CN106517449B - Solution regeneration device capable of improving current efficiency - Google Patents
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- 230000008929 regeneration Effects 0.000 title claims abstract description 170
- 238000011069 regeneration method Methods 0.000 title claims abstract description 170
- 238000004519 manufacturing process Methods 0.000 claims abstract description 32
- 238000010612 desalination reaction Methods 0.000 claims description 61
- KWGKDLIKAYFUFQ-UHFFFAOYSA-M lithium chloride Chemical compound [Li+].[Cl-] KWGKDLIKAYFUFQ-UHFFFAOYSA-M 0.000 claims description 24
- AMXOYNBUYSYVKV-UHFFFAOYSA-M lithium bromide Chemical compound [Li+].[Br-] AMXOYNBUYSYVKV-UHFFFAOYSA-M 0.000 claims description 14
- 239000003011 anion exchange membrane Substances 0.000 claims description 6
- 239000012528 membrane Substances 0.000 claims description 4
- 238000005341 cation exchange Methods 0.000 claims description 3
- 238000000034 method Methods 0.000 abstract description 20
- 230000008569 process Effects 0.000 abstract description 14
- 238000007791 dehumidification Methods 0.000 abstract description 9
- 238000004378 air conditioning Methods 0.000 abstract description 8
- 238000011033 desalting Methods 0.000 abstract 3
- 239000000243 solution Substances 0.000 description 214
- 238000000909 electrodialysis Methods 0.000 description 20
- 239000007864 aqueous solution Substances 0.000 description 17
- 239000007789 gas Substances 0.000 description 11
- 229910052736 halogen Inorganic materials 0.000 description 11
- 150000002367 halogens Chemical class 0.000 description 11
- 239000012266 salt solution Substances 0.000 description 7
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 6
- 150000001447 alkali salts Chemical class 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 6
- 238000005265 energy consumption Methods 0.000 description 6
- 239000000463 material Substances 0.000 description 6
- 230000010287 polarization Effects 0.000 description 6
- 230000009471 action Effects 0.000 description 4
- 230000007423 decrease Effects 0.000 description 4
- 239000001257 hydrogen Substances 0.000 description 4
- 229910052739 hydrogen Inorganic materials 0.000 description 4
- 239000002699 waste material Substances 0.000 description 4
- 238000009792 diffusion process Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000003792 electrolyte Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 2
- 239000007795 chemical reaction product Substances 0.000 description 2
- 230000005684 electric field Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 230000005012 migration Effects 0.000 description 2
- 238000013508 migration Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 238000012824 chemical production Methods 0.000 description 1
- 230000001627 detrimental effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000003411 electrode reaction Methods 0.000 description 1
- 239000008151 electrolyte solution Substances 0.000 description 1
- 229940021013 electrolyte solution Drugs 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 238000004146 energy storage Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000003230 hygroscopic agent Substances 0.000 description 1
- 239000003014 ion exchange membrane Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000005057 refrigeration Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
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- C02F1/4693—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis electrodialysis
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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- C02F2201/46—Apparatus for electrochemical processes
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Abstract
Description
技术领域technical field
本发明属于蓄能空调装置、化工生产技术领域,具体来说,涉及一种可提高电流效率的溶液再生装置。The invention belongs to the technical fields of energy storage air conditioners and chemical production, and in particular relates to a solution regeneration device capable of improving current efficiency.
