GB2554406A - Plasma abatement - Google Patents

Plasma abatement Download PDF

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Publication number
GB2554406A
GB2554406A GB1616286.9A GB201616286A GB2554406A GB 2554406 A GB2554406 A GB 2554406A GB 201616286 A GB201616286 A GB 201616286A GB 2554406 A GB2554406 A GB 2554406A
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United Kingdom
Prior art keywords
plasma
stream
reaction chamber
passivation
passivation layer
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GB1616286.9A
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GB201616286D0 (en
Inventor
Magni Simone
Soo Choi Yun
Kyoo Ko Chan
James Attwood Mark
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Edwards Korea Ltd
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Edwards Korea Ltd
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Application filed by Edwards Korea Ltd filed Critical Edwards Korea Ltd
Priority to GB1616286.9A priority Critical patent/GB2554406A/en
Publication of GB201616286D0 publication Critical patent/GB201616286D0/en
Priority to TW106213595U priority patent/TWM561683U/en
Priority to KR2020170004992U priority patent/KR20180000936U/en
Priority to CN201721240822.2U priority patent/CN207868157U/en
Publication of GB2554406A publication Critical patent/GB2554406A/en
Withdrawn legal-status Critical Current

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    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/061Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/32Separation 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
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23MCASINGS, LININGS, WALLS OR DOORS SPECIALLY ADAPTED FOR COMBUSTION CHAMBERS, e.g. FIREBRIDGES; DEVICES FOR DEFLECTING AIR, FLAMES OR COMBUSTION PRODUCTS IN COMBUSTION CHAMBERS; SAFETY ARRANGEMENTS SPECIALLY ADAPTED FOR COMBUSTION APPARATUS; DETAILS OF COMBUSTION CHAMBERS, NOT OTHERWISE PROVIDED FOR
    • F23M5/00Casings; Linings; Walls
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/061Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
    • F23G7/063Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating electric heating
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/061Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
    • F23G7/065Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating using gaseous or liquid fuel
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01JELECTRIC DISCHARGE TUBES OR DISCHARGE LAMPS
    • H01J37/00Discharge tubes with provision for introducing objects or material to be exposed to the discharge, e.g. for the purpose of examination or processing thereof
    • H01J37/32Gas-filled discharge tubes
    • H01J37/32431Constructional details of the reactor
    • H01J37/32798Further details of plasma apparatus not provided for in groups H01J37/3244 - H01J37/32788; special provisions for cleaning or maintenance of the apparatus
    • H01J37/32816Pressure
    • H01J37/32834Exhausting
    • H01J37/32844Treating effluent gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2259/00Type of treatment
    • B01D2259/80Employing electric, magnetic, electromagnetic or wave energy, or particle radiation
    • B01D2259/818Employing electrical discharges or the generation of a plasma
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23MCASINGS, LININGS, WALLS OR DOORS SPECIALLY ADAPTED FOR COMBUSTION CHAMBERS, e.g. FIREBRIDGES; DEVICES FOR DEFLECTING AIR, FLAMES OR COMBUSTION PRODUCTS IN COMBUSTION CHAMBERS; SAFETY ARRANGEMENTS SPECIALLY ADAPTED FOR COMBUSTION APPARATUS; DETAILS OF COMBUSTION CHAMBERS, NOT OTHERWISE PROVIDED FOR
    • F23M2900/00Special features of, or arrangements for combustion chambers
    • F23M2900/05001Preventing corrosion by using special lining materials or other techniques
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23MCASINGS, LININGS, WALLS OR DOORS SPECIALLY ADAPTED FOR COMBUSTION CHAMBERS, e.g. FIREBRIDGES; DEVICES FOR DEFLECTING AIR, FLAMES OR COMBUSTION PRODUCTS IN COMBUSTION CHAMBERS; SAFETY ARRANGEMENTS SPECIALLY ADAPTED FOR COMBUSTION APPARATUS; DETAILS OF COMBUSTION CHAMBERS, NOT OTHERWISE PROVIDED FOR
    • F23M2900/00Special features of, or arrangements for combustion chambers
    • F23M2900/05004Special materials for walls or lining
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/30Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]

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  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • General Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • Analytical Chemistry (AREA)
  • Combustion & Propulsion (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • General Chemical & Material Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Plasma & Fusion (AREA)
  • Plasma Technology (AREA)
  • Physical Or Chemical Processes And Apparatus (AREA)

