Patent Application
20160145123
This utility application claims priority to European Patent Application No. 14194376.1, filed Nov. 21, 2014, and is incorporated herein by reference.
1. Technical Field
The present invention relates to a device, a system, and a method for the treatment of liquid effluents (wastewaters).
2. Related Art
Various systems of a known type for treating effluents rely upon the use of one or more of the following treatment means for formation of reactive chemical species that react with and break down the undesirable substances in the effluent:
For instance, the document No. WO2013/079858 A1 mentioned previously relates to a system for treating liquid and gaseous effluents, where the effluent is subjected to the combined action of a plasma discharge generated by two opposed electrodes and of ultraviolet radiation generated by a system of separate lamps inserted in a bed of porous microbeads that act as photocatalysts.
However, the device described in the aforesaid document envisages generation of the plasma discharge with a voltage of between 5 V and 220 V. It is, however, known that at this voltage it is not possible to achieve dielectric breakdown in aqueous liquids, which prevents treatment of these liquids in a direct way with cold plasma in this type of device.
This dictates, precisely, adoption of a separate system for emission of ultraviolet radiation for treating effluents using a photocatalyst, with evident complications of a structural nature of the treatment device, as well as with consequent and evident complications in terms of flexibility of the solution.
The object of the invention is to overcome the technical problems mentioned previously. In particular, the object of the invention is to provide a method, a system, and a device for the treatment of liquid effluents that enable an effective treatment of the effluents, including the aqueous effluents, with maximized effectiveness, and without the need to provide a number of treatment sources, where the term “treatment sources” is used to identify in a generic way one or more devices designed to generate the aforementioned treatment means (for example, plasma discharge and ultraviolet radiation).
In particular, the object of the invention is achieved by a method for supplying a device for plasma treatment of liquid effluents, wherein the device comprises a casing defining a treatment volume and a first electrode and a second electrode facing into said treatment volume, the method comprising the steps of:
wherein each electric discharge occurs when a voltage value of said voltage pulse reaches a threshold value that causes dielectric breakdown in said discharge gap of variable width.
Furthermore, the object of the invention is achieved by a system for the treatment of liquid effluents by means of electric discharges, the system comprising:
Finally, the object of the invention is achieved by a device for plasma treatment of liquid effluents including:
The object of the invention is achieved by a device, a system, and a method for the treatment of liquid effluents having the characteristics forming the subject of the ensuing claims, which form an integral part of the technical teaching provided herein in relation to the invention.
Various preferred embodiments of the invention will now be described with reference to the annexed drawings, which are provided purely by way of non-limiting example, and wherein:
In
The pulse generator 9 in turn includes a high-voltage generator 10 connected to a nanopulse generator 12.
The high-voltage generator 10, which is per se known, receives the supply directly from the power supply 8 and includes a first stage configured for rectification of the input current and subsequent conversion into DC current, and a second stage wherein a transformation is provided that increases the voltage into the high-voltage range.
The output terminals of the high-voltage generator 10 are connected to the input terminals of the nanopulse generator 12, the detail of which is represented in
The nanopulse generator 12 includes a high-voltage electrode 14 and a ground electrode 16 (in
The treatment device 4 includes a casing 17, which defines within it a treatment volume for the effluent and in which, moreover, a first electrode 18 and a second electrode 20 face. The first electrode 18 is electrically connected to the high-voltage electrode 14, whereas the second electrode 20 is electrically connected to a third electrode 22, which, together with a fourth electrode 24—the latter connected to the ground electrode 16 of the pulse generator 9—, defines the high-voltage switch.
At least one between the electrodes 22 and 24 can be moved away from or towards the other electrode in order to vary the width of the discharge gap G6, which is comprised between the electrodes 22 and 24 themselves.
With reference to
With reference to
In the end plate 26 there are moreover provided a number of openings that include:
The position of the inlet and outlet orifices is dictated, as will be seen shortly, by the partition of the treatment volume within the casing 17.
At the opposite end of the casing 17, the electrode 20 is mounted in the end plate 28 so as to be axially movable within the treatment volume. Moreover, as may be seen in
Set within the casing 17 is a cylindrical septum 30 mounted coaxial with respect to the casing 17, which is also cylindrical.
The cylindrical septum 30 is fixed to the end plates 26, 28 and creates a partition of the treatment volume of the device 4 into a core section CS and a shell section SS. The core section CS corresponds to a cylindrical volume that contains the electrodes 18, 20 and has a larger diameter than the electrode 20 by an amount sufficient to create an annulus around it for inlet of the fluid from the orifice 4IN.
The shell section SS is, instead, a cylindrical annular region surrounding the core section CS. The core section and the shell section CS, SS are in fluid communication through one or more radial openings 31 provided in the septum 30. The one or more radial openings 31 give out into an annular transfer chamber 32, which is radially delimited by the casing 17 and by the septum 30, whereas in an axial direction it is delimited by the end plate 28 at a first end and by a first annular filter F1 at a second end.