背景技术Background technique
近年来,建筑中传统制冷空调设备引起的能源紧张问题日趋严峻,而利用热湿独立处理方法可以显著降低热湿环境控制系统的能耗,因此热湿独立处理的调节方法受到了广泛关注。在众多热湿独立处理空调系统中,溶液除湿空调系统是一种基于液体吸湿剂除湿技术的极具潜力的新型空调方式。电渗析是膜分离技术中的一种。它是在直流电场作用下,以电位差为动力,利用离子交换膜的选择透过性,把电解质从溶液中分离出来的电化学分离过程。在电渗析器的运行过程中,一些隔室(浓缩室)的溶液浓度有所提高,而另一些隔室(淡化室)的溶液浓度有所降低。溶液除湿空调系统采用的除湿剂大部分(氯化锂溶液、氯化钙溶液、溴化锂溶液)都是电解质溶液,而除湿剂的再生过程实质上就是溶液浓缩的过程。因此,采用电渗析方法可以获得一种新型的电渗析溶液再生方法。In recent years, the energy shortage problem caused by traditional refrigeration and air-conditioning equipment in buildings has become increasingly serious, and the use of heat and humidity independent treatment methods can significantly reduce the energy consumption of heat and humidity environment control systems. Therefore, the adjustment methods of heat and humidity independent treatment have received extensive attention. Among many air conditioning systems with independent heat and humidity treatment, solution dehumidification air conditioning system is a new type of air conditioning method with great potential based on liquid hygroscopic agent dehumidification technology. Electrodialysis is one of the membrane separation technologies. It is an electrochemical separation process in which the electrolyte is separated from the solution under the action of a DC electric field, using the potential difference as the driving force and using the selective permeability of the ion exchange membrane. During the operation of the electrodialyser, the concentration of the solution in some compartments (concentration chambers) increases and in other compartments (desalination chambers) the concentration of solution decreases. Most of the dehumidifiers (lithium chloride solution, calcium chloride solution, lithium bromide solution) used in the solution dehumidification air conditioning system are electrolyte solutions, and the regeneration process of the dehumidifier is essentially the process of solution concentration. Therefore, a new method of regeneration of electrodialysis solution can be obtained by using the electrodialysis method.
然而,电渗析再生器的电极室在运行过程中会不断的发生极化反应并消耗极水溶液,因此在电渗析再生器的运行过程中需要对极水溶液进行及时补充。电渗析再生器通过将淡化室中的溶质离子向再生室进行迁移来实现对除湿溶液的再生,因此电极室中的极化反应在对溶液再生没有帮助的同时还会造成极水溶液的浪费,进而增加了电渗析再生器运行时的物料成本。另一方面,电渗析再生器电极室的极化反应会产生卤素气体,卤素气体具有较强的刺激性和毒性,直接排放会对环境造成一定危害,而对卤素气体进行处理则会增加电渗析再生器的运行成本。此外,在溶液除湿空调系统中,除湿溶液通常都具有比较高的浓度。例如,当采用氯化锂溶液作为除湿溶液时,其质量浓度范围通常为35%左右。当采用传统电渗析再生器对除湿溶液进行再生时,淡化室溶液与极水溶液的浓度应同再生室溶液相差不大,否则较大的浓度差会使得再生室溶液中的溶质向相邻隔室的溶液中大量迁移,弱化了电渗析再生器的实际再生效果,从而导致电渗析再生器具有较低的电流效率。例如,当采用氯化锂溶液作为除湿溶液,电渗析再生器再生室溶液和淡化室溶液质量浓度范围均为35%左右,极水溶液质量浓度范围为15~20%时,此时再生室溶液与电极室溶液之间的浓度差为20%左右,实验结果表明电渗析再生器的电流效率只有50%左右。这增加了电渗析再生器消耗的电能,但淡化室溶液和电极室溶液浓度较高会导致电渗析再生器运行时的物料成本较高,因此实际的电渗析再生器会采用浓度较低的极水溶液。例如,当采用氯化锂溶液作为除湿溶液时,极水溶液质量浓度范围为15~20%。即以牺牲电流效率为代价降低电渗析再生器运行中的物料成本。However, the electrode chamber of the electrodialysis regenerator will continuously undergo polarization reaction and consume the extremely aqueous solution during the operation process, so the extremely aqueous solution needs to be replenished in time during the operation of the electrodialysis regenerator. The electrodialysis regenerator realizes the regeneration of the dehumidifying solution by migrating the solute ions in the desalination chamber to the regeneration chamber. Therefore, the polarization reaction in the electrode chamber does not help the solution regeneration and also causes the waste of the extremely aqueous solution, and further Increased material costs for electrodialysis regenerator operation. On the other hand, the polarization reaction of the electrode chamber of the electrodialysis regenerator will generate halogen gas. The halogen gas is highly irritating and toxic, and the direct discharge will cause certain harm to the environment, and the treatment of the halogen gas will increase the electrodialysis The operating cost of the regenerator. In addition, in the solution dehumidification air conditioning system, the dehumidification solution usually has a relatively high concentration. For example, when a lithium chloride solution is used as the dehumidifying solution, its mass concentration range is usually about 