CN115159637B - Device for desalting seawater and recovering acid and alkali - Google Patents
Device for desalting seawater and recovering acid and alkali Download PDFInfo
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- 239000002253 acid Substances 0.000 title claims abstract description 44
- 239000003513 alkali Substances 0.000 title claims abstract description 42
- 238000011033 desalting Methods 0.000 title claims abstract description 7
- 239000013535 sea water Substances 0.000 title claims description 31
- 238000010612 desalination reaction Methods 0.000 claims abstract description 65
- 239000012528 membrane Substances 0.000 claims abstract description 45
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical group [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 claims abstract description 42
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 32
- 239000002585 base Substances 0.000 claims abstract description 30
- 238000002242 deionisation method Methods 0.000 claims abstract description 27
- 239000002245 particle Substances 0.000 claims abstract description 16
- 239000007788 liquid Substances 0.000 claims abstract description 15
- 239000000446 fuel Substances 0.000 claims abstract description 14
- 230000000813 microbial effect Effects 0.000 claims abstract description 14
- 238000003756 stirring Methods 0.000 claims abstract description 5
- 238000011084 recovery Methods 0.000 claims description 32
- 239000003011 anion exchange membrane Substances 0.000 claims description 26
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 21
- 238000005341 cation exchange Methods 0.000 claims description 16
- 230000002572 peristaltic effect Effects 0.000 claims description 16
- 239000012267 brine Substances 0.000 claims description 15
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 claims description 15
- 239000000243 solution Substances 0.000 claims description 15
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 14
- 239000013505 freshwater Substances 0.000 claims description 14
- 229910001069 Ti alloy Inorganic materials 0.000 claims description 9
- 239000002028 Biomass Substances 0.000 claims description 6
- 238000005260 corrosion Methods 0.000 claims description 5
- 230000007797 corrosion Effects 0.000 claims description 5
- 238000005192 partition Methods 0.000 claims description 5
- 230000005611 electricity Effects 0.000 claims description 2
- 239000003792 electrolyte Substances 0.000 claims 1
- 150000002500 ions Chemical class 0.000 abstract description 13
- 238000001179 sorption measurement Methods 0.000 abstract description 6
- 238000004519 manufacturing process Methods 0.000 abstract description 4
- 230000005540 biological transmission Effects 0.000 abstract description 3
- 239000003014 ion exchange membrane Substances 0.000 abstract description 3
- 150000007513 acids Chemical class 0.000 abstract description 2
- 238000002156 mixing Methods 0.000 abstract 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 11
- -1 salt ions Chemical class 0.000 description 9
- 150000003839 salts Chemical class 0.000 description 9
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 6
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- 238000009792 diffusion process Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 229910052739 hydrogen Inorganic materials 0.000 description 4
- 239000001257 hydrogen Substances 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- 229910001415 sodium ion Inorganic materials 0.000 description 4
- 230000007423 decrease Effects 0.000 description 3
- 241000251468 Actinopterygii Species 0.000 description 2
- 241000196324 Embryophyta Species 0.000 description 2
- WQZGKKKJIJFFOK-GASJEMHNSA-N Glucose Natural products OC[C@H]1OC(O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-GASJEMHNSA-N 0.000 description 2
- WQZGKKKJIJFFOK-VFUOTHLCSA-N beta-D-glucose Chemical compound OC[C@H]1O[C@@H](O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-VFUOTHLCSA-N 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000001913 cellulose Substances 0.000 description 2
- 229920002678 cellulose Polymers 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000009826 distribution Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000008103 glucose Substances 0.000 description 2
- GPRLSGONYQIRFK-UHFFFAOYSA-N hydron Chemical compound [H+] GPRLSGONYQIRFK-UHFFFAOYSA-N 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 2
- 238000005342 ion exchange Methods 0.000 description 2
- 230000007246 mechanism Effects 0.000 description 2
- 230000008929 regeneration Effects 0.000 description 2
- 238000011069 regeneration method Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 229910052719 titanium Inorganic materials 0.000 description 2
- 239000010936 titanium Substances 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000003990 capacitor Substances 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 238000009296 electrodeionization Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 238000007710 freezing Methods 0.000 description 1
