CN114940553B - Monopole type and multipole type electric control ion exchange reactor and group - Google Patents
Monopole type and multipole type electric control ion exchange reactor and group Download PDFInfo
- Publication number
- CN114940553B CN114940553B CN202210416104.5A CN202210416104A CN114940553B CN 114940553 B CN114940553 B CN 114940553B CN 202210416104 A CN202210416104 A CN 202210416104A CN 114940553 B CN114940553 B CN 114940553B
- Authority
- CN
- China
- Prior art keywords
- ion exchange
- electric control
- control ion
- electrode plates
- anode
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Active
Links
- 238000005342 ion exchange Methods 0.000 title claims abstract description 177
- 230000005405 multipole Effects 0.000 title claims abstract 19
- 230000005404 monopole Effects 0.000 title claims abstract 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 28
- 229910001868 water Inorganic materials 0.000 claims description 24
- 229910052797 bismuth Inorganic materials 0.000 claims description 21
- JCXGWMGPZLAOME-UHFFFAOYSA-N bismuth atom Chemical compound [Bi] JCXGWMGPZLAOME-UHFFFAOYSA-N 0.000 claims description 21
- 229920000128 polypyrrole Polymers 0.000 claims description 21
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 20
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N Phenol Chemical compound OC1=CC=CC=C1 ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 claims description 20
- 239000011575 calcium Substances 0.000 claims description 20
- 230000005684 electric field Effects 0.000 claims description 20
- 239000010405 anode material Substances 0.000 claims description 17
- 239000010406 cathode material Substances 0.000 claims description 17
- PAYRUJLWNCNPSJ-UHFFFAOYSA-N Aniline Chemical compound NC1=CC=CC=C1 PAYRUJLWNCNPSJ-UHFFFAOYSA-N 0.000 claims description 16
- 229920000767 polyaniline Polymers 0.000 claims description 16
- JLVVSXFLKOJNIY-UHFFFAOYSA-N Magnesium ion Chemical compound [Mg+2] JLVVSXFLKOJNIY-UHFFFAOYSA-N 0.000 claims description 15
- 229910001424 calcium ion Inorganic materials 0.000 claims description 15
- 238000005265 energy consumption Methods 0.000 claims description 15
- 229910001425 magnesium ion Inorganic materials 0.000 claims description 15
- 239000002351 wastewater Substances 0.000 claims description 15
- 239000000498 cooling water Substances 0.000 claims description 14
- 239000000126 substance Substances 0.000 claims description 14
- 229910000000 metal hydroxide Inorganic materials 0.000 claims description 13
- 150000004692 metal hydroxides Chemical class 0.000 claims description 13
- 230000001590 oxidative effect Effects 0.000 claims description 13
- AJQLEJAVGARHGQ-UHFFFAOYSA-N dithiosalicylic acid Chemical compound OC1=CC=CC=C1C(S)=S AJQLEJAVGARHGQ-UHFFFAOYSA-N 0.000 claims description 12
- WQYVRQLZKVEZGA-UHFFFAOYSA-N hypochlorite Chemical compound Cl[O-] WQYVRQLZKVEZGA-UHFFFAOYSA-N 0.000 claims description 12
- 244000005700 microbiome Species 0.000 claims description 12
- DCYOBGZUOMKFPA-UHFFFAOYSA-N iron(2+);iron(3+);octadecacyanide Chemical compound [Fe+2].[Fe+2].[Fe+2].[Fe+3].[Fe+3].[Fe+3].[Fe+3].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-] DCYOBGZUOMKFPA-UHFFFAOYSA-N 0.000 claims description 11
- 239000003344 environmental pollutant Substances 0.000 claims description 9
- 231100000719 pollutant Toxicity 0.000 claims description 9
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 claims description 8
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 claims description 8
- 150000004945 aromatic hydrocarbons Chemical class 0.000 claims description 8
- 229910052791 calcium Inorganic materials 0.000 claims description 8
- 239000011777 magnesium Substances 0.000 claims description 8
- 229910052749 magnesium Inorganic materials 0.000 claims description 8
- CXKWCBBOMKCUKX-UHFFFAOYSA-M methylene blue Chemical compound [Cl-].C1=CC(N(C)C)=CC2=[S+]C3=CC(N(C)C)=CC=C3N=C21 CXKWCBBOMKCUKX-UHFFFAOYSA-M 0.000 claims description 8
- 229960000907 methylthioninium chloride Drugs 0.000 claims description 8
- 150000002989 phenols Chemical class 0.000 claims description 8
- 150000003839 salts Chemical class 0.000 claims description 8
- 125000002887 hydroxy group Chemical group [H]O* 0.000 claims description 7
- 238000000034 method Methods 0.000 claims description 6
- 229910001415 sodium ion Inorganic materials 0.000 claims description 6
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 5
- 229910002804 graphite Inorganic materials 0.000 claims description 5
- 239000010439 graphite Substances 0.000 claims description 5
- 229910001385 heavy metal Inorganic materials 0.000 claims description 5
- 239000000463 material Substances 0.000 claims description 5
- -1 polydithio diphenylamine Polymers 0.000 claims description 5
- 239000004065 semiconductor Substances 0.000 claims description 5
- 239000011734 sodium Substances 0.000 claims description 5
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims description 4
- 230000006698 induction Effects 0.000 claims description 4
- 238000001223 reverse osmosis Methods 0.000 claims description 4
- 150000001875 compounds Chemical class 0.000 claims 12
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 claims 1
- 238000005516 engineering process Methods 0.000 abstract description 16
- 238000004134 energy conservation Methods 0.000 abstract 1
- 150000002500 ions Chemical class 0.000 description 15
- 238000000926 separation method Methods 0.000 description 9
- 238000010586 diagram Methods 0.000 description 8
- 239000002131 composite material Substances 0.000 description 5
- 238000005341 cation exchange Methods 0.000 description 4
- 239000008367 deionised water Substances 0.000 description 4
- 229910021641 deionized water Inorganic materials 0.000 description 4
- 238000011084 recovery Methods 0.000 description 4
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 3
- 238000005349 anion exchange Methods 0.000 description 3
- 239000010842 industrial wastewater Substances 0.000 description 3
- 239000012528 membrane Substances 0.000 description 3
- 241000282414 Homo sapiens Species 0.000 description 2
- 101001121408 Homo sapiens L-amino-acid oxidase Proteins 0.000 description 2
- 101000827703 Homo sapiens Polyphosphoinositide phosphatase Proteins 0.000 description 2
- 102100026388 L-amino-acid oxidase Human genes 0.000 description 2
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- 102100023591 Polyphosphoinositide phosphatase Human genes 0.000 description 2
- 101100012902 Saccharomyces cerevisiae (strain ATCC 204508 / S288c) FIG2 gene Proteins 0.000 description 2
- 101100233916 Saccharomyces cerevisiae (strain ATCC 204508 / S288c) KAR5 gene Proteins 0.000 description 2
- 150000001450 anions Chemical class 0.000 description 2
- 150000001768 cations Chemical class 0.000 description 2
- 230000000593 degrading effect Effects 0.000 description 2
- DMBHHRLKUKUOEG-UHFFFAOYSA-N diphenylamine Chemical compound C=1C=CC=CC=1NC1=CC=CC=C1 DMBHHRLKUKUOEG-UHFFFAOYSA-N 0.000 description 2
- 231100000331 toxic Toxicity 0.000 description 2
- 230000002588 toxic effect Effects 0.000 description 2