A second annular filter F2 is set in the proximity of the first end plate 26 so as to define an annular jacket 34, housed in which are vitreous beads (i.e., beads made of silica material) coated with a photocatalyst. In a preferred embodiment, the photocatalyst used is a film of titanium dioxide (TiO2).
The axial extension of the jacket 34 is chosen so as to be always larger than the width of the discharge gap G4. This means that the axial length of the jacket 34 is chosen in such a way as to cover the entire range of variability of the discharge gap G4 itself.
The filter F2 delimits axially, together with the second end plate 26, an annular collecting chamber 36, which is again delimited in a radial direction by the septum 30 and the casing 17. The annular chamber 36 is thus set in a peripheral region of the treatment device 4 and is in fluid communication with the outlet orifices 4OUT_1 and 4OUT_2, for which it now becomes clear why they are positioned peripherally.
With reference to
In particular, the first parallel of capacitors includes a first capacitor C1 and a second capacitor C11 and has terminals connected one to the branch 120, the other to the branch 121, and both downstream of the resistors R1, R4.
The second parallel of capacitors includes a third capacitor C2 and a fourth capacitor C22 and has terminals connected one to the branch 120, the other to the branch 121, and both downstream of the resistors R2, R5.
The third parallel of capacitors includes a fifth capacitor C3 and a sixth capacitor C33 and has terminals connected one to the branch 120, the other to the branch 121, and both downstream of the resistors R3, R6.
Furthermore, the parallels of capacitors, which are set in succession, are connected together by means of a first high-voltage switch SG1 and a second high-voltage switch SG2, each equipped with a first electrode A and a second electrode B, wherein the electrode A is connected to the branch 120 whereas the electrode B is connected to the branch 121.
Provided that the branch 120 is connected to a high-voltage electrode of the generator 10, whereas the branch 121 is connected to ground, all the parallels of capacitors will have a terminal connected to ground and a terminal connected to the high voltage; likewise, all the high-voltage switches SG1, SG2 have the electrode A connected to the high-voltage branch, whereas the electrode B is connected to ground. Furthermore, the electrode A of each high-voltage switch is connected to the parallel of capacitors immediately upstream thereof, whereas the electrode B of each high-voltage switch is connected to the parallel of capacitors immediately downstream thereof.
In this regard, it will be noted that the high-voltage electrode 14 of the generator 12 is functionally an electrode of type A, i.e., connected to the high-voltage branch 120 and to the electrode 20, whereas the ground electrode 16 to which the electrode 24 of the high-voltage switch 6 is connected is functionally an electrode of type B.
The circuit diagram of the nanopulse generator illustrated herein is to be deemed as corresponding to a preferred solution, albeit purely representative. It will be noted in fact that the number of parallels of capacitors and of high-voltage switches may vary even significantly with respect to what is illustrated in
Operation of the system 1 is described in what follows.
The system 1 is configured for treatment of any liquid effluent (within which contaminant are present) by means of an electric discharge between the electrodes 18 and 20.
Thanks to the provision of the pulse generator 9 and of the variable-width voltage switch 6, the electric discharge between the electrodes 18, 20 can assume characteristics such as to maximize the efficiency of the treatment.
These characteristics correspond ideally to the representation of
As anticipated,
With reference, in particular, to
Each voltage pulse is characterized by a first rising edge PD, which corresponds to the discharge of the nanopulse generator, and a falling edge DS, which corresponds to the discharge process (i.e., the process of dielectric breakdown with arc discharge between the electrodes 22, 24) of the high-voltage switch 6 and to the consequent electric discharge in the discharge gap G4 between the electrodes 18, 20.
Each pulse has a duration, respectively, δt1 and δt2, where ideally the values γt1 and γt2 are identical. The successive peaks are separated from one another by a distance in time ΔtV, which in ideal conditions is constant in all the series of successive pulses.
With reference to
Supply of the effluent to be treated may be performed by any known system, for example a hydraulic pump driven by a motor. The liquid effluent that enters through the orifice 4IN pervades the core section CS and the discharge gap G4 between the two electrodes 18, 20.
In the discharge gap G4, the liquid effluent is subjected to an electric discharge that is triggered between the electrodes 18, 20 as a consequence of closing of the circuit by means of the discharge in the high-voltage switch 6 in the way that will be described hereinafter.