35%. When the traditional electrodialysis regenerator is used to regenerate the dehumidifying solution, the concentration of the desalination chamber solution and the extremely aqueous solution should be similar to that of the regeneration chamber solution, otherwise a large concentration difference will cause the solute in the regeneration chamber solution to move to the adjacent compartment. A large amount of migration in the solution of the electrodialysis regenerator weakens the actual regeneration effect of the electrodialysis regenerator, resulting in a lower current efficiency of the electrodialysis regenerator. For example, when lithium chloride solution is used as the dehumidifying solution, the mass concentration range of the solution in the regeneration chamber of the electrodialysis regenerator and the solution in the desalination chamber is about 35%, and the mass concentration range of the extremely aqueous solution is 15-20%. The concentration difference between the electrode chamber solutions is about 20%, and the experimental results show that the current efficiency of the electrodialysis regenerator is only about 50%. This increases the power consumption of the electrodialysis regenerator, but the higher concentration of the desalination chamber solution and the electrode chamber solution will lead to higher material costs during the operation of the electrodialysis regenerator, so the actual electrodialysis regenerator will use a lower concentration electrode. aqueous solution. For example, when a lithium chloride solution is used as the dehumidifying solution, the mass concentration range of the extremely aqueous solution is 15-20%. That is, at the expense of sacrificing current efficiency, the material cost in the operation of the electrodialysis regenerator is reduced.
发明内容SUMMARY OF THE INVENTION
技术问题:本发明的目的是提供一种可提高电流效率的溶液再生装置,实现对溶液除湿空调系统中再生溶液的再生,且提高再生过程中的电流效率。Technical problem: The purpose of the present invention is to provide a solution regeneration device that can improve the current efficiency, realize the regeneration of the regeneration solution in the solution dehumidification air conditioning system, and improve the current efficiency in the regeneration process.
技术方案:为解决上述技术问题,本发明实施例提供一种可提高电流效率的溶液再生装置,该再生装置包括消耗溶液回路、再生溶液回路和电源,其中,Technical solution: In order to solve the above technical problems, the embodiment of the present invention provides a solution regeneration device that can improve the current efficiency. The regeneration device includes a consumption solution circuit, a regeneration solution circuit and a power supply, wherein,
所述再生溶液回路包括再生溶液槽和溶液再生器的再生室,所述再生溶液槽出口通过第一溶液泵和再生室入口连接,再生室出口和再生溶液槽入口连接;所述消耗溶液回路包括溶液再生器的阳极室、阴极室和淡化室,以及消耗溶液槽、第一生产槽和第二生产槽;消耗溶液槽出口通过第二溶液泵和淡化室入口连接,淡化室出口分别与阳极室入口和阴极室入口连接,阳极室出口和第一生产槽入口连接,阴极室出口和第二生产槽入口连接;所述电源的正极与溶液再生器的阳极连接,电源的负极与溶液再生器的阴极连接。The regeneration solution circuit includes a regeneration solution tank and a regeneration chamber of a solution regenerator, the outlet of the regeneration solution tank is connected to the inlet of the regeneration chamber through a first solution pump, and the outlet of the regeneration chamber is connected to the inlet of the regeneration solution tank; the consumption solution loop includes The anode chamber, cathode chamber and desalination chamber of the solution regenerator, as well as the consumption solution tank, the first production tank and the second production tank; the outlet of the consumption solution tank is connected with the inlet of the desalination chamber through the second solution pump, and the outlet of the desalination chamber is respectively connected with the anode chamber The inlet is connected to the inlet of the cathode chamber, the outlet of the anode chamber is connected to the inlet of the first production tank, and the outlet of the cathode chamber is connected to the inlet of the second production tank; the positive electrode of the power supply is connected to the anode of the solution regenerator, and the negative electrode of the power supply is connected to the Cathode connection.