- BWGNESOTFCXPMA-UHFFFAOYSA-N Dihydrogen disulfide Chemical compound SS BWGNESOTFCXPMA-UHFFFAOYSA-N 0.000 description 1
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 description 1
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 description 1
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 1
- 229910001454 Ni2+ Inorganic materials 0.000 description 1
- VEQPNABPJHWNSG-UHFFFAOYSA-N Nickel(2+) Chemical compound [Ni+2] VEQPNABPJHWNSG-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- 238000009388 chemical precipitation Methods 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
- 238000009713 electroplating Methods 0.000 description 1
- 239000011737 fluorine Substances 0.000 description 1
- 229910052731 fluorine Inorganic materials 0.000 description 1
- QWPPOHNGKGFGJK-UHFFFAOYSA-N hypochlorous acid Chemical compound ClO QWPPOHNGKGFGJK-UHFFFAOYSA-N 0.000 description 1
- 229910052744 lithium Inorganic materials 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 239000011572 manganese Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000008204 material by function Substances 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 238000005272 metallurgy Methods 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Classifications
-
- 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J47/00—Ion-exchange processes in general; Apparatus therefor
- B01J47/02—Column or bed processes
- B01J47/026—Column or bed processes using columns or beds of different ion exchange materials in series
- B01J47/028—Column or bed processes using columns or beds of different ion exchange materials in series with alternately arranged cationic and anionic exchangers
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J47/00—Ion-exchange processes in general; Apparatus therefor
- B01J47/02—Column or bed processes
- B01J47/06—Column or bed processes during which the ion-exchange material is subjected to a physical treatment, e.g. heat, electric current, irradiation or vibration
-
- 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
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/32—Hydrocarbons, e.g. oil
- C02F2101/322—Volatile compounds, e.g. benzene
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/38—Organic compounds containing nitrogen
-
- 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
- C02F2201/002—Construction details of the apparatus
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (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)
Abstract
Description
技术领域Technical Field
本发明涉及电控离子交换节能技术领域,具体为一种单极式、复极式电控离子交换反应器及群组。The invention relates to the technical field of electrically controlled ion exchange energy saving, in particular to a monopolar and bipolar electrically controlled ion exchange reactor and a group thereof.
背景技术Background technique
随着时代的进步和社会的发展,人类对洁净生活环境的需求越来越迫切。从事冶金、电镀、矿业加工、电池生产等行业的企业会产生数量巨大的工业废水,这种废水中包含大量的毒性离子,如氟、铅、镉、汞等,同时也包含如锂、钴、镍、锰等高附加值金属离子。工业废水的排放不仅会对人类健康产生巨大的威胁,同时也是一种资源的浪费。所以,工业废水中的毒性离子的去除和高附加值离子的分离回收逐渐成为近年来科学研究的热点问题。With the progress of the times and the development of society, human beings have an increasingly urgent need for a clean living environment. Enterprises engaged in metallurgy, electroplating, mining processing, battery production and other industries will produce a huge amount of industrial wastewater, which contains a large number of toxic ions, such as fluorine, lead, cadmium, mercury, etc., as well as high-value-added metal ions such as lithium, cobalt, nickel, and manganese. The discharge of industrial wastewater not only poses a huge threat to human health, but is also a waste of resources. Therefore, the removal of toxic ions in industrial wastewater and the separation and recovery of high-value-added ions have gradually become hot issues in scientific research in recent years.
现有的离子分离技术主要有化学沉淀技术、离子交换技术、膜分离技术和电化学技术等,但能耗巨大、易产生二次污染、设备庞大、流程复杂等问题始终制约着这些技术的应用。Existing ion separation technologies mainly include chemical precipitation technology, ion exchange technology, membrane separation technology and electrochemical technology, but problems such as huge energy consumption, easy to generate secondary pollution, bulky equipment and complex processes have always restricted the application of these technologies.
电控离子交换是结合了离子交换、电化学技术的新型离子选择性分离技术,通过电化学调节电位响应型离子交换功能材料的氧化/还原状态来控制目标离子的置入/释放,实现水中离子快速、高效的分离回收。目前,电控离子交换作为一种环境友好的新型、高效、绿色的离子分离回收技术备受国内外学者的关注,该技术已被用于Na+、Cs+、Ca2+、Mg2+、Ni2+、Pb2+、Cu2+等阳离子以及ClO4 -、F-、I-、Cl-、Br-等阴离子的选择性分离。Electro-controlled ion exchange is a new ion selective separation technology that combines ion exchange and electrochemical technology. It controls the placement/release of target ions by electrochemically regulating the oxidation/reduction state of potential-responsive ion exchange functional materials, thereby achieving rapid and efficient separation and recovery of ions in water. At present, electro-controlled ion exchange has attracted much attention from scholars at home and abroad as a new, environmentally friendly, efficient, and green ion separation and recovery technology. This technology has been used for the selective separation of cations such as Na + , Cs + , Ca2+ , Mg2+ , Ni2+ , Pb2 +, and Cu2 + , as well as anions such as ClO4- , F- , I- , Cl- , and Br- .
然而,以电控离子交换技术为基础构建的单极式与复极式电控离子交换反应器及其在工作中的连接方式尚未见报道。However, there are no reports on monopolar and bipolar electrically controlled ion exchange reactors based on electrically controlled ion exchange technology and their connection methods during operation.
发明内容Summary of the invention
针对现有技术中存在的问题,本发明提供一种单极式、复极式电控离子交换反应器及群组,依据阳电极板和阴电极板之间不同连接方式分别形成单极式、复极式电控离子交换反应器;再依据单极式、复极式电控离子交换反应器各自不用的连接方式形成多种反应器群组,以适配不同电压电流范围的电源,拓展电控离子交换技术的应用范围。In view of the problems existing in the prior art, the present invention provides a monopolar and bipolar electrically controlled ion exchange reactor and group, wherein the monopolar and bipolar electrically controlled ion exchange reactors are respectively formed according to different connection modes between the anode electrode plate and the cathode electrode plate; and then a plurality of reactor groups are formed according to different connection modes of the monopolar and bipolar electrically controlled ion exchange reactors to adapt to power supplies with different voltage and current ranges, thereby expanding the application scope of the electrically controlled ion exchange technology.
本发明是通过以下技术方案来实现:The present invention is achieved through the following technical solutions:
一种单极式电控离子交换反应器,包括等数量的多个阳电极板和多个阴电极板;所述多个阳电极板与所述多个阴电极板平行且交错排布;多个所述阳电极板的同一端直接连接形成阳极,所述阳极与工作电源的正极连接;多个所述阳电极板之间并联连接;多个所述阴电极板的同一端直接连接形成阴极,所述阴极与工作电源的负极连接;多个所述阴电极板之间为并联连接。A monopolar electrically controlled ion exchange reactor comprises an equal number of anode plates and cathode plates; the anode plates are parallel to and staggered with the cathode plates; the anode plates are directly connected at the same end to form an anode, which is connected to the positive pole of a working power supply; the anode plates are connected in parallel; the cathode plates are directly connected at the same end to form a cathode, which is connected to the negative pole of a working power supply; and the cathode plates are connected in parallel.