On account of the supply voltages and of the waveform of the voltage signal applied across the electrodes 18, 20, two effects are obtained that concur in maximizing the effectiveness of the treatment itself, which are described in what follows.
i) The supply with voltage pulses of extremely high amplitude (up to 110 kV) and very short duration (on average approximately 100 ns, each at a variable frequency from 1 to 250 Hz) enables setting up of the electric discharge with the maximum efficiency possible. It is in fact known that the electric discharge in liquid effluents with characteristics of conductivity higher than 70 μS is rendered difficult by the setting-up of high-density currents linked to the movement of the ions, which dissipate a considerable part of the energy introduced into the system. Application of extremely high voltages in an instantaneous and pulsed way enables setting-up of high-density currents of charged particles (i.e., a discharge) with a preferential direction, at the same time countering the phenomenon of dissipation of the charged particles themselves in non-preferential directions within the effluent, which is naturally an electric conductor.
The inventors have noted that the dielectric breakdown with subsequent generation of plasma discharges in aqueous effluents can occur only in these conditions of supply, since outside such conditions the effectiveness of the discharge would be minimal and, as in the case of the solution described in the document mentioned at the beginning of the present description, it would require the use of supplementary devices for activation of the photocatalyst.
ii) The electric discharge in the discharge gap G4 generates a strong shock wave accompanied by setting-up of an intense electromagnetic field and of extremely high local temperatures. The electromagnetic field and the high local temperatures in the core section CS have an immediate biocidal effect on the pollutant species present within the effluent, sterilizing the liquid in a practically instantaneous way.
Furthermore, once again on account of the characteristics of the supply signal of the electrodes 18, 20, the electric discharge generated between these electrodes directly emits ultraviolet radiation, which is transmitted by irradiation from the core section CS to the shell section SS, in this way activating the photocatalyst sensitive to ultraviolet radiation and enabling a further treatment of the liquid effluent to be carried out in order to eliminate any further undesirable residual species.
As may be seen in
Next, the completely treated effluent comes out of the jacket 34, first gathering in the annular chamber 36 and then abandoning the treatment device 4 through the orifices 4OUT_1 and 4OUT_2.
The characteristics of the electric discharge between the electrodes 18, 20 can moreover be varied according to the requirements thanks to the possibility of movement of the electrodes 18, 20 themselves with respect to one another.
With reference to
By increasing the discharge gap G4 to intermediate values, the electric discharge between the electrodes 18, 20 assumes the characteristics of an indirect discharge of the corona type designated by the reference CD in
By increasing once again the width of the discharge gap G4, it is possible to get the treatment device 4 to function as illustrated in
In this way, the characteristics of the electric discharge that is set up between the electrodes 18, 20 are of a hybrid nature. In other words, the electric discharge—here designated as a whole by the reference HD—has the characteristics of an arc discharge AD in the region comprised between the tip of the electrode 18 and the free surface of the liquid effluent, whereas it has the characteristics of a corona discharge CD in the region comprised between the free surface of the liquid effluent and the front plane surface of the electrode 20.
The possibility of varying the distance between the electrodes 18, 20 thus enables adaptation of the characteristics of the discharge to the type of contaminant present in the liquid effluent to be treated.
With reference to
The above degree of freedom enables modulation of the frequency and amplitude of the voltage pulses applied across the electrodes 18, 20.
With reference to
Recalling, in fact, the general principles of operation of a Marx generator, during the charging phase all the parallels of capacitors C1-C11, C2-C22, and C3-C33 are subjected to the supply voltage ΔV12 that charges the plates thereof. Simultaneously, the same difference of potential is applied across the high-voltage switches SG1 and SG2. As soon as dielectric breakdown is induced within the first of the high-voltage switches (SG1, the one upstream) the first two parallels of capacitors are connected in series so that the second high-voltage switch SG2 is subjected to application of a voltage (ideally) twice the voltage ΔV12, which causes practically instantaneously immediate dielectric breakdown thereof.
In the case of a greater number of capacitors and high-voltage switches, the discharge of the circuit of the Marx generator triggers a chain effect on the high-voltage switches, which leads to setting-up of a voltage between the electrodes 14 and 16 that is equal—ideally—to n times the voltage ΔV12, where n is the number of the parallels of capacitors (or of capacitors equivalent to the parallel).
At the moment of discharge of the circuit of the nanopulse generator 12, the electrodes 14 and 16 are in view of a load that includes the treatment device 4 and the high-voltage switch 6 connected in series together.
The circuit downstream of the electrodes 14, 16 is thus an open circuit on account of the absence of electric discharge between the electrodes of the high-voltage switch 6. Strictly speaking, also the discharge gap between the electrodes 18, 20 brings about in effect an opening of the electrical circuit; however, the presence of the liquid effluent between the electrodes 18, 20 bestows on the treatment device 4 a behaviour of a prevalently resistive type.