作为优选例,所述溶液再生器中依次设有阳极、阳极室、淡化室、再生室、阴极室和阴极,阳极室和淡化室之间设有阴离子交换膜,淡化室和再生室之间设有阳离子交换膜,再生室和阴极室之间设有阴离子交换膜。As a preferred example, the solution regenerator is provided with an anode, an anode chamber, a desalination chamber, a regeneration chamber, a cathode chamber and a cathode in sequence, an anion exchange membrane is arranged between the anode chamber and the desalination chamber, and an anion exchange membrane is arranged between the desalination chamber and the regeneration chamber. There is a cation exchange membrane, and an anion exchange membrane is arranged between the regeneration chamber and the cathode chamber.
作为优选例,所述电源为直流电源。As a preferred example, the power source is a DC power source.
作为优选例,从所述淡化室流出的消耗溶液的质量浓度比流入再生室的再生溶液的质量浓度小2~5%;流入淡化室的消耗溶液的质量浓度小于或等于流入再生室的再生溶液的质量浓度。As a preferred example, the mass concentration of the depleted solution flowing out of the desalination chamber is 2-5% smaller than that of the regeneration solution flowing into the regeneration chamber; the mass concentration of the depleted solution flowing into the desalination chamber is less than or equal to the regeneration solution flowing into the regeneration chamber mass concentration.
作为优选例,所述消耗溶液槽中的溶液为质量浓度为35%的消耗溶液;再生溶液槽中的溶液为质量浓度为35%的再生溶液;流入再生室的再生溶液的质量浓度为35%,流出再生室的再生溶液的质量浓度为37~40%; 流入淡化室的消耗溶液的质量浓度为35%,流出淡化室的消耗溶液的质量浓度为30~33%。As a preferred example, the solution in the consumption solution tank is a consumption solution with a mass concentration of 35%; the solution in the regeneration solution tank is a regeneration solution with a mass concentration of 35%; the mass concentration of the regeneration solution flowing into the regeneration chamber is 35% , the mass concentration of the regeneration solution flowing out of the regeneration chamber is 37~40%; the mass concentration of the consumption solution flowing into the desalination chamber is 35%, and the mass concentration of the consumption solution flowing out of the desalination chamber is 30~33%.
作为优选例,所述消耗溶液为氯化锂或溴化锂溶液,所述再生溶液为氯化锂或溴化锂溶液。As a preferred example, the consumption solution is lithium chloride or lithium bromide solution, and the regeneration solution is lithium chloride or lithium bromide solution.
有益效果:与现有技术相比,本发明实施例具有以下有益效果:Beneficial effects: Compared with the prior art, the embodiments of the present invention have the following beneficial effects:
本发明实施例的再生装置中,溶液再生器的淡化室出口分别与溶液再生器的阳极室入口和溶液再生器的阴极室入口连接,利用淡化室中质量浓度降低的消耗溶液供应溶液再生器的电极室,且阳极室和阴极室中的消耗溶液的质量浓度低于再生溶液槽中的再生溶液的质量浓度2~5%。这提高了溶液再生装置的电流效率,降低了溶液再生装置的耗能。同时,利用第一生产槽和第二生产槽入口收集电极室中的极化反应生成的化工领域需要的卤素气体、氢气以及碱式盐溶液,避免了电极室中极水溶液的无谓浪费,同时也节省了对卤素气体进行处理时的运行成本。In the regeneration device of the embodiment of the present invention, the outlet of the desalination chamber of the solution regenerator is respectively connected with the inlet of the anode chamber of the solution regenerator and the inlet of the cathode chamber of the solution regenerator, and the consumed solution with reduced mass concentration in the desalination chamber is used to supply the outlet of the solution regenerator. The electrode chamber, and the mass concentration of the consumed solution in the anode chamber and the cathode chamber is 2-5% lower than the mass concentration of the regeneration solution in the regeneration solution tank. This improves the current efficiency of the solution regeneration device and reduces the energy consumption of the solution regeneration device. At the same time, the halogen gas, hydrogen gas and basic salt solution required in the chemical field generated by the polarization reaction in the electrode chamber are collected by the inlets of the first production tank and the second production tank, which avoids the unnecessary waste of the extremely aqueous solution in the electrode chamber, and also reduces the waste of the electrode chamber. Saves running costs when handling halogen gases.
附图说明Description of drawings
图1 是本发明实施例的结构示意图。FIG. 1 is a schematic structural diagram of an embodiment of the present invention.