- 230000008014 freezing Effects 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 238000003895 groundwater pollution Methods 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 230000001681 protective effect Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 150000005837 radical ions Chemical class 0.000 description 1
- 238000006722 reduction reaction Methods 0.000 description 1
- 230000004044 response Effects 0.000 description 1
- 238000013341 scale-up Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 238000011282 treatment Methods 0.000 description 1
Classifications
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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
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
- C02F1/4691—Capacitive deionisation
-
- 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/08—Seawater, e.g. for desalination
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/009—Apparatus with independent power supply, e.g. solar cells, windpower or fuel cells
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/14—Maintenance of water treatment installations
-
- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/50—Fuel cells
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- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Water Supply & Treatment (AREA)
- Environmental & Geological Engineering (AREA)
- Engineering & Computer Science (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Electrochemistry (AREA)
- Molecular Biology (AREA)
- Health & Medical Sciences (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
本发明提供了一种微生物燃料电池耦合流动电极脱盐及回收酸碱的装置。该装置包括微生物燃料电池、流动电极电容去离子装置、外电路和酸碱生产室;其中,所述微生物燃料电池作为电源与所述流动电极电容去离子装置和所述外电路构成回路。利用微生物燃料电池作为电源;调整钛网正极与电极液的位置,使钛网正极紧靠离子交换膜,减小电荷传输距离,提高离子吸附能力;在电极液流动区域安装若干组相对转动的扰流搅拌装置,增强流动电极液中活性炭颗粒的掺混,大幅改善了脱盐效率;生产酸碱时,用矩形梳齿状双层膜结构,增大了双极膜与离子交换膜的接触面积,缩短了离子在酸碱室中移动的距离,提升了产酸产碱的均匀性,提高了酸碱生产效率。
The invention provides a device for desalting and recovering acid and alkali of a microbial fuel cell coupled with a flow electrode. The device includes a microbial fuel cell, a flowing electrode capacitive deionization device, an external circuit and an acid-base production chamber; wherein the microbial fuel cell serves as a power source to form a loop with the flowing electrode capacitive deionization device and the external circuit. Use microbial fuel cells as power sources; adjust the position of the titanium mesh positive electrode and the electrode liquid so that the titanium mesh positive electrode is close to the ion exchange membrane, reduce the charge transmission distance and improve the ion adsorption capacity; install several sets of relatively rotating disturbances in the electrode liquid flow area. The flow stirring device enhances the blending of activated carbon particles in the flowing electrode solution, greatly improving the desalination efficiency; when producing acids and bases, a rectangular comb-shaped double-layer membrane structure is used to increase the contact area between the bipolar membrane and the ion exchange membrane. It shortens the distance that ions move in the acid-base chamber, improves the uniformity of acid and alkali production, and improves acid-base production efficiency.
Description
技术领域Technical field
本发明涉及一种能够脱盐及回收酸碱的微生物燃料电池耦合流动电极装置,属于微生物燃料电池、流动电极电容去离子和酸碱生产技术领域。The invention relates to a microbial fuel cell coupled flow electrode device capable of desalting and recovering acid and alkali, and belongs to the technical fields of microbial fuel cells, flow electrode capacitive deionization and acid and alkali production.
背景技术Background technique
随着社会的快速发展,人类的生活条件日益提高,与之伴随的资源短缺、能源紧张等问题也渐渐暴露出来。尤其是淡水资源匮乏的问题,需要着重处理。到现在,已经有很多方法被提出来解决这类问题,比如膜分离、蒸馏、离子交换、电去离子和冷冻脱盐等,但是这些技术都需要外加能源而且能耗比较高,不利于循环经济的发展。除此之外微生物燃料电池对于浓盐水的脱盐效率不太理想,并且在脱盐时也不能连续的进行,微生物燃料电池耦合电容去离子的局限性还体现在只能用于脱盐、净化污水等等,没有在其他方面表现出大的优势。With the rapid development of society, human living conditions are improving day by day, and the accompanying problems such as resource shortage and energy tension are gradually exposed. In particular, the problem of scarcity of freshwater resources needs to be addressed. Up to now, many methods have been proposed to solve such problems, such as membrane separation, distillation, ion exchange, electrodeionization and freezing desalination, etc. However, these technologies require external energy and have relatively high energy consumption, which is not conducive to the circular economy. develop. In addition, the desalination efficiency of microbial fuel cells for concentrated brine is not ideal, and desalination cannot be carried out continuously. The limitation of microbial fuel cells coupled capacitor deionization is also reflected in that it can only be used for desalination, purification of sewage, etc. , does not show big advantages in other aspects.
