WO2022090737A2 - Gas abatement by plasma - Google Patents
Gas abatement by plasma Download PDFInfo
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- WO2022090737A2 WO2022090737A2 PCT/GB2021/052820 GB2021052820W WO2022090737A2 WO 2022090737 A2 WO2022090737 A2 WO 2022090737A2 GB 2021052820 W GB2021052820 W GB 2021052820W WO 2022090737 A2 WO2022090737 A2 WO 2022090737A2
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01J—ELECTRIC DISCHARGE TUBES OR DISCHARGE LAMPS
- H01J37/00—Discharge tubes with provision for introducing objects or material to be exposed to the discharge, e.g. for the purpose of examination or processing thereof
- H01J37/32—Gas-filled discharge tubes
- H01J37/32431—Constructional details of the reactor
- H01J37/32798—Further details of plasma apparatus not provided for in groups H01J37/3244 - H01J37/32788; special provisions for cleaning or maintenance of the apparatus
- H01J37/32816—Pressure
- H01J37/32834—Exhausting
- H01J37/32844—Treating effluent gases
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- H—ELECTRICITY
- H05—ELECTRIC TECHNIQUES NOT OTHERWISE PROVIDED FOR
- H05H—PLASMA TECHNIQUE; PRODUCTION OF ACCELERATED ELECTRICALLY-CHARGED PARTICLES OR OF NEUTRONS; PRODUCTION OR ACCELERATION OF NEUTRAL MOLECULAR OR ATOMIC BEAMS
- H05H1/00—Generating plasma; Handling plasma
- H05H1/24—Generating plasma
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01J—ELECTRIC DISCHARGE TUBES OR DISCHARGE LAMPS
- H01J37/00—Discharge tubes with provision for introducing objects or material to be exposed to the discharge, e.g. for the purpose of examination or processing thereof
- H01J37/32—Gas-filled discharge tubes
- H01J37/32431—Constructional details of the reactor
- H01J37/3244—Gas supply means
- H01J37/32449—Gas control, e.g. control of the gas flow
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/32—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by electrical effects other than those provided for in group B01D61/00
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/68—Halogens or halogen compounds
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- C—CHEMISTRY; METALLURGY
- C23—COATING METALLIC MATERIAL; COATING MATERIAL WITH METALLIC MATERIAL; CHEMICAL SURFACE TREATMENT; DIFFUSION TREATMENT OF METALLIC MATERIAL; COATING BY VACUUM EVAPORATION, BY SPUTTERING, BY ION IMPLANTATION OR BY CHEMICAL VAPOUR DEPOSITION, IN GENERAL; INHIBITING CORROSION OF METALLIC MATERIAL OR INCRUSTATION IN GENERAL
- C23C—COATING METALLIC MATERIAL; COATING MATERIAL WITH METALLIC MATERIAL; SURFACE TREATMENT OF METALLIC MATERIAL BY DIFFUSION INTO THE SURFACE, BY CHEMICAL CONVERSION OR SUBSTITUTION; COATING BY VACUUM EVAPORATION, BY SPUTTERING, BY ION IMPLANTATION OR BY CHEMICAL VAPOUR DEPOSITION, IN GENERAL
- C23C16/00—Chemical coating by decomposition of gaseous compounds, without leaving reaction products of surface material in the coating, i.e. chemical vapour deposition [CVD] processes
- C23C16/44—Chemical coating by decomposition of gaseous compounds, without leaving reaction products of surface material in the coating, i.e. chemical vapour deposition [CVD] processes characterised by the method of coating
- C23C16/4412—Details relating to the exhausts, e.g. pumps, filters, scrubbers, particle traps
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01J—ELECTRIC DISCHARGE TUBES OR DISCHARGE LAMPS
- H01J37/00—Discharge tubes with provision for introducing objects or material to be exposed to the discharge, e.g. for the purpose of examination or processing thereof
- H01J37/32—Gas-filled discharge tubes
- H01J37/32009—Arrangements for generation of plasma specially adapted for examination or treatment of objects, e.g. plasma sources
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01J—ELECTRIC DISCHARGE TUBES OR DISCHARGE LAMPS
- H01J37/00—Discharge tubes with provision for introducing objects or material to be exposed to the discharge, e.g. for the purpose of examination or processing thereof
- H01J37/32—Gas-filled discharge tubes
- H01J37/32431—Constructional details of the reactor
- H01J37/32458—Vessel
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- H—ELECTRICITY
- H05—ELECTRIC TECHNIQUES NOT OTHERWISE PROVIDED FOR