图中有:溶液再生器1、阳极室101、阳极室入口1011、阳极室出口1012、阴极室102、阴极室入口1021、阴极室出口1022、再生室103、再生室入口1031、再生室出口1032、淡化室104、淡化室入口1041、淡化室出口1042、阳极105、阴极106、再生溶液槽2、再生溶液槽出口201、再生溶液槽入口202、消耗溶液槽3、消耗溶液槽出口301、消耗溶液槽入口302、第一生产槽4、第一生产槽入口401、第二生产槽5、第二生产槽入口501、电源6、第一溶液泵7、第二溶液泵8。In the figure: solution regenerator 1, anode chamber 101,
具体实施方式Detailed ways
下面结合附图,对本发明实施例的技术方案作进一步的描述。The technical solutions of the embodiments of the present invention will be further described below with reference to the accompanying drawings.
如图1所示,本发明实施例的一种可提高电流效率的溶液再生装置,包括消耗溶液回路、再生溶液回路和电源6。所述再生溶液回路包括溶液再生器1的再生室103和再生溶液槽2,所述再生溶液槽出口201通过第一溶液泵7和再生室入口1031连接,再生室出口1032和再生溶液槽入口202连接。所述消耗溶液回路包括溶液再生器1的阳极室101、阴极室102和淡化室104,以及消耗溶液槽3、第一生产槽4和第二生产槽5;消耗溶液槽出口301通过第二溶液泵8和淡化室入口1041连接,淡化室出口1042分别与阳极室入口1011和阴极室入口1021连接,阳极室出口1012和第一生产槽入口401连接,阴极室出口1022和第二生产槽入口501连接。所述电源6的正极与溶液再生器1的阳极105连接,电源6的负极与溶液再生器1的阴极106连接。As shown in FIG. 1 , a solution regeneration device capable of improving current efficiency according to an embodiment of the present invention includes a consumption solution circuit, a regeneration solution circuit and a power source 6 . The regeneration solution circuit includes the regeneration chamber 103 of the solution regenerator 1 and the regeneration solution tank 2. The regeneration
上述实施例的装置中,消耗溶液回路和再生溶液回路共用同一溶液再生器1。所述溶液再生器1中依次设有阳极105、阳极室101、淡化室104、再生室103、阴极室102和阴极106。优选的,电源6为直流电源。In the device of the above embodiment, the consumption solution circuit and the regeneration solution circuit share the same solution regenerator 1 . The solution regenerator 1 is provided with an
上述实施例的装置工作时,对于再生溶液回路而言,将再生溶液通过第一溶液泵7从再生溶液槽2加压进入溶液再生器1的再生室103中。再生溶液与淡化室104中的消耗溶液发生传质过程后,浓度提高,从稀溶液变成浓溶液;随后浓溶液流回再生溶液槽2中,从而完成再生溶液闭式循环。When the device of the above embodiment is working, for the regeneration solution circuit, the regeneration solution is pressurized from the regeneration solution tank 2 by the first solution pump 7 into the regeneration chamber 103 of the solution regenerator 1 . After the regeneration solution and the consumed solution in the desalination chamber 104 undergo a mass transfer process, the concentration increases from a dilute solution to a concentrated solution; then the concentrated solution flows back into the regeneration solution tank 2 to complete the closed cycle of the regeneration solution.