At the moment of discharge of the circuit of the nanopulse generator 12, the discharge voltage thereof is instantaneously applied across the switch 6. Given that the circuit is open, there is no passage of current within the device 4. Consequently, both the electrodes 18, 20 are subject to the same voltage, which coincides with the voltage of the electrode 14. Nevertheless, the same voltage is also applied on the electrode 22. There is no voltage drop simply owing to the fact that at the instant of start of the discharge of the generator 12 no passage of current occurs between the electrode 14 and the electrode 22. The maximum voltage that can be reached on the electrode 22 (corresponding to the maximum discharge voltage of the generator 12) depends upon the width of the gap G6, given that, as this width varies, the dielectric strength of the discharge gap G6 varies. The peak voltage corresponds in fact to the threshold voltage that causes dielectric breakdown in the switch 6. The greater the width of the gap G6, the higher its dielectric strength, and the higher the peak voltage of the process of discharge of the generator 12. The smaller the width of the gap G6, the lower its dielectric strength, and the lower the peak voltage of the process of discharge of the generator 12.
Whatever the threshold voltage value that produces dielectric breakdown of the switch 6, once this is reached, the circuit closes and the current passes through the electrodes 18, 20, on the terminals of which the same voltage difference exists as the one existing between the electrodes 14 and 16. This creates an electric discharge in the discharge gap G4, with consequent generation of plasma and treatment of the liquid between them according to the modalities and the effects described previously (see, in particular, point ii) above).
The duration, frequency, and electrical parameters of the discharge in the reaction device 4 depend upon the geometry of the switch 6, in particular upon the width of the gap G6, which can be regulated.
In particular, a high-voltage switch where the gap G6 has a smaller width will cause a discharge that has shorter duration and is characterized by a threshold voltage value for dielectric breakdown in the gap G6 that is lower (as has already been said). The frequency of the voltage pulses will, instead, be higher, in so far as the time constants of charging and discharging of the high-voltage switch 6 and of the entire generator circuit 12 are shorter on account of the lower threshold voltage of the switch 6.
Instead, a high-voltage switch, where the gap G6 has a large width will cause a discharge that is of longer duration and is characterized by a threshold voltage value for dielectric breakdown in the gap G6 that is higher (as has already been said). The frequency of the voltage pulses will, instead, be lower, in so far as the time constants of charging and discharging of the high-voltage switch 6 and of the entire generator circuit 12 are longer on account of the higher threshold voltage of the switch 6.
In brief, each voltage pulse is caused by discharging of the nanopulse generator 12, which induces dielectric breakdown and the discharge in the high-voltage switch 6, which in turn closes the circuit across the generator 12 generating the electric discharge in the discharge gap G4 between the electrodes 18, 20. The frequency, duration, and amplitude of the pulses is modulated by varying the width of the gap G6.
With reference to
In particular, the person skilled in the branch will appreciate how the characteristics of the voltage signal across the electrodes 18, 20 markedly depend upon the characteristics of the discharge that is triggered within the high-voltage switch 6, which may vary also in the intervals between one pulse and the next.
This may be due, for example, to even minor variations of the relative humidity of the air present in the high-voltage switch between the electrodes 22 and 24 or to variations in the composition of the air itself (for example, owing to the presence of ionized species).
Not only this, but, as may be noted in
As may be noted from
In this connection,
Instead, a second test discharge conducted on the same solution highlights formation of three peaks P1, P2, P3 once again separated by intervals and followed by damping oscillations.
Nevertheless, with reference to
Once again with reference to
Instead, the second (
In this case, on account of the lower frequency of the processes of discharge of the high-voltage switch 6, the time constants of the damping oscillations are in any case not sufficient to degrade the subsequent voltage peaks, so that the a third peak P3 appears—albeit of very reduced amplitude—downstream of the second peak P2.
Thanks to the system 1 and the device 4 according to the invention (and to the innumerable possible regulations), as well as to the method of treatment based upon application of a pulsed electrical signal it is possible to treat any contaminated liquid effluent without resorting to a plurality of different treatment sources as is the case in known solutions.
With the treatment device, system, and method according to the invention, the very electric discharge between the electrodes 18, 20 already has characteristics such as not to induce dissipation of energy and, simultaneously, emit ultraviolet radiation for treatment, by means of a photocatalyst, of the residual noxious species within the liquid effluent.
Of course, the details of construction and the embodiments may vary widely with respect to what has been described and illustrated herein, without thereby departing from the scope of the present invention, as defined by the annexed claims.
For instance, in alternative embodiments it is possible to use electrodes 18, 20 having an identical shape, for example a pair of tip electrodes.
Obviously, many modifications and variations of the present invention are possible in light of the above teachings and may be practiced otherwise than as specifically described while within the scope of the appended claims. In addition, the reference numerals in the claims are merely for convenience and are not to be read in any way as limiting.
| Number | Date | Country | Kind |
|---|---|---|---|
| 14194376.1 | Nov 2014 | EP | regional |