优选的,多个所述阳电极板和多个阴电极板交替间隔设置,相邻的所述阳电极板与阴电极板之间的间隔距离为1cm~50cm。Preferably, the plurality of anode electrode plates and the plurality of cathode electrode plates are alternately arranged at intervals, and the interval distance between adjacent anode electrode plates and cathode electrode plates is 1 cm to 50 cm.
优选的,所述工作电源的电流密度为3mA/cm2~20mA/cm2。Preferably, the current density of the working power supply is 3 mA/cm 2 to 20 mA/cm 2 .
优选的,所述阳电极板采用的阳极材料为改性P型半导体双金属氢氧化物、电控重金属离子交换材料、层状双金属氢氧化物/聚吡咯复合物、卤氧化铋、卤氧化铋/聚苯胺复合物和卤氧化铋/聚吡咯复合物中的一种;所述阴电极板采用的阴极材料为亚铁氰化铁、双硫代水杨酸/聚苯胺、双硫代水杨酸/聚吡咯、石墨和聚二硫代二苯胺中的一种。Preferably, the anode material used in the anode electrode plate is one of modified P-type semiconductor double metal hydroxide, electrically controlled heavy metal ion exchange material, layered double metal hydroxide/polypyrrole complex, bismuth oxyhalide, bismuth oxyhalide/polyaniline complex and bismuth oxyhalide/polypyrrole complex; the cathode material used in the cathode electrode plate is one of ferric ferrocyanide, dithiosalicylic acid/polyaniline, dithiosalicylic acid/polypyrrole, graphite and polydithiodiphenylamine.
一种单极式电控离子交换反应器群组,包括多个单极式电控离子交换反应器,多个单极式电控离子交换反应器串联形成单极式电控离子交换反应器串联群组;多个单极式电控离子交换反应器并联形成单极式电控离子交换反应器并联群组;多个单极式电控离子交换反应器并联群组串联形成单极式电控离子交换反应器串并联群组。A monopolar electrically controlled ion exchange reactor group comprises a plurality of monopolar electrically controlled ion exchange reactors, wherein the plurality of monopolar electrically controlled ion exchange reactors are connected in series to form a monopolar electrically controlled ion exchange reactor series group; the plurality of monopolar electrically controlled ion exchange reactors are connected in parallel to form a monopolar electrically controlled ion exchange reactor parallel group; the plurality of monopolar electrically controlled ion exchange reactor parallel groups are connected in series to form a monopolar electrically controlled ion exchange reactor series-parallel group.
一种复极式电控离子交换反应器,包括等数量的多个阳电极板和多个阴电极板;多个所述阳电极板与多个阴电极板平行且交错排布;最外侧的阳电极板为阳极,所述阳极与工作电源的正极连接;最外侧的阴电极板为阴极,所述阴极与工作电源的负极连接。A bipolar electrically controlled ion exchange reactor comprises a plurality of anode electrode plates and a plurality of cathode electrode plates of equal number; the plurality of anode electrode plates and the plurality of cathode electrode plates are arranged in parallel and staggered; the outermost anode electrode plate is an anode connected to the positive electrode of a working power supply; the outermost cathode electrode plate is a cathode connected to the negative electrode of the working power supply.
优选的,所述阳电极板和多个阴电极板间隔设置,相邻的所述阳电极板与阴电极板之间的间隔距离为1cm~50cm。Preferably, the anode electrode plate and the plurality of cathode electrode plates are spaced apart, and the spacing distance between adjacent anode electrode plates and cathode electrode plates is 1 cm to 50 cm.
优选的,所述工作电源的电流密度为3mA/cm2~20mA/cm2。Preferably, the current density of the working power supply is 3 mA/cm 2 to 20 mA/cm 2 .
优选的,所述阳电极板采用的阳极材料为改性P型半导体双金属氢氧化物、电控重金属离子交换材料、层状双金属氢氧化物/聚吡咯复合物、卤氧化铋、卤氧化铋/聚苯胺复合物和卤氧化铋/聚吡咯复合物中的一种;所述阴电极板采用的阴极材料为亚铁氰化铁、双硫代水杨酸/聚苯胺、双硫代水杨酸/聚吡咯、石墨和聚二硫代二苯胺中的一种。Preferably, the anode material used in the anode electrode plate is one of modified P-type semiconductor double metal hydroxide, electrically controlled heavy metal ion exchange material, layered double metal hydroxide/polypyrrole complex, bismuth oxyhalide, bismuth oxyhalide/polyaniline complex and bismuth oxyhalide/polypyrrole complex; the cathode material used in the cathode electrode plate is one of ferric ferrocyanide, dithiosalicylic acid/polyaniline, dithiosalicylic acid/polypyrrole, graphite and polydithiodiphenylamine.
一种复极式电控离子交换反应器群组,包括多个复极式电控离子交换反应器,多个复极式电控离子交换反应器串联形成复极式电控离子交换反应器串联群组;多个复极式电控离子交换反应器并联形成复极式电控离子交换反应器并联群组;多个复极式电控离子交换反应器并联群组串联形成复极式电控离子交换反应器串并联群组。A bipolar electrically controlled ion exchange reactor group comprises a plurality of bipolar electrically controlled ion exchange reactors, wherein the plurality of bipolar electrically controlled ion exchange reactors are connected in series to form a bipolar electrically controlled ion exchange reactor series group; the plurality of bipolar electrically controlled ion exchange reactors are connected in parallel to form a bipolar electrically controlled ion exchange reactor parallel group; and the plurality of bipolar electrically controlled ion exchange reactor parallel groups are connected in series to form a bipolar electrically controlled ion exchange reactor series-parallel group.
与现有技术相比,本发明具有以下有益效果:Compared with the prior art, the present invention has the following beneficial effects:
本发明中根据阳极板和阴极板的不同连接方式形成单极式电控离子交换反应器和复极式电控离子交换反应器,阳电极板和阴电极板的数量根据处理废水的量进行配置,保证离子交换器的废水处理能力,适应不同的工况。In the present invention, a monopolar electrically controlled ion exchange reactor and a bipolar electrically controlled ion exchange reactor are formed according to different connection modes of the anode plate and the cathode plate. The number of the anode plate and the cathode plate is configured according to the amount of wastewater to be treated, thereby ensuring the wastewater treatment capacity of the ion exchanger and adapting to different working conditions.
一种单极式电控离子交换反应器具有低压大电流特,阳电极板工作原理为:在电场作用下,阳电极板表面的目标污染物失去电子直接被氧化,或利用电极表面产生具有强氧化性的氧化剂(-OH,HClO,ClO—等),使目标污染物(苯酚、苯胺、亚甲基蓝、氨氮、酚类、芳烃等有机物和无机盐类)氧化降解,从而高效降解废水。A monopolar electrically controlled ion exchange reactor has the characteristics of low voltage and high current. The working principle of the anode electrode plate is: under the action of the electric field, the target pollutants on the surface of the anode electrode plate lose electrons and are directly oxidized, or the electrode surface is used to produce oxidants with strong oxidizing properties (-OH, HClO, ClO—, etc.), so that the target pollutants (phenol, aniline, methylene blue, ammonia nitrogen, phenols, aromatic hydrocarbons and other organic substances and inorganic salts) are oxidized and degraded, thereby efficiently degrading the wastewater.
