CN105251436A - Assembly line system in which service life of lithium ion sieve adsorbents is prolonged and operating method thereof - Google Patents
Assembly line system in which service life of lithium ion sieve adsorbents is prolonged and operating method thereof Download PDFInfo
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- HBBGRARXTFLTSG-UHFFFAOYSA-N Lithium ion Chemical compound [Li+] HBBGRARXTFLTSG-UHFFFAOYSA-N 0.000 title claims abstract description 62
- 229910001416 lithium ion Inorganic materials 0.000 title claims abstract description 52
- 239000003463 adsorbent Substances 0.000 title abstract description 50
- 238000011017 operating method Methods 0.000 title description 2
- 230000002035 prolonged effect Effects 0.000 title description 2
- 238000001179 sorption measurement Methods 0.000 claims abstract description 130
- 238000000034 method Methods 0.000 claims abstract description 36
- 238000002336 sorption--desorption measurement Methods 0.000 claims abstract description 17
- 238000003795 desorption Methods 0.000 claims description 38
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 claims description 11
- 239000002253 acid Substances 0.000 claims description 10
- 239000000126 substance Substances 0.000 claims description 7
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 claims description 5
- 238000010521 absorption reaction Methods 0.000 claims 7
- 210000000416 exudates and transudate Anatomy 0.000 claims 1
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 abstract description 42
- 229910052744 lithium Inorganic materials 0.000 abstract description 42
- 238000004519 manufacturing process Methods 0.000 abstract description 12
- 238000005516 engineering process Methods 0.000 abstract description 7
- 238000005065 mining Methods 0.000 abstract description 7
- 238000004064 recycling Methods 0.000 abstract description 4
- 238000012546 transfer Methods 0.000 abstract description 4
- 239000002699 waste material Substances 0.000 abstract description 3
- 229910001760 lithium mineral Inorganic materials 0.000 abstract description 2
- 230000009286 beneficial effect Effects 0.000 abstract 1
- 239000000243 solution Substances 0.000 description 28
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 16
- 238000004090 dissolution Methods 0.000 description 16
- 239000007788 liquid Substances 0.000 description 15
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 10
- 239000012267 brine Substances 0.000 description 9
- 239000011572 manganese Substances 0.000 description 9
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 description 9
- 238000005406 washing Methods 0.000 description 9
- 230000008569 process Effects 0.000 description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- 239000003480 eluent Substances 0.000 description 6
- 239000000872 buffer Substances 0.000 description 5
- XGZVUEUWXADBQD-UHFFFAOYSA-L lithium carbonate Chemical compound [Li+].[Li+].[O-]C([O-])=O XGZVUEUWXADBQD-UHFFFAOYSA-L 0.000 description 5
- 238000003860 storage Methods 0.000 description 5
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 4
- 229910052808 lithium carbonate Inorganic materials 0.000 description 4
- 229910021450 lithium metal oxide Inorganic materials 0.000 description 4
- 238000011084 recovery Methods 0.000 description 4
- 229910014689 LiMnO Inorganic materials 0.000 description 3
- 230000007423 decrease Effects 0.000 description 3
- 238000004146 energy storage Methods 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 238000007670 refining Methods 0.000 description 3
- 229910009343 Li1.33 Mn1.67 O4 Inorganic materials 0.000 description 2
- 239000003929 acidic solution Substances 0.000 description 2
- 230000002378 acidificating effect Effects 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 238000010828 elution Methods 0.000 description 2
- 238000005342 ion exchange Methods 0.000 description 2
- 229910052748 manganese Inorganic materials 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 238000009423 ventilation Methods 0.000 description 2
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 1
- UIIMBOGNXHQVGW-DEQYMQKBSA-M Sodium bicarbonate-14C Chemical compound [Na+].O[14C]([O-])=O UIIMBOGNXHQVGW-DEQYMQKBSA-M 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- 150000001340 alkali metals Chemical class 0.000 description 1
- 229910001420 alkaline earth metal ion Inorganic materials 0.000 description 1
- 230000004075 alteration Effects 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 239000007853 buffer solution Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 229910017052 cobalt Inorganic materials 0.000 description 1
- 239000010941 cobalt Substances 0.000 description 1
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000001186 cumulative effect Effects 0.000 description 1
- 125000004122 cyclic group Chemical group 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 229910000625 lithium cobalt oxide Inorganic materials 0.000 description 1
- BFZPBUKRYWOWDV-UHFFFAOYSA-N lithium;oxido(oxo)cobalt Chemical compound [Li+].[O-][Co]=O BFZPBUKRYWOWDV-UHFFFAOYSA-N 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 229910052750 molybdenum Inorganic materials 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- 125000004430 oxygen atom Chemical group O* 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 229910052718 tin Inorganic materials 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- 229910052720 vanadium Inorganic materials 0.000 description 1
- 229910052726 zirconium Inorganic materials 0.000 description 1
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- Manufacture And Refinement Of Metals (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Treatment Of Liquids With Adsorbents In General (AREA)
Abstract
本发明公开了一种提高锂离子筛吸附剂使用寿命的流水线系统及操作方法,该系统为若干串联且首尾连通的吸附塔组成吸附-脱附流水线,每个吸附塔包含:装填在吸附塔内的锂离子筛吸附剂;设置在吸附塔入口处的泵;控制吸附塔入口的第一阀门;及控制吸附塔出口的第二阀门。本发明的流水线系统根据锂离子筛吸附剂的吸附饱和程度,使用流水线轮转的方式及时切换锂离子筛吸附剂的工作状态,在不改进吸附剂微观结构的前提下即可延长吸附剂的使用寿命,提高全寿命期的锂元素吸附转移总量,降低生产成本,提高效费比。本发明有利于将锂离子筛吸附剂及其吸-脱附技术应用于锂元素浓度相对较低的场合,提升锂矿产资源开采和废旧锂电池回收过程中的资源利用率。
The invention discloses an assembly line system and an operation method for improving the service life of a lithium ion sieve adsorbent. The system is composed of a number of adsorption towers connected in series and connected head to tail to form an adsorption-desorption assembly line. Each adsorption tower includes: loaded in the adsorption tower The lithium ion sieve adsorbent; the pump arranged at the inlet of the adsorption tower; the first valve controlling the inlet of the adsorption tower; and the second valve controlling the outlet of the adsorption tower. According to the adsorption saturation degree of the lithium ion sieve adsorbent, the assembly line system of the present invention uses the pipeline rotation mode to switch the working state of the lithium ion sieve adsorbent in time, and can prolong the service life of the adsorbent without improving the microstructure of the adsorbent , increase the total amount of lithium element adsorption and transfer in the whole life cycle, reduce production costs, and improve the cost-effectiveness ratio. The invention is beneficial to applying the lithium ion sieve adsorbent and its adsorption-desorption technology to occasions where the lithium element concentration is relatively low, and improves the resource utilization rate in the mining of lithium mineral resources and the recycling of waste lithium batteries.
