• <tr id="yyy80"></tr>
  • <sup id="yyy80"></sup>
  • <tfoot id="yyy80"><noscript id="yyy80"></noscript></tfoot>
  • 99热精品在线国产_美女午夜性视频免费_国产精品国产高清国产av_av欧美777_自拍偷自拍亚洲精品老妇_亚洲熟女精品中文字幕_www日本黄色视频网_国产精品野战在线观看 ?

    Efficient direction-independent fog harvesting using a corona discharge device with a multi-electrode structure

    2022-08-29 00:43:00DingchenLI李丁晨ChuanLI李傳JiaweiLI李家瑋WendiYANG楊文迪MenghanXIAO肖夢(mèng)涵MingZHANG張明YongYANG楊勇andKexunYU于克訓(xùn)
    Plasma Science and Technology 2022年9期
    關(guān)鍵詞:楊勇張明李家

    Dingchen LI (李丁晨), Chuan LI (李傳),* , Jiawei LI (李家瑋),Wendi YANG (楊文迪), Menghan XIAO (肖夢(mèng)涵), Ming ZHANG (張明),Yong YANG (楊勇) and Kexun YU (于克訓(xùn))

    1 International Joint Research Laboratory of Magnetic Confinement Fusion and Plasma Physics, State Key Laboratory of Advanced Electromagnetic Engineering and Technology,School of Electrical Engineering and Electronics, Huazhong University of Science and Technology, Wuhan 430074, People’s Republic of China

    2 State Key Laboratory of Advanced Electromagnetic Engineering and Technology, School of Electrical Engineering and Electronics, Huazhong University of Science and Technology, Wuhan 430074, People’s Republic of China

    Abstract Efficient collection of water from fog can effectively alleviate the problem of water shortages in foggy but water-scarce areas, such as deserts, islands and so on. Unlike inefficient fog meshes,corona discharge can charge water droplets and further enhance the water-collecting effect.This study proposes a novel multi-electrode collecting structure that can achieve efficient and direction-independent water collection from fog. The multi-electrode structure consists of three parts:a charging electrode,an intercepting electrode and a ground electrode.Four types of watercollecting structures are compared experimentally,and the collection rates from a traditional fog mesh, a wire-mesh electrode with fog coming from a high-voltage electrode, a wire-mesh electrode with fog coming from a ground electrode and a multi-electrode structure are 2-3 g h-1,100-120 g h-1, 60-80 g h-1 and 200-220 g h-1, respectively. The collection rate of the multielectrode structure is 100-150 times that of a traditional fog mesh and 2-4 times that of a wiremesh electrode. These results demonstrate the superiority of the multi-electrode structure in fog collection.In addition,the motion equation of charged droplets in an electric field is also derived,and the optimization strategy of electrode spacing is also discussed.This structure can be applied not only to fog collection, but also to air purification, factory waste gas treatment and other fields.

    Keywords: fog collection, corona discharge, wire-mesh electrode, multi-electrode structure,collection rate

    1. Introduction

    The freshwater resources on Earth only account for about 2%of the total amount of water, and the total amount of fresh water that can be used by humans only accounts for 3‰ [1].The shortage of freshwater resources heavily restricts human life, economy and industrial development [2]. Approaches to obtain fresh water,such as desalination by distillation,reverse osmosis membrane and electrodialysis, can alleviate this problem, but the poor economy and geographic dependence limit its popularization [3, 4]. Atmospheric water is a widely distributed freshwater resource [5]. Its collection has littleimpact on the environment, and the collected water is clean and can be used directly [6]. Therefore, the collection of atmospheric water resources is expected to alleviate the shortage of freshwater resources in water-scarce areas.

    Table 1. Brief summary and comparison of the various methods used to collect water from air.

    Clouds, fog and water vapor are the main three existing forms of atmospheric water resources in the air[7].Compared with clouds and water vapor, fog is closer to the ground and has a larger particle size (1-30 μm), which is beneficial for collection [5, 7, 8]. Therefore, efficient fog collection has always been a research hotspot in the field of environmental protection and sustainable development.So far,typical manual methods of collecting fog are bionic collection, fog nets and a metal organic framework (MOF). The summarized characteristics of the various methods to collect water from air are shown in table 1.They include methods to collecting fog from various aspects, including bionics, physics and molecular structure. However, they have special requirements regarding humidity, location, materials and so on. Cost and collection efficiency have also affected large-scale applications.

    Inspired by electrostatic precipitators, corona discharge has been applied to the fog collection [23]. Corona discharge can generate gaseous ions to charge droplets, which can further be easily collected by a ground electrode under an electric field[23-25].Similar to electrostatic precipitators,the main factors affecting the collection rate include the charge rate of droplets, the collection area of the ground electrode and the speed of the fog droplets [26-29]. According to the theories on electrostatic collection of droplets [30], charged particles and electric fields can increase the collision crosssection of droplets on the ground electrode. The positive role of a large collection area has been demonstrated by the efficient collection of fog under a multilayer ground electrode [31].

    As for the moving speed of fog droplets, it mainly depends on the distribution of the electric and flow fields,which are closely related to the electrode structure [32].Hence, electrode optimization becomes a significant and effective means to improve the droplet collection rate. However, there are few studies on the optimization of electrodes for the electrostatic collection of fog droplets. Therefore,electrostatic precipitators, which also collect particles, can give us some inspiration. Yamamoto et al improved the traditional wire-plate electrode structure to enhance particle collection by using a ground electrode plate with a collection bag [33, 34]. Dau et al improved the needle-plate electrode structure with a bipolar double needle structure,which greatly increases the collection rate [27]. Gao et al compared the collection rates of four high-voltage electrodes with three ground electrodes by numerical simulation[29].These results indicate that electrode structure can change the distribution of electric and flow fields, thereby causing a change in the collection efficiency.

    Thus, a novel multi-electrode structure is proposed here to enhance the droplet collection rate.The multi-electrode structure includes a charging electrode, a ground electrode and an intercepting electrode. These three electrodes divide the electrode region into a charging region and an intercepting region. The basic principle is that fog droplets are fully charged in the charging region,and subsequently repeatedly collected by the ground electrode under the turbulence generated in the intercepting region. The multi-electrode structure not only can effectively enhance the collection rate of droplets, but also can collect droplets regardless of fog direction after further optimization. The motion equation of charged droplets in the electric field is analysed to guide the design of the multi-electrode structure. In addition, the collection rate and power consumption of a wiremesh electrode and a multi-electrode structure under various electrode spacings and voltages are also discussed.

    2. Theoretical analysis

    Fog collecting efficiency is mainly affected by the movement process of droplets, so it is necessary to study the force equations of fog droplets during the collecting process.Considering actual situations, the following assumptions are adopted in this work [8]:

    (1) Fog droplet shape is spherical.

    (2) After fog droplets are fully charged, the amount of charge remains unchanged.

    (3) The interaction between droplets is ignored.

    (4) The effect of gravity is ignored.

    (5) Background gas is still air.

    2.1. Charge of fog droplets

    There are two types of droplet-charging mechanisms, fieldinduced charging and diffusion charging [30, 35, 36], and both are related to the droplet size. Field-induced charging dominates when the droplet radius dp>0.5 μm, and diffusion charging dominates when the radius dp<0.2 μm[8,31].Generally, in nature, the fog droplet size ranges from 4 to 30 μm [8, 37, 38]. The droplet sizes used in this study ranged from 1 to 15 μm, and the particle size spectrum is shown in figure 8(a). Therefore, the dominant charging method of droplets is field-induced charging. The charge model of the droplet caused by the field charge is [30]

    Figure 1. Force diagram of fog droplet under different conditions. (a) The multi-electrode structure. (b) and (c) The force diagram of fog droplets in different regions. (d) Wire-mesh electrode with fog droplets coming from high-voltage electrode (FH condition). (e) Wire-mesh electrode with fog droplets coming from ground electrode (FG condition). (f) Multi-electrode with fog droplets coming from outside. Red ball and silver ball represent charged droplet and neutral droplet, respectively.

    where, ε is relative permittivity, ε0is dielectric constant of vacuum,E0is electric field strength in the ion transport region,dpis droplet diameter and t0is a time constant related to ion concentration,electronic charge and ion mobility.It is generally believed that when charging time t=10t0, the droplet charge reaches a saturation value. The droplet’s saturation charge is

    2.2. Force of the droplet

    Figure 1 shows the force states of fog droplets under various working conditions. The main forces include

    where,Feis electric field force,Fdis the drag force of incoming flow,Fris the air resistance of a droplet,Fiis the drag force of ion wind[39],q is amount of droplet charge,Epis the collecting electric field strength,μ is aerodynamic viscosity, dpis droplet size, u1is incoming wind speed, u is fog droplet velocity, ρ is the density of air and u2is the speed of the ion wind.

    According to the force analysis of droplets in figures 1(b)and(c),it is easy to obtain the motion equation of charged fog droplets in an electric field:

    where m is the mass of a fog droplet.

    In the wire-mesh electrode, when fog droplets enter the electric field from the high-voltage electrode,the electric field force of fog droplets has the same direction as drag force, as shown in figure 1(b). Therefore, the droplets cannot be decelerated in the electric field. When the droplets enter the electric field from the ground electrode,the electric field force of droplets is in the opposite direction from the drag force,as shown in figure 1(c). The fog droplets may decelerate, even retrace. When fog droplet velocity u reduces to zero, the fog droplet reaches the farthest position, and the decelerating distance of the fog droplet passing through the ground electrode is defined as intercepting distance L.

    In order to simplify the calculation of L, the amount of charge when the droplet enters the electric field is considered to be saturated. Substituting equation (3) to equation (6) into equation (7), and integrating them, the velocity equation of fog droplets in the electric field can be obtained:

    The moment when the fog droplet passes the ground electrode is defined as t=0. By further integrating the fog droplet velocity u, the intercepting distance in which the droplets decelerate in the electric field can be obtained.It can be used to estimate the spacing of the interception region of multi-electrode structure.

    Figure 2. Schematic diagram of the experimental setup. According to the fog direction, the electrode order can be wire-mesh or multielectrode. The high-voltage electrodes are made of wires and the ground electrode is made of a stainless steel metal mesh.

    Table 2.Summary of the working conditions of the wire-mesh electrodes and the multi-electrode setup. The working conditions of multielectrode collection of droplets have various intercepting voltages and intercepting electrode spacings.

    3. Experiment and discussion

    3.1. Experimental equipment and working conditions

    As shown in figure 2, the experimental device consists of an insulated frame, an insulator and an electrode. There are two high-voltage electrodes on both sides and a ground electrode in the middle. As the high-voltage electrode, the wire electrode is made of 0.05 mm stainless steel wire with wire spacing of 4 cm.The ground electrode is made of a stainless steel metal mesh, and has the same mesh size as a traditional fog mesh for fog-collection rate comparison. The size of the electrode frame is 25 cm×25 cm, and the effective collection area of the electrode is 20 cm×20 cm.In order to make the droplets coagulated on the electrode fall off as much as possible to prevent blocking the mesh and affecting collection, there is superhydrophobic coating on the ground electrode. All electrodes are fixed on the insulation frame by using four insulators,and the high-voltage electrodes on both sides can move by the sliding slot. The ultrasonic humidifier(HQ-JS130H, HaoQi) is used to generate fog droplets. A beaker,an electronic balance,a particle diameter spectrometer(PW180-8,Shandong NKT)and a microammeter are adopted to measure the collection rate,fog droplet particle size and the current through the ground electrode under various working conditions. The working conditions of the experimental device are summarized in table 2. When the working condition is FH or FG, the arrangement of electrodes is shown in figure 3. The electrodes used in both cases are wire-mesh electrodes.The difference is that in the FH condition,the fog enters the electric field from the wire electrode (high-voltage electrode), while in the FG condition, the fog-charging mesh electrode (ground electrode) enters the electric field. When the working condition is multi-electrode, the electrode equipment is shown in figure 4, and the electrodes are wiremesh-wire electrodes. The two wire electrodes are, respectively, a charging electrode and an intercepting electrode,both of which are connected to a negative high-voltage power supply. Between the two electrodes is the mesh electrode(ground electrode). The fog enters the electric field from the charged electrode.

    3.2. Collection rate of wire-mesh electrodes

    Figure 5 shows the relationship between the droplet collection rate and voltage of the wire-mesh electrode under FH working conditions. Obviously, before the voltage reaches the corona initiation voltage, the ground electrode mesh acts as an ordinary fog mesh to collect the droplets, and the collection rate is only 2-4 g h-1. In this case, the droplets are collected only by the collision between the droplets and the mesh, and the efficiency is extremely low,as shown in figure 3(II).After corona discharge activates, the collection rate increases significantly with the voltage. This is because corona discharge can charge the fog droplets and drive them to the ground electrode under the action of the electric field.In other words,the charges carried by droplets and the electric field increase the collection area of the mesh, as shown in figure 3(III). In addition, the charged droplets can form an electric field with the ground electrode, which is superimposed on the electric field of the corona discharge, which further strengthens the ability of the mesh wires to capture droplets [40]. This result indicates that corona discharge plays a positive role in improving the collection rate of fog droplets.

    Figure 3.I is a schematic diagram of the experimental device for collecting fog with a wire-mesh electrode.II and III are schematic diagrams of the force without and with the fog droplets charged [30]. (a) and (b) represent the fogging directions of the wire-mesh electrode under different working conditions,(a)represents that the fog enters the electric field from the high-voltage electrode(FH),(b)represents that the fog enters the electric field from the ground electrode (FG). The red and silver balls represent charged droplets and neutral droplets,respectively. Purple lines represent the trajectory of the droplet.

    Figure 4. Schematic diagram of the experimental device for collecting fog with a multi-electrode device. Red and silver balls represent charged droplets and neutral droplets, respectively. The velocity of the charged droplets after being accelerated by the electric field is 2.075-3.15 m s-1.

    As the voltage increases,the collection rate appears to be saturated, which is consistent with the results of previous studies [30]. The saturated collection rate is 80-140 g h-1,which is 40-70 times the fog mesh collection rate.The reason for the saturation value of the collection rate may be that electric field force Fe, drag force of incoming flow Fdand drag force of ion wind Fican accelerate fog droplets, but air resistance of droplet Fralso increases with the speed.Finally,the balance of the four forces has led to no further increase in the collection rate [30]. In addition, the larger the electrode spacing,the higher the voltage required for the collection rate to reach the saturation value. Note that the experimental cutoff voltages under various electrode spacing are derived from the experimental breakdown voltage or maximum output voltage of power supply.

    Figure 5. Collection rate of wire-mesh electrodes with various electrode spacings under the FH condition.

    Although the wire-mesh electrode can increase the collection rate of the fog mesh under the FH condition, the fog can only pass through the mesh once.This means that the fog mesh can only collect fog droplets once,and there will still be a large number of fog droplets passing through the fog mesh.According to previous research, we know that the factors affecting the collection rate of droplets are not only the charge rate, but also the collection area and the driving speed[28,31,41].Flow field and electric field are the main factors that affect the above two factors. Thus, inspired by the electrostatic precipitator, the number of times that fog passes through the ground electrode can be improved by turbulence,so as to increase the collection area [27, 41]. Therefore, a scheme of collecting fog droplets using a wire-mesh electrode under the FG condition is proposed [42].

    The results for the collection rate of a wire-mesh electrode under the FG working condition are shown in figure 6.Similar to FH, when the voltage does not reach the corona initiation voltage, only the ground electrode mesh is used to collect the droplets, and the collection rate is low. However,after the applied voltage reaches the corona initiation voltage,the collection rate first increases and then decreases with the applied voltage. The peak value is 60-80 g h-1, which is 20-40 times the collection rate of ordinary fog mesh, but is lower than FH. This phenomenon can be explained by number of times the droplets pass through the mesh and the charges carried by droplets. When the fog droplet passes through the mesh,it is collected by the ground electrode once,and this case is regarded as fog mesh collection. Then, the droplets are charged in the region with a high electric field.Under the action of flow field and electric field, charged droplets return to the ground electrode again to achieve secondary collection,which can be seen in the droplet trajectory shown in figure 7(b)at 20 kV.Thus,the turbulence caused by corona discharge does increase the number of times the droplets are collected. However, due to the low concentration of charged particles near the ground electrode, the charges carried by fog droplets are insufficient.Therefore,the maximum collection rate of FG is lower than that of FH.

    Figure 6.Collection rate of a wire-mesh electrode with various electrode spacings under the FG condition.

    In addition, the collection rate peak is the balance result of fog speed and reverse motion caused by ionic wind and electric field. For low voltage, the droplets can enter the electric field and return to the ground electrode under the weak action of electric field force and ion wind to complete the collection of droplets, as shown in figure 7(b) at 20 kV.For high voltage, the strong ion wind prevents the droplets from reaching the ground electrode, resulting in a rapid decrease in the collection rate, as shown in figure 7(b) at 25 kV. Note that the fog and ionic wind are in the same direction for FH as shown in figure 7(a), thus there is no obvious peak in figure 5.

    3.3. Collection rate of the multi-electrode structure

    From the above results, it can be seen that the wire-mesh electrode can fully charge the droplets under the FH condition, but it can only be collected once. Under the FG condition,although the wire-mesh electrode can collect the droplets multiple times, the charge rate of the droplets is low. Therefore, a scheme of collecting fog droplets with a multi-electrode structure is proposed, as shown in figure 4. The multielectrode structure includes a charging electrode, an intercepting electrode and a ground electrode.The three electrodes divide the space into two regions: a charging region and an intercepting region. The charging region can ensure the high charging rate of fog droplets, and the intercepting region can generate turbulence, which makes the first uncollected droplets return to the ground electrode to realize the second collection.

    The electrode spacing of the charging region can be set according to the previous experimental results. In order to reduce power consumption and insulation requirements, the electrode spacing of the charging region can be set to 4 cm.It can be seen from figure 5 that when the voltage is 14 kV,the FH collection rate of the wire-mesh electrode reaches saturation. Therefore, the voltage of the charging electrode can be set to 14 kV.For the intercepting region,the electrode spacing can be determined based on the calculation result of equation(11).As shown in figure 8,the particle size range of the fog droplets generated by the ultrasonic humidifier is 1-15 μm.The droplets with various charge rates move in the electric field for a distance of 0.5-1.5 cm in this size range.When setting the electrode spacing, a certain margin is considered to ensure the effective interception of droplets.Therefore, the electrode spacing in the intercepting region should be no less than 4 cm.

    Figure 7.Droplet trajectory under different working conditions when the wire-mesh electrode spacing is 8 cm. (a) FH, (b) FG.

    Figure 9 shows the droplet collection rate of the multielectrode structure under different intercepting region spacings when the charging region spacing is 4 cm and the charging voltage is 14 kV.Similar to the FG condition of the wire-mesh electrode,there is a peak in the collection rate.The maximum collection rate is 210-225 g h-1, which is 2-4 times that of the wire-mesh electrode. However, at the initial stage of voltage applied in the intercepting region, the collection rate is 75-110 g h-1. The main reason for this phenomenon is that the intercepting region in this case has no obvious intercepting effect on the droplets, and this case is equivalent to the FH working condition of the wire-mesh electrode.As the intercepting voltage increases,the collection rate first increases and then decreases. This trend can be explained by that when the intercepting voltage is low, the intercepting region can return the droplets that were not collected by the ground electrode for the first time to the ground electrode to form a secondary collection.In addition,after the droplets enter the interception region, since the intercepting electrode can also generate gas ions in the ionization region,the droplets that are not sufficiently charged in the charging region can supplement the charge in the interception region.However, when the intercepting voltage is high enough, the intensity of ion wind generated in the intercepting region gradually increases,and the droplets cannot reach the ground electrode, resulting in a rapid drop in collection rate.

    Figure 8.Estimation of droplet deceleration distance.(a)The volume ratio of droplet size distribution produced by the ultrasonic humidifier,(b)the deceleration distance of the charged droplet in the electric field.

    Figure 9.Collection rate of the multi-electrode structure with various electrode spacings and intercepting voltages.

    Figure 10.Comparison of the maximum collection rate of different electrode structures. (represents the ordinary fog mesh,represents the wire-mesh electrode under FH,represents the wire-mesh electrode under FG, andrepresents the multielectrode structure).

    In addition, the maximum collection rate of various electrode structures and the corresponding power consumption are compared. As shown in figure 10, the droplet collection rates of the fog mesh, FH, FG and multi-electrode structures are 2-3 g h-1, 80-140 g h-1, 60-80 g h-1and 210-220 g h-1, respectively. Obviously, corona discharge strengthens the fog mesh’s ability to collect droplets, and the multi-electrode structure increases the collecting times of the fog mesh,resulting in a huge increase in its collection area.It can be seen in figure 11 that the power consumption increases with electrode spacing, regardless of electrode structure. The power consumption of the electrode under the three working conditions are 0.67-1.67 W, 0.22-0.43 W and 1.67-2.5 W,respectively. They are economical and efficient, compared with desalination by distillation, and electrodialysis. The power consumption of the multi-electrode structure is significantly higher than those of the others, because both the charging region and the intercepting region consume electric energy.Figure 11 also shows the ratio of power to maximum collection rate. This ratio characterizes the electrical energy consumed per unit collection rate.The ratios in the three cases are 0.0057-0.019, 0.0036-0.0058 and 0.00745-0.0118,respectively. Although the power required per unit collection rate for the multi-electrode structure is the highest,it is only in the order of 10-3. Considering the collection rate and power consumption comprehensively, the optimal electrode spacing in the intercepting region can be set as 4 cm.

    Figure 11.Power consumption for maximum collection efficiency and the ratio of power to maximum collection rate in the three cases.P/C represents the ratio of power to maximum collection rate.

    For the spacing of the charged region, the discharge characteristics and the collection rate need to be comprehensively considered. In addition to the influence of the electrode structure, the corona discharge is also affected by the droplets. After the droplet enters the electric field, it affects the discharge in three aspects: ion mobility, electric field and current.

    For the ion mobility, droplets enter the electric field region and change the gas environment (gas density and relative humidity) around the electrodes. According to previous studies, the ion mobility can be expressed as:

    where, K is the ion mobility,λˉ is the mean free path of the ion,vˉ is the average velocity of thermal motion, and moand M are the masses of ions and gas molecules,respectively.The ionic mobility of the fog environment is as follows [40]:

    where, mais the dry air density and mhis the water vapor content of the air at a relative humidity of 100%; Mais the relative molecular mass of air.Under normal temperature and pressure, the air density is 1.2 kg m-3. When the fog enters the electric field, the water vapor content is about 20 g m-3.Therefore, bringing in equations(13)and(14),it can be seen that the ion mobility is slightly reduced.Specifically,it can be obtained that the ion mobility after fogging is about 98% of that in a dry environment.The reason for this phenomenon is that hydrated ions are generated by corona discharge in a foggy environment [43].

    For the electric field strength, the droplets entering into the electrode area will affect the roughness coefficient of electrode surface,according to Peek’s empirical formula[40]:

    where, r is the radius of wire electrode and m is the surface roughness factor.In a dry environment,m is generally 0.5.In foggy environment, the value of m is generally taken as 0.44[40]. The droplets therefore reduce the onset electric field strength of the electrodes. After the fog is cleared, the onset field strength is about 0.88 times that of the dry environment.The corona inception electric field is reduced, which makes the electrode spacing too small to be more prone to breakdown. In addition, an electric field is formed between the charged droplets and the ground electrode, which superimposes in the same direction the electric field generated by the corona discharge to form a synthetic electric field. The smaller the electrode spacing, the greater the effect of the synthetic electric field on the discharge, which makes the electrodes more susceptible to breakdown. For discharge current,it is closely related to ion mobility[44].According to equations (13) and (14), the ion mobility in the fog environment is slightly reduced. Therefore, its discharge current will also decrease. However, in a dense fog environment,the ion mobility is only reduced by 2%,so the effect of fog droplets on the current is not significant. Comprehensively considering the collection rate, power consumption,compactness of device and so on, the optimal electrode spacing in the intercepting region is set as 4 cm.

    Since the intercepting region and the charging region have the same electrode spacing (4 cm here), the multi-electrode structure can freely adjust the voltage switching direction of the two regions. Therefore, from this perspective, the multi-electrode structure can also collect fog droplets regardless of fog direction.

    In summary, when fog is collected using a multi-electrode structure, the fog intercepting the voltage near the ground electrode by adjusting the voltage of the intercepting electrode achieves the highest collection rate.

    4. Conclusion

    A novel multi-electrode structure with a charging region and an intercepting region is put forward in this paper to improve the collection rate of fog droplets. In this paper, the force equation and the intercepting distance equation of a charged fog droplet in an electric field are given, which provides guidance for the design of electrodes. Then, the collection rates of a wire-mesh electrode under different working conditions and a multi-electrode structure are compared, and the maximum collection rate and power consumption in the above cases are discussed. Finally, according to the theoretical calculation and experimental results, the optimal multielectrode structure is proposed. The innovative electrode structure shows the advantages of high efficiency and independent fog direction. The specific conclusions are as follows:

    (1) The maximum fog droplet collection rate of the wiremesh electrode under the FH condition is 80-140 g h-1.Although it can fully charge fog droplets, the ground electrode can only collect fog droplets once.

    (2) The maximum fog droplet collection rate of the wiremesh electrode under the FG condition is 60-80 g h-1.This condition produces turbulence and enables multiple collection of fog droplets. However, due to the low concentration of charged particles near the ground electrode, the charge rate of fog droplets is also low.

    (3) For the multi-electrode structure, the maximum collection rate can reach 210-220 g h-1, which is 100-150 times that of the fog mesh and 2-4 times that of the wire-mesh electrode.

    (4) The motion distance equation of charged fog droplets in an electric field can be used to guide the design of multi-electrode structures and to ensure low power consumption and efficient collection of fog droplets.

    (5) The design principles of the multi-electrode structure are that the charging region ensures full charge of the droplets and the intercepting region effectively intercepts uncollected droplets.

    In future work, some issues need to be studied, such as the choice of electrode material, electrode size, the arrangement of multilayer ground electrodes and the flow field distribution of the multi-electrode structure.

    Acknowledgments

    This work is supported by the National Key Research and Development Program of China(Nos.2016YFC0401002 and 2016YFC0401006),and National Natural Science Foundation of China (Nos. 51577080 and 51821005).

    ORCID iDs

    Chuan LI (李傳) https://orcid.org/0000-0003-4761-5160

    猜你喜歡
    楊勇張明李家
    楊勇書法作品
    “稱霸”試衣間
    Insights into the regulation mechanism of ring-shaped magnetoelectric energy harvesters via mechanical and magnetic conditions?
    Quantum nature of proton transferring across one-dimensional potential fields?
    故鄉(xiāng)
    牡丹(2020年3期)2020-03-02 02:20:17
    李家正 釉·畫
    二手貨
    數(shù)到一萬捉迷藏
    時(shí)鐘是彎成一圈的尺子
    The variations of suspended sediment concentration in Yangtze River Estuary*
    av卡一久久| 九九在线视频观看精品| 精品久久久久久久久亚洲| 日本猛色少妇xxxxx猛交久久| 色播亚洲综合网| 免费在线观看成人毛片| 欧美高清成人免费视频www| 成年女人看的毛片在线观看| 爱豆传媒免费全集在线观看| 美女内射精品一级片tv| 国产单亲对白刺激| 日韩国内少妇激情av| 亚洲精品自拍成人| 综合色av麻豆| 三级国产精品片| 午夜免费观看性视频| 老司机影院毛片| 黄片wwwwww| a级毛片免费高清观看在线播放| 欧美成人a在线观看| 一级av片app| 在线播放无遮挡| av网站免费在线观看视频 | 超碰av人人做人人爽久久| 亚洲成人久久爱视频| 成人美女网站在线观看视频| 亚洲精品aⅴ在线观看| 亚洲精品色激情综合| 一区二区三区乱码不卡18| 内地一区二区视频在线| 最近中文字幕2019免费版| av国产免费在线观看| av免费在线看不卡| 一级毛片久久久久久久久女| 男人和女人高潮做爰伦理| 亚洲图色成人| 高清午夜精品一区二区三区| 国产av不卡久久| 2021少妇久久久久久久久久久| 直男gayav资源| 色综合色国产| 久久久久久久久大av| 午夜福利在线观看吧| 国产91av在线免费观看| 欧美区成人在线视频| 五月伊人婷婷丁香| 大片免费播放器 马上看| 国产91av在线免费观看| 在线天堂最新版资源| 国产成人免费观看mmmm| 国产精品嫩草影院av在线观看| 自拍偷自拍亚洲精品老妇| 亚洲内射少妇av| 在线 av 中文字幕| 免费看不卡的av| 亚洲精品亚洲一区二区| 在线观看美女被高潮喷水网站| 建设人人有责人人尽责人人享有的 | 国产亚洲午夜精品一区二区久久 | 青春草视频在线免费观看| 肉色欧美久久久久久久蜜桃 | 午夜福利视频1000在线观看| 精品久久久噜噜| 欧美xxⅹ黑人| a级毛片免费高清观看在线播放| 97精品久久久久久久久久精品| 80岁老熟妇乱子伦牲交| 亚洲精品日韩在线中文字幕| 欧美性猛交╳xxx乱大交人| 亚洲精品成人av观看孕妇| 免费看不卡的av| 国产av在哪里看| 99九九线精品视频在线观看视频| 亚洲久久久久久中文字幕| 免费无遮挡裸体视频| 国内揄拍国产精品人妻在线| 亚洲综合精品二区| 日韩视频在线欧美| 精品人妻偷拍中文字幕| 国产高清国产精品国产三级 | 在线免费十八禁| 国产欧美日韩精品一区二区| 亚洲av中文av极速乱| 精品一区在线观看国产| 午夜福利成人在线免费观看| 亚洲电影在线观看av| 亚洲av免费在线观看| 男人和女人高潮做爰伦理| 成年女人在线观看亚洲视频 | 淫秽高清视频在线观看| 韩国高清视频一区二区三区| 国产精品一区二区三区四区免费观看| 国产欧美另类精品又又久久亚洲欧美| 99热6这里只有精品| 18+在线观看网站| 免费看a级黄色片| 欧美日韩视频高清一区二区三区二| 国产69精品久久久久777片| 欧美+日韩+精品| 久久精品国产自在天天线| 国产免费视频播放在线视频 | 夫妻午夜视频| 免费看av在线观看网站| 大香蕉久久网| 亚洲国产欧美在线一区| 国产视频内射| 免费av不卡在线播放| 一本—道久久a久久精品蜜桃钙片 精品乱码久久久久久99久播 | 久久人人爽人人片av| 久久久久免费精品人妻一区二区| 热99在线观看视频| 男人和女人高潮做爰伦理| 只有这里有精品99| 最新中文字幕久久久久| 日韩一区二区视频免费看| 九九在线视频观看精品| 两个人的视频大全免费| 亚洲熟妇中文字幕五十中出| 一区二区三区乱码不卡18| 18禁动态无遮挡网站| 国产在线男女| av在线蜜桃| 亚洲av中文字字幕乱码综合| 夜夜看夜夜爽夜夜摸| 久久99热这里只有精品18| 国产高清国产精品国产三级 | 久久久精品免费免费高清| 三级男女做爰猛烈吃奶摸视频| 国产精品国产三级国产av玫瑰| 人妻少妇偷人精品九色| 成人高潮视频无遮挡免费网站| 亚洲美女视频黄频| 国产黄色视频一区二区在线观看| 国产伦一二天堂av在线观看| 日韩三级伦理在线观看| 日本黄色片子视频| 国产成人精品福利久久| 日韩av免费高清视频| 建设人人有责人人尽责人人享有的 | 欧美成人一区二区免费高清观看| 精品久久久久久久人妻蜜臀av| 街头女战士在线观看网站| 国精品久久久久久国模美| 乱码一卡2卡4卡精品| 一区二区三区高清视频在线| 国产高清有码在线观看视频| 精品国内亚洲2022精品成人| 黄片wwwwww| 99久久精品国产国产毛片| 天堂av国产一区二区熟女人妻| 日产精品乱码卡一卡2卡三| 成人午夜高清在线视频| 黄色欧美视频在线观看| 少妇人妻一区二区三区视频| 午夜精品在线福利| 少妇熟女aⅴ在线视频| 久久久久久久久大av| 乱系列少妇在线播放| 国产成人一区二区在线| 97超视频在线观看视频| 婷婷色av中文字幕| 国产一级毛片七仙女欲春2| 国产亚洲最大av| 亚洲av不卡在线观看| 国产熟女欧美一区二区| 偷拍熟女少妇极品色| 亚洲不卡免费看| 国产女主播在线喷水免费视频网站 | 一级爰片在线观看| av国产免费在线观看| 禁无遮挡网站| 亚洲最大成人中文| 床上黄色一级片| 婷婷色av中文字幕| 国产精品综合久久久久久久免费| 亚洲精品影视一区二区三区av| 青春草视频在线免费观看| 亚洲自拍偷在线| 美女被艹到高潮喷水动态| 汤姆久久久久久久影院中文字幕 | 免费人成在线观看视频色| 91aial.com中文字幕在线观看| 欧美成人一区二区免费高清观看| 特级一级黄色大片| 日韩av免费高清视频| 日产精品乱码卡一卡2卡三| 久久99热6这里只有精品| 三级经典国产精品| 老司机影院毛片| 波野结衣二区三区在线| 午夜福利在线观看免费完整高清在| 熟妇人妻久久中文字幕3abv| 免费av不卡在线播放| 亚洲精品视频女| 婷婷六月久久综合丁香| 97在线视频观看| 99热这里只有是精品在线观看| 国产成人一区二区在线| 97超视频在线观看视频| 国产精品久久久久久久久免| 日韩欧美 国产精品| 观看美女的网站| 乱码一卡2卡4卡精品| 日韩av在线免费看完整版不卡| 免费观看性生交大片5| 老女人水多毛片| 亚洲av国产av综合av卡| 国产在视频线精品| 国产探花极品一区二区| 精品久久久久久久久亚洲| 乱人视频在线观看| 亚洲av国产av综合av卡| 少妇的逼好多水| 精品人妻熟女av久视频| 中文字幕av在线有码专区| 亚洲乱码一区二区免费版| 一级二级三级毛片免费看| 亚洲人与动物交配视频| 久久精品熟女亚洲av麻豆精品 | 久久人人爽人人爽人人片va| 欧美日韩国产mv在线观看视频 | 亚洲自拍偷在线| 在线观看美女被高潮喷水网站| 狂野欧美白嫩少妇大欣赏| 赤兔流量卡办理| 亚洲av中文av极速乱| 国产精品爽爽va在线观看网站| 亚洲成人一二三区av| 91精品一卡2卡3卡4卡| 日本一二三区视频观看| 高清在线视频一区二区三区| 人人妻人人澡人人爽人人夜夜 | 最后的刺客免费高清国语| 中文在线观看免费www的网站| www.av在线官网国产| 亚洲精品成人久久久久久| av一本久久久久| 久久人人爽人人片av| 中文字幕av在线有码专区| 国产免费一级a男人的天堂| 亚洲国产精品专区欧美| 午夜福利视频1000在线观看| 麻豆成人av视频| 亚洲av免费在线观看| 国产精品久久久久久久久免| 蜜臀久久99精品久久宅男| 丰满少妇做爰视频| 少妇高潮的动态图| 18禁在线播放成人免费| 美女被艹到高潮喷水动态| 免费播放大片免费观看视频在线观看| 久久99热6这里只有精品| 亚洲欧美一区二区三区黑人 | 高清午夜精品一区二区三区| 女人十人毛片免费观看3o分钟| 久久精品熟女亚洲av麻豆精品 | 国产精品伦人一区二区| 久久精品人妻少妇| 国产精品嫩草影院av在线观看| 日本熟妇午夜| 日韩强制内射视频| 成人综合一区亚洲| 美女国产视频在线观看| 99久国产av精品| 中文天堂在线官网| 国内精品宾馆在线| 在线a可以看的网站| 一级二级三级毛片免费看| 欧美97在线视频| 久久精品久久久久久噜噜老黄| 国产美女午夜福利| 午夜福利在线观看免费完整高清在| 亚洲欧美日韩卡通动漫| 国产午夜精品论理片| 亚洲av福利一区| 精品99又大又爽又粗少妇毛片| 久久精品人妻少妇| 能在线免费观看的黄片| 三级男女做爰猛烈吃奶摸视频| 国产精品女同一区二区软件| 少妇的逼水好多| 亚洲av.av天堂| 久热久热在线精品观看| .国产精品久久| av在线天堂中文字幕| 老师上课跳d突然被开到最大视频| 亚洲欧美日韩无卡精品| 久久精品国产亚洲网站| 成人亚洲欧美一区二区av| 国产综合精华液| 精品国内亚洲2022精品成人| 亚洲国产av新网站| 欧美日韩亚洲高清精品| 哪个播放器可以免费观看大片| 精品人妻熟女av久视频| 日本-黄色视频高清免费观看| 欧美激情在线99| 日韩在线高清观看一区二区三区| 亚洲av免费在线观看| 亚洲图色成人| 在线观看一区二区三区| 啦啦啦啦在线视频资源| 亚洲精品久久久久久婷婷小说| 久久国内精品自在自线图片| 在线天堂最新版资源| 国精品久久久久久国模美| 久久久久免费精品人妻一区二区| 91久久精品国产一区二区三区| 夜夜爽夜夜爽视频| 日韩制服骚丝袜av| 蜜桃久久精品国产亚洲av| 亚洲国产精品sss在线观看| 国产美女午夜福利| 中文字幕av成人在线电影| 男插女下体视频免费在线播放| 女人久久www免费人成看片| 青春草亚洲视频在线观看| 成年女人在线观看亚洲视频 | 在现免费观看毛片| 欧美xxⅹ黑人| 久久午夜福利片| 日韩欧美一区视频在线观看 | 亚洲欧美清纯卡通| 亚洲国产成人一精品久久久| 日韩成人伦理影院| 国产一区二区三区av在线| 水蜜桃什么品种好| 中文天堂在线官网| 好男人在线观看高清免费视频| av福利片在线观看| 亚洲婷婷狠狠爱综合网| 女人久久www免费人成看片| 久久99热这里只频精品6学生| 久久久欧美国产精品| 午夜激情久久久久久久| 成人美女网站在线观看视频| 精品午夜福利在线看| 国产乱人偷精品视频| 搡女人真爽免费视频火全软件| 女人被狂操c到高潮| 亚洲精品视频女| av女优亚洲男人天堂| 免费观看在线日韩| 亚洲最大成人手机在线| 国产精品一区二区性色av| 18禁裸乳无遮挡免费网站照片| 伦理电影大哥的女人| 69人妻影院| 久久久久久久久久成人| 一个人免费在线观看电影| 伦精品一区二区三区| 国产精品女同一区二区软件| 伊人久久精品亚洲午夜| 色播亚洲综合网| 人妻制服诱惑在线中文字幕| 国产av国产精品国产| 亚洲性久久影院| 免费大片18禁| 久久精品国产亚洲av涩爱| 免费大片18禁| 国产成人精品福利久久| 少妇猛男粗大的猛烈进出视频 | 精品人妻视频免费看| 成年免费大片在线观看| 亚洲成人精品中文字幕电影| 成人二区视频| 97人妻精品一区二区三区麻豆| 麻豆av噜噜一区二区三区| 久久久午夜欧美精品| 欧美xxxx性猛交bbbb| 亚洲av中文av极速乱| 少妇熟女欧美另类| 自拍偷自拍亚洲精品老妇| 美女高潮的动态| 人人妻人人澡欧美一区二区| 99热全是精品| 亚洲av国产av综合av卡| 亚洲一区高清亚洲精品| 亚洲乱码一区二区免费版| 女人被狂操c到高潮| 91av网一区二区| 超碰97精品在线观看| 街头女战士在线观看网站| 青春草国产在线视频| 蜜臀久久99精品久久宅男| 成年免费大片在线观看| 精品人妻视频免费看| 欧美 日韩 精品 国产| 免费观看a级毛片全部| 又爽又黄无遮挡网站| 日本午夜av视频| 国产v大片淫在线免费观看| 国产 一区精品| 蜜桃亚洲精品一区二区三区| 又大又黄又爽视频免费| 精品久久久久久久久久久久久| 久久久成人免费电影| av线在线观看网站| 五月玫瑰六月丁香| 亚洲人成网站在线观看播放| 乱人视频在线观看| 国产成人精品福利久久| 一级毛片我不卡| 色网站视频免费| 插阴视频在线观看视频| 亚洲av日韩在线播放| 亚洲成人久久爱视频| 免费高清在线观看视频在线观看| 特大巨黑吊av在线直播| 九九久久精品国产亚洲av麻豆| 中文字幕免费在线视频6| 成人国产麻豆网| 亚洲天堂国产精品一区在线| 亚洲国产欧美在线一区| 天堂av国产一区二区熟女人妻| 国产精品爽爽va在线观看网站| 亚洲,欧美,日韩| 69av精品久久久久久| h日本视频在线播放| 国产精品久久视频播放| 天堂中文最新版在线下载 | 亚洲国产成人一精品久久久| 亚洲av男天堂| 欧美97在线视频| a级毛片免费高清观看在线播放| 欧美高清成人免费视频www| 成人漫画全彩无遮挡| 熟妇人妻久久中文字幕3abv| 午夜福利在线观看吧| 亚洲欧美一区二区三区黑人 | www.色视频.com| 国产大屁股一区二区在线视频| 久久人人爽人人爽人人片va| 亚洲无线观看免费| 免费观看无遮挡的男女| .国产精品久久| 大香蕉97超碰在线| 男女啪啪激烈高潮av片| 建设人人有责人人尽责人人享有的 | 日韩大片免费观看网站| 大又大粗又爽又黄少妇毛片口| 久久久久久国产a免费观看| 免费看不卡的av| 欧美日韩视频高清一区二区三区二| 麻豆国产97在线/欧美| 日韩三级伦理在线观看| 观看免费一级毛片| 免费在线观看成人毛片| 色网站视频免费| 亚洲aⅴ乱码一区二区在线播放| 麻豆成人av视频| 国国产精品蜜臀av免费| 亚洲在线自拍视频| 亚洲欧美日韩无卡精品| 人妻少妇偷人精品九色| 国产av码专区亚洲av| 卡戴珊不雅视频在线播放| 国产成人一区二区在线| 亚洲精品国产成人久久av| 中文字幕久久专区| 久久久成人免费电影| 欧美日韩亚洲高清精品| 亚洲欧美精品专区久久| 禁无遮挡网站| 80岁老熟妇乱子伦牲交| 国产 一区精品| 国产精品久久久久久精品电影小说 | 久久久午夜欧美精品| 插阴视频在线观看视频| 欧美人与善性xxx| 有码 亚洲区| 国产大屁股一区二区在线视频| 久久精品人妻少妇| 精品久久久精品久久久| 亚洲欧美成人精品一区二区| 国产精品一及| 亚洲一区高清亚洲精品| 男的添女的下面高潮视频| 大片免费播放器 马上看| 国产伦在线观看视频一区| 国产成人福利小说| 国产在视频线在精品| 亚洲美女视频黄频| 嘟嘟电影网在线观看| 久久99蜜桃精品久久| 欧美3d第一页| 亚洲精品成人久久久久久| 建设人人有责人人尽责人人享有的 | 国产成人精品婷婷| 亚洲图色成人| 91av网一区二区| 国产视频内射| 22中文网久久字幕| 一本一本综合久久| 三级男女做爰猛烈吃奶摸视频| 女人十人毛片免费观看3o分钟| 欧美高清成人免费视频www| 亚洲熟妇中文字幕五十中出| 国产高清三级在线| 亚洲国产av新网站| 久久久久久久大尺度免费视频| 午夜福利在线在线| 少妇人妻精品综合一区二区| 91久久精品电影网| 五月天丁香电影| 国产av码专区亚洲av| 精品久久久久久久末码| 伦理电影大哥的女人| 免费观看性生交大片5| 搞女人的毛片| 国产精品精品国产色婷婷| 少妇的逼水好多| 淫秽高清视频在线观看| 亚洲无线观看免费| 搡老妇女老女人老熟妇| 女人久久www免费人成看片| 91久久精品国产一区二区成人| 日韩国内少妇激情av| 日韩强制内射视频| 亚洲丝袜综合中文字幕| 亚洲av.av天堂| 日日啪夜夜爽| 亚洲国产av新网站| av线在线观看网站| 少妇丰满av| 国产精品蜜桃在线观看| 久久99蜜桃精品久久| 亚洲精品日本国产第一区| 欧美三级亚洲精品| 男插女下体视频免费在线播放| 免费av不卡在线播放| 欧美成人一区二区免费高清观看| 成人亚洲精品一区在线观看 | 中文资源天堂在线| a级毛片免费高清观看在线播放| 国产精品不卡视频一区二区| 视频中文字幕在线观看| 国产精品久久久久久久电影| 建设人人有责人人尽责人人享有的 | 成人一区二区视频在线观看| 丝袜美腿在线中文| 中文字幕av成人在线电影| 欧美高清性xxxxhd video| 一边亲一边摸免费视频| 人妻制服诱惑在线中文字幕| 国产精品一区www在线观看| 3wmmmm亚洲av在线观看| 久久这里有精品视频免费| 欧美zozozo另类| 成人毛片60女人毛片免费| 亚洲av电影不卡..在线观看| 国产伦精品一区二区三区视频9| av黄色大香蕉| 国产不卡一卡二| 亚洲av电影在线观看一区二区三区 | 久久精品综合一区二区三区| 在线播放无遮挡| 亚洲欧美日韩卡通动漫| 在线a可以看的网站| 一本久久精品| 日韩av不卡免费在线播放| 非洲黑人性xxxx精品又粗又长| 国产永久视频网站| 一级黄片播放器| 黄片无遮挡物在线观看| 久久草成人影院| 美女大奶头视频| 精品久久久久久成人av| 搡女人真爽免费视频火全软件| 日韩视频在线欧美| 成人午夜高清在线视频| 国产爱豆传媒在线观看| 伊人久久国产一区二区| 免费大片18禁| 两个人的视频大全免费| av线在线观看网站| 欧美一区二区亚洲| 欧美xxⅹ黑人| 精品久久久久久成人av| 最近视频中文字幕2019在线8| 欧美区成人在线视频| 国产精品一二三区在线看| 美女黄网站色视频| 少妇熟女aⅴ在线视频| 亚洲欧美一区二区三区国产| 国产成人免费观看mmmm| 亚洲,欧美,日韩| 国产人妻一区二区三区在| 久久精品夜夜夜夜夜久久蜜豆| 国产在线男女| 性色avwww在线观看| 97人妻精品一区二区三区麻豆| a级一级毛片免费在线观看| 最后的刺客免费高清国语| 日本色播在线视频| 国产淫语在线视频| av国产久精品久网站免费入址| 亚洲欧美日韩无卡精品| 午夜免费观看性视频| 久久午夜福利片| 亚洲国产精品sss在线观看| 99久久精品一区二区三区| 国语对白做爰xxxⅹ性视频网站| 亚洲乱码一区二区免费版| 久久精品熟女亚洲av麻豆精品 | 亚洲精品一二三| 日本欧美国产在线视频| 欧美bdsm另类| 午夜日本视频在线| 午夜久久久久精精品| 综合色丁香网| 日韩欧美 国产精品| videos熟女内射| 欧美zozozo另类| 只有这里有精品99|