对于消耗溶液回路而言,将消耗溶液通过第二溶液泵8从消耗溶液槽3加压进入溶液再生器的淡化室104。在淡化室104中,消耗溶液与再生室103中的再生溶液发生传质过程后,浓度降低,变成稀溶液;随后稀溶液进入阳极室101和阴极室102中,并通过控制电源6,在阳极室和阴极室发生极化反应,阳极室101中极水溶液反应生成卤素气体,将卤素气体排入第一生产槽4中,阴极室102中极水溶液反应生成氢气和碱式盐溶液,将氢气和碱式盐溶液排入第二生产槽5中,从而完成消耗溶液开式循环。通过设置第一生产槽4和第二生产槽5,收集卤素气体、氢气和碱式盐溶液,可作为物料,用于相应的化工企业。For the consumption solution loop, the consumption solution is pressurized from the
上述实施例的装置中,作为优选,从所述淡化室104流出的消耗溶液的质量浓度比流入再生室103的再生溶液的质量浓度小2~5%;流入淡化室104的消耗溶液的质量浓度小于或等于流入再生室103的再生溶液的质量浓度。从淡化室104流出的消耗溶液的质量浓度比流入再生室103的再生溶液的质量浓度小2~5%,可以提高电流效率,降低能耗。例如,消耗溶液槽3中的溶液为质量浓度为35%的消耗溶液;再生溶液槽2中的溶液为质量浓度为35%的再生溶液。流入再生室103的再生溶液的质量浓度为35%,流出再生室103的再生溶液的质量浓度为37~40%。流入淡化室104的消耗溶液的质量浓度为35%,流出淡化室104的消耗溶液的质量浓度为30~33%。消耗溶液为氯化锂或溴化锂溶液,再生溶液为氯化锂或溴化锂溶液。In the device of the above embodiment, preferably, the mass concentration of the depleted solution flowing out of the desalination chamber 104 is 2-5% lower than the mass concentration of the regeneration solution flowing into the regeneration chamber 103; the mass concentration of the depleted solution flowing into the desalination chamber 104 Less than or equal to the mass concentration of the regeneration solution flowing into the regeneration chamber 103 . The mass concentration of the consumed solution flowing out of the desalination chamber 104 is 2-5% lower than the mass concentration of the regeneration solution flowing into the regeneration chamber 103, which can improve the current efficiency and reduce the energy consumption. For example, the solution in the
上述实施例的装置中,利用淡化室104中浓度降低的消耗溶液,供应阳极室101和阴极室102。从结构上来说,利用淡化室104中浓度降低的消耗溶液供应阳极室101和阴极室102,使得再生装置省去了设置极水溶液槽,不再需要额外的极水溶液循环,极大的降低了再生装置运行时的物料成本,简化了装置结构。In the apparatus of the above-described embodiment, the anode chamber 101 and the cathode chamber 102 are supplied with a depleted solution with a reduced concentration in the desalination chamber 104 . Structurally, the anode chamber 101 and the cathode chamber 102 are supplied with a depleted solution with a reduced concentration in the desalination chamber 104, so that the regeneration device does not need to set up an extremely aqueous solution tank, and no additional extremely aqueous solution circulation is required, which greatly reduces regeneration. The material cost during the operation of the device simplifies the device structure.
从功能上来说,进入淡化室的消耗溶液的质量浓度略高于流出淡化室的消耗溶液的质量浓度。这样使得极水溶液的质量浓度与再生室中的再生溶液的质量浓度、以及淡化室中的消耗溶液的质量浓度相差不大,例如2~5%。这减少了再生室中再生溶液中的溶质向相邻隔室的溶液中的有害迁移,从而提高了溶液再生装置的电流效率,降低了整个装置的耗能。Functionally, the mass concentration of the depleted solution entering the desalination chamber is slightly higher than the mass concentration of the depleted solution exiting the desalination chamber. In this way, the mass concentration of the extremely aqueous solution is not much different from the mass concentration of the regeneration solution in the regeneration chamber and the mass concentration of the consumed solution in the desalination chamber, for example, 2-5%. This reduces the detrimental migration of solutes from the regeneration solution in the regeneration chamber to the solution in the adjacent compartment, thereby increasing the current efficiency of the solution regeneration device and reducing the energy consumption of the entire device.
