CN201347357Y - High-concentration ozone generating device - Google Patents
High-concentration ozone generating device Download PDFInfo
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- CN201347357Y CN201347357Y CNU2008202186594U CN200820218659U CN201347357Y CN 201347357 Y CN201347357 Y CN 201347357Y CN U2008202186594 U CNU2008202186594 U CN U2008202186594U CN 200820218659 U CN200820218659 U CN 200820218659U CN 201347357 Y CN201347357 Y CN 201347357Y
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Abstract
Description
技术领域 technical field
本实用新型属于气体放电物理学、等离子体物理、环境科学等技术领域,涉及一种高浓度臭氧产生装置。The utility model belongs to the technical fields of gas discharge physics, plasma physics, environmental science and the like, and relates to a high-concentration ozone generating device.
背景技术 Background technique
产生高浓度臭氧一直是国内外研究热点,日本三菱电机和东芝三菱电机等单位新研制成功窄间隙(0.3~0.25mm)臭氧发生器,臭氧浓度分别达到180g/Nm3、350g/Nm3。日本富士电机近期研制了放电极、接地极同时水冷却的臭氧发生器,臭氧浓度达到200g/Nm3。从理论研究表明,臭氧浓度还有较大的提高空间,尚须进一步加以研究解决其相关技术。Generating high-concentration ozone has always been a research hotspot at home and abroad. Japan’s Mitsubishi Electric and Toshiba Mitsubishi Electric have newly developed narrow-gap (0.3-0.25mm) ozone generators with ozone concentrations of 180g/Nm 3 and 350g/Nm 3 respectively. Japan's Fuji Electric has recently developed an ozone generator with water-cooled discharge electrodes and ground electrodes at the same time, with an ozone concentration of 200g/Nm 3 . Theoretical research shows that there is still a large room for improvement in ozone concentration, and further research is needed to solve its related technologies.
目前臭氧产生装置存在不足之处是放电间隙还有变窄空间;多数放电极还没有冷却,由于臭氧热分解阻碍臭氧浓度进一步地提高;目前臭氧产生器中电离放电场太长,通常达到0.4~1m,使已产生的臭氧由于活性粒子激励而分解,因而制约了臭氧浓度的进一步地提高;由于电离放电电场太长,阻碍了臭氧产生器的进一步小型化。The shortcomings of the current ozone generators are that the discharge gap still has narrowing space; most discharge electrodes have not been cooled, and the further increase of ozone concentration is hindered by the thermal decomposition of ozone; the ionization discharge field in the current ozone generator is too long, usually reaching 0.4~ 1m, the generated ozone is decomposed due to the excitation of active particles, thus restricting the further increase of the ozone concentration; because the ionization discharge electric field is too long, it hinders the further miniaturization of the ozone generator.
发明内容 Contents of the invention
本实用新型的目的是针对现有臭氧产生装置产生的臭氧浓度比较低、体积大、能耗较高的问题,而提供了一种高浓度臭氧产生装置。该装置的放电极、接地极同时用去离子水冷却,降低了臭氧的热分解;并采用高介电常数、高电阻率的Al2O3材料形成的电介质薄层,同时又采用超窄放电间隙方法,提高了电离放电电场强度,强化了氧气解离反应,提高了臭氧产生量,同时又可以相应地提高了氧气流速,有利于抑制臭氧热分解反应,实现了臭氧产生装置的小型化。The purpose of the utility model is to provide a high-concentration ozone generating device aiming at the problems of relatively low ozone concentration, large volume and high energy consumption produced by the existing ozone generating device. The discharge electrode and the ground electrode of the device are cooled with deionized water at the same time, which reduces the thermal decomposition of ozone; and uses a thin dielectric layer formed of Al 2 O 3 material with high dielectric constant and high resistivity, and uses ultra-narrow discharge The gap method increases the electric field intensity of the ionization discharge, strengthens the oxygen dissociation reaction, increases the amount of ozone produced, and at the same time increases the flow rate of oxygen accordingly, which is beneficial to inhibit the thermal decomposition reaction of ozone, and realizes the miniaturization of the ozone generating device.