阴电极板工作原理为:在电场作用下,阴极呈还原状态得到电子,溶液中的阳离子置入膜内以中和膜内过剩的负电荷,从而阴极从溶液中捕捉离子(钠离子、钙离子、镁离子),实现溶液中离子的高效分离。The working principle of the cathode plate is: under the action of the electric field, the cathode is in a reduced state and obtains electrons, and the cations in the solution are placed in the membrane to neutralize the excess negative charge in the membrane, so that the cathode captures ions (sodium ions, calcium ions, magnesium ions) from the solution to achieve efficient separation of ions in the solution.
一种复极式电控离子交换反应器具有高压小电流特点,可适配不同电压电流范围的电源。A bipolar electrically controlled ion exchange reactor has the characteristics of high voltage and low current and can be adapted to power supplies with different voltage and current ranges.
一种单极式电控离子交换反应器群组和一种复极式电控离子交换反应器群组以两种电控离子交换反应器为基础,构建的反应器串联、并联和串并联连接群组简单易行,适用于多种复杂工作电路系统,极大的拓展了电控离子交换技术的应用范围。A unipolar electrically controlled ion exchange reactor group and a bipolar electrically controlled ion exchange reactor group are based on two electrically controlled ion exchange reactors. The reactor series, parallel and series-parallel connection groups are simple and easy to construct, suitable for a variety of complex working circuit systems, and greatly expand the application scope of electrically controlled ion exchange technology.
本发明中反应器连接方式经合理搭配与使用,可极大的减少反应器所需能耗,降低目标离子的分离回收成本。The reactor connection mode of the present invention can greatly reduce the energy consumption required for the reactor and reduce the separation and recovery cost of the target ions through reasonable matching and use.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
图1为本发明一种单极式电控离子交换反应器的示意图;FIG1 is a schematic diagram of a monopolar electrically controlled ion exchange reactor of the present invention;
图2为本发明一种复极式电控离子交换反应器的示意图;FIG2 is a schematic diagram of a bipolar electrically controlled ion exchange reactor of the present invention;
图3为本发明一种单极式电控离子交换反应器的串联群组的示意图;FIG3 is a schematic diagram of a series group of monopolar electrically controlled ion exchange reactors according to the present invention;
图4为本发明一种单极式电控离子交换反应器的并联群组的示意图;FIG4 is a schematic diagram of a parallel group of monopolar electrically controlled ion exchange reactors according to the present invention;
图5为本发明一种单极式电控离子交换反应器的串并联群组的示意图;FIG5 is a schematic diagram of a series-parallel group of monopolar electrically controlled ion exchange reactors of the present invention;
图6为本发明一种复极式电控离子交换反应器的串联群组的示意图;FIG6 is a schematic diagram of a series group of bipolar electrically controlled ion exchange reactors according to the present invention;
图7为本发明一种复极式电控离子交换反应器的并联群组的示意图;FIG7 is a schematic diagram of a parallel group of bipolar-type electrically controlled ion exchange reactors according to the present invention;
图8为本发明一种复极式电控离子交换反应器的串并联群组的示意图。FIG8 is a schematic diagram of a series-parallel group of bipolar electrically controlled ion exchange reactors according to the present invention.
具体实施方式Detailed ways
下面结合具体的实施例对本发明做进一步的详细说明,所述是对本发明的解释而不是限定。The present invention is further described in detail below in conjunction with specific embodiments, which are intended to explain the present invention rather than to limit it.
本发明公开了一种单极式电控离子交换反应器,参照图1,包括等数量的多个阳电极板和多个阴电极板;多个阳电极板与多个阴电极板平行且交错正向相对排布;多个阳电极板和多个阴电极板交替间隔设置,相邻的阳电极板与阴电极板之间的间隔距离为1~50cm。The present invention discloses a monopolar electrically controlled ion exchange reactor, which, referring to FIG1 , comprises a plurality of anode electrode plates and a plurality of cathode electrode plates of equal number; the plurality of anode electrode plates and the plurality of cathode electrode plates are arranged parallel to and staggered in a positive direction relative to each other; the plurality of anode electrode plates and the plurality of cathode electrode plates are arranged alternately and at intervals, and the interval distance between adjacent anode electrode plates and cathode electrode plates is 1 to 50 cm.
多个阳电极板的同一端直接连接形成阳极,多个阳电极板之间并联;多个阴电极板的同一端直接连接形成阴极,多个阴电极板之间为并联连接。The same end of multiple positive electrode plates is directly connected to form an anode, and the multiple positive electrode plates are connected in parallel; the same end of multiple negative electrode plates is directly connected to form a cathode, and the multiple negative electrode plates are connected in parallel.
其中,阳电极板采用的阳极材料为改性P型半导体双金属氢氧化物、电控重金属离子交换材料、层状双金属氢氧化物/聚吡咯复合物、卤氧化铋、卤氧化铋/聚苯胺复合物和卤氧化铋/聚吡咯复合物中的一种。Among them, the anode material used in the anode electrode plate is one of modified P-type semiconductor double metal hydroxide, electrically controlled heavy metal ion exchange material, layered double metal hydroxide/polypyrrole complex, bismuth oxyhalide, bismuth oxyhalide/polyaniline complex and bismuth oxyhalide/polypyrrole complex.
阴电极板采用的阴极材料为亚铁氰化铁、双硫代水杨酸/聚苯胺、双硫代水杨酸/聚吡咯、石墨和聚二硫代二苯胺中的一种。The cathode material used in the cathode electrode plate is one of ferric ferrocyanide, dithiosalicylic acid/polyaniline, dithiosalicylic acid/polypyrrole, graphite and polydithiodiphenylamine.
使用时,多个阳电极板的同一端直接连接形成的阳极与工作电源的正极相连,多个阴电极板的同一端直接连接形成的阴极与工作电源负极的连接。即,将等数量电控离子交换反应器中的电控阴、阳电极板平行且正向相对排布,同时,将反应器中的所有电控阳离子交换极板(即阳电极板)与工作电源的正极直接连接,所有电控阳离子交换极板之间并联连接;将反应器中的所有电控阴离子交换极板(即阴电极板)与工作电源的负极直接连接,所有电控阴离子交换极板之间并联连接,即为单极式电控离子交换反应器,该反应器的特点为在低工作电压下可产生较大的工作电流。When in use, the anode formed by directly connecting the same end of multiple positive electrode plates is connected to the positive electrode of the working power supply, and the cathode formed by directly connecting the same end of multiple negative electrode plates is connected to the negative electrode of the working power supply. That is, the electrically controlled negative and positive electrode plates in equal numbers of electrically controlled ion exchange reactors are arranged in parallel and positively relative to each other, and at the same time, all electrically controlled cation exchange plates (i.e., positive electrode plates) in the reactor are directly connected to the positive electrode of the working power supply, and all electrically controlled cation exchange plates are connected in parallel; all electrically controlled anion exchange plates (i.e., negative electrode plates) in the reactor are directly connected to the negative electrode of the working power supply, and all electrically controlled anion exchange plates are connected in parallel, which is a monopolar electrically controlled ion exchange reactor, which is characterized by being able to generate a large working current at a low working voltage.