本实施例的溶液再生装置中,在直流电场的作用下,溶液中的阴阳离子向阳极和阴极迁移,通过阳离子交换膜和阴离子交换膜的作用,造成再生室103中溶液浓度提高,淡化室104中溶液浓度降低,实质上就是将淡化室104中溶液中的部分溶质传递到再生室103的溶液中。因此,理论上来说,再生室103溶液多了多少溶质,淡化室104溶液就少了多少溶质,从而造成了再生室103溶液浓度提高,淡化室104溶液浓度降低。溶液除湿空调要求除湿溶液质量浓度为37~40%,所以通过调节电源6的供应电流,来调节再生室103溶液的质量浓度。电流越大,再生室103溶液浓度提高的越多,所以通过调节电流来确保从再生室103流出的再生溶液质量浓度为37~40%。当从再生室103流出的再生溶液质量浓度为37~40%时,从淡化室104流出的消耗溶液的质量浓度相应为30~33%。In the solution regeneration device of this embodiment, under the action of the DC electric field, the anions and cations in the solution migrate to the anode and the cathode, and through the action of the cation exchange membrane and the anion exchange membrane, the concentration of the solution in the regeneration chamber 103 increases, and the desalination chamber 104 The reduction of the concentration of the solution in the desalination chamber 104 essentially means that part of the solute in the solution in the desalination chamber 104 is transferred to the solution in the regeneration chamber 103 . Therefore, theoretically speaking, the more solute in the solution in the regeneration chamber 103, the less solute in the solution in the desalination chamber 104, resulting in an increase in the concentration of the solution in the regeneration chamber 103 and a decrease in the concentration of the solution in the desalination chamber 104. The solution dehumidifying air conditioner requires the mass concentration of the dehumidifying solution to be 37-40%, so the mass concentration of the solution in the regeneration chamber 103 is adjusted by adjusting the supply current of the power supply 6 . The larger the current is, the more the concentration of the solution in the regeneration chamber 103 increases. Therefore, the current is adjusted to ensure that the mass concentration of the regeneration solution flowing out of the regeneration chamber 103 is 37-40%. When the mass concentration of the regeneration solution flowing out from the regeneration chamber 103 is 37-40%, the mass concentration of the consumption solution flowing out from the desalination chamber 104 is correspondingly 30-33%.
下面例举一实例。An example is given below.
再生溶液为氯化锂溶液。再生溶液从再生溶液槽2中流出时为稀溶液,质量浓度为35%。再生溶液通过第一溶液泵7从再生溶液槽2 流入再生室103中。再生溶液与淡化室104中的消耗溶液发生传质过程后,浓度提高,形成质量浓度为37~40%的浓溶液,从再生室103流出,返回再生溶液槽2中。The regeneration solution is lithium chloride solution. When the regeneration solution flows out from the regeneration solution tank 2, it is a dilute solution with a mass concentration of 35%. The regeneration solution flows from the regeneration solution tank 2 into the regeneration chamber 103 by the first solution pump 7 . After the regeneration solution and the depleted solution in the desalination chamber 104 undergo a mass transfer process, the concentration increases to form a concentrated solution with a mass concentration of 37-40%, which flows out from the regeneration chamber 103 and returns to the regeneration solution tank 2.
消耗溶液为氯化锂溶液。消耗溶液通过消耗溶液槽入口302加入消耗溶液槽3中。此时消耗溶液为质量浓度35%的稀溶液。通过第二溶液泵8,将消耗溶液从消耗溶液槽3流入淡化室104中。消耗溶液与再生室103中的再生溶液发生传质过程后,浓度降低,变成质量浓度为30~33%的稀溶液。也就是说,消耗溶液流入淡化室104时的质量浓度大于流出淡化室104时的质量浓度,相差2~5%。该消耗溶液从淡化室104流出后,进入阳极室101和阴极室102中。消耗溶液在阳极室101和阴极室102中的质量浓度小于再生室103中再生溶液的质量浓度,也小于淡化室104中消耗溶液的质量浓度。通过控制电源6,在阳极室和阴极室发生极化反应。在此过程中,除了离子电迁移和电极反应这两个主要过程以外,还会发生电解质的浓差扩散。由于再生室103中再生溶液平均浓度高于淡化室104中消耗溶液的质量浓度,且淡化室中消耗溶液的平均质量浓度高于两个电极室中的溶液质量浓度。在浓度差作用下,电解质会由浓度高的隔室向浓度低的隔室扩散,扩散速度随浓度差的增高而增长。这一过程会降低再生室103中再生溶液的浓度,对再生装置的再生过程产生副作用,从而降低了相同电流条件下再生装置的再生效果,降低了再生装置的电流效率,使得再生装置再生相同溶液时耗能增加。因此,与传统电渗析再生器中浓度差为20%左右,本发明实施例的再生装置降低了电极室与再生室之间的浓度差,只有2~5%,弱化了再生过程中的浓差扩散,从而提高了再生装置的电流效率,并降低了装置的能耗。The consumed solution is lithium chloride solution. The consumption solution is added to the
上述实施例的装置中,阳极室101中极水溶液反应生成卤素气体,将卤素气体排入第一生产槽4中,阴极室102中极水溶液反应生成氢气和碱式盐溶液,将氢气和碱式盐溶液排入第二生产槽5中。利用第一生产槽4和第二生产槽5收集极水溶液反应生成物,避免直接排除造成环境污染。第一生产槽4和第二生产槽5收集极水溶液反应生成物可以作为化工领域中的物料,实现废物再利用。In the device of the above embodiment, the extremely aqueous solution in the anode chamber 101 reacts to generate halogen gas, and the halogen gas is discharged into the first production tank 4, and the extremely aqueous solution in the cathode chamber 102 reacts to generate hydrogen and basic salt solution. The salt solution is discharged into the second production tank 5 . The first production tank 4 and the second production tank 5 are used to collect the reaction product of the extremely aqueous solution, so as to avoid direct elimination and cause environmental pollution. The first production tank 4 and the second production tank 5 collect the reaction product of the extremely aqueous solution, which can be used as a material in the chemical field to realize waste recycling.