本实用新型解决其技术所采用技术方案是:The technical solution adopted by the utility model to solve its technology is:
本实用新型是采用去离子水冷却放电极和接地极;间隙距离为0.04~0.25mm;介电常数(≥10),高绝缘电阻率(≥1014Ω·cm)的Al2O3制成厚度为0.47~1.0mm电介质薄层。由于采用了上述的方法,实现了放电间隙中放电通道中的电离折合电场强度达到450~1500Td,电子平均能量达到10~24eV的强电离放电。这将把更多氧分子电离、解离和激发成高浓度活性粒子,在电场参数调控作用将产生更多的臭氧。众所周知,促使臭氧分解的电子能量为2.0~8.0eV,而强电离放电的电子平均能量达到10eV以上,具有2.0~8.0eV的电子数量将大幅度降低,因而抑制了臭氧再分解。实现了调控臭氧浓度及产生效率,提高了臭氧浓度;同时又控制了臭氧的再分解。The utility model adopts deionized water to cool the discharge electrode and the ground electrode; the gap distance is 0.04-0.25mm; the dielectric constant (≥10), high insulation resistivity (≥10 14 Ω·cm) is made of Al 2 O 3 Thickness of 0.47 ~ 1.0mm thin dielectric layer. Due to the adoption of the above method, a strong ionization discharge in which the ionization equivalent electric field intensity in the discharge channel in the discharge gap reaches 450-1500Td and the average electron energy reaches 10-24eV is realized. This will ionize, dissociate and excite more oxygen molecules into high-concentration active particles, and more ozone will be generated in the regulation of electric field parameters. As we all know, the energy of electrons that promote the decomposition of ozone is 2.0-8.0eV, while the average energy of electrons in strong ionization discharge reaches more than 10eV, and the number of electrons with 2.0-8.0eV will be greatly reduced, thus inhibiting the re-decomposition of ozone. The regulation and control of ozone concentration and production efficiency are realized, and the ozone concentration is improved; at the same time, the re-decomposition of ozone is controlled.
另一方面本实用新型采用了0.04~0.25mm的超窄间隙,将成倍数提高了氧气通过间隙的流速,有助于把生成臭氧产生的热量带走,降低了放电间隙中的温度,进而控制了臭氧的热分解反应,进而提高臭氧浓度及产生效率;同时又利于臭氧快速输运出去,减少了臭氧的分解机率,也同样利于臭氧浓度及效率再提升。On the other hand, the utility model adopts an ultra-narrow gap of 0.04-0.25mm, which increases the flow rate of oxygen passing through the gap by multiples, helps to take away the heat generated by ozone formation, reduces the temperature in the discharge gap, and then controls The thermal decomposition reaction of ozone improves the ozone concentration and production efficiency; at the same time, it facilitates the rapid transport of ozone, reduces the decomposition probability of ozone, and is also conducive to the improvement of ozone concentration and efficiency.
本实用新型的效果和益处是:在放电极、接地极同时水冷却条件下,采用了超窄放电间隙的相应技术,促使臭氧浓度提升到160~420g/Nm3;由于实现了强电离放电生成臭氧,并将大大地减少了电离放电电场长度(即电极长度),同时也实现了臭氧产生装置的小型化。The effects and benefits of the utility model are: under the condition of water cooling of the discharge electrode and the ground electrode at the same time, the corresponding technology of the ultra-narrow discharge gap is adopted to promote the ozone concentration to 160-420g/Nm 3 ; due to the realization of strong ionization discharge generation Ozone will greatly reduce the length of the ionization discharge electric field (that is, the length of the electrode), and also realize the miniaturization of the ozone generating device.
附图说明Description of drawings
图1是臭氧与氧分子离解面积与电子能量关系图。Figure 1 is a graph showing the relationship between the dissociation area of ozone and oxygen molecules and the energy of electrons.
图2是等离子体中电子能量分布图。Figure 2 is a diagram of the energy distribution of electrons in the plasma.