一种复极式电控离子交换反应器,参照图2,包括等数量的多个阳电极板和多个阴电极板;多个阳电极板与所述多个阴电极板平行且交错正向相对排布,多个阳电极板和多个阴电极板交替间隔设置,相邻的阳电极板与阴电极板之间的间隔距离为1cm~50cm。A bipolar electrically controlled ion exchange reactor, referring to FIG2 , comprises a plurality of anode electrode plates and a plurality of cathode electrode plates of equal number; the plurality of anode electrode plates are parallel to the plurality of cathode electrode plates and are arranged in an interlaced positive direction relative to each other, the plurality of anode electrode plates and the plurality of cathode electrode plates are alternately arranged at intervals, and the interval distance between adjacent anode electrode plates and cathode electrode plates is 1 cm to 50 cm.
多个阳电极板中最外侧的阳电极板为阳极;多个阴电极板中最外侧的阴电极板为阴极。The outermost anode electrode plate among the plurality of anode electrode plates is an anode; the outermost cathode electrode plate among the plurality of cathode electrode plates is a cathode.
使用时,阳极与工作电源的正极连接,阴极与工作电源的负极连接。即,将电控离子交换反应器中的电控阴、阳离子交换极板平行排列,同时,反应器中仅最外侧电控阳离子交换极板与工作电源的正极连接,仅最外侧的电控阴离子交换极板与工作电源的负极连接,即为复极式电控离子交换反应器,该反应器的特点为在高工作电压下产生较小的工作电流。When in use, the anode is connected to the positive electrode of the working power supply, and the cathode is connected to the negative electrode of the working power supply. That is, the electrically controlled anion and cation exchange plates in the electrically controlled ion exchange reactor are arranged in parallel, and at the same time, only the outermost electrically controlled cation exchange plate in the reactor is connected to the positive electrode of the working power supply, and only the outermost electrically controlled anion exchange plate is connected to the negative electrode of the working power supply, which is a bipolar electrically controlled ion exchange reactor, which is characterized by generating a small working current under a high working voltage.
电控离子交换反应器的连接组合方式分为串联连接、并联连接和串并联连接三种。串联连接为将单极式电控离子交换反应器或复极式电控离子交换反应器串联连接在工作电路中。并联连接为将单极式电控离子交换反应器或复极式电控离子交换反应器并联连接在工作电路中。串并联连接为将所述电控离子交换反应器串并联连接在工作电路中,即,将多个单极式电控离子交换反应器或多个复极式电控离子交换反应器并联在一起组成反应器群组,再将多个反应器群组串联在一起。The connection combination modes of the electrically controlled ion exchange reactor are divided into three types: series connection, parallel connection and series-parallel connection. Series connection is to connect the monopolar electrically controlled ion exchange reactor or the bipolar electrically controlled ion exchange reactor in series in the working circuit. Parallel connection is to connect the monopolar electrically controlled ion exchange reactor or the bipolar electrically controlled ion exchange reactor in parallel in the working circuit. Series-parallel connection is to connect the electrically controlled ion exchange reactor in series and parallel in the working circuit, that is, multiple monopolar electrically controlled ion exchange reactors or multiple bipolar electrically controlled ion exchange reactors are connected in parallel to form a reactor group, and then multiple reactor groups are connected in series.
一种单极式电控离子交换反应器群组,包括多个单极式电控离子交换反应器,根据多个单极式电控离子交换反应器之间的连接方式形成单极式电控离子交换反应器串联群组、单极式电控离子交换反应器并联群组和单极式电控离子交换反应器串并联群组。A monopolar electrically controlled ion exchange reactor group includes a plurality of monopolar electrically controlled ion exchange reactors. According to the connection mode between the plurality of monopolar electrically controlled ion exchange reactors, a monopolar electrically controlled ion exchange reactor series group, a monopolar electrically controlled ion exchange reactor parallel group and a monopolar electrically controlled ion exchange reactor series-parallel group are formed.
参照图3,多个单极式电控离子交换反应器串联形成单极式电控离子交换反应器串联群组。3 , a plurality of monopolar electrically controlled ion exchange reactors are connected in series to form a monopolar electrically controlled ion exchange reactor series group.
参照图4,多个单极式电控离子交换反应器并联形成单极式电控离子交换反应器并联群组。4 , a plurality of monopolar electrically controlled ion exchange reactors are connected in parallel to form a monopolar electrically controlled ion exchange reactor parallel group.
参照图5,多个单极式电控离子交换反应器并联群组串联形成单极式电控离子交换反应器串并联群组。5 , a plurality of monopolar electrically controlled ion exchange reactor parallel groups are connected in series to form a monopolar electrically controlled ion exchange reactor series-parallel group.
一种复极式电控离子交换反应器群组,包括多个复极式电控离子交换反应器,根据多个复极式电控离子交换反应器之间的连接方式形成复极式电控离子交换反应器串联群组、复极式电控离子交换反应器并联群组和复极式电控离子交换反应器串并联群组。A bipolar electrically controlled ion exchange reactor group includes a plurality of bipolar electrically controlled ion exchange reactors. A bipolar electrically controlled ion exchange reactor series group, a bipolar electrically controlled ion exchange reactor parallel group and a bipolar electrically controlled ion exchange reactor series-parallel group are formed according to the connection mode between the plurality of bipolar electrically controlled ion exchange reactors.
参照图6,多个复极式电控离子交换反应器串联形成复极式电控离子交换反应器串联群组。6 , a plurality of bipolar electrically controlled ion exchange reactors are connected in series to form a bipolar electrically controlled ion exchange reactor series group.
参照图7,多个复极式电控离子交换反应器并联形成复极式电控离子交换反应器并联群组。7 , a plurality of bipolar electrically controlled ion exchange reactors are connected in parallel to form a bipolar electrically controlled ion exchange reactor parallel group.
参照图8,多个复极式电控离子交换反应器并联群组串联形成复极式电控离子交换反应器串并联群组。8 , a plurality of bipolar electric-controlled ion exchange reactor parallel groups are connected in series to form a bipolar electric-controlled ion exchange reactor series-parallel group.
使用时,对于任一连接方式,工作电源电流密度为3mA/cm2~20mA/cm2。When in use, for any connection mode, the working power supply current density is 3mA/cm 2 to 20mA/cm 2 .
在实际应用中,以苯酚、苯胺、亚甲基蓝、氨氮、酚类、芳烃等有机物和无机盐类为目标污染物。捕捉的离子为钠离子、钙离子、镁离子中的一种。In practical applications, organic substances and inorganic salts such as phenol, aniline, methylene blue, ammonia nitrogen, phenols, aromatic hydrocarbons, etc. are targeted pollutants. The captured ions are one of sodium ions, calcium ions, and magnesium ions.
实施例1Example 1
如图3所示,由三个单极式电控离子交换反应器串联组成单极式电控离子交换反应器串联群组。其中第一个单极式电控离子交换反应器的所有阳电极板与工作电源的正极相连,第三个单极式电控离子交换反应器的所有阴电极板与工作电源的负极相连。阳电极板采用的阳极材料为卤氧化铋/聚苯胺复合物,阴电极板采用的阴极材料为亚铁氰化铁。As shown in FIG3 , a monopolar electrically controlled ion exchange reactor series group is formed by three monopolar electrically controlled ion exchange reactors connected in series. All positive electrode plates of the first monopolar electrically controlled ion exchange reactor are connected to the positive electrode of the working power supply, and all negative electrode plates of the third monopolar electrically controlled ion exchange reactor are connected to the negative electrode of the working power supply. The anode material used in the positive electrode plate is a bismuth oxyhalide/polyaniline composite, and the cathode material used in the negative electrode plate is ferric ferrocyanide.