Description
技术领域 technical field
本发明属于矿产资源开采和固体废弃物回收领域,涉及一种锂离子筛吸附剂在锂资源开采或回收生产线上的使用方法,具体来说,涉及一种通过轮转切换流水线状态来提高锂离子筛吸附剂使用寿命的方法。 The invention belongs to the fields of mining of mineral resources and recycling of solid waste, and relates to a method for using a lithium ion sieve adsorbent on a lithium resource mining or recovery production line, specifically, to a method for improving the lithium ion sieve by rotating and switching the state of the assembly line. The method of adsorbent lifetime.
背景技术 Background technique
随着数字化资讯时代以及新能源时代的到来,锂二次电池已经成为综合性能最好、应用最广泛的便携式以及可移动式储能设备,尤其是近年来电动汽车、混合动力汽车以及储能电站等大规模储能应用需求爆发,锂二次电池产量成倍增长,电池已经成为锂资源最主要的消耗方向。锂资源在新能源时代的战略意义堪比过去一百年来石油的战略地位,然而目前锂资源的开采速度已经难以满足锂电池产业快速增长的需求,针对这一问题的主要对策有三: With the advent of the digital information era and the new energy era, lithium secondary batteries have become the most comprehensive performance and the most widely used portable and mobile energy storage devices, especially in recent years for electric vehicles, hybrid vehicles and energy storage power stations. The demand for large-scale energy storage applications has exploded, and the output of lithium secondary batteries has doubled. Batteries have become the main consumption direction of lithium resources. The strategic significance of lithium resources in the new energy era is comparable to the strategic position of petroleum in the past 100 years. However, the current mining speed of lithium resources has been difficult to meet the rapidly growing demand of the lithium battery industry. There are three main countermeasures for this problem:
一是研究改进从液态锂矿产资源中提取锂元素的技术,因为地球上可开采的锂资源中液态形式占一半以上,在中国领土上这一比例更是高达80%以上。 The first is to study and improve the technology of extracting lithium from liquid lithium mineral resources, because liquid forms account for more than half of the mineable lithium resources on the earth, and this proportion is as high as more than 80% in China.
二是开发从现有锂矿(包括固态和液态)开采、精炼生产线所排放尾液中回收流失的锂元素的技术,因为现有开采、精炼生产线所排放尾液中流失的锂元素最多可高达总量的40%。 The second is to develop technologies for recovering the lost lithium element from the tail liquid discharged from the existing lithium ore (including solid and liquid) mining and refining production lines, because the lithium element lost in the tail liquid discharged from the existing mining and refining production lines can be as high as 40% of the total.
三是开发从废旧锂电池中回收锂元素的技术,现有的废旧锂电池回收技术不成熟,且主要目的是回收钴酸锂电池中的钴元素,对各种类型废旧锂电池中锂元素的回收技术尚在研究中。 The third is to develop technology for recovering lithium elements from waste lithium batteries. The existing waste lithium battery recovery technology is immature, and the main purpose is to recover cobalt elements in lithium cobalt oxide batteries. Recycling technology is still under study.
锂离子筛吸附剂在上述三种锂资源开采及回收技术中都有广泛的应用前景,其中LMO(锂金属氧化物)类型锂离子筛吸附剂更是拥有良好的选择性吸附能力,可以将提取锂元素和分离杂质(精炼)这两个过程一并解决。这其中被研究得最深入、选择性吸附能力最好的是锰系锂离子筛吸附剂,如LiMnO2.5(通常也记为Li1.6Mn1.6O4)、Li4Mn5O12(通常也记为Li1.33Mn1.67O4)等,但它们有一个共同的弱点,就是在吸附-脱附循环使用的过程中会缓慢溶解。 Lithium ion sieve adsorbents have broad application prospects in the above three lithium resource mining and recovery technologies. Among them, LMO (lithium metal oxide) type lithium ion sieve adsorbents have good selective adsorption capacity and can extract The two processes of lithium element and separation of impurities (refining) are solved together. Among them, manganese-based lithium-ion sieve adsorbents, which have been studied most deeply and have the best selective adsorption capacity, such as LiMnO 2.5 (usually also denoted as Li 1.6 Mn 1.6 O 4 ), Li 4 Mn 5 O 12 (commonly denoted as Li 1.33 Mn 1.67 O 4 ), etc., but they have a common weakness, that is, they will slowly dissolve during the adsorption-desorption cycle.
发明内容 Contents of the invention
本发明的目的是为了减轻锂离子筛吸附剂在使用过程中的溶解作用,让所有在实际使用中随吸附时间或脱附时间的延长存在溶解损耗加剧特性的锂离子筛吸附剂减少损耗,拥有更长的寿命,从而降低使用成本、提高效益。 The purpose of the present invention is to reduce the dissolution of the lithium ion sieve adsorbent during use, so that all lithium ion sieve adsorbents that have the characteristics of increased dissolution loss with the prolongation of the adsorption time or desorption time in actual use reduce the loss, and have Longer life, thereby reducing the cost of use and improving efficiency.