上述实施例的装置可以在高温高湿的气候条件下,对除湿溶液进行稳定高效的再生,并且可以通过太阳能光伏发电进行驱动,尤其适用于进行卤素气体、氢气或碱式盐溶液生产工作的企业建筑。同时,该装置还可以利用夜间低谷低价电进行蓄能,从而缓解电力负荷峰谷差,并达到提高系统经济性的目的。此外,该装置还可以获得高浓度除湿溶液以用于深度除湿领域。The device of the above embodiment can regenerate the dehumidifying solution stably and efficiently under the climatic conditions of high temperature and high humidity, and can be driven by solar photovoltaic power generation, and is especially suitable for enterprises that produce halogen gas, hydrogen or basic salt solution. architecture. At the same time, the device can also use low-cost electricity at night to store energy, so as to alleviate the peak-to-valley difference in power load and achieve the purpose of improving system economy. In addition, the device can also obtain high-concentration dehumidification solution for use in the field of deep dehumidification.
以上显示和描述了本发明的基本原理、主要特征和优点。本领域的技术人员应该了解,本发明不受上述具体实施例的限制,上述具体实施例和说明书中的描述只是为了进一步说明本发明的原理,在不脱离本发明精神和范围的前提下,本发明还会有各种变化和改进,这些变化和改进都落入要求保护的本发明范围内。本发明要求保护的范围由权利要求书及其等效物界定。The foregoing has shown and described the basic principles, main features and advantages of the present invention. It should be understood by those skilled in the art that the present invention is not limited by the above-mentioned specific embodiments, and the descriptions in the above-mentioned specific embodiments and the specification are only to further illustrate the principle of the present invention, without departing from the spirit and scope of the present invention, the present invention Various changes and modifications of the invention are also possible, all of which fall within the scope of the claimed invention. The claimed scope of the present invention is defined by the claims and their equivalents.
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Publication number | Priority date | Publication date | Assignee | Title |
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CN103041675A (en) * | 2012-12-13 | 2013-04-17 | 东南大学常州研究院 | Solution regeneration apparatus for solution deep dehumidifying system |
CN203090721U (en) * | 2012-12-13 | 2013-07-31 | 东南大学常州研究院 | Solution regenerative apparatus for solution depth dehumidification system |
CN105148688A (en) * | 2015-08-19 | 2015-12-16 | 无锡伊佩克科技有限公司 | Novel solar solution coupling regeneration system |
CN106517449A (en) * | 2017-01-06 | 2017-03-22 | 南京工业大学 | Solution regeneration device capable of improving current efficiency |
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Publication number | Priority date | Publication date | Assignee | Title |
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CN103041675A (en) * | 2012-12-13 | 2013-04-17 | 东南大学常州研究院 | Solution regeneration apparatus for solution deep dehumidifying system |
CN203090721U (en) * | 2012-12-13 | 2013-07-31 | 东南大学常州研究院 | Solution regenerative apparatus for solution depth dehumidification system |
CN105148688A (en) * | 2015-08-19 | 2015-12-16 | 无锡伊佩克科技有限公司 | Novel solar solution coupling regeneration system |
CN106517449A (en) * | 2017-01-06 | 2017-03-22 | 南京工业大学 | Solution regeneration device capable of improving current efficiency |
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