在工作电源电压为30V,初始电流为2A的条件下处理15L循环冷却水,在电场作用下阳电极板开始产生羟基自由基等氧化性物质,去除水中微生物并降解循环冷却水,钙镁离子被捕获到呈负电性的阴电极板上。通电15min后,循环冷却水COD值从50mg/L降到10mg/L,COD去除率达到80%,总硬度(钙硬和镁硬)从12mmol/L降到9mmol/L,能耗为3.6KWh·L-1。When the working power supply voltage is 30V and the initial current is 2A, 15L of circulating cooling water is treated. Under the action of the electric field, the positive electrode plate begins to produce oxidizing substances such as hydroxyl radicals, removes microorganisms in the water and degrades the circulating cooling water. Calcium and magnesium ions are captured on the negatively charged negative electrode plate. After 15 minutes of power on, the COD value of the circulating cooling water drops from 50mg/L to 10mg/L, the COD removal rate reaches 80%, the total hardness (calcium hardness and magnesium hardness) drops from 12mmol/L to 9mmol/L, and the energy consumption is 3.6KWh·L -1 .
实施例2Example 2
如图4所示,由三个单极式电控离子交换反应器并联组成单极式电控离子交换反应器并联群组。其中每个单极式电控离子交换反应器的所有阳电极板与工作电源的正极相连,所有阴电极板与工作电源的负极相连。阳电极板采用的阳极材料为层状双金属氢氧化物/聚吡咯复合物,阴电极板采用的阴极材料为双硫代水杨酸/聚苯胺复合物。As shown in FIG4 , three monopolar electrically controlled ion exchange reactors are connected in parallel to form a monopolar electrically controlled ion exchange reactor parallel group. All positive electrode plates of each monopolar electrically controlled ion exchange reactor are connected to the positive electrode of the working power supply, and all negative electrode plates are connected to the negative electrode of the working power supply. The anode material used in the positive electrode plate is a layered double metal hydroxide/polypyrrole composite, and the cathode material used in the negative electrode plate is a dithiosalicylic acid/polyaniline composite.
在工作电源电压为10V,初始电流为6A的条件下处理15L循环冷却水。在电场作用下阳电极板开始产生羟基自由基、次氯酸根等氧化性物质去除水中微生物并降解循环冷却水,钙镁离子被捕获到呈负电性的阴电极板上。通电10min后,循环冷却水COD值从50mg/L降到8mg/L,COD去除率达到84%,总硬度(钙硬和镁硬)从12mmol/L降到8mmol/L,能耗为2.4KWh·L-1。15L circulating cooling water was treated under the condition of working power supply voltage of 10V and initial current of 6A. Under the action of electric field, the positive electrode plate began to produce hydroxyl radicals, hypochlorite and other oxidizing substances to remove microorganisms in water and degrade circulating cooling water, and calcium and magnesium ions were captured on the negatively charged negative electrode plate. After 10 minutes of power on, the COD value of circulating cooling water dropped from 50mg/L to 8mg/L, the COD removal rate reached 84%, the total hardness (calcium hardness and magnesium hardness) dropped from 12mmol/L to 8mmol/L, and the energy consumption was 2.4KWh·L -1 .
实施例3Example 3
如图5所示,由三个单极式电控离子交换反应器并联组成单极式电控离子交换反应器并联群组,再将两个单极式电控离子交换反应器并联群组串联在工作电路中。其中第一个单极式电控离子交换反应器并联群组的所有阳电极板与工作电源的正极相连,第二个单极式电控离子交换反应器并联群组的所有阴电极板与工作电源的负极相连。阳电极板采用的阳极材料为卤氧化铋,阴电极板采用的阴极材料为亚铁氰化铁。As shown in FIG5 , three monopolar electrically controlled ion exchange reactors are connected in parallel to form a monopolar electrically controlled ion exchange reactor parallel group, and then two monopolar electrically controlled ion exchange reactor parallel groups are connected in series in a working circuit. All positive electrode plates of the first monopolar electrically controlled ion exchange reactor parallel group are connected to the positive electrode of the working power supply, and all negative electrode plates of the second monopolar electrically controlled ion exchange reactor parallel group are connected to the negative electrode of the working power supply. The anode material used in the positive electrode plate is bismuth oxyhalide, and the cathode material used in the negative electrode plate is ferric ferrocyanide.
在工作电源电压为10V,电流为12A的条件下处理15L二级反渗透浓水,在电场作用下阳电极板开始产生羟基自由基等氧化性物质去除水中微生物并降解循环冷却水,水中部分钠、钙、镁离子被捕获到呈负电性的阴电极板上。通电15min后,二级反渗透浓水COD值从383.75mg/L降到71.56mg/L,COD去除率达到81.35%,总硬度(钙硬和镁硬)从0.05mmol/L降到0.02mmol/L,能耗为7.2KWh·L-1。Under the condition of working power supply voltage of 10V and current of 12A, 15L secondary reverse osmosis concentrated water was treated. Under the action of electric field, the positive electrode plate began to produce hydroxyl free radicals and other oxidizing substances to remove microorganisms in water and degrade circulating cooling water. Some sodium, calcium and magnesium ions in water were captured on the negatively charged negative electrode plate. After 15 minutes of power on, the COD value of secondary reverse osmosis concentrated water dropped from 383.75mg/L to 71.56mg/L, the COD removal rate reached 81.35%, the total hardness (calcium hardness and magnesium hardness) dropped from 0.05mmol/L to 0.02mmol/L, and the energy consumption was 7.2KWh·L -1 .
实施例4Example 4
如图6所示,由三个复极式电控离子交换反应器串联组成复极式电控离子交换反应器串联群组。其中第一个复极式电控离子交换反应器的最外侧阳电极板与工作电源的正极相连,第三个复极式电控离子交换反应器的最外侧阴电极板与工作电源的负极相连。阳电极板采用的阳极材料为卤氧化铋/聚苯胺复合物,阴电极板采用的阴极材料为聚二硫代二苯胺复合物。As shown in FIG6 , a bipolar type electrically controlled ion exchange reactor series group is formed by three bipolar type electrically controlled ion exchange reactors connected in series. The outermost anode electrode plate of the first bipolar type electrically controlled ion exchange reactor is connected to the positive electrode of the working power supply, and the outermost cathode electrode plate of the third bipolar type electrically controlled ion exchange reactor is connected to the negative electrode of the working power supply. The anode material used in the anode electrode plate is a bismuth oxyhalide/polyaniline complex, and the cathode material used in the cathode electrode plate is a polydisulfide diphenylamine complex.