为达到上述目的,本发明提供了一种提高锂离子筛吸附剂使用寿命的流水线系统,该系统为若干串联且首尾连通的吸附塔组成吸附-脱附流水线,每个吸附塔包含: In order to achieve the above object, the present invention provides a pipeline system that improves the service life of the lithium-ion sieve adsorbent. The system is composed of a number of adsorption towers connected in series and head to tail to form an adsorption-desorption pipeline. Each adsorption tower includes:
装填在吸附塔内的锂离子筛吸附剂; Lithium ion sieve adsorbent packed in the adsorption tower;
设置在吸附塔入口处的泵; A pump arranged at the inlet of the adsorption tower;
控制吸附塔入口的第一阀门;及 a first valve controlling the inlet to the adsorption column; and
控制吸附塔出口的第二阀门。 The second valve controlling the outlet of the adsorption tower.
所述的锂离子筛吸附剂与吸附塔顶部之间预留有缓冲层。吸附塔顶部设置有通气弯管以保持吸附塔与大气畅通。 A buffer layer is reserved between the lithium ion sieve adsorbent and the top of the adsorption tower. The top of the adsorption tower is provided with a ventilation elbow to keep the adsorption tower open to the atmosphere.
所述的锂离子筛吸附剂的主要组分随吸附时间或脱附时间的延长有加剧溶解损耗的特性。 The main components of the lithium ion sieve adsorbent have the characteristic of intensifying dissolution loss with the prolongation of the adsorption time or desorption time.
本发明还提供了利用上述流水线系统提高锂离子筛吸附剂使用寿命的操作方法,该方法通过切换第一阀门、第二阀门状态,使得串联的吸附塔轮流置于吸附-脱附循环中的吸附阶段或脱附阶段;所述的切换阀门状态,是指通过手动或自动程序控制阀门,从而改变流入吸附塔的溶液来源以及流出吸附塔的溶液去向。 The present invention also provides an operation method for improving the service life of the lithium-ion sieve adsorbent by using the above-mentioned assembly line system. The method switches the state of the first valve and the second valve so that the adsorption towers connected in series are placed in the adsorption-desorption cycle in turn. stage or desorption stage; the switching valve state refers to controlling the valve through manual or automatic procedures, thereby changing the source of the solution flowing into the adsorption tower and the destination of the solution flowing out of the adsorption tower.
所述的吸附阶段,是指将待吸附Li+溶液经一个吸附塔的第一阀门泵入,受塔内的锂离子筛吸附剂吸附后,通过塔出口的第二阀门流入其后次第串联的若干吸附塔;直至该塔出口溶液中Li+浓度高于第一预定值时该塔的吸附阶段结束。所述的待吸附Li+溶液须经预处理,该预处理是指调节其pH值为7~8.5,然后加入碳酸盐或碳酸氢盐,使得其中的碳酸根与碳酸氢根物质的量终浓度之和大于该溶液中锂离子终浓度的50%。 The described adsorption stage refers to that the Li + solution to be adsorbed is pumped in through the first valve of an adsorption tower, and after being adsorbed by the lithium ion sieve adsorbent in the tower, it flows through the second valve at the outlet of the tower into the subsequent series of A plurality of adsorption towers; until the Li + concentration in the outlet solution of the tower is higher than the first predetermined value, the adsorption phase of the tower ends. The Li + solution to be adsorbed must be pretreated, and the pretreatment refers to adjusting its pH value to 7-8.5, and then adding carbonate or bicarbonate, so that the amount of carbonate and bicarbonate substances therein is final. The sum of the concentrations is greater than 50% of the final concentration of lithium ions in the solution.
所述的脱附阶段,是指该塔的吸附阶段结束后,通过其第一阀门泵入酸性溶液,使得吸附塔中锂离子筛吸附剂的Li+脱附,溶入到酸性溶液中,由其第二阀门排出备用;直至排出液中Li+浓度低于第二预定值时该塔的脱附阶段结束。 Described desorption phase refers to that after the adsorption phase of the tower ends, the acidic solution is pumped through its first valve, so that the Li + desorption of the lithium ion sieve adsorbent in the adsorption tower is dissolved in the acidic solution, by Its second valve discharges for standby; until the Li + concentration in the discharged liquid is lower than the second predetermined value, the desorption phase of the tower ends.
所述的第一预定值为该吸附塔入口的溶液中Li+浓度的50%~85%,优选为50%~70%;所述的第二预定值为100~400ppm,优选为100~200ppm。 The first predetermined value is 50%~85% of the Li concentration in the solution at the inlet of the adsorption tower , preferably 50%~70%; the second predetermined value is 100~400ppm, preferably 100~200ppm .
每个吸附塔在达到出口浓度第一预定值后,切换阀门状态进入脱附阶段,或改变控制条件及预定值进入下一个吸附阶段;每个吸附塔在达到出口浓度第二预定值后,切换阀门状态进入吸附阶段,或改变控制条件及预定值进入下一个脱附阶段。 After each adsorption tower reaches the first predetermined value of the outlet concentration, switch the valve state to enter the desorption stage, or change the control conditions and predetermined values to enter the next adsorption stage; after each adsorption tower reaches the second predetermined value of the outlet concentration, switch The valve state enters the adsorption stage, or changes the control conditions and predetermined values to enter the next desorption stage.
本发明的方法有效减轻了锂离子筛吸附剂在使用中的化学溶解,延长使用寿命、降低使用成本,同时也能降低最终排放尾液中的锂元素含量,获取尽可能多的经济效益和环境效益。 The method of the present invention effectively reduces the chemical dissolution of the lithium ion sieve adsorbent in use, prolongs the service life, reduces the use cost, and can also reduce the lithium element content in the final discharge tail liquid, so as to obtain as much economic benefit and environmental protection as possible. benefit.
附图说明 Description of drawings
图1是按照本发明布置的吸附塔组在吸附步骤和洗涤-脱附步骤之间4:1分配的流动状态示意图,其中前四个塔处于串联的级联吸附步骤,最后一个塔正在与酸储存罐之间循环即处于脱附步骤。 Fig. 1 is the flow state schematic diagram of the 4:1 distribution between the adsorption step and the washing-desorption step of the adsorption tower group arranged according to the present invention, wherein the first four towers are in the cascade adsorption steps connected in series, and the last tower is being connected with acid Circulation between storage tanks is the desorption step.