图3是电子平均能量ε与折合电场强度关系曲线图。Fig. 3 is a graph showing the relationship between the average electron energy ε and the reduced electric field intensity.
图4是本实用新型实施例1结构示意正视剖面图。Fig. 4 is a schematic front sectional view of the structure of
图5是本实用新型实施例1的侧视剖面图。Fig. 5 is a side sectional view of
图6是本实用新型实施例2的结构侧视剖面图。Fig. 6 is a side sectional view of the structure of
图7是本实用新型实施例3的结构侧视剖面图。Fig. 7 is a side sectional view of the structure of
其中1.氧气;2、7.冷却水;3.接地极;4.放电间隙;5.电介质层;6.放电极;8.臭氧和氧气;9.高压电缆;10.交变高压电源;11.隔片;12.绝缘层;13.冷却器;14.离子交换器;15、16.阀体。1. Oxygen; 2, 7. Cooling water; 3. Ground electrode; 4. Discharge gap; 5. Dielectric layer; 6. Discharge electrode; 8. Ozone and oxygen; 9. High voltage cable; 10. Alternating high voltage power supply; 11. Separator; 12. Insulation layer; 13. Cooler; 14. Ion exchanger; 15, 16. Valve body.
具体实施方式 Detailed ways
下面结合技术方案和附图详细叙述本实用新型的具体实施方式。The specific embodiment of the utility model is described in detail below in conjunction with technical scheme and accompanying drawing.
从图1的臭氧分子与氧分子解离截面积与电子能量关系曲线可知,被电场加速电子垂直激励离解氧分子,从O2(x3∑g-)基态激励到O2(A3Δu+)状态时,所需垂直激励能量为6.1eV,是禁阻跃迁;从O2(X3∑g-)基态激励到O2(B3∑u-)状态时,氧分子垂直激励能量为8.4eV;然而臭氧离解的激励能量却为2eV,放电间隙中电子从放电电场取得能量≥8.4eV时,氧分子才能分解、电离成氧原子、离子和自由基等并与氧分子碰撞后生成臭氧,可见具有2.0~8.4eV之间能量的电子对产生臭氧没有一点用途,这部分能量好像只是为了专门用来分解臭氧之用。氧分子离解、电离及臭氧生成的等离子体反应式是:From the relationship curve between the dissociation cross-sectional area of ozone molecules and oxygen molecules and electron energy in Figure 1, it can be known that the electrons accelerated by the electric field are vertically excited to dissociate oxygen molecules from the ground state of O 2 (x 3 ∑g - ) to O 2 (A 3 Δu + ) state, the required vertical excitation energy is 6.1eV, which is a forbidden transition; when excited from the ground state of O 2 (X 3 ∑g - ) to the state of O 2 (B 3 ∑u - ), the vertical excitation energy of oxygen molecules is 8.4 eV; however, the excitation energy for ozone dissociation is 2eV. When the electrons in the discharge gap obtain energy ≥ 8.4eV from the discharge electric field, oxygen molecules can decompose and ionize into oxygen atoms, ions and free radicals, etc., and generate ozone after colliding with oxygen molecules. It can be seen that electrons with energies between 2.0 and 8.4 eV are useless for generating ozone, and this part of energy seems to be used exclusively for decomposing ozone. The plasma reaction formula of oxygen molecular dissociation, ionization and ozone generation is:
O2(x3∑g-)+e*→O2(A3∑u+)+e (1)O 2 (x 3 ∑g - )+e * →O 2 (A 3 ∑u + )+e (1)
→O(3P)+O(3P)+e→O( 3P )+O( 3P )+e
O2(x3∑g-)+e*→O2(B3∑u-)+e (2)O 2 (x 3 ∑g - )+e * →O 2 (B 3 ∑u - )+e (2)
→O(1D)+O(3P)+e→O( 1D )+O( 3P )+e
O2(x3∑g-)+e*→O2(A3πu+)+e (3)O 2 (x 3 ∑g - )+e * →O 2 (A 3 πu + )+e (3)
→O(3P)+O+(1S0)+2e→O( 3 P)+O + ( 1 S 0 )+2e
O+O2+M→O3 *+M→O3+M (4)O+O 2 +M→O 3 * +M→O 3 +M (4)
