流速27m3/h,产水流速20.25m3/h(排入氧化池),浓水以流速6.75m3/h进入二级软化器,经过一级反渗透系统,硝酸锂浓度被浓缩提高至原水(电池级硝酸锂生产废水)的4倍;The designed water recovery rate of the primary reverse osmosis unit is 75%, the influent flow rate is 27m 3 /h, the product water flow rate is 20.25m 3 /h (discharged into the oxidation tank), and the concentrated water enters the secondary softener at a flow rate of 6.75m 3 /h , after a first-stage reverse osmosis system, the concentration of lithium nitrate is concentrated and increased to 4 times that of raw water (battery-grade lithium nitrate production wastewater);
S4:二级软化器产水进入二级反渗透单元进行浓缩分离,二级反渗透单元浓缩分离所得产水作为循环冷却水排出;S4: The water produced by the secondary softener enters the secondary reverse osmosis unit for concentration and separation, and the product water obtained from the concentration and separation of the secondary reverse osmosis unit is discharged as circulating cooling water;
二级反渗透单元设计产水回收率60%,进水流速6.75m3/h,产水流速4.05m3/h(排入氧化池),浓水以流速2.7m3/h进入电渗析单元,经过二级反渗透单元,硝酸锂浓度被浓缩提高至原水的10倍;The design water recovery rate of the two-stage reverse osmosis unit is 60%, the influent flow rate is 6.75m 3 /h, the product water flow rate is 4.05m 3 /h (discharged into the oxidation tank), and the concentrated water enters the electrodialysis unit at a flow rate of 2.7m 3 /h , through the secondary reverse osmosis unit, the concentration of lithium nitrate is concentrated and increased to 10 times that of raw water;
S5:二级反渗透单元浓缩分离所得浓水进入电渗析单元,通过电渗析进行盐水分离,盐水分离所得产水(电渗析产超滤产水)直接排放,盐水分离所得浓水作为生产原料提锂回用,完成电池级硝酸锂生产废水的处理。S5: Concentrated water obtained from the concentration and separation of the two-stage reverse osmosis unit enters the electrodialysis unit, and brine is separated by electrodialysis. Lithium reuse, complete the treatment of battery-grade lithium nitrate production wastewater.
电渗析单元设计进水流速2.75m3/h,产生浓水的流速为0.27m3/h,产水流速2.43m3/h。经过电渗析单元,硝酸锂浓度被浓缩提高至原水的55倍,达到生产硝酸锂的生产的水质要求。The designed water flow rate of the electrodialysis unit is 2.75m 3 /h, the flow rate of concentrated water is 0.27m 3 /h, and the flow rate of product water is 2.43m 3 /h. After the electrodialysis unit, the concentration of lithium nitrate is concentrated and increased to 55 times that of the raw water, meeting the water quality requirements for the production of lithium nitrate.
实施例3Example 3
在实施例2的基础上,将步骤S5中的直接排放的盐水分离所得产水(电渗析产超滤产水)回流至一级反渗透单元继续处理,此时加大一级反渗透系统的处理量,提高处理流速。On the basis of Example 2, the obtained product water (electrodialysis and ultrafiltration product water) obtained by the direct discharge of brine separation in step S5 is returned to the primary reverse osmosis unit for further processing. Processing capacity, increase processing flow rate.
显然,上述实施例仅仅是为清楚地说明所作的举例,并非对实施方式的限定。对于所属领域的普通技术人员来说,在上述说明的基础上还可以做出其它不同形式变化或变动。这里无需也无法对所有的实施方式予以穷举。而由此所引申出的显而易见的变化或变动仍处于本发明创造的保护范围之中。Apparently, the above-mentioned embodiments are only examples for clear description, and are not intended to limit the implementation. For those of ordinary skill in the art, on the basis of the above description, other changes or changes in various forms can also be made. It is not necessary and impossible to exhaustively list all the implementation manners here. However, the obvious changes or changes derived therefrom are still within the scope of protection of the present invention.
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