在工作电源电压为60V,电流为1A的条件下处理15L苯酚废水,在外加电场和反应器内部产生的感应电场作用下阳电极板开始产生羟基自由基、次氯酸根等氧化性物质去除水中微生物并降解苯酚废水,钙镁离子被捕获到呈负电性的阴电极板上。通电23min后,苯酚废水COD值从400mg/L降到110.52mg/L,COD去除率达到72.37%,总硬度(钙硬和镁硬)从6.06mmol/L降到4.21mmol/L,能耗为5.52KWh·L-1。Under the conditions of 60V working power supply voltage and 1A current, 15L phenol wastewater was treated. Under the action of the external electric field and the induced electric field generated inside the reactor, the positive electrode plate began to produce hydroxyl radicals, hypochlorite and other oxidizing substances to remove microorganisms in the water and degrade phenol wastewater, and calcium and magnesium ions were captured on the negatively charged negative electrode plate. After 23 minutes of power on, the COD value of phenol wastewater dropped from 400mg/L to 110.52mg/L, the COD removal rate reached 72.37%, the total hardness (calcium hardness and magnesium hardness) dropped from 6.06mmol/L to 4.21mmol/L, and the energy consumption was 5.52KWh·L -1 .
实施例5Example 5
如图7所示,由三个复极式电控离子交换反应器并联组成复极式电控离子交换反应器并联群组。其中三个复极式电控离子交换反应器的最外侧阳电极板与工作电源的正极相连,三个复极式电控离子交换反应器的最外侧阴电极板与工作电源的负极相连。阳电极板采用的阳极材料为层状双金属氢氧化物/聚吡咯复合物,阴电极板采用的阴极材料为聚二硫代二苯胺复合物。As shown in FIG7 , three bipolar type electrically controlled ion exchange reactors are connected in parallel to form a bipolar type electrically controlled ion exchange reactor parallel group. The outermost anode plates of the three bipolar type electrically controlled ion exchange reactors are connected to the positive electrode of the working power supply, and the outermost cathode plates of the three bipolar type electrically controlled ion exchange reactors are connected to the negative electrode of the working power supply. The anode material used in the anode plate is a layered double metal hydroxide/polypyrrole composite, and the cathode material used in the cathode plate is a polydiphenyl disulfide composite.
在工作电源电压为20V,初始电流为3A的条件下处理15L苯酚废水,在外加电场和反应器内部产生的感应电场作用下阳电极板开始产生羟基自由基、次氯酸根等氧化性物质去除水中微生物并降解苯酚废水,钙镁离子被捕获到呈负电性的阴电极板上。通电20min后,苯酚废水COD值从400mg/L降到148mg/L,COD去除率达到63%,总硬度(钙硬和镁硬)从6.06mmol/L降到4.85mmol/L,能耗为4.8KWh·L-1。Under the conditions of working power supply voltage of 20V and initial current of 3A, 15L phenol wastewater was treated. Under the action of external electric field and induced electric field generated inside the reactor, the positive electrode plate began to produce hydroxyl free radicals, hypochlorite and other oxidizing substances to remove microorganisms in the water and degrade phenol wastewater, and calcium and magnesium ions were captured on the negatively charged negative electrode plate. After 20 minutes of power on, the COD value of phenol wastewater dropped from 400mg/L to 148mg/L, the COD removal rate reached 63%, the total hardness (calcium hardness and magnesium hardness) dropped from 6.06mmol/L to 4.85mmol/L, and the energy consumption was 4.8KWh·L -1 .
实施例6Example 6
如图8所示,由三个复极式电控离子交换反应器并联组成复极式电控离子交换反应器并联群组,再将两个复极式电控离子交换反应器并联群组串联在工作电路中。其中第一个复极式电控离子交换反应器并联群组的最外侧阳电极板均与工作电源的正极相连,第二个复极式电控离子交换反应器并联群组的最外侧阴电极板均与工作电源的负极相连。阳电极板采用的阳极材料为卤氧化铋/聚吡咯复合物,阴电极板采用的阴极材料为亚铁氰化铁。As shown in FIG8 , three bipolar type electrically controlled ion exchange reactors are connected in parallel to form a bipolar type electrically controlled ion exchange reactor parallel group, and then two bipolar type electrically controlled ion exchange reactor parallel groups are connected in series in a working circuit. The outermost anode electrode plates of the first bipolar type electrically controlled ion exchange reactor parallel group are all connected to the positive electrode of the working power supply, and the outermost cathode electrode plates of the second bipolar type electrically controlled ion exchange reactor parallel group are all connected to the negative electrode of the working power supply. The anode material used for the anode electrode plate is a bismuth oxyhalide/polypyrrole complex, and the cathode material used for the cathode electrode plate is ferric ferrocyanide.
在工作电源电压为40V,电流为3A的条件下处理15L除盐水,在外加电场和反应器内部产生的感应电场作用下阳电极板开始产生羟基自由基等氧化性物质去除水中微生物并降解除盐水,除盐水中钠、钙、镁离子被捕获到呈负电性的阴电极板上。通电5min后,除盐水COD值从25mg/L降到7mg/L,COD去除率达到72%,总硬度(钙硬和镁硬)从8.3mmol/L降到6.48mmol/L,能耗为2.4KWh·L-1。Under the condition of 40V working power supply voltage and 3A current, 15L deionized water was treated. Under the action of external electric field and the induction electric field generated inside the reactor, the positive electrode plate began to produce hydroxyl radicals and other oxidizing substances to remove microorganisms in the water and degrade the deionized water. The sodium, calcium and magnesium ions in the deionized water were captured on the negatively charged negative electrode plate. After 5 minutes of power on, the COD value of the deionized water dropped from 25mg/L to 7mg/L, the COD removal rate reached 72%, the total hardness (calcium hardness and magnesium hardness) dropped from 8.3mmol/L to 6.48mmol/L, and the energy consumption was 2.4KWh·L -1 .
本发明涉及两种电控离子交换反应器及其在工作电路中的连接与组合方式。以电控离子交换技术为基础构建低压大电流单极式电控离子交换反应器和高压小电流复极式电控离子交换反应器,将多个单极式反应器或多个复极式反应器串联连接在工作电路中即为电控离子交换反应器串联群组;将多个单极式反应器或多个复极式反应器并联连接在工作电路中即为电控离子交换反应器并联群组;将多个单极式电控离子交换反应器或多个复极式电控离子交换反应器并联在一起组成反应器群组,再将多个反应器群组串联在一起即为电控离子交换反应器的串并联群组。The present invention relates to two types of electrically controlled ion exchange reactors and their connection and combination methods in a working circuit. Based on the electrically controlled ion exchange technology, a low-voltage, high-current, unipolar electrically controlled ion exchange reactor and a high-voltage, low-current, bipolar electrically controlled ion exchange reactor are constructed. Multiple unipolar reactors or multiple bipolar reactors are connected in series in the working circuit to form an electrically controlled ion exchange reactor series group; multiple unipolar reactors or multiple bipolar reactors are connected in parallel in the working circuit to form an electrically controlled ion exchange reactor parallel group; multiple unipolar electrically controlled ion exchange reactors or multiple bipolar electrically controlled ion exchange reactors are connected in parallel to form a reactor group, and multiple reactor groups are connected in series to form a series-parallel group of electrically controlled ion exchange reactors.