从等离子体电子能量分布曲线图2中可知,目前市场生产臭氧产生装置的放电间隙里电子平均能量均为5.0eV,有的更低些。能量大于8.4eV的电子数目仅为17.4%,而占有2.0~8.4eV电子能量的电子数目高达58.3%,它们成为离解臭氧能量的专业提供者。当放电间隙里的电子平均能量达到23eV时,占有≥8.4eV能量的电子数目增加到80.0%,具有2.0~8.4eV之间能量的电子数目下降到17.1%。这表明强电离放电有利于臭氧的产生,臭氧浓度提高;同时又抑制臭氧的再分解反应。From the plasma electron energy distribution curve in Figure 2, it can be seen that the average energy of electrons in the discharge gap of the ozone generating device currently produced in the market is 5.0eV, and some are even lower. The number of electrons with energy greater than 8.4eV is only 17.4%, while the number of electrons with electron energy between 2.0 and 8.4eV is as high as 58.3%. They become professional providers of energy for dissociated ozone. When the average energy of electrons in the discharge gap reaches 23eV, the number of electrons with energy ≥ 8.4eV increases to 80.0%, and the number of electrons with energy between 2.0 and 8.4eV decreases to 17.1%. This shows that the strong ionization discharge is beneficial to the generation of ozone, and the concentration of ozone is increased; at the same time, it inhibits the re-decomposition reaction of ozone.
放电间隙里的电场强度表达式:The electric field strength expression in the discharge gap:
Eg=Vmεd/(2ldεg+lgεd) (5)Eg=V m ε d /(2l d ε g +lgε d ) (5)
从式5中可见,只有增加外加峰值电压Vm、电介质的介电常数εd;减小放电间隙距离lg和电介质厚度ld,才有可能得到强电离放电的电场强度。It can be seen from
通常用折合电场强度E/N(或E/P)来表征气体放电强度、电离强度。也将间接表征产生臭氧的浓度值多少。图4表示了折合电场强度与电子取得平均能量值的关系曲线。从图4曲线可知,在电离放电电场中的电子具有平均能量大小取决于电离放电电场强度,只有强电离放电过程中电子所具有能量方可使大量O2气体分子离解成单原子、单原子离子等活性粒子,并为合成O3提供了大量活性粒子等基础材料。Usually, the reduced electric field strength E/N (or E/P) is used to characterize the gas discharge strength and ionization strength. It will also indirectly characterize the concentration value of ozone. Figure 4 shows the relationship curve between the reduced electric field intensity and the average energy value obtained by electrons. It can be seen from the curve in Figure 4 that the average energy of electrons in the ionization discharge electric field depends on the strength of the ionization discharge electric field, and only the energy possessed by electrons in the process of strong ionization discharge can dissociate a large number of O2 gas molecules into monatomic and monatomic ions and other active particles, and provide a large number of active particles and other basic materials for the synthesis of O 3 .
根据伯努利气体方程可知:Δp=C(-ΔV)-2,在放电间隙的气体压力与气体流速平方成反比。减小气体放电间隙距离,提高放电间隙里气体流速,提高了E/P(E/N)值,放电间隙里的电子获得能量就增加了。According to Bernoulli's gas equation: Δp=C(-ΔV) -2 , the gas pressure in the discharge gap is inversely proportional to the square of the gas flow rate. Reduce the gas discharge gap distance, increase the gas flow rate in the discharge gap, increase the E/P (E/N) value, and the electrons in the discharge gap will increase their energy.
本实用新型由于采用高强度的高介电常数的电介质薄层即陶瓷材料的厚度仅为0.47~1.0mm,放电间隙极窄,仅为0.01~1.0mm,所以大幅度提高了放电间隙的折合电场强度,进而使放电间隙的高能量电子占有率成倍增加,如图2所示,进而大幅度提高了臭氧浓度和臭氧产生效率。Because the utility model adopts a high-strength high-permittivity dielectric thin layer, that is, the thickness of the ceramic material is only 0.47-1.0 mm, and the discharge gap is extremely narrow, only 0.01-1.0 mm, so the equivalent electric field of the discharge gap is greatly improved. Intensity, and then double the occupancy rate of high-energy electrons in the discharge gap, as shown in Figure 2, and then greatly improve the ozone concentration and ozone generation efficiency.
图4是本实用新型实施例1的结构图,图5为图4的N~N剖视图。在上述图中,10为频率为400~20000Hz的交变高压电源,经高压电缆9与放电极6相连。在对应接地极3的放电极6两平面上均贴冶一层厚度为0.47~1.0mm的Al2O3电介质层5。贴附在放电极6的电介质层5与对应接地极3之间放置数个隔片11,形成2个超窄放电间隙4。当对放电极6施加频率为400~20000Hz交变高电压时,则在放电间隙4里形成强电离放电电场,放电通道中折合电场强度E/n达到450~1500Td;电子具有平均能量达到10~24eV。强电离电场将把氧气1电离、离解和激发成大量的高浓度的活性粒子;在电场参数调控作用下产生高浓度臭氧8。并对放电极6、接地极3同时用去离子水2、7冷却,2是入口的去离子水,7是出口的去离子水,去离子水7通过冷却器13把冷却水温度降到设定值,根据冷却水纯度的设定值调节阀体15、16来确定冷却水7通过离子交换器14的流量;经冷却、去离子的冷却水注入接地极3和放电极6。Fig. 4 is a structural diagram of
图6是本实用新型实施例2的结构侧视剖面图,实施例2与实施例1的不同之处在于放电极6对应接地极3的表面不贴冶电介质层5;相反对应放电极6的接地极3的表面却要分别贴冶电介质层5。Fig. 6 is the structure side view sectional view of
图7是本实用新型实施例3的结构侧视剖面图,实施例3与实施例1的不同之处在于对应放电极6的接地极3表面也同样分别贴冶一层电介质层5。Fig. 7 is a side view sectional view of the structure of
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
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CN105271129A (en) * | 2015-09-30 | 2016-01-27 | 南京华伯仪器科技有限公司 | High concentration ozone generating device |
CN108375651A (en) * | 2018-02-24 | 2018-08-07 | 曹祚 | The detection method and detection device of gas reaction concentration |
CN108638542A (en) * | 2018-05-10 | 2018-10-12 | 重庆新康意安得达尔新材料有限公司 | Pre-coating film production oxidation unit |
CN113277479A (en) * | 2021-04-30 | 2021-08-20 | 大连博羽环保技术开发有限公司 | High-purity, high-concentration and miniaturized ozone generator applied to semiconductor |
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Cited By (7)
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CN105271129A (en) * | 2015-09-30 | 2016-01-27 | 南京华伯仪器科技有限公司 | High concentration ozone generating device |
CN105271129B (en) * | 2015-09-30 | 2017-09-29 | 南京华伯新材料有限公司 | A kind of high concentrition ozone generator |
CN108375651A (en) * | 2018-02-24 | 2018-08-07 | 曹祚 | The detection method and detection device of gas reaction concentration |
CN108375651B (en) * | 2018-02-24 | 2019-10-11 | 恒天摩尔科技(山东)有限公司 | The detection method and detection device of gas reaction concentration |
CN108638542A (en) * | 2018-05-10 | 2018-10-12 | 重庆新康意安得达尔新材料有限公司 | Pre-coating film production oxidation unit |
CN113277479A (en) * | 2021-04-30 | 2021-08-20 | 大连博羽环保技术开发有限公司 | High-purity, high-concentration and miniaturized ozone generator applied to semiconductor |
CN113277479B (en) * | 2021-04-30 | 2023-11-03 | 大连博羽环保技术开发有限公司 | High-purity high-concentration miniaturized ozone generator applied to semiconductor |
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