图2为锂离子筛吸附剂对溶液中Li+吸附量以及Mn元素溶出量相对吸附时间变化的关系曲线图。 Fig. 2 is a graph showing the relationship between the lithium ion sieve adsorbent and the adsorption amount of Li + in the solution and the dissolution amount of Mn element relative to the adsorption time.
具体实施方式 detailed description
以下结合附图通过具体实施例对本发明作进一步的描述,这些实施例仅用于说明本发明,并不是对本发明保护范围的限制。 The present invention will be further described below through specific embodiments in conjunction with the accompanying drawings. These embodiments are only used to illustrate the present invention, and are not intended to limit the protection scope of the present invention.
本发明提供的一种提高锂离子筛吸附剂使用寿命的流水线系统锂离子回收系统,如图1所示,该系统为若干串联且首尾连通的吸附塔(吸附塔A、B、C、D、E)组成吸附-脱附流水线,每个吸附塔包含: A pipeline system lithium ion recovery system for improving the service life of the lithium ion sieve adsorbent provided by the present invention, as shown in Figure 1, the system is a number of adsorption towers connected in series and end to end (adsorption towers A, B, C, D, E) To form an adsorption-desorption pipeline, each adsorption tower contains:
装填在吸附塔内的锂离子筛吸附剂1; Lithium ion sieve adsorbent 1 packed in the adsorption tower;
设置在吸附塔入口处的泵2; A pump 2 arranged at the inlet of the adsorption tower;
控制吸附塔入口的第一阀门3;及 a first valve 3 controlling the inlet of the adsorption tower; and
控制吸附塔出口的第二阀门4。 The second valve 4 controlling the outlet of the adsorption tower.
所述的锂离子筛吸附剂1与吸附塔顶部之间预留有缓冲层5,且吸附塔顶部有通气弯管6以保持吸附塔与大气畅通。 A buffer layer 5 is reserved between the lithium ion sieve adsorbent 1 and the top of the adsorption tower, and there is a ventilation elbow 6 at the top of the adsorption tower to keep the adsorption tower unblocked from the atmosphere.
本发明的流水线系统的操作方法包含以下步骤: The operating method of the assembly line system of the present invention comprises the following steps:
步骤1,装填吸附剂和首次脱附:将5个吸附塔设为一组,编号A、B、C、D、E,其内均装填主要成分是LiMnO2.5(通常也记为Li1.6Mn1.6O4)的锂离子筛吸附剂颗粒,注意在塔顶预留约1/10的缓冲空间并保持和大气畅通。缓慢泵入0.5mol/L盐酸(或0.25mol/L硫酸),流出液送入后续制备碳酸锂的工艺步骤使用。经酸洗充分地进行离子交换处理后得到脱附状态的HMnO2.5,通入清水快速流动洗涤10分钟即可进入吸附-脱附生产循环。 Step 1, loading adsorbent and desorption for the first time: set 5 adsorption towers as a group, numbered A, B, C, D, E, and the main component of them is LiMnO 2.5 (usually also recorded as Li 1.6 Mn 1.6 O 4 ) lithium ion sieve adsorbent particles, pay attention to reserve about 1/10 of the buffer space at the top of the tower and keep it open to the atmosphere. Slowly pump 0.5 mol/L hydrochloric acid (or 0.25 mol/L sulfuric acid), and the effluent is sent to the subsequent process for preparing lithium carbonate for use. HMnO 2.5 in the desorbed state is obtained after acid washing and sufficient ion exchange treatment, and then enters the adsorption-desorption production cycle after passing through clean water for 10 minutes of rapid flow washing.
步骤2,预处理待吸附溶液:在预处理池中将待吸附含锂盐湖卤水用NaOH或KOH等调节pH至7~8,然后根据需要维持的吸附pH值,加入一定量的NaHCO3或NaHCO3+Na2CO3的混合物,使得其中的碳酸根终浓度[CO3 2-]+碳酸氢根终浓度[HCO3 -]之和(单位mol/L)高于溶液中锂离子终浓度的50%;优选的,碳酸氢根终浓度为锂离子终浓度的70%~90%,碳酸根终浓度0。 Step 2, pretreatment of the solution to be adsorbed: In the pretreatment pool, adjust the pH of the lithium-containing salt lake brine to be adsorbed to 7~8 with NaOH or KOH, and then add a certain amount of NaHCO 3 or NaHCO according to the required adsorption pH value 3 + Na 2 CO 3 mixture, so that the sum of the final concentration of carbonate [CO 3 2- ] + the final concentration of bicarbonate [HCO 3 - ] (unit mol/L) is higher than the final concentration of lithium ions in the solution 50%; preferably, the final concentration of bicarbonate is 70% to 90% of the final concentration of lithium ions, and the final concentration of carbonate is 0.
步骤3,A、B、C、D塔吸附:将预处理过的待吸附卤水缓慢连续泵入吸附塔组,使其以适当的流速依次串联通过A、B、C、D号塔。监测A塔入口处溶液的锂离子浓度Xa,以及A塔流出到B塔的溶液中锂离子浓度Xb,当锂离子浓度Xb升高至Xa*50%~60%后,终止该步骤。 Step 3, adsorption in towers A, B, C, and D: slowly and continuously pump the pretreated brine to be adsorbed into the adsorption tower group, making it pass through towers A, B, C, and D in series at an appropriate flow rate. Monitor the lithium ion concentration X a of the solution at the entrance of tower A, and the lithium ion concentration X b in the solution flowing out of tower A to tower B. When the lithium ion concentration X b rises to X a *50%~60%, the process is terminated. step.