Abstract

A plasma torch abatement apparatus 10 for treating an effluent stream 22 with a plasma stream 18 comprises a reaction chamber 26 defined by a reaction chamber wall. The reaction chamber wall is a composite structure comprising a passivation layer (26B, Fig. 4) of passivation material facing the effluent stream 22 and the plasma stream 18 and a substrate layer formed from a substrate material surrounding the passivation layer (26B, Fig. 4), the passivation material being less chemically reactive to the effluent stream 22 and the plasma stream 18 than the substrate material. The substrate layer may be a high alumina cement and may be more resistant to thermal fracture than the passivation layer (26B, Fig. 4). The passivation layer (26B, Fig. 4) may be thinner than the substrate layer and may be painted, chemical vapour deposited, or sprayed onto the substrate layer, or may be a sleeve or tiles fixed to the substrate layer. A method of manufacturing a reaction chamber 26 is also claimed. The chamber may be made by moulding a ceramic mix.

Description

(54) Title of the Invention: Plasma abatement
Abstract Title: Treating waste gas with a plasma stream in a reaction chamber with walls comprising a passivation layer on a substrate (57) A plasma torch abatement apparatus 10 for treating an effluent stream 22 with a plasma stream 18 comprises a reaction chamber 26 defined by a reaction chamber wall. The reaction chamber wall is a composite structure comprising a passivation layer (26B, Fig. 4) of passivation material facing the effluent stream 22 and the plasma stream 18 and a substrate layer formed from a substrate material surrounding the passivation layer (26B, Fig. 4), the passivation material being less chemically reactive to the effluent stream 22 and the plasma stream 18 than the substrate material. The substrate layer may be a high alumina cement and may be more resistant to thermal fracture than the passivation layer (26B, Fig. 4). The passivation layer (26B, Fig. 4) may be thinner than the substrate layer and may be painted, chemical vapour deposited, or sprayed onto the substrate layer, or may be a sleeve or tiles fixed to the substrate layer. A method of manufacturing a reaction chamber 26 is also claimed. The chamber may be made by moulding a ceramic mix.
Figure GB2554406A_D0001
This print incorporates corrections made under Section 117(1) of the Patents Act 1977.
At least one drawing originally filed was informal and the print reproduced here is taken from a later filed formal copy.
12 17
Figure GB2554406A_D0002
Figure GB2554406A_D0003
12 17
Figure GB2554406A_D0004
Figure GB2554406A_D0005
FIG. 3
12 17
Figure GB2554406A_D0006
- 1 PLASMA ABATEMENT
FIELD OF THE INVENTION
The present invention relates to plasma abatement.
BACKGROUND
Thermal plasma torches are known and are typically used for treating an effluent gas stream from a manufacturing process tool used in, for example, the semiconductor or flat panel display manufacturing industry. During such manufacturing, 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 or toxicity.
One approach to remove the PFCs and other compounds from the effluent gas stream is to use a radiant burner as described, for example, in EP1773474. However, when fuel gases normally used for abatement by combustion are undesirable or not readily available, it is also known to use a plasma torch abatement device. The plasma generated by the plasma abatement device is used to destroy or abate unwanted compounds within the effluent gas stream.
Existing plasma abatement devices each have their own shortcomings. Accordingly, it is desired to provide an improved plasma abatement device.
SUMMARY
According to a first aspect, there is provided a plasma torch abatement apparatus for treatment of an effluent stream from a processing tool with a plasma stream, comprising: a reaction chamber defined by a reaction chamber wall for receiving the effluent stream and the plasma stream, the reaction chamber wall comprising a composite structure having a passivation layer facing the effluent stream and the plasma stream, the passivation layer being formed from a passivation
-2material, the composite structure having a substrate layer formed from a substrate material surrounding the passivation layer, the passivation material being less chemically reactive to the effluent stream and the plasma stream than the substrate material.
The first aspect recognises that although reaction chambers have advantages (for example, simpler installation, enhanced safety due to no need of fuel gas), plasma abatement devices face a set of different challenges from burners and currently have own their shortcomings. In particular, existing reaction chambers might suffer from poor life due to the intense chemical environment within the reaction chamber. The high temperatures generated by a thermal plasma torch can induce acute chemical reactions useful to break PFC chemical bonds. However, these high temperatures can also quickly deteriorate the parts downstream such as the reaction chamber. Also thermal energy might be lost ineffectively to the coolant with detriment to the Destruction and Removal Efficiency (DRE). Accordingly, a reaction chamber for a plasma torch abatement apparatus may be provided. The plasma torch abatement apparatus may be for treatment of an effluent stream from a processing tool. The treatment of the effluent stream may be with a