- H05H—PLASMA TECHNIQUE; PRODUCTION OF ACCELERATED ELECTRICALLY-CHARGED PARTICLES OR OF NEUTRONS; PRODUCTION OR ACCELERATION OF NEUTRAL MOLECULAR OR ATOMIC BEAMS
- H05H1/00—Generating plasma; Handling plasma
- H05H1/24—Generating plasma
- H05H1/26—Plasma torches
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- H—ELECTRICITY
- H05—ELECTRIC TECHNIQUES NOT OTHERWISE PROVIDED FOR
- H05H—PLASMA TECHNIQUE; PRODUCTION OF ACCELERATED ELECTRICALLY-CHARGED PARTICLES OR OF NEUTRONS; PRODUCTION OR ACCELERATION OF NEUTRAL MOLECULAR OR ATOMIC BEAMS
- H05H1/00—Generating plasma; Handling plasma
- H05H1/24—Generating plasma
- H05H1/26—Plasma torches
- H05H1/32—Plasma torches using an arc
- H05H1/42—Plasma torches using an arc with provisions for introducing materials into the plasma, e.g. powder or liquid
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/10—Oxidants
- B01D2251/102—Oxygen
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/10—Oxidants
- B01D2251/104—Ozone
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/20—Reductants
- B01D2251/202—Hydrogen
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/20—Reductants
- B01D2251/208—Hydrocarbons
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/30—Alkali metal compounds
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/40—Alkaline earth metal or magnesium compounds
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/20—Halogens or halogen compounds
- B01D2257/206—Organic halogen compounds
- B01D2257/2066—Fluorine
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0216—Other waste gases from CVD treatment or semi-conductor manufacturing
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2259/00—Type of treatment
- B01D2259/80—Employing electric, magnetic, electromagnetic or wave energy, or particle radiation
- B01D2259/818—Employing electrical discharges or the generation of a plasma
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/32—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by electrical effects other than those provided for in group B01D61/00
- B01D53/323—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by electrical effects other than those provided for in group B01D61/00 by electrostatic effects or by high-voltage electric fields
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01J—ELECTRIC DISCHARGE TUBES OR DISCHARGE LAMPS
- H01J2237/00—Discharge tubes exposing object to beam, e.g. for analysis treatment, etching, imaging
- H01J2237/32—Processing objects by plasma generation
- H01J2237/327—Arrangements for generating the plasma
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
- Y02C20/00—Capture or disposal of greenhouse gases
- Y02C20/30—Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]
Definitions
- the field of the invention relates to plasma abatement.
- Embodiments relate to an apparatus and method for treating an effluent stream from a semiconductor processing tool.
- Plasma abatement apparatus are known and are typically used for, amongst other things, treating an effluent gas stream from a manufacturing process tool used in, for example, the semiconductor or flat panel display manufacturing industry.
- a manufacturing process tool used in, for example, the semiconductor or flat panel display manufacturing industry.
- residual fluorinated or perfluorinated compounds (PFCs) and other compounds exist in the effluent gas stream pumped from the process tool. These compounds are difficult to remove from the effluent gas stream and their release into the environment is undesirable because they are known to have relatively high greenhouse activity.
- a plasma abatement apparatus for treating an effluent stream from a semiconductor processing tool, the plasma abatement apparatus comprising: a plasma device configured to generate a plasma stream from a plasma gas; an effluent stream aperture configured to convey the effluent stream into the plasma stream for treatment by the plasma stream; a first aperture positioned to deliver a reducing reactant to a first region of the plasma stream; and a second aperture positioned to deliver an oxidising reactant to a second region of the plasma stream, wherein the second region is located at a position of the plasma stream which is cooler than the first region.
- the apparatus may be a plasma abatement apparatus.
