WO2015154706A1 - Auxiliary purifying device for water purifier - Google Patents

Auxiliary purifying device for water purifier Download PDF

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Publication number
WO2015154706A1
WO2015154706A1 PCT/CN2015/076239 CN2015076239W WO2015154706A1 WO 2015154706 A1 WO2015154706 A1 WO 2015154706A1 CN 2015076239 W CN2015076239 W CN 2015076239W WO 2015154706 A1 WO2015154706 A1 WO 2015154706A1
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Prior art keywords
water
permeable membrane
water purifier
anode electrode
cathode
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PCT/CN2015/076239
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French (fr)
Chinese (zh)
Inventor
肖志邦
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大连双迪创新科技研究院有限公司
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Publication of WO2015154706A1 publication Critical patent/WO2015154706A1/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis

Definitions

  • the invention relates to a water purifier auxiliary purification device, belonging to the technical field of water electrolysis equipment.
  • the residual chlorine in the water interacts with residual organic matter, which may generate new harmful substances (such as strong carcinogen chloroform, etc.) that are not in the source water.
  • new harmful substances such as strong carcinogen chloroform, etc.
  • the toxic by-products caused by the above residual chlorine cannot be removed by a simple method such as boiling water.
  • the existing water purifiers on the market that deal with the “faucet water” are all physical treatment processes that use media to adsorb or use harmful membranes of various pore sizes to intercept and filter harmful substances in the water. Since the activated carbon-based adsorbent material is easily saturated and the various filter membranes are easily contaminated by bacteria or blocked or damaged by organic matter, the actual situation is not sufficient to purify the pollutants in the water as expected by the theoretical design. However, the physical water treatment process also has the advantage that no toxic by-products are formed. In contrast, although the chemical water treatment process has many advantages such as being cheap, simple, and efficient, it has not been widely used in daily water treatment. The reason is that the chemical water treatment process requires sufficient reaction time.
  • the water purifier In daily water use, the water purifier is only a few seconds from the start-up to the effluent. The residence time of the pollutants in the water purifier is too short to complete the relevant chemical reaction treatment.
  • the chemical water treatment process may be accompanied by certain The toxic side effects.
  • the chemical oxidation reaction process can strongly inactivate bacteria, deeply degrade organic matter, and remove various harmful substances in water, the various strong oxidation factors generated by chemical oxidation are basically non-selective and uncontrollable. Improperly, it is very likely to produce new substances that are not in the source water, which in turn jeopardizes the safety of drinking water. Because of this, in the daily life of drinking water purification treatment, the application of chemical water treatment process can be said to be cautious.
  • the technical problem to be solved by the invention is to propose a water purifier auxiliary device with better sterilizing ability, which can extract water rich in hydrogen and low in oxidation-reduction potential suitable for human drinking.
  • a water purifier auxiliary purification device comprising a water container provided with a water inlet, the water inlet being connected with the water purifier; characterized in that: The housing of the water container is provided with a cathode electrode and an anode electrode, and further comprises an electrolytic power source for supplying power to the cathode electrode and the anode electrode; a water permeable membrane is disposed between the pair of cathode electrodes and the anode electrode, and the water permeability
  • the separator covers the anode electrode, and the distance ⁇ between the water-permeable membrane and the cathode electrode ranges from 0 ⁇ ⁇ ⁇ 10 mm, and the water-permeable membrane of the water-permeable membrane has a water-permeable pore diameter of 2 mm or more and 1 nm or more.
  • the water permeable membrane of the present invention is also called a water permeable membrane, and refers to a water permeability pore diameter ranging from millimeters to nanometers, including various filtration membranes used in daily water treatment, such as ultrafiltration membrane (UF), nanofiltration membrane (NF) and microfiltration. Filter membrane (MF), etc.
  • UF ultrafiltration membrane
  • NF nanofiltration membrane
  • MF Filter membrane
  • the water permeable membrane is covered on the anode electrode, which means that the water permeable membrane and the anode electrode are substantially zero-pitch.
  • the water permeable membrane in the apparatus of the present invention is not a conventionally used ionic membrane, but is a separator which has never been used in the field of water electrolysis, and the inventors have innovatively introduced the permeable membrane into a water electrolysis apparatus as a yin. , a separator between the anode electrodes.
  • the normal reaction to water electrolysis is that the cathode hydrogen evolution (gas), the anodic oxygen evolution (gas), the H + ions tend to the cathode region, and the OH - ions tend to the anode region.
  • a water permeable membrane is disposed between the anode and the cathode, and the electrolytic cell is divided into two reaction spaces of a cathode chamber and an anode chamber.
  • the distance ⁇ between the water-permeable membrane and the cathode electrode is greater than zero, that is, the volume of the cathode chamber is greater than zero, the hydrogen evolution reaction of the cathode proceeds normally, hydrogen gas is generated, and the oxidation-reduction potential of the cathode chamber and the entire container water is decreased.
  • the innumerable micropore storage space of the diaphragm is equivalent to one micro water resistance in parallel in the electrolysis current path of the cathode and the anode electrode. Because the distance ⁇ between the cathode electrode and the membrane is small, the water resistance drop of the cathode chamber can be neglected, and the external electrolytic voltage mainly acts on the water-permeable membrane, and the unit voltage intensity in each micropore is extremely high.
  • the water-permeable pore size of the water-permeable separator is small (micron or nanometer), and the high-energy electrons released from the cathode are dense in the micropores, which is equivalent to decomposing a large discharge electrode (cathode) into an infinite number of small radii of curvature. electrode. Therefore, not only the electrolytic oxidation-reduction reaction of water in the micropores of the water-permeable membrane can be sufficiently performed, and O 2 migrated from the anode to the pores of the membrane is bombarded by high-energy electrons and a strong electric field generates oxygen bubbles, and stimulates a chain reaction to induce a water body. Self-gasification, forming a continuous and stable plasma discharge in the micropores, generating a large number of oxidation factors, and finally diffusing into the container water through the cathode region.
  • the present invention provides an innovative effect of providing a water permeable membrane between the cathode and the anode electrode, and covering the anode with the water permeable membrane and controlling the distance between the water permeable membrane and the cathode electrode, the direct effects of which are:
  • the device of the invention can not only obtain beneficial water with low redox-rich hydrogen-rich potential, but also generate a considerable amount of strong oxidizing factor in water, which has greater sterilization and purification capability than other existing hydrogen-rich water preparation techniques. Upgrade
  • the water-permeable separator can usually be very thin (for example, the thickness of the ultrafiltration membrane can be 0.1mm to 0.5mm). After the separator is added between the anode and the cathode, the spacing between the anode and the cathode can be stably maintained at substantially equal to the isolation.
  • the thickness range of the film, the electrolysis voltage under the same working condition can be very low, even if it is only powered by a 3.7V lithium battery, it can form an operating current of 2 amps or more, which cannot be done by the prior art;
  • the plasma discharge efficient reaction factor and the like make the actual power consumption of the device of the present invention much lower than that of the similar device.
  • When covering the carbon material anode it is also effective to prevent the carbon particles from peeling off and causing a short circuit.
  • the permeable pore size of the water permeable membrane further affects the effect of the apparatus of the present invention in treating water.
  • the water permeable pore size is small, the effect of suppressing the oxygen evolution reaction of the anode is good, and the decrease of the water permeability pore diameter is equivalent to the decrease of the radius of curvature of the discharge electrode, which is also favorable for the plasma discharge; however, the water permeability pore size is too small, and the oxygen is oxidized to the anode.
  • the permeable pore size selection of the membrane is also related to various factors such as the mechanical strength of the membrane.
  • the water permeable membrane is a single layer water permeable membrane or a multilayer water permeable membrane.
  • the single-layer water-permeable membrane is preferably an ultrafiltration membrane or a water-permeable membrane made of a carbonaceous material;
  • the multilayer water-permeable membrane is at least two layers superposed and laminated, wherein a layer of the water-permeable membrane close to the anode electrode is used.
  • the normal hydrogen evolution reaction can be ensured, and the harmful substances in the water are adsorbed to the activated carbon membrane for oxidative degradation, and the oxidizing substances in the water are not inhibited too much, and the biological indicators are prevented from being deteriorated. It is especially suitable for the treatment of domestic water for the purpose of “drinking”. Further, if the water permeable membrane is at least two layers superposed and laminated, and wherein one of the water permeable membranes adjacent to the anode electrode has conductivity and a micron-sized pore diameter (for example, made of conductive ceramic or activated carbon fiber), Will bring further changes as follows:
  • the inhibition of oxygen evolution on the anode can be enhanced, and on the other hand, the pollutants in the source water can be adsorbed in the pores of the conductive ceramic or activated carbon fiber, and subjected to direct oxidation and indirect oxidation of the anode. Degraded by deep degradation.