国内通常采用将浓盐水引入蒸发池,但此法弊端也较为明显,若构造不合理极易造成浓盐水泄漏,渗入到地下水体中造成对地下水的污染。国外通常利用浓盐水进行灌溉耐盐度高的植物或利用浓盐水养殖咸水鱼类(如目前澳大利亚正在探索利用浓盐水养殖咸水鱼类),还可作为生态景区的补充水,但一般来说适合浓盐水的植物种类及地域较少,难以形成规模。因此,现如今的浓盐水处理大多都有局限性。于是,提供一种将浓盐水回收再利用,变成高性价比产物的方法成了社会发展的趋势与挑战。In China, concentrated salt water is usually introduced into the evaporation pond, but this method has obvious disadvantages. If the structure is unreasonable, it can easily cause the concentrated salt water to leak and seep into the groundwater body, causing groundwater pollution. Abroad, concentrated salt water is usually used to irrigate plants with high salinity tolerance or to breed saltwater fish (for example, Australia is currently exploring the use of concentrated salt water to breed saltwater fish). It can also be used as supplementary water for ecological scenic spots, but generally It is said that there are few plant species and regions suitable for concentrated salt water, making it difficult to scale up. Therefore, most of today's concentrated brine treatments have limitations. Therefore, providing a method to recycle concentrated brine into cost-effective products has become a social development trend and challenge.
CN207566948U公开了一种微生物燃料电池与电容去离子联用的脱盐装置。但是该装置脱盐时,电极会达到饱和,然后需要一系列电极再生操作,把钛集电极与阴极电极、阳极电极连接的导线拆开,使钛集电极上的两根导线连接形成短路放电。相当的繁琐,且不能实现连续脱盐,电极再生过后流出的浓盐水,也没有得到应有的利用。CN207566948U discloses a desalination device combining a microbial fuel cell and capacitive deionization. However, when the device is desalted, the electrode will reach saturation, and then a series of electrode regeneration operations are required to disconnect the wires connecting the titanium collector to the cathode and anode electrodes, so that the two wires on the titanium collector are connected to form a short-circuit discharge. It is quite cumbersome and cannot achieve continuous desalination. The concentrated brine flowing out after electrode regeneration has not been utilized as it should.
CN107624106A公开了一种电容去离子进行连续水脱盐、离子分离和选择性去除和浓缩离子的单模块流动电极装置。这个装置的集流体位于流动电极液的外侧,距离子交换膜较远,电荷传输能力被削减,随着脱盐过程的进行,流动电极液的流动会逐渐趋向稳定,电极液流道是有一定空间的,一旦流动电极液稳定下来,流动电极液内的活性炭颗粒会趋向两个极端,靠近膜的活性炭颗粒吸附量多,远离膜的活性炭颗粒吸附量少,会使流动电极液吸附离子均匀性差,造成流动电极利用率低、脱盐性能大打折扣等问题。CN107624106A discloses a single-module flow electrode device for capacitive deionization for continuous water desalination, ion separation, and selective removal and concentration of ions. The current collector of this device is located outside the flowing electrode liquid, far away from the sub-exchange membrane, and the charge transfer capacity is reduced. As the desalination process proceeds, the flow of the flowing electrode liquid will gradually become stable, and there is a certain space in the electrode liquid flow channel. , once the flowing electrode solution stabilizes, the activated carbon particles in the flowing electrode solution will tend to two extremes. The activated carbon particles close to the membrane will absorb more, and the activated carbon particles far away from the membrane will adsorb less, which will make the adsorption of ions by the flowing electrode solution poor. This results in problems such as low utilization of the flow electrode and greatly reduced desalination performance.
发明内容Contents of the invention
发明目的:针对以上问题,本发明提供了一种能够实现脱盐,并且能够回收酸碱的微生物燃料电池耦合流动电极装置。Purpose of the invention: In response to the above problems, the present invention provides a microbial fuel cell coupled flow electrode device that can achieve desalination and recover acid and alkali.