- the apparatus may treat or abate an effluent stream from a semiconductor processing tool.
- the apparatus may comprise a plasma device or generator which generates a plasma stream from a plasma gas.
- the apparatus may comprise an effluent stream aperture or opening which conveys the effluent stream into the plasma stream.
- the effluent stream may then be treated by the plasma stream.
- the apparatus may comprise a first aperture or opening which delivers a reducing reactant into a first location, region or zone of the plasma stream.
- That first aperture may be the same aperture that delivers the plasma gas to the plasma device and from which the plasma is generated.
- the apparatus may comprise a second aperture or opening which is positioned to deliver an oxidizing reactant to a second location, region or zone of the plasma stream.
- the second region may be located to deliver the oxidizing reactant to a position within the plasma stream which is cooler than the position where the reducing reactant is delivered.
- the reducing reagent is introduced into a hotter or more active region of the plasma stream and the oxidizing reagent is introduced into a cooler or less active region of the plasma stream.
- the reducing reaction enables the reducing reaction to be more effective since the reducing reactant is present in the hotter region and the absence of the oxidizing reactant in this hotter region reduces the presence of thermally created undesirable oxides.
- the introduction of the oxidizing reactant helps to remove by-products generated by the reducing reaction, and because the oxidizing reactant is introduced into the cooler region of the plasma stream, the amount of undesirable thermally generated oxides is reduced.
- the first region may be located at a position of the plasma stream which is hotter than the second region.
- the first region may be located at a position within the plasma stream which achieves a temperature of 1000°C or more.
- the second region may be located at a position within the plasma stream which achieves a temperature of no more than or less than 1000°C.
- the second region may be located at a position within the plasma stream which achieves a temperature of 500°C or more.
- the second region may be located downstream of the first region.
- the first region may be located upstream of the second region.
- the reducing reactant may be pre-mixed with the plasma gas prior to the combined reactant and plasma gas being delivered to the plasma device.
- the first region may be located proximate or near to the plasma device.
- the second region may be located distal or away from the plasma device.
- the apparatus may comprise a reaction chamber which is positioned to receive the plasma stream and the second region may be located within the reaction chamber.
- the reducing reactant may comprise H2.
- the apparatus may comprise a hydrogen generator configured to generate the H2 in situ by electrolysis.
- the apparatus may comprise a power generator employed to generate the plasma stream or a secondary power source configured to power the hydrogen generator.
- the reducing the reactant may comprise NH3.
- the first aperture may be configured to deliver an ammonia salt such as ammonium carbonate (NH4)2CO3, or the like to generate the NH3 by thermal decomposition within the first region.
- an ammonia salt such as ammonium carbonate (NH4)2CO3, or the like to generate the NH3 by thermal decomposition within the first region.
- the apparatus may comprise a heater configured to generate the NH3 by thermal decomposition of an ammonia salt such as ammonium carbonate (NH4)2CO3, or the like.
- an ammonia salt such as ammonium carbonate (NH4)2CO3, or the like.
- the reducing reactant may comprise a hydrocarbon (CxH y ) such as propane, methane and the like.
- the reducing reactant may comprise an alkaline earth metal such as beryllium, magnesium, calcium, strontium, and/or barium.
- the reducing reactant may comprise an alkaline earth salt.
- the reducing reactant may comprise an alkaline metal such as lithium, sodium, potassium, rubidium.
- the reducing reactant may comprise an alkaline salt.
- the oxidizing reactant may comprise O2.
- the oxidizing reactant may comprise O3.
- a method of treating an effluent stream from a semiconductor processing tool comprising: generating a plasma stream from a plasma gas; conveying the effluent stream into the plasma stream for treatment by the plasma stream; delivering a reducing reactant to a first region of the plasma stream; and delivering an oxidising reactant to a second region of the plasma stream which is located at a position of the plasma stream which is cooler than the first region.
- the method may comprise locating the first region at a position of the plasma stream which is hotter than the second region.
- the method may comprise locating the first region at a position of the plasma stream which achieves a temperature of at least 1000°C.
- the method may comprise locating the second region at a position of the plasma stream which achieves a temperature of no more than 1000°C.
- the method may comprise locating the second region at a position of the plasma stream which achieves a temperature of at least 500°C.
- the method may comprise locating the second region downstream of the first region.
- the method may comprise locating the first region upstream of the second region.
- the method may comprise locating premixing the reducing reactant with the plasma gas prior to delivery to the plasma device.
- the method may comprise locating the first region proximate the plasma device.
- the method may comprise locating the second region distal the plasma device.
- the method may comprise receiving the plasma stream in a reaction chamber and locating the second region within the reaction chamber.
- the reducing reactant may comprise H2.
- the method may comprise generating the H2 in situ by electrolysis.
- the method may comprise generating the H2 using a hydrogen generator powered by a power generator employed to generate the plasma stream or by a secondary power source.
- the reducing the reactant may comprise NH3.
- the method may comprise generating the NH3 by thermal decomposition of an ammonia salt such as ammonium carbonate (NH4)2CO3, or the like.
- an ammonia salt such as ammonium carbonate (NH4)2CO3, or the like.
- the reducing reactant may comprise a hydrocarbon (CxH y ) such as propane, methane and the like.
- the reducing reactant may comprise an alkaline earth metal such as beryllium, magnesium, calcium, strontium, and/or barium.
- the reducing reactant may comprise an alkaline earth salt.
- the reducing reactant may comprise an alkaline metal such as lithium, sodium, potassium, rubidium.
- the reducing reactant may comprise an alkaline salt.
- the oxidizing reactant may comprise O2.
- the oxidizing reactant may comprise O3.
- a plasma abatement apparatus for treating an effluent stream from a semiconductor processing tool, said plasma abatement apparatus comprising: a first aperture positioned to deliver a reducing reactant premixed with a plasma gas to a plasma device configured to generate a plasma stream having the reducing agent in a first region of the plasma stream; an effluent stream aperture configured to convey said effluent stream into said plasma stream for treatment by said plasma stream; and a second aperture positioned to deliver an oxidising reactant to a second region of said plasma stream, wherein said second region is located at a position of said plasma stream which is cooler than said first region.
- the apparatus of the third aspect may have the optional features of the first aspect set out above.
- a method of treating an effluent stream from a semiconductor processing tool comprising: delivering a reducing reactant premixed with a plasma gas to a plasma device; generating a plasma stream having the reducing agent in a first region of the plasma stream; conveying said effluent stream into said plasma stream for treatment by said plasma stream; and delivering an oxidising reactant to a second region of said plasma stream which is located at a position of said plasma stream which is cooler than said first region.
- the method of the fourth aspect may have the optional features of the second aspect set out above.
- Figure 1 illustrates a DC plasma torch according to one embodiment
- Figure 2 shows an arrangement similar to that of Figure 1 but which utilizes an inductively coupled plasma torch
- Figure 3 is similar to that shown in Figure 1 but the reducing reactant is introduced inside or in close proximity to the cathode;
- Figure 4 shows an arrangement which is similar to that shown in Figure 2 but with the reducing reagent being injected inside or in close proximity to the gas discharge of the insulated tube of the plasma torch;
- FIGS 5A to 5E show abatement performance under different configurations.
- Some embodiments provide an arrangement which improves the abatement efficiency of a plasma abatement apparatus. This is achieved by splitting the introduction of reactants into the plasma stream.
- a reducing reactant is delivered at a first position into the plasma stream and an oxidizing reactant is introduced at a second position in the plasma stream.
- the reducing reactant may be premixed with the plasma gas and so the first position may be the position where the plasma gas is first introduced or may be downstream of this position but upstream of the second position. This enables reducing reactants to be introduced at a higher temperature or more active region of the plasma stream and oxidizing reactants to be introduced at a lower temperature or less active region of the plasma stream.
- Introducing the oxidizing reactants at the lower temperature region of the plasma stream reduces the production of unwanted oxides while ensuring that the reduction of some compounds can still occur in the higher temperature region. Improved abatement performance is achieved with lower levels of unwanted by-products compared to introducing the reducing and oxidising reactants together.
- FIG. 1 illustrates a DC plasma torch 100A according to one embodiment.
- a nozzled anode 3 is co-located with a coaxial cathode 2.
- a constant direct current power supply 1 is electrically coupled with the cathode 2 and the anode 3.
- a plasma gas carrier conduit 5B is positioned to deliver a plasma gas carrier 5A into a void between the cathode 2 and the anode 3. Downstream of the anode 3 is located a reaction chamber 8.
- An effluent stream conduit 9B is positioned to deliver an effluent stream 9A to a position between the anode 3 and the reaction chamber 8.
- a reducing reactant conduit 11 B is positioned to deliver a reducing reactant 11 A to a position between the anode 3 and the reaction chamber 8.
- An oxidizing reactant conduit 12B is positioned in the wall of the reaction chamber 8 to deliver an oxidizing reactant 12A into the reaction chamber 8.
- a controller 4 is coupled with the power supply 1 and the source of the plasma gas carrier 5A, the source of the reducing reactant 11 A and the source of the oxidizing reactant 12A.
- the controller 4 switches the power supply 1 to create a voltage difference between the cathode 2 and the anode 3 to initiate the plasma.
- the plasma drives a constant direct current (DC) between the cathode 2 and the anode 3 (the power supply 1 operates as constant current power supply).
- the controller 4 causes the plasma gas carrier 5A to be delivered via the plasma gas carrier conduit 5B which creates a plasma plume 10 through a DC arc discharge between the cathode 2 and the anode 3.
- the plasma plume 10 extends into the reaction chamber 8.
- the discharge is sustained by the injection of the plasma gas carrier 5A.
- the effluent stream 9A is conveyed to the plasma plume 10 by the effluent stream conduit 9B.
- the abatement reaction then takes place inside the reaction chamber 8, which is typically cylindrical in shape and provides thermal insulation. Hence, the effluent stream 9A mixes with the plasma plume 10 within the reaction chamber 8.
- the controller 4 controls the introduction of the reducing reactant 11 A through the reducing reactant conduit 11 B.
- the reducing reactant 11 A mixes with the effluent stream 9A in a hotter zone 6 of the plasma plume 10.
- the hotter zone 6 experiences a temperature in excess of 1000°C.
- a generating device 20 under the control of the controller 4 generates the reducing reactant 11 A (such as H2 by electrolysis or NH3 by thermal decomposition).
- the controller 4 controls the introduction of the oxidizing reactant 12A via the oxidizing reactant conduit 12B into a cooler zone 7 of the plasma plume 10, which is downstream of the hotter zone 6.
- the cooler zone 7 experiences a temperature which is greater than around 500°C but which is lower than 1000°C.
- Figures 5A to 5E show abatement performance under different configurations.
- One of the main challenges for abatement by means of thermal plasma torch is to achieve high efficiency of the abatement process so that the torch power can be reduced to its lowest possible amount. This results in a lower cost of operation due to the lower electrical energy demand.
- Another challenge in abatement by means of thermal plasma torches is to reduce the level of unwanted NOx emissions.
- oxygen can act as an inhibitor of the plasma phase reactions due to its electro negative nature (i.e. it attracts bonding electrons and can quench the plasma state).
- the arrangement such as that shown in Figure 1 can improve the efficiency of the abatement process as this limits the abatement reaction within the hotter zone 6 to those related to the breakdown of C-F, S-F and F-F bindings and the reducing reactants converting F species into HF.
- the arrangement shown in Figure 1 also helps to reduce the likelihood of oxygen-rich reactants reacting with N2 radicals at higher temperatures. By introducing the oxygen-rich reactants in the lower temperature zone 7, this results in lower amounts of NOx.
- Figure 5A shows thermal equilibrium simulations of a mixture of CF 4 and N2 (at concentrations of 1 % and 99% respectively).
- the injection of different reagents has a stoichiometry to maximize the destruction and removal efficiency (DRE) of CF4.
- DRE destruction and removal efficiency
- One abatement route for CF4 is its oxidisation into COF2. This is shown in Figure 5A through the injection of just O2 into the hot zone 6 of the plasma stream 6.
- the COF2 is then hydrolysed into HF in the cold wet part of the abatement apparatus (not shown).
- the efficiency of the abatement can be improved if, rather than injecting O2 into the hot zone 6, instead just H2O is injected.
- Figure 5E shows that the concurrent injection of H2 and O2 does not provide the same results as the two-step abatement process illustrated in Figures 5C and 5D since, as can be seen, significant amounts of NOx and other unwanted byproducts can still be generated.
- FIG 2 shows an arrangement similar to that of Figure 1 but which utilizes an inductively coupled plasma torch 100B.
- the plasma plume 10 is generated by ionizing the plasma gas carrier 5A which is injected into an insulated tube 16 via a plasma gas carrier conduit 15.
- Electromagnetic energy to sustain the discharge is supplied via a radio frequency power supply 13 coupled through coils 14.
- a matching box 17 is provided to match the load provided by the gas discharge 18.
- Figure 3 is similar to that shown in Figure 1 but the reducing reactant 11A is introduced inside or in close proximity to the cathode 2 so that it mixes with the plasma gas carrier 5A to maximize its ionization and effectiveness as a reactant.
- a further advantage of this arrangement is that NH3 may be generated when N2 is employed as a plasma gas and this can reduce the baseline amount of NOx emission from the plasma torch 100C (such as when the effluent stream 9A does not include any compounds other than a purge compound).
- Figure 4 shows an arrangement which is similar to that shown in Figure 2 but with the reducing reagent 11 A being injected inside or in close proximity to the gas discharge 18 of the insulated tube 16 of the plasma torch 100D to provide similar advantages to those described with reference to Figure 3 above.
- hydrogen is used as the reducing agent
- other reducing agents such as an alkaline earth metal such as beryllium, magnesium, calcium, strontium, barium and the like and/or an alkaline earth salt may be used.
- other reducing agents such as NH3, and/or a hydrocarbon such as propane, methane and the like may be used.
- the NH3 may be generated by thermal decomposition of an ammonia salt such as ammonium carbonate (NH4)2COs, or the like either within the first region 6 or in-situ by the generating device 20.
- an ammonia salt such as ammonium carbonate (NH4)2COs, or the like either within the first region 6 or in-situ by the generating device 20.
- the hydrogen may be generated in-situ through electrolysis by the generating device 20.
- oxygen is used as the oxidizing reactant, it will be appreciated that other oxidizing reactants such as ozone.
- the reducing reactant is shown being introduced between the anode 3 and the reaction chamber 8, it will be appreciated that this need not be the case and that the reducing reactant simply needs to be introduced at a location where the plasma stream is hotter than the location where the oxidizing reactant is introduced.
- Some embodiments address the optimization of thermal plasma abatement with the aim of reducing thermal NOx generation and increasing abatement reaction efficiency. Looking at thermal equilibrium simulations, it has become apparent that the abatement reactions involving the reduction of fluorinated species, F2, CFx and SFy into HF require much higher temperatures of the oxidation reaction of other abatement byproducts such as CO and CxHy.
- Some embodiments involve a thermal plasma abatement in two steps: 1 ) a hydrogen-rich reagent is injected in a much hotter reaction zone or premixed with torch plasma gas 2) the oxygen-rich reagents are injected further downstream in a relatively less hot zone. This provides for a split injection of two kinds of reagents in thermal plasma abatement.
- REFERENCE SIGNS power supply 1 13 anode 2 cathode 3 controller 4 plasma gas carrier 5A plasma gas carrier conduit 5B; 15 hotter zone 6 cooler zone 7 reaction chamber 8 effluent stream 9A effluent stream conduit 9B plasma plume 10 reducing reactant 11 A reducing reactant conduit 11 B oxidising reactant 12A oxidising reactant conduit 12B coils 14 insulated tube 16 matching box 17 generating device 20 plasma torch 100A; 100B; 100C; 100D
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Abstract
Description
Claims
Priority Applications (4)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202180088839.3A CN116671257A (en) | 2020-11-02 | 2021-11-01 | Gas abatement by plasma |
| US18/250,653 US20230402260A1 (en) | 2020-11-02 | 2021-11-01 | Gas abatement by plasma |
| KR1020237018287A KR102930745B1 (en) | 2020-11-02 | 2021-11-01 | Plasma reduction device |
| JP2023527001A JP7674477B2 (en) | 2020-11-02 | 2021-11-01 | Gas abatement using plasma |
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| Application Number | Priority Date | Filing Date | Title |
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| GB2017320.9A GB2600691A (en) | 2020-11-02 | 2020-11-02 | Plasma abatement |
| GB2017320.9 | 2020-11-02 |
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| WO2022090737A2 true WO2022090737A2 (en) | 2022-05-05 |
| WO2022090737A3 WO2022090737A3 (en) | 2022-08-18 |
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| JP (1) | JP7674477B2 (en) |
| KR (1) | KR102930745B1 (en) |
| CN (1) | CN116671257A (en) |
| GB (1) | GB2600691A (en) |
| TW (1) | TW202225478A (en) |
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| WO2026159772A1 (en) * | 2025-01-21 | 2026-07-30 | カンケンテクノ株式会社 | Plasma abatement method and device therefor |
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| EP1773474A1 (en) | 2004-08-04 | 2007-04-18 | The BOC Group plc | Gas abatement |
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| US4519993A (en) * | 1982-02-16 | 1985-05-28 | Mcgill Incorporated | Process of conversion for disposal of chemically bound nitrogen in industrial waste gas streams |
| JP3928018B2 (en) * | 1997-03-17 | 2007-06-13 | 株式会社ダイヘン | CFC plasma arc decomposition method and apparatus |
| US6213049B1 (en) * | 1997-06-26 | 2001-04-10 | General Electric Company | Nozzle-injector for arc plasma deposition apparatus |
| US7090811B2 (en) * | 2003-12-11 | 2006-08-15 | General Motors Corporation | Method of reducing NOx in diesel engine exhaust |
| EP1904664A2 (en) * | 2005-07-12 | 2008-04-02 | Air Liquide Electronics Systems | Method for plasma treatment of gas effluents |
| KR100619237B1 (en) * | 2006-03-08 | 2006-09-05 | 한국기계연구원 | Plasma reaction method of hardly decomposable gas |
| TW200829325A (en) * | 2007-01-15 | 2008-07-16 | Kanken Techno Co Ltd | Apparatus and method for processing gas |
| US20130118304A1 (en) * | 2011-11-10 | 2013-05-16 | Advanced Magnetic Processes Inc. | High Temperature Reactor System and Method for Producing a Product Therein |
| US9023303B2 (en) * | 2013-04-15 | 2015-05-05 | Airgard, Inc. | Extended or multiple reaction zones in scrubbing apparatus |
| JP6018665B2 (en) | 2014-04-30 | 2016-11-02 | コリア・インスティテュート・オブ・マシナリー・アンド・マテリアルズKorea Institute Of Machinery & Materials | Plasma reactor for contaminant removal |
| GB2534890A (en) * | 2015-02-03 | 2016-08-10 | Edwards Ltd | Thermal plasma torch |
| KR101567746B1 (en) * | 2015-06-16 | 2015-11-09 | 박정봉 | Apparatus for treating exhaust gas |
| GB2540992A (en) * | 2015-08-04 | 2017-02-08 | Edwards Ltd | Control of gas flow and power supplied to a plasma torch in a multiple process chamber gas treatment system |
| GB2567168A (en) * | 2017-10-04 | 2019-04-10 | Edwards Ltd | Nozzle and method |
| GB2571793A (en) * | 2018-03-09 | 2019-09-11 | Edwards Ltd | Abatement |
| KR102031984B1 (en) * | 2018-07-13 | 2019-10-14 | (주)플라즈닉스 | Method and apparatus for treating object gas-containing effluent gas |
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| KR20230097137A (en) | 2023-06-30 |
| JP2023547670A (en) | 2023-11-13 |
| CN116671257A (en) | 2023-08-29 |
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| US20230402260A1 (en) | 2023-12-14 |
| GB202017320D0 (en) | 2020-12-16 |
| JP7674477B2 (en) | 2025-05-09 |
| GB2600691A (en) | 2022-05-11 |
| WO2022090737A3 (en) | 2022-08-18 |
| TW202225478A (en) | 2022-07-01 |
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