  • the second technical solution of the present invention is that the specific coverage of the water permeable membrane and the anode electrode may cover the entire surface of the anode electrode or a part of the surface covering the anode electrode; In the case of a face, it is preferable to cover the surface (also the main reaction surface) of the anode electrode on the side opposite to the cathode electrode.
  • the third technical solution of the present invention is as follows: the cathode electrode is provided with a first through hole, and the first through hole has a diameter of 1 mm or more.
  • the water permeable membrane is provided with a second through hole, and the second through hole has a diameter larger than 2 mm.
  • the second through hole is formed in the water permeable membrane, which is substantially equivalent to generating a small area of the membrane-free electrolysis, or equivalent to introducing a conventional membrane-free electrolysis reaction, and the water treatment effect of the device of the present invention can be appropriately changed. For example, the pH of the water is adjusted.
  • the second through hole is different from the water permeable hole of the water permeable membrane in that the water permeable hole is inherent to the purchased diaphragm itself, and the second through hole is separately fabricated.
  • the above technical solution of the present invention is perfect: when the water container of the device of the present invention is made of a metal material (for example, stainless steel), the housing of the water container can be directly used as a cathode electrode.
  • a metal material for example, stainless steel
  • the above technical solution of the present invention is perfected in that the water inlet of the water container is connected to the water purifier through the sewage outlet of the external water purifier.
  • the water inlet of the water container is connected to the water purifier through an inlet pipe or an outlet pipe connected to the water purifier.
  • the electrolysis power source is a high-frequency narrow pulse width DC pulse power source or an alternating pulse power source whose forward voltage level is greater than a reverse voltage level.
  • FIG. 1 is a schematic structural view of a water purifier auxiliary purification device according to a first embodiment of the present invention.
  • FIG. 2 is a schematic structural view of a water purifier auxiliary purification device according to a second embodiment of the present invention.
  • FIG. 3 is a schematic structural view of a water purifier auxiliary purification device according to a third embodiment of the present invention.
  • FIG. 4 is a schematic view showing the structure of a positive electrode and a negative electrode and a water permeable membrane in the fourth embodiment of the present invention.
  • Fig. 5 is a schematic view showing the structure of a positive electrode and a negative electrode and a water permeable membrane according to a fifth embodiment of the present invention.
  • Fig. 6 is a schematic view showing the structure of a positive electrode and a negative electrode and a water permeable membrane in a sixth embodiment of the present invention.
  • the water purifier auxiliary purifying device of this embodiment is shown in Fig. 1 (including the water container 1 provided with the water inlet 9, the water inlet 9 of the water container 1 is connected to the sewage outlet 6 of the existing water purifier 7, and the water purifier 7
  • the inlet pipe 10-1 and the outlet pipe 10-2 are provided.
  • the housing of the water container 1 is provided with a cathode electrode 2 and an anode electrode 3, and a cathode electrode 2 and an anode electrode 3
  • a water permeable membrane 5 is disposed between the water permeable membrane 5 and the water permeable membrane 5 covering the entire surface of the anode electrode 3.
  • the water-permeable membrane 5 of the present embodiment employs a single-layer PVDF ultrafiltration membrane having an average water permeability of 0.03 ⁇ m and a thickness of 0.1 mm.
  • the ultrafiltration membrane of the present embodiment may also adopt a water permeable filter membrane of other materials, and the average water permeability pore diameter may be between 0.1 and 0.05 micrometers.
  • the cathode electrode 2 of the present embodiment is an inert electrode made of a titanium-based platinum group oxide (coating thickness: 0.8 mm), and the anode electrode 3 is made of a carbonaceous material such as graphite or activated carbon, and the anode and the cathode are both wafers. Shape, no holes on the surface.
  • the cathode electrode 2 and the anode electrode 3 are powered by a DC electrolysis power source 4, and the electrolysis power source 4 is an alternating-current DC pulse power source with a high-level narrow pulse width regulation voltage of 24 volts, and the forward pulse level is greater than the reverse pulse. Level.
  • the water purifier auxiliary purifying device of the embodiment can form a large amount of ultra-micro bubbles mainly composed of hydrogen in the water, and the ultra-micro hydrogen bubbles float up to the water purifier 7 to wash the filter film in the existing water purifier 7 ( Or the outer surface of the activated carbon) 8 prevents the outer surface of the filter membrane (or activated carbon) 8 from scaling, reduces the concentration polarization, and removes the contaminants in the source water by flocculation and precipitation.
  • the strong oxidizing factor produced by the device sterilizes the water and prevents premature saturation of the activated carbon, which greatly prolongs the replacement cycle of the activated carbon.
  • the water purifier auxiliary purifying device of the embodiment is used for docking with a commercially available conventional ultrafiltration water purifier having a nominal flow rate of 380 liters/hour (the water inlet sealing sleeve of the water container 1 is connected to the water purifier of the water purifier). Port 6) was subjected to a water electrolysis experiment.
  • the bubble from the water is zero - the maximum relative bubble content in the experiment is divided into 0 to 5 grades;
  • the color is the yellowest - the corresponding oxidation factor in the water is the most, set to 5;
  • the degree of color change from colorless to color yellow is set to 1, 2, 3, and 4 levels.
  • the water purifier auxiliary purifying apparatus of the present embodiment is an improvement on the basis of the first embodiment.
  • the variation with the first embodiment is: 1) the water receiving container 1 is disposed in the water inlet pipe of the water purifier 7. At 10-1, such a large amount of hydrogen-based ultra-microbubbles and strong oxidizing factors formed in the water purifier auxiliary purification device can enter the water purifier under the action of water pressure, and also play the role of sterilization and cleaning.
  • the water container 1 can also be connected in series with the inlet pipe 10-1 (the water outlet is opened in the water container 1). Further, the water container 1 can also be connected or connected to the outlet pipe 10-2. Pick up.
  • the anode electrode 3 was changed to an inert electrode of a titanium-based platinum group oxide (coating thickness: 0.8 mm).
  • the distance ⁇ between the water permeable membrane 5 and the cathode electrode 2 is 3 mm.
  • a comparative experiment is performed to adjust the coverage of the anode 3 by the water permeable membrane 5: in the first mode, as shown in FIG. 2, the water permeable membrane 5 completely covers the entire surface of the anode electrode 3; The diaphragm 5 covers only the surface of the anode electrode 3 facing the 2/3 side of the cathode electrode 2 (not shown), and the other structural parameters are unchanged in both modes.
  • the experimental conditions were also the same as in the first embodiment.
  • the two kinds of coverage methods of the permeable membrane 5 for the anode electrode 3 were tested separately, and the test results are shown in Table 2 below:
  • the hydrogen content in the water and bubbles increases, the oxidation-reduction potential decreases, the alkalinity strengthens, and the oxidation factor decreases; on the contrary, the oxidation factor in the water increases.
  • the water purifier auxiliary purifying device of this embodiment is an improvement on the basis of the first embodiment.
  • the variation with the first embodiment is: 1) the water container 1 is made of stainless steel and serves as a cathode electrode. 2; 2) The distance ⁇ between the water permeable membrane 5 and the cathode electrode 2 is 2 mm.
  • the water purifier auxiliary purification device of the present embodiment was subjected to a water electrolysis experiment, and the electrolysis time was 20 minutes.
  • Other experimental conditions and detection methods were the same as those in the first embodiment.
  • the experimental results are shown in Table 3 below:
  • the water purifier auxiliary purifying apparatus of this embodiment is an improvement based on the first embodiment.
  • the variation with the first embodiment is: 1) the cathode electrode 2 is uniformly provided with 24 diameters of ⁇ 1 mm. a through hole; 2) the distance ⁇ between the water permeable membrane 5 and the cathode electrode 2 is 4 mm; 3) the anode electrode 3 is changed to an inert electrode coated with a platinum group oxide (coating thickness: 0.8 mm); 4) permeable to water Part of the surface of the diaphragm 5 covering the anode electrode 3 The face (the entire surface of the anode electrode 3 facing the side of the cathode electrode 2).
  • the water purifier auxiliary purification device of the present embodiment was subjected to a water electrolysis experiment, and the electrolysis time was 20 minutes.
  • Other experimental conditions and detection methods were the same as those in the first embodiment.