本发明所提及的电控离子交换反应器,可适配不同电压电流范围的电源。本发明中电控离子交换反应器群组之间的组合与连接方式简单易行,可使电控离子交换反应器适用于各种复杂情况的工作电路,极大的拓展了电控离子交换技术的应用范围,在高效降解废水回收离子资源、提高水体水质的同时有效减少了反应器所需能耗,降低了分离目标离子的成本。The electrically controlled ion exchange reactor mentioned in the present invention can be adapted to power supplies with different voltage and current ranges. The combination and connection method between the electrically controlled ion exchange reactor groups in the present invention are simple and easy to implement, which can make the electrically controlled ion exchange reactor applicable to working circuits in various complex situations, greatly expanding the application scope of the electrically controlled ion exchange technology, effectively reducing the energy consumption required by the reactor while efficiently degrading wastewater to recycle ion resources and improve water quality, and reducing the cost of separating target ions.
Claims (2)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202210416104.5A CN114940553B (en) | 2022-04-20 | 2022-04-20 | Monopole type and multipole type electric control ion exchange reactor and group |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202210416104.5A CN114940553B (en) | 2022-04-20 | 2022-04-20 | Monopole type and multipole type electric control ion exchange reactor and group |
Publications (2)
Publication Number | Publication Date |
---|---|
CN114940553A CN114940553A (en) | 2022-08-26 |
CN114940553B true CN114940553B (en) | 2024-06-11 |
Family
ID=82906933
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202210416104.5A Active CN114940553B (en) | 2022-04-20 | 2022-04-20 | Monopole type and multipole type electric control ion exchange reactor and group |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN114940553B (en) |
Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5425858A (en) * | 1994-05-20 | 1995-06-20 | The Regents Of The University Of California | Method and apparatus for capacitive deionization, electrochemical purification, and regeneration of electrodes |
CN1249697A (en) * | 1997-01-28 | 2000-04-05 | 派尼逖克斯公司 | Electrochemically assisted ion exchange |
WO2001078879A1 (en) * | 2000-04-14 | 2001-10-25 | Sampson Richard L | Electrolytic process and apparatus for the controlled oxidation and reduction of inorganic and organic species in aqueous solutions |
CN102256904A (en) * | 2008-12-17 | 2011-11-23 | 通用电气公司 | Ion-exchange device and regeneration method of ion-exchange meterial thereof |
CN105948188A (en) * | 2016-06-29 | 2016-09-21 | 太原理工大学 | Continuous electric-control ionic separation device and process |
CN106315870A (en) * | 2015-06-17 | 2017-01-11 | 中国石油化工股份有限公司 | Industrial circulating cooling water sterilization hardness-removal device and treatment method |
CN113200584A (en) * | 2021-05-18 | 2021-08-03 | 山西宛若科技环保有限公司 | Electrode material and device for electrochemically treating circulating cooling water |
CN113896313A (en) * | 2021-11-03 | 2022-01-07 | 太原理工大学 | A kind of process method for electrochemical treatment of wastewater and co-production of hydrogen |
-
2022
- 2022-04-20 CN CN202210416104.5A patent/CN114940553B/en active Active
Patent Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5425858A (en) * | 1994-05-20 | 1995-06-20 | The Regents Of The University Of California | Method and apparatus for capacitive deionization, electrochemical purification, and regeneration of electrodes |
CN1249697A (en) * | 1997-01-28 | 2000-04-05 | 派尼逖克斯公司 | Electrochemically assisted ion exchange |
WO2001078879A1 (en) * | 2000-04-14 | 2001-10-25 | Sampson Richard L | Electrolytic process and apparatus for the controlled oxidation and reduction of inorganic and organic species in aqueous solutions |
CN102256904A (en) * | 2008-12-17 | 2011-11-23 | 通用电气公司 | Ion-exchange device and regeneration method of ion-exchange meterial thereof |
CN106315870A (en) * | 2015-06-17 | 2017-01-11 | 中国石油化工股份有限公司 | Industrial circulating cooling water sterilization hardness-removal device and treatment method |
CN105948188A (en) * | 2016-06-29 | 2016-09-21 | 太原理工大学 | Continuous electric-control ionic separation device and process |
CN113200584A (en) * | 2021-05-18 | 2021-08-03 | 山西宛若科技环保有限公司 | Electrode material and device for electrochemically treating circulating cooling water |
CN113896313A (en) * | 2021-11-03 | 2022-01-07 | 太原理工大学 | A kind of process method for electrochemical treatment of wastewater and co-production of hydrogen |
Non-Patent Citations (2)
Title |
---|
张招贤等.《钛电极反应工程学》.冶金工业出版社,2009,第41-43页. * |
蛇形流场电控离子交换装置用于选择性提锂;张正等;化工学报;第74卷(第5期);第2022-2033页 * |
Also Published As
Publication number | Publication date |
---|---|
CN114940553A (en) | 2022-08-26 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Ge et al. | Long-term performance of a 200 liter modularized microbial fuel cell system treating municipal wastewater: treatment, energy, and cost | |
Li et al. | Efficacy of Cu (II) as an electron-shuttle mediator for improved bioelectricity generation and Cr (VI) reduction in microbial fuel cells | |
Qin et al. | Nickel ion removal from wastewater using the microbial electrolysis cell | |
Forrestal et al. | Sustainable desalination using a microbial capacitive desalination cell | |
US9469554B2 (en) | Bipolar electrode and supercapacitor desalination device, and methods of manufacture | |
CN102976559B (en) | Anaerobic ammonia oxidation microbe reverse electroosmosis sewage treatment and power generation method and device | |
US20080105551A1 (en) | Supercapacitor desalination devices and methods of making the same | |
CN102603039A (en) | Coupling desalination method and device | |
CN103966626B (en) | A kind of microbiological fuel cell that improves drives microorganism electrolysis cell to reclaim polymetallic method | |
KR20110027710A (en) | Supercapacitor, supercapacitor desalination cell, supercapacitor desalination device and supercapacitor manufacturing method | |
CN111138009B (en) | Water treatment recovery device based on metal-air battery and method thereof | |
CN107954523A (en) | A kind of method of bioelectrochemical system and wastewater treatment | |
KR20170126436A (en) | Coopper based flow batteries | |
KR20170142753A (en) | Method for a renewable energy storage and manufacturing the utilization equipment of mixed redox flow batteries | |
CN102092821A (en) | Application method of high-property activated carbon fibers in treatment of industrial waster water by electrocoagulation | |
CN106830204B (en) | Method and device for degrading pollutants in water by exciting permanganate through electrochemical cathode | |
Tomar et al. | Exploring the potential of metal-doped perovskite-oxides as oxygen reduction catalyst for enhancing the performance of microbial desalination cells | |
CN114940553B (en) | Monopole type and multipole type electric control ion exchange reactor and group | |
CN105540750A (en) | Method for microelectrolysis-pulse electrocoagulation coupled treatment of dye wastewater | |
Huang et al. | Efficient in situ utilization of caustic for sequential recovery and separation of Sn, Fe, and Cu in microbial fuel cells | |
KR20170031099A (en) | Rechargeable battery containing zinc ions | |
CN105060504B (en) | A method for intermittently connecting two MFCs in parallel with no power output to increase voltage to treat heavy metal wastewater | |
JP7578963B2 (en) | Primary Metal Batteries | |
CN111342022A (en) | A carbon-coated Na3MnTi(PO4)3/C composite electrode and its preparation method and application | |
KR102041554B1 (en) | Hybrid power generation system and self supporting hydrogen-electricity complex charge station using reverse electrodialysis power generation appartus with effective hydrogen-electricity generation |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |