The object of the invention is an electrostatic air filter, in particular for ventilation of air.
There is a common necessity to filtrate ventilation air delivered to zones of human presence or for technological purposes. The problem of air contamination, in particular smog, concerns virtually all urbanised areas. Due to the bad condition of the air, the number of people with allergies of atmospheric origin is quickly increasing. Various techniques are used for elimination of undesired components from the air.
It is common knowledge to use mechanical nonwoven, cyclotron, electrostatic and other filters for the removal of solid particles and aerosols. Various absorbers or catalysts, for instance activated carbon or ozone, are used to remove gaseous contaminants.
Mechanical filters are mainly in the form of suitably thick nonwoven mats assembled in the form of flat, pleated or baggy elements.
Electrostatic filters known in prior art use the phenomena of electrostatic attraction and corona discharge which cause ionisation of air.
Many known electrostatic filters are assembled from numerous elements consisting of corona electrodes which cause heavy ionisation of a gaseous medium (e.g. air) and of earthed collecting electrodes. Due to the impact of a strong electric field which is directed transversely to the direction of air flowing through the filter, electrified solid particles and aerosols are deposited on the collecting electrodes. Electrostatic precipitators of this type are used primarily in the industry for the removal of contaminants created in various technological processes, e.g. chimney smoke, etc.
Industrial electrostatic precipitators are unsuitable for ventilation applications for the following reasons:
Filters for residential premises operating on the basis of electrostatic precipitation are also known—the so-called “air purifiers”—but their efficiency is low due to the necessity to limit the emission of ozone and nitrogen oxides in the order of 20-50%, which is why they operate on the basis of constant recirculation of air in the given room.
An additional problem of very precise filters involves preventing air leakages in a manner which bypasses the filter. Even minimum leakage in the mounting of the filter causes considerable limitation of the maximum attainable performance.
It was an object of the invention to provide an electrostatic air filter having increased efficiency of filtration in relation to the known filters of this kind; the filter having also high absorbability in order to decrease the frequency of maintenance, as well as a compact construction.
It was an additional objective of the invention to provide a filter which would be easy to service, but in which the unfiltered air would not enter the filter outlet due to leakage.
It was also an object of the invention to provide an electrostatic air filter in which the emission of ozone and nitrogen oxides would be limited.
According to the invention, an electrostatic air filter connected to a high voltage source has been developed, comprising an air flow channel having an inlet and an outlet, in which at the air inlet side there is an ion generator comprising at least one corona electrode and at least one cumulative electrode, the corona electrodes and the cumulative electrodes being electrically connected to each other, while the cumulative electrodes are insulated from the corona electrodes, so that corona discharges may occur between the corona electrodes and cumulative electrodes due to a potential difference, the corona discharges causing ionisation of contaminant particles present in the air flowing through the channel.
The filter according to the invention is characterised in that downstream of the ion generator in the air flow channel a separator of contaminant particles is located, comprising an input electrode and an output electrode spaced apart from the input electrode, both electrodes enabling the flow of air therethrough in a direction away from the input electrode towards the output electrode and further to the channel outlet, and in that during the operation of the filter a potential difference exists between the corona electrodes and the input electrode, and another potential difference exists between the input electrode and the output electrode, so that the electric field strength in the space between the input electrode and the output electrode is directed opposite to the electric field strength in the space between the ion generator and the input electrode.
Preferably, the input electrode and the output electrode have a cylindrical shape, so that the output electrode surrounds the input electrode.
The input electrode is preferably adapted to the deposition of contaminant particles thereon; it is most preferably made of a conductive nonwoven or a spongiform material, optionally coated with activated carbon.
Preferably, a filter layer made of a material with low electrical conductivity is located in the space between the input electrode and the output electrode there is.
Preferably, the potential of the corona electrodes and the output electrode is positive, while the potential of the input electrode equals zero.
Optionally, the potential of the corona electrodes and the output electrode is positive, while the potential of the input electrode is negative.
The potential of the corona electrodes and the output electrode may also be negative, while the potential of the input electrode may equal zero.
Possibly, the potential of the corona electrodes and the output electrode is negative, while the potential of the input electrode is positive.
Preferably, the potential of the corona electrode is positive, the potential of the input electrode is negative, while the potential of the output electrode equals zero.
In another embodiment, the potential of the corona electrode may be negative, the potential of the input electrode may be positive, while the potential of the output electrode may equal zero.
Preferably, the air flow channel constitutes a filter housing in which the ion generator and the particle separator are assembled in a manner which is tight and enables the disassembly of the ion generator and the separator for servicing purposes.
Preferably, in the channel housing, between the guides in which the separator is seated, there is at least one opening connecting the space between the guides and the separator to the external surroundings.
Preferably, the filter comprises a pre-filter upstream of the ion generator, for mechanical separation of contaminant particles.
Preferably, the potential difference between the corona electrodes and the cumulative electrodes is adjustable and ranges between 2 and 80 kV.
Preferably, the potential difference between the corona electrodes and the input electrode is greater than the potential difference between the corona electrodes and the cumulative electrodes.
The input electrode and/or the output electrode may have the form of a mesh or perforated sheet metal, possibly of a surface with ribs or folds, or in the form of segments situated at an angle with respect to each other.
Preferably, the potential difference between the input electrode and the output electrode is adjustable and ranges between several and several dozen kV, preferably between 2 and 50 kV.
Preferably, the filter comprises at least two corona electrodes which are connected to each other in series.
In a preferable embodiment, the corona electrodes are in the form of discs and they are placed on an insulator which is preferably located in the shield.
Preferably, the input electrode is rotary, the output electrode comprises a slit, while the insert of the filtering layer is movable on the surface of the rotating input electrode, so that its ends extend through said slit, which enables its replacement.
The primary advantage of the air filter according to the invention is that due to the use of the separator of contaminant particles, relatively small corona discharges occurring in the ion generator are sufficient to achieve effective filtration. This is of great significance since the corona discharges are always accompanied by the undesired production of ozone and nitrogen oxides, as well as electromagnetic disturbance. The ozone and nitrogen oxides, which are created in known industrial electrostatic precipitators, are harmful to the human health and deteriorate the quality of air. In the filter according to the invention, more efficient electrification of solid particles occurs due to the additional impact-based electrification of ions originating from the corona discharge occurring within the space between the corona and cumulative electrodes and the input electrode, while the remaining free ions are slowed down in the separator and remain in a longer contact with the solid particles, enabling their more efficient electrification.
Embodiments of the air filter according to the invention are presented in the drawing, where:
As shown in
Downstream of the ion generator 2 in the flow channel 1 there is a separator of contaminant particles 6, comprising an input electrode 7 and an output electrode 8. The electrodes 7 and 8 have a construction enabling the air to flow through them in a direction from the input electrode 7 towards the output electrode 8 and further to the channel outlet. Both electrodes 7 and 8 are made from an electro-conductive material, or a material with proper electric conductivity enabling the dissipation of electrostatic charges accumulated thereon. Preferably, the input electrode 7 and the output electrode 8 are made of metal and can have the form of a mesh or a perforated plate. The input electrode 7 or/and the output electrode 8 may also be made of conductive nonwoven or a spongiform material, preferably coated with activated carbon.
An additional filtering layer 10 of an electrically nonconductive material, e.g. with a nonwoven or spongiform structure, may be located in the space 9 between the electrodes 7 and 8. In the case where nonconductive particles are being filtered, the filtering layer 10 may fill the whole space 9 between the electrodes 7 and 8. In the case of filtering conductive particles, for example coal soot, electrically insulating air space should be preferably maintained between the filtering layer 10 and the output electrode 8.
Both the ion generator 2 and the separator 6 are mounted in respective guides 11 enabling removal of these elements from the housing for servicing purposes, and at the same time providing proper tightness.
Optionally, an air pre-filter 12 for mechanical separation of contaminant particles may be placed upstream of the ion generator 2. If the filter according to the invention is mounted in a ventilation system downstream of the air handling unit, then the pre-filter 12 is not necessary.
The filter housing according to the invention is adapted to being connected to a channel-based ventilation system downstream of the pre-filter 12 and the fresh air supply fan 13, as seen in
The corona electrodes 3 carry high voltage relative to the cumulative electrodes 4, the high voltage being created by the high voltage generator. The potential difference U1 between the corona electrodes 3 and the cumulative electrodes 4 may be adjusted and it preferably ranges between 2 and 80 kV.
Various embodiments of potentials between the corona electrodes 3, the input electrodes 7 and the output electrodes 8 are possible. The point is that the electric field strength vector in the space 9 (between the input electrode 7 and the output electrode 8) should be directed opposite to the electric field strength vector in the space 15 (between the generator 2 and the input electrode 7), so that the forces generated by these fields would cause acceleration of the charged particles in the space 15 and slowing down in the space 9.
In the first embodiment, the potential of the corona electrodes 3 and the output electrode 8 is positive, while the potential of the input electrode 7 equals zero.
In the second embodiment, the potential of the corona electrodes 3 and the output electrode 8 is positive, but the potential of the input electrode 7 is negative.
In the third embodiment, the potential of the corona electrodes 3 and the output electrode 8 is negative, while the potential of the input electrode 7 equals zero.
In the fourth embodiment, the potential of the corona electrodes 3 and the output electrode 8 is negative, but the potential of the input electrode 7 is positive.
In the fifth embodiment, the potential of the corona electrode 3 is positive, the potential of the input electrode 7 it is negative, and for the output electrode 8 it equals zero.
In the sixth embodiment, the potential of the corona electrode 3 is negative, the potential of the input electrode 7 it is positive, and for the output electrode 8 it equals zero.
In the case of the first and second embodiment, i.e. with positive polarisation of the corona electrodes 3, the emission of ozone is lower than for negative polarisation.
Due to the impact of the corona discharge phenomenon, the air flowing through the ion generator 2 becomes saturated with positive or negative ions created as a result of corona discharges, depending on the adopted polarisation of the corona electrodes 3. These ions transfer the electric charge to any contaminants present in the flowing air. The corona discharge occurs virtually only on corona electrodes 3.
In the ion generator 2, partial deposition of only a slight amount of contaminant particles occurs on cumulative electrodes 4, on which between approximately 9% and approximately 10% of particles are deposited. Most of the charged particles 16 flow on, to the separator of contaminant particles 6.
Upon leaving the ion generator 2, the air comprising electrified particles of contaminants 16, while flowing through the space 15 between the ion generator 2 and the input electrode 7, becomes affected by strong electric field generated by the potential difference U2 between the corona electrodes 3 and the input electrode 7 of the separator 6.
As mentioned above, the potential of the input electrode 7 may equal zero (the electrode is earthed), or more preferably it is of an opposite sign in relation to the corona electrodes 3. The electrical voltage U2 between the corona electrodes 3 and the input electrode 7 is adjustable and it may range between approximately 3 kV and approximately 50 kV. The value of this voltage depends on the distance between the electrodes 3 and 7, the amount of eliminated contaminants and the required efficiency of filtration. The input electrode 7 through which the air flows is made of metal or a material with proper electrical conductivity enabling the dissipation of the electrical charge accumulated thereon, and it can have the form of a mesh, perforated plate or/and conductive nonwoven material, preferably comprising activated carbon. In the space 15 between the ion separator 2 and the input electrode 7 additional ionisation of air occurs, caused by the existence of an electric field; charged contaminant particles 16 subjected to this field are accelerated by the action of the electrostatic force F1, and due to numerous collisions they can additionally electrify other neutral or oppositely charged solid or fluid particles. In this manner, the number of charged particles increases, but this is no longer a direct result of the corona discharge. Upon reaching the input electrode 7 of the separator 6, the majority of particles 16 are electrostatically deposited on its surface and on an additional filtering layer 10, e.g. of a conductive nonwoven material (if present). A part of the solid particles flows with the air into the space 9 between the input 7 and output 8 electrodes. This space, along with the electrodes 7 and 8, constitutes a kind of an electrical capacitor, in which strong electric field is generated due to the impact of the potential difference U3 of electrodes 7 and 8, the electric field having a strength vector directed opposite to the electric field strength vector in the space 15, causing the charged particles 17 and gaseous ions present in the space 9 to stop due to the action of the electrostatic force F2. Because of this, the stopped particles 18 are deposited on the input electrode 7 and possibly on an additional filtering layer 10. The presence of the additional layer 10, e.g. of nonwoven material, increases the efficiency of filtration considerably. The voltage U3 between the input electrode 7 and the output electrode 8 may range from a few to several tens kilovolts. Both the input 7 and the output 8 electrode may also comprise a layer with activated carbon. This may have the form of a nonwoven material, a sponge of carbon granules. The activated carbon decreases the amount of harmful gases and smells, also reducing the trace ozone and nitrogen oxides created in the generator 2. Very precise separation of virtually all solid particles and aerosols takes place in the additional filtering layer 10 of the separator 6.