步骤4,B、C、D、E塔吸附,A塔脱附:步骤3终止后,立即切换管路阀门状态(手动或自动程控),让预处理池中的溶液直接泵入B塔,而后依次流经C、D、E塔。同时A塔进入洗涤和脱附状态——用清水快速洗涤A塔5~10分钟,随后缓慢泵入含0.5mol/L盐酸或0.25mol/L硫酸的洗脱液(实际为也含有较低浓度Li+的重复使用酸性洗脱液),监测塔出口的锂浓度或酸浓度。 Step 4: Adsorption in towers B, C, D, and E, and desorption in tower A: After step 3 is terminated, immediately switch the status of the pipeline valve (manual or automatic program control), so that the solution in the pretreatment pool is directly pumped into tower B, and then Flow through C, D, E towers in turn. At the same time, tower A enters the state of washing and desorption—wash tower A quickly with clean water for 5-10 minutes, and then slowly pump into the eluent containing 0.5mol/L hydrochloric acid or 0.25mol/L sulfuric acid (actually, it also contains a lower concentration Li + repeated use of acidic eluent), monitoring the lithium concentration or acid concentration at the outlet of the tower.
根据具体要求,较高锂含量(不重复使用)的洗脱液即可送往后续制备碳酸锂的工艺步骤;而当A塔出口处的锂浓度下降到一定值之后,将出口液回收到酸储存罐供后续洗脱时重复使用;再待出口锂浓度继续下降到一个更低的确定值如100~200ppm时,终止A塔脱附步骤。将结束脱附的吸附塔A用清水快速洗涤10分钟,此时吸附塔处于脱附结束的备便状态,可以重新进入下一次吸附步骤。 According to specific requirements, the eluent with higher lithium content (not reused) can be sent to the subsequent process step of preparing lithium carbonate; and when the lithium concentration at the outlet of tower A drops to a certain value, the outlet liquid is recovered to the acid The storage tank is reused for subsequent elution; and when the lithium concentration at the outlet continues to drop to a lower definite value such as 100-200ppm, the desorption step of tower A is terminated. Quickly wash the adsorption tower A with clean water for 10 minutes after the desorption is completed. At this time, the adsorption tower is in the state of ready for desorption and can re-enter the next adsorption step.
步骤5,C、D、E、A塔吸附,B塔脱附:参照步骤4,在步骤4终止后,切换管路阀门使得待吸附溶液依次流过C、D、E、A塔进行交换吸附,同时B塔进入洗涤和脱附状态。 Step 5, adsorption in towers C, D, E, and A, and desorption in tower B: refer to step 4, after step 4 is terminated, switch the pipeline valve so that the solution to be adsorbed flows through towers C, D, E, and A in sequence for exchange adsorption , while Tower B enters the state of washing and desorption.
步骤6,D、E、A、B塔吸附,C塔脱附:参照步骤4,在步骤5终止后,D、E、A、B塔进入交换吸附步骤,同时C塔进入洗涤和脱附状态。 Step 6, towers D, E, A, and B are adsorbed, and tower C is desorbed: refer to step 4. After step 5 is terminated, towers D, E, A, and B enter the exchange adsorption step, and tower C enters the washing and desorption state at the same time .
步骤7,E、A、B、C塔吸附,D塔脱附:参照步骤4,在步骤6终止后,E、A、B、C塔进入交换吸附步骤,同时D塔进入洗涤和脱附状态。 Step 7, towers E, A, B, and C are adsorbed, tower D is desorbed: refer to step 4, after step 6 is terminated, towers E, A, B, and C enter the exchange adsorption step, and tower D enters the washing and desorption state at the same time .
步骤8,A、B、C、D塔吸附,E塔脱附:参照步骤4,在步骤7终止后,A、B、C、D塔进入交换吸附步骤,同时E塔进入洗涤和脱附状态。如图1所示,其中E塔与酸储存罐构成循环回路。该步骤结束经清水快速洗涤后应切换阀门,使得A塔与酸储存罐间泵入和泵出循环,而E塔则串接到D塔后;预处理池中的待吸附Li+溶液直接泵入B塔,次第流经C、D、E塔后排出,此为步骤4。重复4~8步,即可将整个吸附-脱附循环流水线轮转切换、连续运行。 Step 8, towers A, B, C, and D are adsorbed, tower E is desorbed: refer to step 4, after step 7 is terminated, towers A, B, C, and D enter the exchange adsorption step, and tower E enters the washing and desorption state at the same time . As shown in Figure 1, the E tower and the acid storage tank constitute a circulation loop. After this step is finished and washed quickly with clear water, the valve should be switched so that the pump-in and pump-out cycles between Tower A and the acid storage tank, while Tower E is connected in series to Tower D; the Li + solution to be adsorbed in the pretreatment pool is directly pumped Enter B tower, discharge through C, D, E tower successively, this is step 4. Repeat steps 4 to 8, and the entire adsorption-desorption cycle pipeline can be rotated and operated continuously.
所述的锂离子筛吸附剂简记为“LMO”,其中的金属元素“M”可以是Al、Sn、Ti、V、Cr、Mn、Fe、Co、Ni、Zr、Mo等元素的一种或多种;“L”是Li,但也可包含其它碱金属、碱土金属离子的混合(非定比化合物如LixMg1.33-xMn1.67O4),“O”是氧原子。“L”“M”“O”的比例可变且不必为整数。除LMO类型的锂离子筛吸附剂外,该方法同样适用于其它类型的锂离子筛吸附剂循环处理含锂溶液的工艺,只要其主要组分随吸附时间或脱附时间的延长有加剧溶解损耗的特性。 The lithium ion sieve adsorbent is abbreviated as "LMO", and the metal element "M" can be one of Al, Sn, Ti, V, Cr, Mn, Fe, Co, Ni, Zr, Mo and other elements or more; "L" is Li, but it can also contain a mixture of other alkali metals and alkaline earth metal ions (non-proportional compounds such as Li x Mg 1.33-x Mn 1.67 O 4 ), "O" is an oxygen atom. The proportions of "L", "M" and "O" are variable and need not be integers. In addition to the LMO type lithium ion sieve adsorbent, this method is also applicable to other types of lithium ion sieve adsorbents for recycling lithium-containing solutions, as long as the main components have increased dissolution loss with the extension of adsorption time or desorption time characteristics.
如图2所示,用单一吸附柱吸附上述预处理过的含锂(700ppm)卤水时,流出液中锂浓度的减少量Δ[Li]从接近700ppm逐渐下降,也就是说吸附柱从溶液中吸附锂的能力从接近完全吸附逐渐下降;与此同时,柱中吸附材料溶解到溶液中的Mn含量却从低于仪器检测下限逐渐上升,虽然只有不到0.3ppm的溶出浓度,但数百次循环的使用中累计溶解损耗会很严重。相关测试表明,化学溶解与吸附剂的吸附饱和程度有密切关系,在吸附饱和度几乎为0的“未吸附”状态,即使长时间浸泡,吸附剂的化学溶解仍很轻微,可以认为吸附饱和度很低的状态下等效吸附时间较短。 As shown in Figure 2, when a single adsorption column is used to adsorb the above-mentioned pretreated lithium-containing (700ppm) brine, the decrease in the concentration of lithium in the effluent Δ[Li] gradually decreases from close to 700ppm, that is to say, the adsorption column from the solution The ability to adsorb lithium gradually decreases from close to complete adsorption; at the same time, the content of Mn dissolved in the solution by the adsorbent material in the column gradually increases from below the detection limit of the instrument. Although the dissolution concentration is less than 0.3ppm, hundreds of times Cumulative dissolution losses over cyclic use can be severe. Relevant tests have shown that chemical dissolution is closely related to the degree of adsorption saturation of the adsorbent. In the "unadsorbed" state where the adsorption saturation is almost 0, even if soaked for a long time, the chemical dissolution of the adsorbent is still very slight. It can be considered that the adsorption saturation The equivalent adsorption time is shorter in a very low state.
因此,使用上述方案切换流水线状态,可以使吸附剂较长时间与已被前塔吸附掉部分因而锂浓度降低的溶液接触,因此较长时间停留在吸附饱和程度较低的状态;仅在串联吸附步骤的最后阶段作为首塔短期接触较高浓度的原液,迅速达到给定控制条件下的近吸附饱和状态,然后很快就被轮转替换出吸附塔组而切换到脱附步骤。这种工艺流程安排不仅减少了吸附剂停留在吸附饱和状态的(等效)时间,事实上由于向前轮替,也缩短了每个塔在吸附步骤的实际时间。另一方面,刚脱附完毕的吸附剂吸附饱和程度最低,轮转替换进吸附塔组时作为串联吸附的末塔,能够最大限度的榨取溶液中残留的锂元素,尽可能减少随尾液排放而流失的锂资源。 Therefore, using the above scheme to switch the state of the pipeline can make the adsorbent contact with the solution that has been absorbed by the front tower for a long time and the lithium concentration is reduced, so it stays in a state with a low degree of adsorption saturation for a long time; only in series adsorption In the final stage of the step, the first column is exposed to a higher concentration of raw liquid for a short period of time, and quickly reaches the near adsorption saturation state under given control conditions, and then is quickly replaced by the rotation of the adsorption column group to switch to the desorption step. This process flow arrangement not only reduces the (equivalent) time that the adsorbent stays in the adsorption saturation state, it actually shortens the actual time each column spends in the adsorption step due to forward rotation. On the other hand, the adsorption saturation degree of the adsorbent that has just been desorbed is the lowest, and when it is replaced by rotation into the adsorption tower group, it is used as the last tower of series adsorption, which can extract the residual lithium element in the solution to the maximum extent, and reduce the amount of lithium that is discharged from the tail liquid as much as possible. Lost lithium resources.
上述工艺方法中流水线分为5个吸附塔串联,实际吸附-脱附流水线上的分段装置数量(如吸附塔数量)可以有二个或多个,各分段组成流水线的方式可以为串联、并联、混联。上述工艺方法中各分段仅在吸附条件、脱附条件这两种状态条件之间轮转切换,生产中也可以根据实际需要令各分段在不同的pH值、温度、辅助离子浓度等多参数条件状态之间切换。 In the above-mentioned process, the pipeline is divided into five adsorption towers connected in series, and the number of segmented devices (such as the number of adsorption towers) on the actual adsorption-desorption pipeline can be two or more, and the way each segment forms the pipeline can be series, Parallel, mixed. In the above-mentioned process, each section only switches between the two state conditions of adsorption condition and desorption condition. During production, each section can also be set at different pH values, temperatures, auxiliary ion concentrations and other multi-parameters according to actual needs. Toggle between conditional states.
实施例1 Example 1
将5个吸附塔设为一组,编号A、B、C、D、E,其内均装填主要成分是LiMnO2.5(Li1.6Mn1.6O4)的锂离子筛吸附剂颗粒,注意在塔顶预留约1/10的缓冲空间并保持和大气畅通。缓慢泵入0.25mol/L稀硫酸,流出液含脱附的锂,送入后续制备碳酸锂的工艺步骤使用。经酸洗充分地进行离子交换处理后得到脱附状态的HMnO2.5,通入清水快速流动洗涤10~15分钟。 Set 5 adsorption towers as a group, numbered A, B, C, D, E, all of which are filled with lithium ion sieve adsorbent particles whose main component is LiMnO 2.5 (Li 1.6 Mn 1.6 O 4 ). Reserve about 1/10 of the buffer space and keep it open to the atmosphere. Slowly pump in 0.25mol/L dilute sulfuric acid, and the effluent contains desorbed lithium, which is sent to the subsequent process for preparing lithium carbonate for use. HMnO 2.5 in the desorbed state is obtained after acid washing and sufficient ion exchange treatment, and is washed with clean water for 10 to 15 minutes.