  • the experimental results are shown in Table 3 below:
  • the water purifier auxiliary purification device of the present embodiment is an improvement on the basis of the fourth embodiment, and the variation with the first embodiment is: 1) as shown in FIG. 5, the water permeable membrane 5 is made of an activated carbon fiber membrane (felt) 5- 1 and a super-filtration membrane 5-2 superposed and laminated to form a two-layer water-permeable membrane, the activated carbon fiber membrane 5-1 is close to the anode electrode 3 (toward the anode electrode 3) and covers the entire surface of the anode electrode 3, facing the cathode electrode 2 ( The ultrafiltration membrane 5-2 facing away from the anode electrode 3) covers a part of the surface of the anode electrode 3 (the entire surface of the anode electrode 3 toward the side of the cathode electrode 2), and both ends of the ultrafiltration membrane 5-2 slightly exceed the anode electrode; 2) The distance ⁇ between the water permeable membrane 5 and the cathode electrode 2 is 5 mm; 3) the anode electrode 3 is changed to the same inertness as the
  • the water purifier auxiliary purification device of the present embodiment was subjected to a water electrolysis experiment, and the electrolysis time was 20 minutes.
  • the other experimental conditions were the same as those in the first embodiment.
  • the experimental results are shown in Table 4 below:
  • the water purifying device auxiliary purifying device of the present embodiment has a water permeability diaphragm 5 which is a two-layer water permeable material formed by superimposing an activated carbon fiber membrane (fel) 5-1 and an ultrafiltration membrane 5-2.
  • the separator can therefore adsorb a large amount of oxidizing factors in water, thereby making water which is more suitable for human consumption and rich in hydrogen and low in oxidation-reduction potential.
  • the water purifier auxiliary purification device of the present embodiment is an improvement on the basis of the fifth embodiment, and the variation of the fifth embodiment is: 1) the activated carbon fiber membrane (felt) 5-1 is replaced by a water permeable membrane made of a conductive ceramic; 2) As shown in Fig. 6, the ultrafiltration membrane 5-2 facing the cathode electrode 2 (reverse from the anode electrode 3) covers the three side surfaces of the anode electrode 3; 3) the distance ⁇ between the water permeable membrane and the cathode electrode 2 is 9 mm .
  • the water purifier auxiliary purification device of the present invention is not limited to the specific technical solutions described in the above embodiments, such as: 1) the anode electrode 3 may be an inert electrode of other materials; 2) the distance ⁇ between the water permeable membrane 5 and the cathode electrode 2 It may be any spacing of 0 ⁇ 10mm, such as 7mm, 8mm or 10mm, etc.; 3) The water permeable membrane 5 may also be a stack of three or more layers of different materials; 4) the cathode electrode 2 and the anode electrode 3 The shape may also be various shapes including a circle and a square; 5) The technical solutions of the above-described various embodiments of the present invention may be cross-combined with each other to form a new technical solution; All technical solutions formed by equivalent replacement are the scope of protection required by the present invention.

Abstract

Disclosed is an auxiliary purifying device for a water purifier, which belongs to the technical field of electrolysis devices. The device comprises a water-holding container (1) provided with a water inlet (9), wherein the water inlet (9) is in communication with a water purifier (7); the water holding container (1), in the housing, is provided with a cathode (2) and an anode (3), and also comprises an electrolysis power source (4) which supplies power for the cathode (2) and the anode (3); a water permeable membrane (5) is arranged between the paired cathode (2) and anode (3); the anode (3) is covered with the water permeable membrane (5); the distance δ between the water permeable membrane (5) and the cathode (2) is in the range of 0 ≤δ ≤10.

Description

净水器辅助净化装置Water purifier auxiliary purification device 技术领域Technical field
本发明涉及一种净水器辅助净化装置,属于水电解设备技术领域。The invention relates to a water purifier auxiliary purification device, belonging to the technical field of water electrolysis equipment.
背景技术Background technique
由市政提供的民众日常生活用水,即使自来水厂出厂水质安全指标基本达标,输送到民众用水终端的“龙头水”,由于下述原因,也己经成为一种(特殊的)微污染水:The daily water supply of the people provided by the municipal government, even if the water quality safety indicators of the waterworks are basically up to standard, the “faucet water” delivered to the public water terminal has become a (special) micro-polluted water for the following reasons:
1)水环境污染日益恶化,现有自来水厂处理工艺陈旧,出厂水质已经难以达标(特别是在突发饮用水卫生事件的情况下);1) The water environment pollution is deteriorating, the existing water treatment plant is outdated, and the water quality of the factory has been difficult to meet the standards (especially in the case of sudden drinking water hygiene incidents);
2)输水管网系统带来的二次污染;2) secondary pollution caused by the water distribution network system;
3)水中余氯与残留有机物相互作用,可能生成源水中没有的新的有害物质(例如强致癌物三氯甲烷,等等)。尤其是,上述余氯导致的毒副产物,用诸如把水烧开的简单方法并不能去除。3) The residual chlorine in the water interacts with residual organic matter, which may generate new harmful substances (such as strong carcinogen chloroform, etc.) that are not in the source water. In particular, the toxic by-products caused by the above residual chlorine cannot be removed by a simple method such as boiling water.
因此,为保障饮水的绝对安全,有必要对龙头水加以再净化处理。Therefore, in order to ensure the absolute safety of drinking water, it is necessary to re-purify the faucet water.
市场上现有以“龙头水”为处理对象的净水器,均属于以介质吸附或采用各种孔径的过滤膜将水中的有害物加以拦截滤除的物理方式处理工艺。由于活性炭类吸附材料很容易饱和失效,而各种过滤膜又很容易被细菌污染或有机物阻塞或破损,因此实际情况是并不能如理论设计所期望那样作到对水中污染物的充分净化。但物理方式水处理工艺也有一个优点,就是不会生成毒副产物。相比而言,化学水处理工艺虽然具有廉价简单高效等诸多优点,但迄今尚未见有在日常生活用水处理场合广泛应用。究其原因,一是化学水处理工艺需要足够的反应时间。而在日常生活用水场合,净水器从开机到出水仅仅数秒钟,污染物在净水器中停留时间太短,根本来不及完成相关化学反应处理;其二是,化学水处理工艺有可能伴随一定的毒副作用。例如,尽管化学氧化反应工艺可强效灭活细菌,深度降解有机物,去除水中的各种有害物质,但化学氧化法所生成的各类强氧化因子基本是无选择性、不可控的,若处理不当极可能产生源水中没有的新物质,反而危及饮水安全。正因为如此,在民众日常生活饮用水净化处理场合,对于化学水处理工艺的应用可以说是慎之又慎。然而,在水环境前所未有严重污染、传统物理净水器已力不从心的今天,重新审视关注化学水处理在生活饮用水净化处理应用的可能性,创新开发一种既能 高效除去水中污染物又无毒副产物、高度安全的化学氧化水质净化方法与装置,具有十分重要的现实意义。The existing water purifiers on the market that deal with the “faucet water” are all physical treatment processes that use media to adsorb or use harmful membranes of various pore sizes to intercept and filter harmful substances in the water. Since the activated carbon-based adsorbent material is easily saturated and the various filter membranes are easily contaminated by bacteria or blocked or damaged by organic matter, the actual situation is not sufficient to purify the pollutants in the water as expected by the theoretical design. However, the physical water treatment process also has the advantage that no toxic by-products are formed. In contrast, although the chemical water treatment process has many advantages such as being cheap, simple, and efficient, it has not been widely used in daily water treatment. The reason is that the chemical water treatment process requires sufficient reaction time. In daily water use, the water purifier is only a few seconds from the start-up to the effluent. The residence time of the pollutants in the water purifier is too short to complete the relevant chemical reaction treatment. Second, the chemical water treatment process may be accompanied by certain The toxic side effects. For example, although the chemical oxidation reaction process can strongly inactivate bacteria, deeply degrade organic matter, and remove various harmful substances in water, the various strong oxidation factors generated by chemical oxidation are basically non-selective and uncontrollable. Improperly, it is very likely to produce new substances that are not in the source water, which in turn jeopardizes the safety of drinking water. Because of this, in the daily life of drinking water purification treatment, the application of chemical water treatment process can be said to be cautious. However, in the unprecedented water pollution environment, the traditional physical water purifier has been unable to do so today, re-examine the possibility of focusing on the application of chemical water treatment in drinking water purification treatment, and innovatively develop a It is of great practical significance to efficiently remove pollutants from water and non-toxic by-products and highly safe chemical oxidation water purification methods and devices.
发明内容Summary of the invention
本发明要解决的技术问题是:提出一种具有较好杀菌能力的净水器辅助装置,该装置可以制取出适宜人饮用的富含氢且氧化还原电位低的水。The technical problem to be solved by the invention is to propose a water purifier auxiliary device with better sterilizing ability, which can extract water rich in hydrogen and low in oxidation-reduction potential suitable for human drinking.