技术方案:本发明所述一种用于海水脱盐及回收酸碱的装置,所述装置包括脱盐系统和酸碱回收系统,其中,脱盐系统包括去离子脱盐装置,所述去离子脱盐装置的电极液流动区域设有若干个扰流搅拌器,相邻的扰流搅拌器转动方向相反,用以搅拌电极液中的活性炭颗粒;所述酸碱回收系统包括酸室和碱室,酸室和碱室通过隔板(108)分开,在酸室和碱室均设有矩形梳齿状双极膜,酸室中双极膜一侧设有阴离子交换膜,碱室中双极膜的一侧设有阳离子交换膜,阴离子交换膜和阳离子交换膜均与耐酸碱腐蚀的钛合金支架贴合。Technical solution: a device for seawater desalination and acid-base recovery according to the present invention. The device includes a desalination system and an acid-base recovery system. The desalination system includes a deionization and desalination device. The electrodes of the deionization and desalination device The liquid flow area is provided with several turbulence stirrers, and the adjacent turbulence stirrers rotate in opposite directions to stir the activated carbon particles in the electrode liquid; the acid-base recovery system includes an acid chamber and an alkali chamber, and the acid chamber and the alkali chamber The chambers are separated by partitions (108). Both the acid chamber and the alkali chamber are provided with rectangular comb-shaped bipolar membranes. One side of the bipolar membrane in the acid chamber is provided with an anion exchange membrane, and one side of the bipolar membrane in the alkali chamber is provided with an anion exchange membrane. There is a cation exchange membrane, and both the anion exchange membrane and the cation exchange membrane are bonded to the titanium alloy stent that is resistant to acid and alkali corrosion.
其中,所述去离子脱盐装置包括流动电极液、底板、对应设置的钛网负极和钛网正极,钛网负极和钛网正极的内侧均设有阴离子交换膜,钛网正极紧靠阴离子交换膜,阴离子交换膜之间设有阳离子交换膜,钛网负极和钛网正极外侧均设有底板,钛网负极紧靠底板,扰流搅拌器位于钛网负极与阴离子交换膜所形成的空间以及钛网正极和底板形成的空间内,流动电极液通过蠕动泵在前述的空间内循环流动。Wherein, the deionization and desalting device includes a flowing electrode solution, a bottom plate, and corresponding titanium mesh negative electrodes and titanium mesh positive electrodes. The titanium mesh negative electrode and the titanium mesh positive electrode are equipped with anion exchange membranes on the inside, and the titanium mesh positive electrode is close to the anion exchange membrane. , there is a cation exchange membrane between the anion exchange membrane, a bottom plate is provided outside the titanium mesh negative electrode and the titanium mesh positive electrode, the titanium mesh negative electrode is close to the bottom plate, and the spoiler stirrer is located in the space formed by the titanium mesh negative electrode and the anion exchange membrane and the titanium mesh In the space formed by the positive electrode of the mesh and the bottom plate, the flowing electrode liquid circulates in the aforementioned space through a peristaltic pump.
其中,扰流搅拌器的转速为15-20RPM。Among them, the rotation speed of the turbulent mixer is 15-20RPM.
其中,所述脱盐系统还包括海水室、淡水室,所述海水室通过三通阀与去离子脱盐装置相连,所述淡水室与去离子脱盐装置相连。Wherein, the desalination system also includes a seawater chamber and a freshwater chamber. The seawater chamber is connected to the deionization and desalination device through a three-way valve, and the freshwater chamber is connected to the deionization and desalination device.
其中,所述酸碱回收系统还包括浓盐水室,所述钛合金支架固定设置在浓盐水室的上部。Wherein, the acid-base recovery system also includes a concentrated brine chamber, and the titanium alloy bracket is fixedly arranged on the upper part of the concentrated brine chamber.
其中,所述酸室内的双极膜上部设有阳极电极,所述碱室内的双极膜上部设有阴极电极。Wherein, an anode electrode is arranged on the upper part of the bipolar membrane in the acid chamber, and a cathode electrode is arranged on the upper part of the bipolar membrane in the alkali chamber.
其中,阳极电极外表面附有有机生物质。Among them, organic biomass is attached to the outer surface of the anode electrode.
其中,有机生物质为低浓度有机废水、纤维素、葡萄糖、甲烷中的一种。Among them, organic biomass is one of low-concentration organic wastewater, cellulose, glucose, and methane.
其中,所述阳极电极和阴极电极产生的电通过导线供脱盐系统使用。Wherein, the electricity generated by the anode electrode and the cathode electrode is used by the desalination system through wires.
其中,所述酸碱回收系统为立体槽,立体槽的上部开设有出气口。Wherein, the acid-base recovery system is a three-dimensional tank, and an air outlet is provided at the upper part of the three-dimensional tank.
其中,所述酸室通过蠕动泵后设有盐酸出口,所述碱室通过蠕动泵后设有氢氧化钠出口。Wherein, the acid chamber is provided with a hydrochloric acid outlet after passing through the peristaltic pump, and the alkali chamber is provided with a sodium hydroxide outlet after passing through the peristaltic pump.
其中,脱盐系统还包括阀门,阀门通过管道分别与脱盐系统和酸碱回收系统相连。Among them, the desalination system also includes valves, which are connected to the desalination system and the acid-base recovery system through pipelines.
脱盐机理:海水中的钠离子被钛网正极的斥力推进阳离子交换膜进入到盐化区,海水中的氯离子被钛网正极较强的吸引力带进流动电极液中,被活性炭颗粒吸附,由于蠕动泵的驱动力,海水中的氯离子被流动电极液带到另一侧的阴离子交换膜,受到钛网负极的斥力,被推进盐化区,因此盐化区可以收集浓盐水,由于淡化区盐离子的浓度减小,从而产出淡水。Desalting mechanism: The sodium ions in seawater are pushed by the repulsive force of the titanium mesh positive electrode into the cation exchange membrane and enter the salinization zone. The chloride ions in the seawater are brought into the flowing electrode solution by the strong attraction of the titanium mesh positive electrode and are adsorbed by the activated carbon particles. Due to the driving force of the peristaltic pump, the chloride ions in the seawater are brought to the anion exchange membrane on the other side by the flowing electrode solution, and are pushed into the salinization zone by the repulsive force of the titanium mesh negative electrode. Therefore, the salinization zone can collect concentrated brine, and due to desalination The concentration of salt ions in the zone decreases, thereby producing fresh water.
酸碱回收机理:酸室中的双极膜(氢氧根离子扩散侧朝上)向内扩散氢离子,浓盐水室中的氯离子被阳极电极吸引而通过阴离子交换膜进入酸室,与氢离子结合成盐酸。隔板右侧的碱室中的双极膜(氢离子扩散侧朝上)向内扩散氢氧根离子,浓盐水室中的钠离子被阴极吸引,通过阳离子交换膜进入碱室,与氢氧根离子结合成氢氧化钠。Acid-base recovery mechanism: The bipolar membrane in the acid chamber (hydroxide ion diffusion side faces upward) diffuses hydrogen ions inward. The chloride ions in the concentrated brine chamber are attracted by the anode electrode and enter the acid chamber through the anion exchange membrane, where they interact with hydrogen. The ions combine to form hydrochloric acid. The bipolar membrane in the alkali chamber on the right side of the partition (the hydrogen ion diffusion side faces upward) diffuses hydroxide ions inward. The sodium ions in the concentrated brine chamber are attracted by the cathode, enter the alkali chamber through the cation exchange membrane, and interact with the hydroxide ions. The radical ions combine to form sodium hydroxide.
有益效果:与现有技术性相比,本发明具有以下显著优点:Beneficial effects: Compared with existing technology, the present invention has the following significant advantages:
(1)本发明将脱盐与回收酸碱结合起来用于处理海水,可以同时达到海水淡化变成淡水,及将海水中的盐变为酸与碱进行回收的双重效果。(1) The present invention combines desalination and recovery of acid and alkali to treat seawater, which can simultaneously achieve the dual effects of desalinating seawater into fresh water and recovering salts in seawater into acid and alkali.
(2)本发明的酸碱回收系统将钛网正极紧靠阴离子交换膜,使得电荷传输距离减小,改善流动电极液内活性炭颗粒的吸附效果;(2) The acid-base recovery system of the present invention places the titanium mesh positive electrode close to the anion exchange membrane, which reduces the charge transmission distance and improves the adsorption effect of activated carbon particles in the flowing electrode solution;
(3)本发明的脱盐系统在流动电极液中安置若干组相对转动的扰流搅拌器,使流动电极液中活性炭颗粒的运动规律得以控制,让几乎每一个活性炭颗粒都能吸附上离子,实现离子吸附均匀性,提高了流动电极液的利用率和脱盐效果;(3) The desalination system of the present invention installs several sets of relatively rotating stirrers in the flowing electrode liquid, so that the movement patterns of the activated carbon particles in the flowing electrode liquid can be controlled, so that almost every activated carbon particle can adsorb ions, achieving The uniformity of ion adsorption improves the utilization rate and desalination effect of the flowing electrode solution;
(4)本发明的酸碱回收系统采用矩形梳齿状双层膜,让双极膜与离子交换膜接触面积增大,容积减小,利用钛合金骨架支撑,既耐酸碱腐蚀,也能保护膜不易变形,从而改善离子的分布均匀性,加快了离子结合成酸碱的速率。(4) The acid-base recovery system of the present invention adopts a rectangular comb-shaped double-layer membrane to increase the contact area between the bipolar membrane and the ion exchange membrane and reduce the volume. It is supported by a titanium alloy skeleton, which is resistant to acid and alkali corrosion and can The protective film is not easily deformed, thereby improving the uniformity of ion distribution and speeding up the rate at which ions combine to form acids and bases.