The corona electrodes 3 are placed at a technological distance X from the input electrode 7, the distance being adapted to the value of the potential difference U2 between the corona electrodes 3 and the input electrode 7.
The size of the filter is selected so that the speed V of air flowing through the separator 6 would range between 0.2 m/s and 3 m/s. For such a speed range, pneumatic resistances of the whole filter are relatively low and range between 10 and 150 Pa. The lower the flow rate, the more efficient the filtration for the given electrical power.
In a case when the pre-filter 12 is placed upstream of the ion generator 2, mechanical separation of large particles exceeding approximately 0.5 mm proceeds therein.
As explained above, the specific feature of the whole process as compared to other encountered solutions also involves the fact that a relatively small corona discharge is sufficient for successful filtration. The separator 6 enables very efficient use of the removed ion particles generated during corona discharges in the ion generator 2 for electrification. Due to this, the electrical charge emitted during the corona discharge, which is necessary for efficient deposition of particles, is considerably lower. As a consequence, the deposition of particles on the electrode 7 and in particular in the filtering layer 10 requires an amount of energy which is much lower compared to known solutions. For successful filtering, typical electrostatic filters need very high saturation of air with ions, and besides this there is a need for stronger corona discharges and power of supplied electrical energy.
In practice, the achieved efficiency of removing from the air the particles of a diameter between 0.1 and 100 μm amounts to 99.97%. At the same time, ozone emission is considerably below 50 μg in 1 m3 of the air flowing through the filter (the allowable ozone emission is 120 μg/m3).
As shown in
The filter according to the invention combines the features of two filtration methods, i.e. the electrostatic filtration and the filtration of so-called “absolute” mechanical nonwoven filters. Its advantages include:
In these embodiments, the corona electrodes 3, carrying high voltage, are placed on a bushing insulator 25 and preferably in an additional shield 22, also constituting an amplifier of the electric field between the shield 22 and the input electrode 7 of the particle separator 6. In this manner, the electrical insulators of the corona electrodes 3 are protected against too rapid contamination. Electro-conductive contaminations, e.g. soot, deposited on the insulator 25, are disadvantageous, since they cause a drop in the electrical strength of the insulator, generation of harmful leakage currents and discharges on the surface of the insulator.
High voltage is supplied to the contact 26 and to the corona electrodes 3 via the insulator 25. The shield 22, having the same electrical potential as the corona electrodes 3, protects the insulator 25 against contaminated air. In the embodiments of
The whole separator 6 is seated along with the insulator 25, the shield 22 and the corona electrodes 3 in the bottom 28. The connection of the separator 6 to the bottom 28 should be tight along the whole perimeter. Everything is placed in the air flow channel housing 1 consisting generally of two parts:
Such realisation of the filter according to the invention enables easy periodic removal of the whole system of the separator 6 and ion generator 2 from the housing through a service cover (not shown). Upon disassembling the output electrode 8, it is possible to replace the filtering layer 10, clean the electrodes 3 and all the electrically insulating elements.
In
In the case of the gases with a very high solid particle contents exceeding 10 mg/m3, it is preferable for the filter housing according to the invention to enable repeated removal of the contaminated filtering layer 10 from the area of operation and its replacement with a clean filtering layer. Repeated replacement of the layer 10 considerably extends the time of uninterrupted operation of the filter.
The rollers 30a, 30b, 30c should be made of an electrically insulating material and they should have a separate driving mechanism synchronised with the drive of the bottom 28.
The slit 8a of the output electrode 8 enables, on the one hand, the introduction of a clean layer 10 into the mobile input electrode 7, and on the other hand, the removal of a used layer 10 from the separator 6. The mobile electrode 7 moves the layer 10 along its circumference. The drive system rotating the bottom 28 and the whole high voltage system are not shown in the figures.
Embodiments of the filter according to the invention presented in
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P 423617 | Nov 2017 | PL | national |
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20190160475 A1 | May 2019 | US |