为了解决上述技术问题,本发明提出的技术方案是:一种净水器辅助净化装置,包括设有进水口的盛水容器,所述进水口与净水器连通;其特征在于:所述盛水容器的壳体内设有阴电极和阳电极,还包括用于对所述阴电极和阳电极供电的电解电源;成对的阴电极和阳电极之间设有透水性隔膜,所述透水性隔膜覆盖在阳电极上,所述透水性隔膜与阴电极的间距δ范围是0≤δ≤10毫米,所述透水性隔膜的透水孔径小于等于2毫米且大于等于1纳米。In order to solve the above technical problem, the technical solution proposed by the present invention is: a water purifier auxiliary purification device, comprising a water container provided with a water inlet, the water inlet being connected with the water purifier; characterized in that: The housing of the water container is provided with a cathode electrode and an anode electrode, and further comprises an electrolytic power source for supplying power to the cathode electrode and the anode electrode; a water permeable membrane is disposed between the pair of cathode electrodes and the anode electrode, and the water permeability The separator covers the anode electrode, and the distance δ between the water-permeable membrane and the cathode electrode ranges from 0 ≤ δ ≤ 10 mm, and the water-permeable membrane of the water-permeable membrane has a water-permeable pore diameter of 2 mm or more and 1 nm or more.
本发明的透水性隔膜也叫透水膜,是指透水孔径从毫米级到纳米级,包括日常水处理使用的各种过滤膜,如:超滤膜(UF)、纳滤膜(NF)和微滤膜(MF)等。The water permeable membrane of the present invention is also called a water permeable membrane, and refers to a water permeability pore diameter ranging from millimeters to nanometers, including various filtration membranes used in daily water treatment, such as ultrafiltration membrane (UF), nanofiltration membrane (NF) and microfiltration. Filter membrane (MF), etc.
上述技术方案中所述透水性隔膜覆盖在阳电极上,是指透水性隔膜与阳电极之间基本是零间距。In the above technical solution, the water permeable membrane is covered on the anode electrode, which means that the water permeable membrane and the anode electrode are substantially zero-pitch.
上述本发明申请公开的技术方案工作机理陈述如下:The working mechanism of the technical solution disclosed in the above application of the present invention is as follows:
本发明装置中所述透水性隔膜并非常规采用的离子膜,而是在水电解领域中从未用过的一种隔离膜,本发明人创新地将该透水性隔膜引入水电解装置中作为阴、阳电极间的隔离膜。The water permeable membrane in the apparatus of the present invention is not a conventionally used ionic membrane, but is a separator which has never been used in the field of water electrolysis, and the inventors have innovatively introduced the permeable membrane into a water electrolysis apparatus as a yin. , a separator between the anode electrodes.
对水电解的正常反应是,阴极析氢(气)、阳极析氧(气),H+离子趋向阴极区域,而OH-离子则趋向阳极区域。本发明装置中,阴、阳电极之间设置有透水性隔膜,将电解池分割为阴极室和阳极室两个反应空间。The normal reaction to water electrolysis is that the cathode hydrogen evolution (gas), the anodic oxygen evolution (gas), the H + ions tend to the cathode region, and the OH - ions tend to the anode region. In the device of the present invention, a water permeable membrane is disposed between the anode and the cathode, and the electrolytic cell is divided into two reaction spaces of a cathode chamber and an anode chamber.
1)透水性隔膜与阴电极的间距δ大于零,即阴极室容积大于零,阴极析氢反应正常进行,生成氢气,阴极室、进而整个容器水的氧化还原电位下降1) The distance δ between the water-permeable membrane and the cathode electrode is greater than zero, that is, the volume of the cathode chamber is greater than zero, the hydrogen evolution reaction of the cathode proceeds normally, hydrogen gas is generated, and the oxidation-reduction potential of the cathode chamber and the entire container water is decreased.
H++e-→H H+H→H2↑H+e-→H- H + +e - →H H+H→H 2 ↑H+e - →H -
2)阳极室析氧反应为2) The oxygen evolution reaction in the anode chamber is
①从水里迁移到阳极表面的液相传质吸附1 liquid phase mass transfer adsorption from water to anode surface
OH-(水)→OH-(阳极表面)OH - (water) → OH - (anode surface)
②在阳极表面发生的反应2 reactions occurring on the surface of the anode
OH-→OH+e- OH - → OH+e -
OH+OH→O+H2OOH+OH→O+H 2 O
OH+OH-→O+e-+H2OOH+OH - →O+e - +H 2 O
O+O→O2O+O→O 2
由于透水性隔膜覆盖在阳电极上,相当于阳极室容积=0,阳极析氧反应因隔膜对阳极的覆盖受到干扰。在阳极脱附转化反应生成的H2O以及在阳极析出的氧气,由于无处释放,只能在克服了透水性隔离膜的透水水阻后,穿过隔膜中无数微孔通道向阴极室迁移。Since the water permeable membrane covers the anode electrode, which corresponds to the anode chamber volume=0, the anode oxygen evolution reaction is disturbed by the membrane covering the anode. The H 2 O generated at the anode desorption reaction and the oxygen evolved at the anode, due to nowhere to be released, can only migrate through the numerous microporous channels in the membrane to the cathode chamber after overcoming the water permeability of the water permeable separator. .
3)本发明装置中,隔膜的无数微孔蓄水空间,等效于阴、阳电极电解电流通路中相互并联的一个个微小水电阻。因阴电极与膜之间间距δ很小,阴极室水电阻压降可以忽略不计,外加电解电压主要作用在透水性隔膜上,每个微孔中单位电压强度极高。再加上透水性隔离膜的透水孔径很小(微米级乃至纳米级),从阴极释放的高能电子在微孔中密集,相当于将一个大的放电电极(阴极)分解为无数个小曲率半径电极。因此,不仅在透水性隔膜微孔中对水电解氧化还原反应可充分进行,从阳极迁移到膜孔内的O2受高能电子的轰击及强电场作用生成氧气泡,并激发连锁反应,诱发水体自身气化,在微孔内形成连续稳定的等离子放电,生成大量氧化因子,最终通过阴极区域扩散到容器水中。3) In the device of the present invention, the innumerable micropore storage space of the diaphragm is equivalent to one micro water resistance in parallel in the electrolysis current path of the cathode and the anode electrode. Because the distance δ between the cathode electrode and the membrane is small, the water resistance drop of the cathode chamber can be neglected, and the external electrolytic voltage mainly acts on the water-permeable membrane, and the unit voltage intensity in each micropore is extremely high. In addition, the water-permeable pore size of the water-permeable separator is small (micron or nanometer), and the high-energy electrons released from the cathode are dense in the micropores, which is equivalent to decomposing a large discharge electrode (cathode) into an infinite number of small radii of curvature. electrode. Therefore, not only the electrolytic oxidation-reduction reaction of water in the micropores of the water-permeable membrane can be sufficiently performed, and O 2 migrated from the anode to the pores of the membrane is bombarded by high-energy electrons and a strong electric field generates oxygen bubbles, and stimulates a chain reaction to induce a water body. Self-gasification, forming a continuous and stable plasma discharge in the micropores, generating a large number of oxidation factors, and finally diffusing into the container water through the cathode region.
综合上述反应过程可知,本发明通过创新的在阴、阳电极之间设设置透水性隔膜,并将该透水性隔膜覆盖阳极以及控制透水性隔膜与阴电极的间距,带来的直接效果是:In summary of the above reaction process, the present invention provides an innovative effect of providing a water permeable membrane between the cathode and the anode electrode, and covering the anode with the water permeable membrane and controlling the distance between the water permeable membrane and the cathode electrode, the direct effects of which are:
1)本发明装置不仅可制取得到氧化还原电位低富含氢的有益健康水,同时在水中还生成相当多的强氧化因子,较之其它现有富氢水制取技术,杀菌净化能力大大提升;1) The device of the invention can not only obtain beneficial water with low redox-rich hydrogen-rich potential, but also generate a considerable amount of strong oxidizing factor in water, which has greater sterilization and purification capability than other existing hydrogen-rich water preparation techniques. Upgrade
2)透水性隔离膜通常可以很薄(例如超滤膜的厚度可做到0.1mm~0.5mm),在阴阳极之间加入隔离膜后,可以将阴阳电极之间间距稳定保持在基本等于隔离膜的厚度范围,同等工況下的电解电压可以很低,甚至仅仅以一块3.7V锂电池供电,可以形成2安培以上的工作电流,现有技术是无法做到的;加上膜中发生的等离子放电高效反应因素等,使得本发明装置的实际功耗较之同类装置大大降低。当覆盖碳材质阳极时,还可有效防止碳颗粒剥落造成短路。2) The water-permeable separator can usually be very thin (for example, the thickness of the ultrafiltration membrane can be 0.1mm to 0.5mm). After the separator is added between the anode and the cathode, the spacing between the anode and the cathode can be stably maintained at substantially equal to the isolation. The thickness range of the film, the electrolysis voltage under the same working condition can be very low, even if it is only powered by a 3.7V lithium battery, it can form an operating current of 2 amps or more, which cannot be done by the prior art; The plasma discharge efficient reaction factor and the like make the actual power consumption of the device of the present invention much lower than that of the similar device. When covering the carbon material anode, it is also effective to prevent the carbon particles from peeling off and causing a short circuit.