附图说明Description of the drawings
图1是本发明用于海水脱盐及回收酸碱的装置结构图;Figure 1 is a structural diagram of the device used for seawater desalination and acid and alkali recovery according to the present invention;
图2是去离子脱盐装置结构图;Figure 2 is a structural diagram of the deionization and desalination device;
图3是本发明用于海水脱盐及回收酸碱的装置工作流程图;Figure 3 is a working flow chart of the device used for seawater desalination and acid and alkali recovery according to the present invention;
具体实施方式Detailed ways
下面结合附图对本发明技术方案作进一步的说明。The technical solution of the present invention will be further described below in conjunction with the accompanying drawings.
本发明所述一种用于海水脱盐及回收酸碱的装置如图1所示,所述用于海水脱盐及回收酸碱的装置包括脱盐系统200和酸碱回收系统100。A device for seawater desalination and acid-base recovery according to the present invention is shown in Figure 1. The device for seawater desalination and acid-base recovery includes a desalination system 200 and an acid-base recovery system 100.
其中,所述脱盐系统200包括海水室201、淡水室204和去离子脱盐装置203,海水室201通过三通阀202与去离子脱盐装置203相连,淡水室204与去离子脱盐装置203相连。淡水室204下部设有淡水出水口205,去离子脱盐装置203通过阀门206与酸碱回收系统100相连。The desalination system 200 includes a seawater chamber 201, a freshwater chamber 204 and a deionization and desalination device 203. The seawater chamber 201 is connected to the deionization and desalination device 203 through a three-way valve 202, and the freshwater chamber 204 is connected to the deionization and desalination device 203. A fresh water outlet 205 is provided at the bottom of the fresh water chamber 204, and the deionization and desalination device 203 is connected to the acid-base recovery system 100 through a valve 206.
其中,所述去离子脱盐装置203如图3所示,所述去离子脱盐装置203包括蠕动泵2031、流动电极液2037、底板2038、对应设置的钛网负极2032和钛网正极2033,钛网负极2032和钛网正极2033的内侧均设有阴离子交换膜2034,钛网正极2033紧靠阴离子交换膜2034,两个阴离子交换膜2034之间设有阳离子交换膜2035,阳离子交换膜2035将去离子脱盐装置203分为淡化区和盐化区。钛网负极2032和钛网正极2033外侧均设有底板2038,钛网负极2032紧靠底板2038,钛网负极2032和阴离子交换膜2034形成一个空间,钛网正极2033和底板2038形成一个空间,然后在前述形成的空间内设有若干个扰流搅拌器2036,蠕动泵2031将流动电极液2037在前述的形成的空间内循环流动。前述形成的空间内填充活性炭颗粒。相邻的扰流搅拌器2036转动方向相反,用以搅拌电极液中的活性炭颗粒。扰流搅拌器2036的转速为15-20RPM。Among them, the deionization and desalination device 203 is shown in Figure 3. The deionization and desalination device 203 includes a peristaltic pump 2031, a flowing electrode solution 2037, a bottom plate 2038, a corresponding titanium mesh negative electrode 2032 and a titanium mesh positive electrode 2033. The titanium mesh Anion exchange membrane 2034 is provided inside the negative electrode 2032 and the titanium mesh positive electrode 2033. The titanium mesh positive electrode 2033 is close to the anion exchange membrane 2034. There is a cation exchange membrane 2035 between the two anion exchange membranes 2034. The cation exchange membrane 2035 will deionize. The desalination device 203 is divided into a desalination area and a salinization area. There is a bottom plate 2038 on the outside of the titanium mesh negative electrode 2032 and the titanium mesh positive electrode 2033. The titanium mesh negative electrode 2032 is close to the bottom plate 2038. The titanium mesh negative electrode 2032 and the anion exchange membrane 2034 form a space. The titanium mesh positive electrode 2033 and the bottom plate 2038 form a space. Then Several turbulence stirrers 2036 are provided in the aforementioned space, and the peristaltic pump 2031 circulates the flowing electrode liquid 2037 in the aforementioned formed space. The space formed above is filled with activated carbon particles. The adjacent turbulence stirrers 2036 rotate in opposite directions and are used to stir the activated carbon particles in the electrode solution. The rotation speed of the spoiler mixer 2036 is 15-20RPM.
其中,所述酸碱回收系统100包括酸室、碱室、浓盐水室115,酸室和碱室通过隔板108分开,在酸室和碱室均设有矩形梳齿状的双极膜104,酸室中双极膜104一侧设有阴离子交换膜107,碱室中双极膜104的一侧设有阳离子交换膜109,阴离子交换膜107和阳离子交换膜109均与耐酸碱腐蚀的钛合金支架113贴合。钛合金支架113固定设置在浓盐水室115的上部。酸室内的双极膜104上部设有阳极电极103,碱室内的双极膜104上部设有阴极电极111。其中,阳极电极103外表面附有有机生物质。阳极电极103和阴极电极111构成微生物燃料电池。有机生物质可以为低浓度有机废水、纤维素、葡萄糖、甲烷等等。阳极电极103和阴极电极111通过导线101供脱盐系统100的去离子脱盐装置203相连。整个酸碱回收系统100为立体槽,立体槽的上部开设有出气口102。酸室外面设有蠕动泵105,蠕动泵105将盐酸从盐酸出口106排出,所述碱室外面也设有蠕动泵(105),蠕动泵105将氢氧化钠从氢氧化钠出口114排出。Among them, the acid-base recovery system 100 includes an acid chamber, an alkali chamber, and a concentrated salt water chamber 115. The acid chamber and the alkali chamber are separated by a partition 108. Both the acid chamber and the alkali chamber are provided with rectangular comb-shaped bipolar membranes 104. , an anion exchange membrane 107 is provided on one side of the bipolar membrane 104 in the acid chamber, and a cation exchange membrane 109 is provided on one side of the bipolar membrane 104 in the alkali chamber. Both the anion exchange membrane 107 and the cation exchange membrane 109 are resistant to acid and alkali corrosion. Titanium alloy bracket 113 fit. The titanium alloy bracket 113 is fixedly installed on the upper part of the concentrated brine chamber 115 . An anode electrode 103 is provided on the upper part of the bipolar membrane 104 in the acid chamber, and a cathode electrode 111 is provided on the upper part of the bipolar membrane 104 in the alkali chamber. Among them, organic biomass is attached to the outer surface of the anode electrode 103. The anode electrode 103 and the cathode electrode 111 constitute a microbial fuel cell. Organic biomass can be low-concentration organic wastewater, cellulose, glucose, methane, etc. The anode electrode 103 and the cathode electrode 111 are connected to the deionization and desalination device 203 of the desalination system 100 through a wire 101 . The entire acid-base recovery system 100 is a three-dimensional tank, and an air outlet 102 is provided at the upper part of the three-dimensional tank. A peristaltic pump 105 is provided outside the acid chamber. The peristaltic pump 105 discharges hydrochloric acid from the hydrochloric acid outlet 106. A peristaltic pump (105) is also provided outside the alkali chamber. The peristaltic pump 105 discharges sodium hydroxide from the sodium hydroxide outlet 114.
采用本发明所述用于海水脱盐及回收酸碱的装置工作时如图3所示,供电时,微生物在阳极电极103消耗有机生物质产生二氧化碳和电子,二氧化碳由出气口102排出,电子移动到阴极电极111发生还原反应,产生水;酸室中的双极膜104(氢氧根离子扩散侧朝上)向内扩散氢离子,浓盐水室115中的氯离子被阳极电极103吸引而通过阴离子交换膜107进入酸室,与氢离子结合成盐酸利用蠕动泵105从盐酸出口106处收集。隔板108右侧的碱室中的双极膜112(氢离子扩散侧朝上)向内扩散氢氧根离子,浓盐水室115中的钠离子被阴极111吸引,通过阳离子交换膜109进入碱室,与氢氧根离子结合成氢氧化钠利用蠕动泵105从氢氧化钠出口114处收集,矩形梳齿状双层膜104与阴离子交换膜107和阳离子交换膜109接触面积增大,容积减小,利用钛合金支架113支撑,钛合金支架113既耐酸碱腐蚀,也能保护双层膜104及阴离子交换膜107和阳离子交换膜109不易变形,从而改善离子的分布均匀性,加快了离子结合成酸碱的速率;微生物燃料电池通过导线101向去离子装置203供电,海水进入盐水室201后被三通阀202分流,一部分进入到去离子装置203的淡化区,海水中的钠离子被钛网正极2033的斥力推进阳离子交换2034进入到盐化区,海水中的氯离子被钛网正极2033较强的吸引力带进流动电极液2037中,被活性炭颗粒吸附,由于钛网正极紧靠阴离子交换膜,使得电荷传输距离减小,改善了流动电极内的活性炭颗粒吸附效果,由于扰流搅拌装置2036的介入,活性炭颗粒的运动规律得以控制,让几乎每一个活性炭颗粒都能吸附上氯离子,实现离子吸附均匀性,提高了流动电极液的利用率和脱盐效果。由于蠕动泵2031的驱动力,海水中的氯离子被流动电极液2037带到另一侧的阴离子交换膜2034,受到钛网负极2032的斥力,被推进盐化区,因此盐化区可以收集浓盐水,由阀门206控制排入浓盐水室115,淡化区由于盐离子的浓度减小,从而产出淡水,流入淡水室204收集,从淡水室出口205排出系统供人们使用。The device for seawater desalination and acid-base recovery according to the present invention works as shown in Figure 3. When power is supplied, microorganisms consume organic biomass at the anode electrode 103 to produce carbon dioxide and electrons. The carbon dioxide is discharged from the air outlet 102, and the electrons move to The cathode electrode 111 undergoes a reduction reaction to produce water; the bipolar membrane 104 in the acid chamber (hydroxide ion diffusion side faces upward) diffuses hydrogen ions inward, and the chloride ions in the concentrated brine chamber 115 are attracted by the anode electrode 103 and pass through the anions. The exchange membrane 107 enters the acid chamber and combines with hydrogen ions to form hydrochloric acid, which is collected from the hydrochloric acid outlet 106 by the peristaltic pump 105 . The bipolar membrane 112 (hydrogen ion diffusion side facing upward) in the alkali chamber on the right side of the partition 108 diffuses hydroxide ions inwardly, and the sodium ions in the concentrated brine chamber 115 are attracted by the cathode 111 and enter the alkali through the cation exchange membrane 109 chamber, combined with hydroxide ions to form sodium hydroxide, which is collected from the sodium hydroxide outlet 114 using a peristaltic pump 105. The contact area of the rectangular comb-shaped double-layer membrane 104 with the anion exchange membrane 107 and the cation exchange membrane 109 increases, and the volume decreases. Small, it is supported by a titanium alloy bracket 113. The titanium alloy bracket 113 is not only resistant to acid and alkali corrosion, but also can protect the double-layer membrane 104, the anion exchange membrane 107 and the cation exchange membrane 109 from being easily deformed, thereby improving the uniformity of ion distribution and speeding up the ion exchange process. The rate of combining into acid and alkali; the microbial fuel cell supplies power to the deionization device 203 through the wire 101. After the seawater enters the brine chamber 201, it is diverted by the three-way valve 202, and part of it enters the desalination area of the deionization device 203. The sodium ions in the seawater are The repulsive force of the titanium mesh positive electrode 2033 pushes the cation exchange 2034 into the salinization zone. The chloride ions in the seawater are brought into the flowing electrode solution 2037 by the strong attraction of the titanium mesh positive electrode 2033, and are adsorbed by the activated carbon particles. Since the titanium mesh positive electrode is close to The anion exchange membrane reduces the charge transmission distance and improves the adsorption effect of activated carbon particles in the flow electrode. Due to the intervention of the flow stirring device 2036, the movement pattern of the activated carbon particles is controlled, allowing almost every activated carbon particle to adsorb chlorine. ions, achieving uniform ion adsorption and improving the utilization rate and desalination effect of the flowing electrode solution. Due to the driving force of the peristaltic pump 2031, the chloride ions in the seawater are brought to the anion exchange membrane 2034 on the other side by the flowing electrode liquid 2037, and are pushed into the salinization zone by the repulsive force of the titanium mesh negative electrode 2032. Therefore, the salinization zone can collect concentrated The salt water is controlled by the valve 206 and is discharged into the concentrated salt water chamber 115. As the concentration of salt ions decreases in the desalination area, fresh water is produced, flows into the fresh water chamber 204 for collection, and is discharged from the system through the outlet 205 of the fresh water chamber for people to use.
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KR20150003094A (en) * | 2013-06-28 | 2015-01-08 | 한국에너지기술연구원 | Flow-electrode capacitive deionizaion apparatus using ion exchange membranes |
CN107624106A (en) * | 2015-01-16 | 2018-01-23 | Dwi莱布尼茨互动材料研究所协会 | Method for continuous water desalination and ion separation by capacitive deionization and its single-module flow electrode device |
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