在预处理池中将待吸附含锂盐湖卤水用碳酸盐或NaOH调节pH至7~8,然后根据锂含量加入一定量的NaHCO3——例如本实例用含锂700ppm的溶液,则加入NaHCO3使得终浓度[HCO3 -]=0.075mol/L;由于实际应用的工厂里饱和碳酸锂溶液和稀硫酸溶液的价格远低于碳酸氢钠,生产线上的实际工艺是按物质的量比2:1加入Li2CO3和H2SO4,使得终浓度[HCO3 -]=0.07~0.075mol/L。 In the pretreatment pool, adjust the pH of the lithium-containing salt lake brine to be adsorbed to 7~8 with carbonate or NaOH, and then add a certain amount of NaHCO 3 according to the lithium content—for example, this example uses a solution containing 700ppm lithium, then add NaHCO 3 to make the final concentration [HCO 3 - ]=0.075mol/L; because the price of saturated lithium carbonate solution and dilute sulfuric acid solution in the practical factory is much lower than that of sodium bicarbonate, the actual process on the production line is based on the ratio of the amount of substance to 2 :1 Add Li 2 CO 3 and H 2 SO 4 so that the final concentration [HCO 3 - ]=0.07~0.075mol/L.
将预处理过的待吸附卤水缓慢连续泵入吸附塔组,使其以适当的流速依次串联通过A、B、C、D号塔。A塔入口处溶液的锂离子浓度约700ppm,所以当A塔流出到B塔的溶液中锂离子浓度Xb升高至>400ppm后,终止该步骤。切换管路阀门状态,让预处理池中的溶液直接泵入B塔,而后依次流经C、D、E塔。同时A塔进入洗涤和脱附状态——用清水快速洗涤A塔10分钟,随后缓慢泵入0.25mol/L硫酸洗脱液(实际生产中为含较低浓度Li+的重复使用酸性洗脱液)。 The pretreated brine to be adsorbed is slowly and continuously pumped into the adsorption tower group, making it pass through A, B, C, and D towers in series at an appropriate flow rate. The lithium ion concentration of the solution at the entrance of tower A is about 700ppm, so when the lithium ion concentration X b in the solution flowing out of tower A to tower B rises to >400ppm, this step is terminated. Switch the state of the pipeline valve so that the solution in the pretreatment tank is directly pumped into tower B, and then flows through towers C, D, and E in sequence. At the same time, tower A enters the state of washing and desorption—wash tower A with clean water for 10 minutes, and then slowly pump 0.25mol/L sulfuric acid eluent (in actual production, it is a reusable acidic eluent containing lower concentration Li + ).
根据具体要求,较高锂含量(不重复使用)的洗脱液即可送往后续制备碳酸锂的工艺步骤;而当A塔出口处的锂浓度下降到一定值之后——例如本实例中锂含量下降到300~350ppm时,将出口液回收到酸储存罐,供后续洗脱时重复使用;再待锂含量继续下降到100ppm,终止脱附步骤。将结束脱附的吸附塔A用清水快速洗涤10分钟,此时吸附塔处于脱附结束的备便状态,可以重新进入下一次吸附步骤。 According to specific requirements, the eluent with higher lithium content (not reused) can be sent to the subsequent process step of preparing lithium carbonate; and when the lithium concentration at the outlet of tower A drops to a certain value—for example, lithium in this example When the content drops to 300-350ppm, the outlet liquid is recovered to the acid storage tank for reuse in subsequent elution; and then the desorption step is terminated when the lithium content continues to drop to 100ppm. Quickly wash the adsorption tower A with clean water for 10 minutes after the desorption is completed. At this time, the adsorption tower is in the state of ready for desorption and can re-enter the next adsorption step.
依照如下表1进行流水线上各塔的轮转切换,切换的判断标准依然是>400ppm终止吸附步骤,<100ppm终止脱附步骤。 According to the following table 1, the rotation switching of each tower on the pipeline is carried out. The judgment standard of switching is still >400ppm to stop the adsorption step, and <100ppm to stop the desorption step.
表1:流水线上各塔轮转切换状态的状态表 Table 1: The status table of the rotation switching status of each tower on the pipeline
该方案是实际工业生产中使用的动态法,对比将五个吸附塔并联使用的办法,该方案仅需约1/2的时间即可令每一个吸附柱(轮流)达到吸附饱和,且吸附剂处于接近吸附饱和状态下的时间更短,因此化学溶解损耗显著减小。初步测算表明,在实现相同的锂元素吸-脱附转移总量的前提下,该方法比多塔并联且同时切换吸附、脱附步骤的方法吸附剂溶解损耗减少60%以上,因而可以延长使用寿命,降低使用成本、提高效益。 This scheme is a dynamic method used in actual industrial production. Compared with the method of using five adsorption towers in parallel, this scheme only needs about 1/2 of the time to make each adsorption column (in turn) reach adsorption saturation, and the adsorbent The time spent near adsorption saturation is shorter, so the chemical dissolution loss is significantly reduced. Preliminary calculations show that under the premise of achieving the same total amount of lithium element adsorption-desorption transfer, this method reduces the dissolution loss of the adsorbent by more than 60% compared with the method of parallel connection of multiple towers and switching the adsorption and desorption steps at the same time, so it can be extended. service life, reduce the cost of use and improve efficiency.
实施例2 Example 2
参照实施例1的步骤进行,但仅在预处理池中将待吸附含锂卤水用Ca(OH)2或NaOH调节pH至约8.5,而不加入NaHCO3等碳酸盐、碳酸氢盐缓冲。此方法适用于无法获得廉价碳酸(氢)盐的生产条件,由于没有缓冲剂,吸附率一开始就迅速下降,因此需要在每个塔前补充碱并重复使用待吸附液直至其中锂含量降低到一定值。 Refer to the steps of Example 1, but only adjust the pH of the lithium-containing brine to be adsorbed to about 8.5 with Ca(OH) 2 or NaOH in the pretreatment tank, without adding carbonate and bicarbonate buffer such as NaHCO 3 . This method is suitable for production conditions where cheap carbonate (bi)carbonate cannot be obtained. Since there is no buffer, the adsorption rate drops rapidly at the beginning, so it is necessary to replenish alkali before each tower and reuse the liquid to be adsorbed until the lithium content in it is reduced to A certain value.
本实例用含锂700ppm的初始待吸附卤水,预处理后缓慢泵入吸附塔组A、B、C、D,监测D塔流出液中的锂浓度,其值迅速上升至>300ppm时将流出液排回到预处理池,同时使用自动调节装置向预处理池中补充Ca(OH)2或NaOH,使得预处理池中的溶液始终保持在pH约8.5的状态。除了向预处理池中添加碱液外,还要在每个塔前(除首塔)根据pH值在线补充碱液,使得流入每个塔的溶液pH值都维持在约8.5。令待吸附卤水反复循环流动,直至出口液的含锂量下降到<300ppm时,将出口液直接排放而不再回流到预处理池,预处理池中更换新卤水。 In this example, the initial brine to be adsorbed containing 700ppm of lithium is slowly pumped into adsorption tower groups A, B, C, and D after pretreatment, and the lithium concentration in the effluent of tower D is monitored. When the value rises rapidly to >300ppm, the effluent Drain back to the pretreatment tank, and at the same time use the automatic adjustment device to supplement Ca(OH) 2 or NaOH to the pretreatment tank, so that the solution in the pretreatment tank is always maintained at a pH of about 8.5. In addition to adding lye to the pretreatment tank, lye should be supplemented online according to the pH value before each tower (except the first tower), so that the pH value of the solution flowing into each tower is maintained at about 8.5. Let the brine to be adsorbed circulate repeatedly until the lithium content of the outlet liquid drops to <300ppm, then discharge the outlet liquid directly without returning to the pretreatment tank, and replace the new brine in the pretreatment tank.
监测首塔出口液的锂离子浓度,当首塔出口与入口的锂浓度相差<20ppm时,终止本步骤,将首塔A塔离线清洗和脱附(参照实施例1),同时B、C、D、E组吸附步骤开始。各组轮转切换吸附步骤和脱附步骤的安排表参照例1执行,切换步骤的判断标准均为首塔出口与入口的锂浓度相差<20ppm。 Monitor the lithium ion concentration of the outlet liquid of the first tower. When the lithium concentration difference between the outlet of the first tower and the inlet is less than 20ppm, this step is terminated, and the tower A of the first tower is cleaned and desorbed off-line (refer to Example 1), while B, C, The adsorption step of group D and E starts. The arrangement table of each group of rotation switching adsorption step and desorption step is carried out with reference to Example 1, and the judgment standard of the switching step is that the difference between the lithium concentration at the outlet and the inlet of the first tower is <20ppm.
该方法是在无法获得廉价碳酸(氢)盐的生产条件下,对实施例1的一种替代方法,其吸附速率较例1低很多,因此每个吸附-脱附循环的耗时增加较多。该方法中吸附剂的溶解损耗同样比传统工艺显著减轻,寿命延长。 This method is an alternative method to Example 1 under the production conditions where cheap (bi)carbonate cannot be obtained, and its adsorption rate is much lower than that of Example 1, so the time-consuming increase of each adsorption-desorption cycle is relatively large . The dissolution loss of the adsorbent in this method is also significantly reduced compared with the traditional process, and the service life is prolonged.
实施例3 Example 3
参照实施例1的步骤进行,但吸附剂换成Li1.33Mn1.67O4-PVC颗粒,该吸附剂也存在着随停留在近吸附饱和状态时间的延长而加剧溶解损耗的特性。因此,用本方法同样可以在实现相同的锂元素吸-脱附转移总量的前提下,比多塔并联且同时切换吸-脱附步骤的方法中吸附剂溶解损耗减少约40%——相比例1该吸附剂的锂离子吸附饱和容量较低,因此较快接近吸附饱和,溶解减轻程度不如例1明显。 The steps of Example 1 were followed, but the adsorbent was replaced by Li 1.33 Mn 1.67 O 4 -PVC particles. This adsorbent also has the characteristic of intensifying the dissolution loss with the prolongation of staying in the state near adsorption saturation. Therefore, this method can also achieve the same total amount of lithium element adsorption-desorption transfer, and the adsorption-desorption steps can be reduced by about 40%. In Example 1, the lithium ion adsorption saturation capacity of the adsorbent is relatively low, so it approaches adsorption saturation quickly, and the degree of dissolution reduction is not as obvious as in Example 1.
本发明针对多种锂离子筛吸附剂的共同弱点,即在实际使用中存在随吸附时间或脱附时间的延长而溶解损耗加剧的特性,采取策略:将多个吸附塔级联组成吸附-脱附流水线,通过程序控制将不同的吸附塔(因而相应塔中的吸附剂)轮流置于吸附-脱附循环的不同阶段,从而及时切换吸附剂所处工作状态,这样可在不改进吸附剂微观结构的前提下延长吸附剂的使用寿命,提高全寿命期的锂元素吸附转移总量。 The present invention aims at the common weakness of various lithium ion sieve adsorbents, that is, in actual use, there is a characteristic that the dissolution loss increases with the prolongation of the adsorption time or desorption time, and adopts a strategy: multiple adsorption towers are cascaded to form an adsorption-desorption Attached assembly line, through program control, different adsorption towers (and thus the adsorbents in the corresponding towers) are placed in different stages of the adsorption-desorption cycle in turn, so as to switch the working state of the adsorbent in time, so that the microscopic adsorption of the adsorbent can be improved. On the premise of the structure, the service life of the adsorbent is extended, and the total amount of lithium element adsorption and transfer in the whole life cycle is increased.
尽管本发明的内容已经通过上述优选实施例作了详细介绍,但应当认识到上述的描述不应被认为是对本发明的限制。在本领域技术人员阅读了上述内容后,对于本发明的多种修改和替代都将是显而易见的。因此,本发明的保护范围应由所附的权利要求来限定。 Although the content of the present invention has been described in detail through the above preferred embodiments, it should be understood that the above description should not be considered as limiting the present invention. Various modifications and alterations to the present invention will become apparent to those skilled in the art upon reading the above disclosure. Therefore, the protection scope of the present invention should be defined by the appended claims.
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