3)通过对隔离膜与电极性状等的适当选择及调整,可以控制水中氧化因子的生成,以适应不同场合的饮用水需求。 3) By properly selecting and adjusting the separator and electrode properties, the formation of oxidation factors in water can be controlled to meet the needs of drinking water in different occasions.
本发明装置中,透水性隔膜的透水孔径大小进一步影响本发明装置处理水的效果。透水孔径小,则对阳极析氧气化反应的抑制效果好,而且透水孔径减小相当于放电电极的曲率半径减小,也有利于等离子放电的进行;但是透水孔径过小,对阳极析氧气化反应抑制过度,相当于大幅度提高了阳极析氧电位,在外加电解电压不变的情况下,阴阳极之间的电解电流大大下降,反而导致本发明装置中所期望的各种反应不能进行。此外,膜的透水孔径选择还关联到膜的机械强度等多种因素。经实践中反复试验,根据不同的饮用水需求综合考虑,本发明装置选择透水膜的孔径范围从2毫米到1纳米之间,涵盖日常生活水处理常用的超滤膜、纳滤膜和微滤膜。In the apparatus of the present invention, the permeable pore size of the water permeable membrane further affects the effect of the apparatus of the present invention in treating water. When the water permeable pore size is small, the effect of suppressing the oxygen evolution reaction of the anode is good, and the decrease of the water permeability pore diameter is equivalent to the decrease of the radius of curvature of the discharge electrode, which is also favorable for the plasma discharge; however, the water permeability pore size is too small, and the oxygen is oxidized to the anode. Excessive reaction suppression corresponds to a substantial increase in the oxygen evolution potential of the anode, and the electrolytic current between the anode and the cathode is greatly lowered in the case where the applied electrolytic voltage is constant, which in turn causes various reactions desired in the apparatus of the present invention to be impossible. In addition, the permeable pore size selection of the membrane is also related to various factors such as the mechanical strength of the membrane. Through trial and error in practice, according to different drinking water needs, the device has a pore size ranging from 2 mm to 1 nm, covering ultrafiltration membranes, nanofiltration membranes and microfiltration commonly used in daily water treatment. membrane.
上述本发明技术方案的完善一是:所述透水性隔膜是单层透水性隔膜或者是多层透水性隔膜。其中,单层透水性隔膜优选超滤膜或采用碳质材料制成的透水性隔膜;多层透水性隔膜是叠加复合而成的至少二层,其中靠近阳电极的一层透水性隔膜是采用碳质材料制成的透水性隔膜;当所述透水性隔膜采用碳质材料制成的单层透水性隔膜时,阳电极可优选含有碳质材料的阳电极。One improvement of the above technical solution of the present invention is that the water permeable membrane is a single layer water permeable membrane or a multilayer water permeable membrane. Wherein, the single-layer water-permeable membrane is preferably an ultrafiltration membrane or a water-permeable membrane made of a carbonaceous material; the multilayer water-permeable membrane is at least two layers superposed and laminated, wherein a layer of the water-permeable membrane close to the anode electrode is used. A water permeable membrane made of a carbonaceous material; when the water permeable membrane is a single-layer water permeable membrane made of a carbonaceous material, the anode electrode may preferably contain an anode electrode of a carbonaceous material.
通过上述对本发明技术方案的完善一,可以在保证正常析氢反应的同时,又将水中有害物质吸附到活性炭膜中进行氧化降解,而且抑制水中的氧化物质不至于太多,防止生物指标变差,尤其适合对以“饮”为目的的生活水进行处理。进一步地,倘若透水性隔膜是叠加复合而成的至少二层,且其中靠近阳电极的一层透水性隔膜具有导电性和微米级孔径(例如是由导电性陶瓷或活性炭纤维制成),则将带来进一步的下述变化:Through the above improvement of the technical scheme of the present invention, the normal hydrogen evolution reaction can be ensured, and the harmful substances in the water are adsorbed to the activated carbon membrane for oxidative degradation, and the oxidizing substances in the water are not inhibited too much, and the biological indicators are prevented from being deteriorated. It is especially suitable for the treatment of domestic water for the purpose of “drinking”. Further, if the water permeable membrane is at least two layers superposed and laminated, and wherein one of the water permeable membranes adjacent to the anode electrode has conductivity and a micron-sized pore diameter (for example, made of conductive ceramic or activated carbon fiber), Will bring further changes as follows:
1)因为具有良好导电性,其本身产生的电压降很小,因此保证了水中等离子放电仍主要在靠向阴极一侧的非导电的、透水孔径更小的透水膜(一般选择为超滤膜)中进行。1) Because of its good electrical conductivity, the voltage drop generated by itself is small, thus ensuring that the plasma discharge in water is still mainly on the non-conductive, water-permeable pore-permeable membrane on the cathode side (generally selected as ultrafiltration membrane) In progress.
2)由于介质的多孔性,一方面可以强化对阳极析氧的抑制,另一方面可以将源水中的污染物吸附在导电性陶瓷或活性炭纤维的孔隙里,受到阳极的直接氧化和间接氧化作用而深度降解去除。2) Due to the porosity of the medium, on the one hand, the inhibition of oxygen evolution on the anode can be enhanced, and on the other hand, the pollutants in the source water can be adsorbed in the pores of the conductive ceramic or activated carbon fiber, and subjected to direct oxidation and indirect oxidation of the anode. Degraded by deep degradation.
3)对自来水中残留余氯有很好吸附,并在阳极作用下转化为无害氯离子,大大降低了水中残留余氯可能生成毒副产物的危险。3) The residual chlorine in the tap water is well adsorbed and converted into harmless chloride ions under the action of the anode, which greatly reduces the risk of residual by-products in the water.
上述本发明技术方案的完善二是:透水性隔膜与阳电极的具体覆盖可以是覆盖阳电极的全部表面,也可以是覆盖阳电极的部分表面;当覆盖阳电极的部分表 面时,优选覆盖阳电极相对阴电极一侧的表面(也是主要反应面)。The second technical solution of the present invention is that the specific coverage of the water permeable membrane and the anode electrode may cover the entire surface of the anode electrode or a part of the surface covering the anode electrode; In the case of a face, it is preferable to cover the surface (also the main reaction surface) of the anode electrode on the side opposite to the cathode electrode.
上述本发明技术方案完善三是:所述阴电极上开有第一通孔,所述第一通孔的孔径大于等于1毫米。通过这样的改进,可以有利于阴极反应更充分进行,并将阴电极与隔离膜之间区域产生的氢气泡更好导出。The third technical solution of the present invention is as follows: the cathode electrode is provided with a first through hole, and the first through hole has a diameter of 1 mm or more. By such an improvement, it is possible to facilitate the cathode reaction to proceed more fully, and to better derive the hydrogen bubbles generated in the region between the cathode electrode and the separator.
上述本发明技术方案完善四是:所述透水性隔膜上开有第二通孔,所述第二通孔的孔径大于2毫米。在透水性隔膜上开有第二通孔,实质等效于产生一个个的无膜电解小区域,或者说相当于引入叠加了常规无膜电解反应,可以适当改变本发明装置的水处理效果,例如调整水的pH值等。第二通孔与透水性隔膜的透水孔区别在于:透水孔是采购的隔膜自身固有的,第二通孔则是另外单独制作的。The above technical solution of the present invention is perfect: the water permeable membrane is provided with a second through hole, and the second through hole has a diameter larger than 2 mm. The second through hole is formed in the water permeable membrane, which is substantially equivalent to generating a small area of the membrane-free electrolysis, or equivalent to introducing a conventional membrane-free electrolysis reaction, and the water treatment effect of the device of the present invention can be appropriately changed. For example, the pH of the water is adjusted. The second through hole is different from the water permeable hole of the water permeable membrane in that the water permeable hole is inherent to the purchased diaphragm itself, and the second through hole is separately fabricated.
上述本发明技术方案完善五是:当本发明装置盛水容器为金属材质(例如不锈钢)时,可直接以盛水容器的壳体作为阴电极。The above technical solution of the present invention is perfect: when the water container of the device of the present invention is made of a metal material (for example, stainless steel), the housing of the water container can be directly used as a cathode electrode.
上述本发明技术方案完善六是:所述盛水容器的进水口通过外接净水器的排污口与净水器连通。The above technical solution of the present invention is perfected in that the water inlet of the water container is connected to the water purifier through the sewage outlet of the external water purifier.
上述本发明技术方案完善七是:所述盛水容器的进水口通过连接净水器的进水管或出水管与净水器连通。The above technical solution of the present invention is perfect: the water inlet of the water container is connected to the water purifier through an inlet pipe or an outlet pipe connected to the water purifier.
上述本发明技术方案完善八是:所述电解电源是高电平窄脉宽的直流脉冲电源或正向电压电平大于反向电压电平的交变脉冲电源。The above technical solution of the present invention is perfect: the electrolysis power source is a high-frequency narrow pulse width DC pulse power source or an alternating pulse power source whose forward voltage level is greater than a reverse voltage level.
附图说明DRAWINGS
下面结合附图对本发明的净水器辅助净化装置作进一步说明。The water purifier auxiliary purification device of the present invention will be further described below with reference to the accompanying drawings.
图1是本发明实施例一的净水器辅助净化装置的结构示意图。1 is a schematic structural view of a water purifier auxiliary purification device according to a first embodiment of the present invention.
图2是本发明实施例二的净水器辅助净化装置的结构示意图。2 is a schematic structural view of a water purifier auxiliary purification device according to a second embodiment of the present invention.
图3是本发明实施例三的净水器辅助净化装置的结构示意图。3 is a schematic structural view of a water purifier auxiliary purification device according to a third embodiment of the present invention.
图4是本发明实施例四中的正负极以及透水性隔膜的结构示意图。4 is a schematic view showing the structure of a positive electrode and a negative electrode and a water permeable membrane in the fourth embodiment of the present invention.
图5是本发明实施例五中的正负极以及透水性隔膜的结构示意图。Fig. 5 is a schematic view showing the structure of a positive electrode and a negative electrode and a water permeable membrane according to a fifth embodiment of the present invention.
图6是本发明实施例六中的正负极以及透水性隔膜的结构示意图。Fig. 6 is a schematic view showing the structure of a positive electrode and a negative electrode and a water permeable membrane in a sixth embodiment of the present invention.
具体实施方式detailed description
实施例一 Embodiment 1
本实施例的净水器辅助净化装置参见图1(包括设有进水口9的盛水容器1,盛水容器1的进水口9外接现有净水器7的排污口6,净水器7设有进水管10-1和出水管10-2。盛水容器1壳体内设有阴电极2和阳电极3,阴电极2和阳电极3 之间设有透水性隔膜5,透水性隔膜5紧贴阳电极3上,透水性隔膜5包覆阳电极3的全部表面,透水性隔膜5与阴电极2的间距δ=1mm。本实施例的透水性隔膜5采用平均透水孔径0.03微米的单层PVDF超滤膜,厚度为0.1mm。当然本实施例的超滤膜也可以采用其他材质的透水性滤膜,平均透水孔径在0.1~0.05微米之间均可。The water purifier auxiliary purifying device of this embodiment is shown in Fig. 1 (including the water container 1 provided with the water inlet 9, the water inlet 9 of the water container 1 is connected to the sewage outlet 6 of the existing water purifier 7, and the water purifier 7 The inlet pipe 10-1 and the outlet pipe 10-2 are provided. The housing of the water container 1 is provided with a cathode electrode 2 and an anode electrode 3, and a cathode electrode 2 and an anode electrode 3 A water permeable membrane 5 is disposed between the water permeable membrane 5 and the water permeable membrane 5 covering the entire surface of the anode electrode 3. The distance between the water permeable membrane 5 and the cathode electrode 2 is δ = 1 mm. The water-permeable membrane 5 of the present embodiment employs a single-layer PVDF ultrafiltration membrane having an average water permeability of 0.03 μm and a thickness of 0.1 mm. Of course, the ultrafiltration membrane of the present embodiment may also adopt a water permeable filter membrane of other materials, and the average water permeability pore diameter may be between 0.1 and 0.05 micrometers.
本实施例的阴电极2为钛基覆涂铂族氧化物(涂层厚度为0.8毫米)制成的惰性电极,阳电极3采用石墨或活性炭等碳质材料制成,阴阳电极均为圆片形,表面均不开孔。The cathode electrode 2 of the present embodiment is an inert electrode made of a titanium-based platinum group oxide (coating thickness: 0.8 mm), and the anode electrode 3 is made of a carbonaceous material such as graphite or activated carbon, and the anode and the cathode are both wafers. Shape, no holes on the surface.
本实施例阴电极2、阳电极3采用直流的电解电源4进行供电,电解电源4为高电平窄脉宽稳压24伏的交变直流脉冲电源,且正向脉冲电平大于反向脉冲电平。In this embodiment, the cathode electrode 2 and the anode electrode 3 are powered by a DC electrolysis power source 4, and the electrolysis power source 4 is an alternating-current DC pulse power source with a high-level narrow pulse width regulation voltage of 24 volts, and the forward pulse level is greater than the reverse pulse. Level.
本实施例的净水器辅助净化装置可以在水中形成有大量以氢气为主的超微气泡,超微氢气泡上浮到净水器7中,可以冲洗现有净水器7中的过滤膜(或活性炭)8的外表面,防止过滤膜(或活性炭)8的外表面结垢,减轻浓差极化,使源水中的污染物絮凝沉淀而去除。同时装置产生的强氧化因子对水进行杀菌,并防止活性碳过早饱和,大幅度延长活性碳的更换周期。The water purifier auxiliary purifying device of the embodiment can form a large amount of ultra-micro bubbles mainly composed of hydrogen in the water, and the ultra-micro hydrogen bubbles float up to the water purifier 7 to wash the filter film in the existing water purifier 7 ( Or the outer surface of the activated carbon) 8 prevents the outer surface of the filter membrane (or activated carbon) 8 from scaling, reduces the concentration polarization, and removes the contaminants in the source water by flocculation and precipitation. At the same time, the strong oxidizing factor produced by the device sterilizes the water and prevents premature saturation of the activated carbon, which greatly prolongs the replacement cycle of the activated carbon.
采用本实施例的净水器辅助净化装置与一台标称流量为380升/小时的市售常规超滤净水器对接(盛水容器1的进水口密封套接到该净水器的排污口6)进行了水电解实验。盛水容器1的内腔为:直径D=120mm,高80毫米;将该净水器内的超滤滤芯去除,以市供自来水(TDS=187mg/L)将净水器(连同盛水容器)注满水(约20升),关闭净水器的进水口10-1,电解时间为30分钟,每隔5分钟从净水器中取水样测定一次;The water purifier auxiliary purifying device of the embodiment is used for docking with a commercially available conventional ultrafiltration water purifier having a nominal flow rate of 380 liters/hour (the water inlet sealing sleeve of the water container 1 is connected to the water purifier of the water purifier). Port 6) was subjected to a water electrolysis experiment. The inner cavity of the water container 1 is: diameter D=120mm, height 80mm; the ultrafiltration filter element in the water purifier is removed, and the water purifier is provided with the city tap water (TDS=187mg/L) (together with the water container) Filled with water (about 20 liters), close the water inlet 10-1 of the water purifier, the electrolysis time is 30 minutes, and the water sample is taken from the water purifier every 5 minutes;
以下实验中,水中气泡量(强度)以及水中氧化因子多少采用定性观测方法:In the following experiments, the amount of bubbles (strength) in water and the amount of oxidation factor in water were determined by qualitative observation:
①水中气泡量(强度)的目测分级:1 Visual classification of the amount of bubbles (strength) in water:
从水中气泡为零~实验中相对气泡含量最大,分为0~5级;The bubble from the water is zero - the maximum relative bubble content in the experiment is divided into 0 to 5 grades;
②水中氧化因子的测定。2 Determination of oxidation factor in water.
如前所述,由于氧化因子在水中存留时间极为短暂,现有的检测方法(例如化学反应法和捕获法)的分析选择性和可信度还难以令人满意。同时考虑到本发明装置系专用于日常用水的处理,侧重关心的是氧化因子的变化趋势级宏观作用。因此为简化重复实验工作量,专门研发了定性了解水中氧化因子总量的滴定液。通过自制滴定液滴定到水中后,观察水体颜色的变黄程度,分为5级,定性判定 水中氧化因子含量:As mentioned earlier, since the retention time of the oxidation factor in water is extremely short, the analytical selectivity and reliability of existing detection methods (such as chemical reaction methods and capture methods) are still unsatisfactory. At the same time, it is considered that the device of the present invention is dedicated to the daily water treatment, and the focus is on the macroscopic effect of the change trend of the oxidation factor. Therefore, in order to simplify the repetitive experimental workload, a titration solution that qualitatively understands the total amount of oxidizing factors in water has been specially developed. After self-made titration of droplets into water, observe the degree of yellowing of water color, divided into 5 levels, qualitative judgment Oxidation factor content in water:
无色——对应水中氧化因子基本为零,设为0级;Colorless - the corresponding oxidation factor in water is essentially zero, set to level 0;
颜色最黄——对应水中氧化因子相对最多,设为5级;The color is the yellowest - the corresponding oxidation factor in the water is the most, set to 5;
从无色到颜色最黄中间颜色变化的程度不同分设为1、2、3和4级。The degree of color change from colorless to color yellow is set to 1, 2, 3, and 4 levels.
实验结果如下表1:The experimental results are shown in Table 1:
表1Table 1
Figure PCTCN2015076239-appb-000001
Figure PCTCN2015076239-appb-000001
实验结果分析Analysis of results
1、通过排水集气-燃烧方法并测量水中溶解氢含量,可以确定水中生成的大量气泡主要表现为氢气泡;1. Through the drainage gas-burning method and measuring the dissolved hydrogen content in water, it can be determined that a large number of bubbles generated in the water mainly represent hydrogen bubbles;
2、随电解时间的增加,水中的氢以及氧化因子量均呈正比例增长;2. With the increase of electrolysis time, the amount of hydrogen and oxidation factor in water increased in a positive proportion;
3、阳电极3碳质材料的吸附作用,水中产生的氧化因子将减少,从而制成适宜饮用的水。3. Adsorption of the carbonaceous material of the anode electrode 3, the oxidation factor produced in the water will be reduced, thereby making water suitable for drinking.
实施例二 Embodiment 2
本实施例的净水器辅助净化装置是在实施例一基础上的改进,如图2所示,与实施例一的变化是:1)将盛水容器1设置在净水器7的进水管10-1处,这样净水器辅助净化装置在水中形成的大量以氢气为主的超微气泡和强氧化因子可以在水压的作用下进入净水器,同样起到达到杀菌和清洁的作用。当然,盛水容器1也可以与进水管10-1进行串接(再在盛水容器1开有出水口),进一步地,盛水容器1也可以与出水管10-2进行并接或串接。The water purifier auxiliary purifying apparatus of the present embodiment is an improvement on the basis of the first embodiment. As shown in FIG. 2, the variation with the first embodiment is: 1) the water receiving container 1 is disposed in the water inlet pipe of the water purifier 7. At 10-1, such a large amount of hydrogen-based ultra-microbubbles and strong oxidizing factors formed in the water purifier auxiliary purification device can enter the water purifier under the action of water pressure, and also play the role of sterilization and cleaning. . Of course, the water container 1 can also be connected in series with the inlet pipe 10-1 (the water outlet is opened in the water container 1). Further, the water container 1 can also be connected or connected to the outlet pipe 10-2. Pick up.
2)阳电极3变更为钛基覆涂铂族氧化物(涂层厚度为0.8毫米)的惰性电极。2) The anode electrode 3 was changed to an inert electrode of a titanium-based platinum group oxide (coating thickness: 0.8 mm).
3)透水性隔膜5与阴电极2的间距δ是3mm。 3) The distance δ between the water permeable membrane 5 and the cathode electrode 2 is 3 mm.
本实施例调整透水性隔膜5对阳电极3的覆盖方式进行对比实验:第一种方式如图2所示,透水性隔膜5完全包覆阳电极3的全部表面;第二种方式,透水性隔膜5仅仅覆盖阳电极3朝向阴电极2一侧2/3部分表面(图中示未出),两种方式中其它结构参数均不变。实验条件也与实施例一相同。分别试验透水性隔膜5对阳电极3的二种覆盖方式,测试结果如下表2:In this embodiment, a comparative experiment is performed to adjust the coverage of the anode 3 by the water permeable membrane 5: in the first mode, as shown in FIG. 2, the water permeable membrane 5 completely covers the entire surface of the anode electrode 3; The diaphragm 5 covers only the surface of the anode electrode 3 facing the 2/3 side of the cathode electrode 2 (not shown), and the other structural parameters are unchanged in both modes. The experimental conditions were also the same as in the first embodiment. The two kinds of coverage methods of the permeable membrane 5 for the anode electrode 3 were tested separately, and the test results are shown in Table 2 below:
表2Table 2
Figure PCTCN2015076239-appb-000002
Figure PCTCN2015076239-appb-000002
实验结果分析Analysis of results
一定范围内,随透水性隔膜5对阳电极3的增加,水中及气泡中的含氢量增加、氧化还原电位下降、碱性加强,氧化因子减少;反之,水中氧化因子则增多。Within a certain range, with the increase of the anode electrode 3 by the water-permeable membrane 5, the hydrogen content in the water and bubbles increases, the oxidation-reduction potential decreases, the alkalinity strengthens, and the oxidation factor decreases; on the contrary, the oxidation factor in the water increases.
实施例三 Embodiment 3
本实施例的净水器辅助净化装置是在实施例一基础上的改进,如图3所示,与实施例一的变化是:1)盛水容器1壳体为不锈钢材质,并作为阴电极2;2)透水性隔膜5与阴电极2的间距δ是2mm。The water purifier auxiliary purifying device of this embodiment is an improvement on the basis of the first embodiment. As shown in FIG. 3, the variation with the first embodiment is: 1) the water container 1 is made of stainless steel and serves as a cathode electrode. 2; 2) The distance δ between the water permeable membrane 5 and the cathode electrode 2 is 2 mm.
将本实施例的净水器辅助净化装置进行水电解实验,电解时间20分钟,其他实验条件和检测方法与实施例一相同,实验结果如下表3:The water purifier auxiliary purification device of the present embodiment was subjected to a water electrolysis experiment, and the electrolysis time was 20 minutes. Other experimental conditions and detection methods were the same as those in the first embodiment. The experimental results are shown in Table 3 below:
表3table 3
Figure PCTCN2015076239-appb-000003
Figure PCTCN2015076239-appb-000003
实施例四 Embodiment 4
本实施例的净水器辅助净化装置是在实施例一基础上的改进,如图4所示,与实施例一的变化是:1)阴电极2上均布开有24个直径φ1mm的第一通孔;2)透水性隔膜5与阴电极2的间距δ是4mm;3)阳电极3变更为钛基覆涂铂族氧化物(涂层厚度为0.8毫米)的惰性电极;4)透水性隔膜5包覆阳电极3的部分表 面(阳电极3朝向阴电极2一侧的全部表面)。The water purifier auxiliary purifying apparatus of this embodiment is an improvement based on the first embodiment. As shown in FIG. 4, the variation with the first embodiment is: 1) the cathode electrode 2 is uniformly provided with 24 diameters of φ1 mm. a through hole; 2) the distance δ between the water permeable membrane 5 and the cathode electrode 2 is 4 mm; 3) the anode electrode 3 is changed to an inert electrode coated with a platinum group oxide (coating thickness: 0.8 mm); 4) permeable to water Part of the surface of the diaphragm 5 covering the anode electrode 3 The face (the entire surface of the anode electrode 3 facing the side of the cathode electrode 2).
将本实施例的净水器辅助净化装置进行水电解实验,电解时间20分钟,其他实验条件和检测方法与实施例一相同,实验结果如下表3:The water purifier auxiliary purification device of the present embodiment was subjected to a water electrolysis experiment, and the electrolysis time was 20 minutes. Other experimental conditions and detection methods were the same as those in the first embodiment. The experimental results are shown in Table 3 below:
表3table 3
Figure PCTCN2015076239-appb-000004
Figure PCTCN2015076239-appb-000004
实施例五 Embodiment 5
本实施例的净水器辅助净化装置是在实施例四基础上的改进,与实施例一的变化是:1)如图5所示,透水性隔膜5是由活性炭纤维膜(毡)5-1和超滤膜5-2叠加复合而成的二层透水性隔膜,活性炭纤维膜5-1靠近阳电极3(朝向阳电极3)并且包覆阳电极3的全部表面,朝向阴电极2(背离阳电极3)的超滤膜5-2包覆阳电极3的部分表面(阳电极3朝向阴电极2一侧的全部表面),并且超滤膜5-2的两端略微超出阳电极;2)透水性隔膜5与阴电极2的间距δ是5mm;3)阳电极3改为与阴电极2相同的采用钛基覆涂铂族氧化物(涂层厚度为0.8毫米)制成的惰性电极,呈圆形片状。The water purifier auxiliary purification device of the present embodiment is an improvement on the basis of the fourth embodiment, and the variation with the first embodiment is: 1) as shown in FIG. 5, the water permeable membrane 5 is made of an activated carbon fiber membrane (felt) 5- 1 and a super-filtration membrane 5-2 superposed and laminated to form a two-layer water-permeable membrane, the activated carbon fiber membrane 5-1 is close to the anode electrode 3 (toward the anode electrode 3) and covers the entire surface of the anode electrode 3, facing the cathode electrode 2 ( The ultrafiltration membrane 5-2 facing away from the anode electrode 3) covers a part of the surface of the anode electrode 3 (the entire surface of the anode electrode 3 toward the side of the cathode electrode 2), and both ends of the ultrafiltration membrane 5-2 slightly exceed the anode electrode; 2) The distance δ between the water permeable membrane 5 and the cathode electrode 2 is 5 mm; 3) the anode electrode 3 is changed to the same inertness as the cathode electrode 2 by using a titanium-based platinum group oxide (coating thickness: 0.8 mm) The electrode has a circular sheet shape.
将本实施例的净水器辅助净化装置进行水电解实验,电解时间20分钟,其他实验条件与实施例一相同,实验结果如下表4:The water purifier auxiliary purification device of the present embodiment was subjected to a water electrolysis experiment, and the electrolysis time was 20 minutes. The other experimental conditions were the same as those in the first embodiment. The experimental results are shown in Table 4 below:
表4Table 4
Figure PCTCN2015076239-appb-000005
Figure PCTCN2015076239-appb-000005
由实验结果可得出:本实施例的净水器辅助净化装置,由于透水性隔膜5是由活性炭纤维膜(毡)5-1和超滤膜5-2叠加复合而成的二层透水性隔膜,因此可以大量吸附水中氧化因子,从而制成更适宜人饮用的富含氢及氧化还原电位低的水。From the experimental results, it can be concluded that the water purifying device auxiliary purifying device of the present embodiment has a water permeability diaphragm 5 which is a two-layer water permeable material formed by superimposing an activated carbon fiber membrane (fel) 5-1 and an ultrafiltration membrane 5-2. The separator can therefore adsorb a large amount of oxidizing factors in water, thereby making water which is more suitable for human consumption and rich in hydrogen and low in oxidation-reduction potential.
实施例六 Embodiment 6
本实施例的净水器辅助净化装置是在实施例五基础上的改进,与实施例五的变化是:1)活性炭纤维膜(毡)5-1由导电性陶瓷制成的透水膜取代;2)如图6所示,朝向阴电极2(背离阳电极3)的超滤膜5-2包覆阳电极3的三个侧表面;3)透水性隔膜与阴电极2的间距δ是9mm。 The water purifier auxiliary purification device of the present embodiment is an improvement on the basis of the fifth embodiment, and the variation of the fifth embodiment is: 1) the activated carbon fiber membrane (felt) 5-1 is replaced by a water permeable membrane made of a conductive ceramic; 2) As shown in Fig. 6, the ultrafiltration membrane 5-2 facing the cathode electrode 2 (reverse from the anode electrode 3) covers the three side surfaces of the anode electrode 3; 3) the distance δ between the water permeable membrane and the cathode electrode 2 is 9 mm .
本发明的净水器辅助净化装置不局限于上述实施例所述的具体技术方案,比如:1)阳电极3可以是其他材料的惰性电极;2)透水性隔膜5与阴电极2的间距δ可以是0~10mm的任意间距,比如7mm、8mm或10mm等;3)透水性隔膜5也可以是三层或更多层不同材质的隔膜叠加而成;4)阴电极2和阳电极3的形状也可以是包括圆形和方形的各种形状;5)本发明的上述多个实施例的技术方案彼此可以交叉组合形成新的技术方案;等等。凡采用等同替换形成的技术方案均为本发明要求的保护范围。 The water purifier auxiliary purification device of the present invention is not limited to the specific technical solutions described in the above embodiments, such as: 1) the anode electrode 3 may be an inert electrode of other materials; 2) the distance δ between the water permeable membrane 5 and the cathode electrode 2 It may be any spacing of 0~10mm, such as 7mm, 8mm or 10mm, etc.; 3) The water permeable membrane 5 may also be a stack of three or more layers of different materials; 4) the cathode electrode 2 and the anode electrode 3 The shape may also be various shapes including a circle and a square; 5) The technical solutions of the above-described various embodiments of the present invention may be cross-combined with each other to form a new technical solution; All technical solutions formed by equivalent replacement are the scope of protection required by the present invention.

Claims (12)

  1. 一种净水器辅助净化装置,包括设有进水口的盛水容器,所述进水口与净水器连通;其特征在于:所述盛水容器的壳体内设有阴电极和阳电极,还包括用于对所述阴电极和阳电极供电的电解电源;成对的阴电极和阳电极之间设有透水性隔膜,所述透水性隔膜覆盖在阳电极上,所述透水性隔膜与阴电极的间距δ范围是0≤δ≤10毫米,所述透水性隔膜的透水孔径小于等于2毫米且大于等于1纳米。A water purifier auxiliary purifying device, comprising a water container provided with a water inlet, the water inlet is connected with the water purifier; characterized in that: the cathode of the water container is provided with a cathode electrode and an anode electrode, and An electrolytic power source for supplying power to the cathode electrode and the anode electrode; a water permeable membrane disposed between the pair of cathode electrodes and the anode electrode, the water permeable membrane covering the anode electrode, the water permeable membrane and the cathode The distance δ of the electrode ranges from 0 ≤ δ ≤ 10 mm, and the water permeable membrane of the water permeable membrane has a water permeability diameter of 2 mm or more and 1 nm or more.
  2. 根据权利要求1所述净水器辅助净化装置,其特征在于:所述透水性隔膜是叠加复合而成的至少二层,其中靠近阳电极的一层透水性隔膜是由碳质材料制成的透水性隔膜。A water purifier auxiliary purifying apparatus according to claim 1, wherein said water permeable membrane is at least two layers superposed and laminated, wherein a permeable membrane adjacent to the anode electrode is made of a carbonaceous material. Water permeable membrane.
  3. 根据权利要求1所述净水器辅助净化装置,其特征在于:所述透水性隔膜是单层透水性隔膜,所述阳电极是含有碳质材料的阳电极。A water purifier auxiliary purification apparatus according to claim 1, wherein said water permeable membrane is a single-layer water permeable membrane, and said anode electrode is an anode electrode containing a carbonaceous material.
  4. 根据权利要求3所述净水器辅助净化装置,其特征在于:所述单层透水性隔膜是超滤膜或采用碳质材料制成的透水性隔膜。A water purifier auxiliary purification apparatus according to claim 3, wherein said single-layer water-permeable membrane is an ultrafiltration membrane or a water-permeable membrane made of a carbonaceous material.
  5. 根据权利要求1-4之任一所述净水器辅助净化装置,其特征在于:所述透水性隔膜覆盖所述阳电极的全部表面。A water purifier auxiliary purification apparatus according to any one of claims 1 to 4, wherein said water permeable membrane covers the entire surface of said anode electrode.
  6. 根据权利要求1-4之任一所述净水器辅助净化装置,其特征在于:所述透水性隔膜覆盖所述阳电极的部分表面。A water purifier auxiliary purification apparatus according to any one of claims 1 to 4, wherein said water permeable membrane covers a part of the surface of said anode electrode.
  7. 根据权利要求1-4之任一所述饮水电解制取装置,其特征在于:所述阴电极上开有第一通孔,所述第一通孔的孔径大于等于1毫米。The drinking water electrolysis preparation device according to any one of claims 1 to 4, wherein the cathode electrode is provided with a first through hole, and the first through hole has a diameter of 1 mm or more.
  8. 根据权利要求1-4之任一所述净水器辅助净化装置,其特征在于:所述透水性隔膜开有第二通孔,所述第二通孔的孔径大于2毫米。The water purifier auxiliary purification device according to any one of claims 1 to 4, wherein the water permeable membrane is opened with a second through hole, and the second through hole has a diameter larger than 2 mm.
  9. 根据权利要求1-4之任一所述净水器辅助净化装置,其特征在于:所述盛水容器的壳体是金属制成的壳体,并直接作为阴电极。A water purifier auxiliary purifying apparatus according to any one of claims 1 to 4, wherein the casing of the water holding container is a metal casing and directly functions as a cathode electrode.
  10. 根据权利要求1-4所述净水器辅助净化装置,其特征在于:所述盛水容器的进水口通过外接净水器的排污口与净水器连通。The water purifier auxiliary purification device according to any one of claims 1 to 4, characterized in that: the water inlet of the water container is connected to the water purifier through the sewage outlet of the external water purifier.
  11. 根据权利要求1-4所述净水器辅助净化装置,其特征在于:所述盛水容器的进水口通过连接净水器的进水管或出水管与净水器连通。The water purifier auxiliary purifying apparatus according to any one of claims 1 to 4, characterized in that: the water inlet of the water container is connected to the water purifier through an inlet pipe or an outlet pipe connected to the water purifier.
  12. 根据权利要求1-4之任一所述净水器辅助净化装置,其特征在于:所述电解电源是高电平窄脉宽的直流脉冲电源或正向电压电平大于反向电压电平的交变脉冲电源。 A water purifier auxiliary purifying apparatus according to any one of claims 1 to 4, wherein said electrolysis power source is a high-frequency narrow pulse width DC pulse power source or a forward voltage level greater than a reverse voltage level Alternating pulse power supply.
PCT/CN2015/076239 2014-04-12 2015-04-10 Auxiliary purifying device for water purifier WO2015154706A1 (en)

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