plasma stream. The reaction chamber may receive the effluent stream and the plasma stream. The reaction chamber may comprise or be defined by a reaction chamber wall. The reaction chamber wall may have a composite structure. The composite structure may have a passivation layer and a substrate layer. The passivation layer may face or be adjacent or be in contact with the effluent stream and the plasma stream. The passivation layer may be formed from or comprise a passivation material. The substrate layer may be formed from or comprise a substrate material. The substrate layer may surround or be provided adjacent the passivation layer, away from the effluent stream and the plasma stream. The passivation material may be less chemically reactive to the effluent stream and the plasma stream than the substrate material. In this way, a composite or multi-layer reaction chamber is provided which has advantageous properties provided by both the substrate layer and the passivation layer, with the passivation layer being more resistant to the
-3effluent stream and the plasma stream and with the bulk material still being capable of coping with thermo-mechanical stress and transfer some heat to the coolant. These features can improve the life of the reaction chamber, which improves the life of the reaction chamber.
In one embodiment, the passivation material is more chemically resistant to the effluent stream and plasma stream than the substrate material.
In one embodiment, the passivation material is more chemically inert to the effluent stream and plasma stream than the substrate material.
In one embodiment, the passivation material is chemically less reactive to halogen radicals in the effluent stream and plasma stream than the substrate material.
In one embodiment, the substrate layer is more resistant to thermal fracture than the passivation layer. Providing a substrate layer that is more resistant to thermal fracture improves the bulk properties of the reaction chamber during rapid thermal cycling.
In one embodiment, the passivation layer is thinner than the substrate layer.
In one embodiment, the passivation material has a higher purity than the substrate material.
In one embodiment, the passivation material comprises at least one of: Alumina, Alumina Mullite, Zirconia, Yttria-Stabilized Zirconia, Zirconia Toughened Alumina, Fused Quartz, Yttria, Hafnia, Aluminosilicate and Lanthanum Hexaboride.
In one embodiment, the passivation layer is at least one of painted, physical deposited, chemical vapour deposited and sprayed onto the substrate layer.
-4ln one embodiment, the passivation layer comprises at least one of a sleeve and tiles fixed onto the substrate layer.
In one embodiment, the substrate material comprises one of a ceramic and a solid.
In one embodiment, the substrate material comprises a cement.
In one embodiment, the substrate material comprises a high alumina castable cement.
In one embodiment, the substrate material comprises AI2O3.
In one embodiment, the substrate material comprises AI2O3 having a purity of at least 90%.
According to a second aspect, there is provided a method of manufacturing a reaction chamber of a plasma torch abatement apparatus for treatment of an effluent stream from a processing tool with a plasma stream, comprising: forming a reaction chamber wall from a composite structure having a passivation layer formed from a passivation material and a substrate layer formed from a substrate material, the passivation layer facing the effluent stream and plasma stream and the passivation material being less chemically reactive to the effluent stream and plasma stream than the substrate material.
In one embodiment, the passivation material is more chemically resistant to the effluent stream and plasma stream than the substrate material.
In one embodiment, the passivation material is more chemically inert to the effluent stream and plasma stream than the substrate material.
-5ln one embodiment, the passivation material is chemically less reactive to halogen radicals in the effluent stream and plasma stream than the substrate material.
In one embodiment, the substrate layer is more resistant to thermal fracture than the passivation layer.
In one embodiment, the passivation layer is thinner than the substrate layer.
In one embodiment, the passivation material has a higher purity than the substrate material.
In one embodiment, the passivation material comprises at least one of: Alumina, Alumina Mullite, Zirconia, Yttria-Stabilized Zirconia, Zirconia Toughened Alumina, Fused Quartz, Yttria, Hafnia and Aluminosilicate and Lanthanum Hexaboride.
In one embodiment, the passivation layer is at least one of painted, physical deposited, chemical vapour deposited and sprayed onto the substrate layer.
In one embodiment, the passivation layer comprises at least one of a sleeve and tiles fixed onto the substrate layer.
In one embodiment, the substrate material comprises one of a ceramic and a solid.
In one embodiment, the substrate material comprises a cement.
In one embodiment, the substrate material comprises a high alumina castable cement.
In one embodiment, the substrate material comprises AI2O3.
-6ln one embodiment, the substrate material comprises AI2O3 having a purity of at least 90%.
In one embodiment, the substrate layer comprises a ceramic mix and the method comprises performing at least one annealing step on the ceramic mix.
In one embodiment, the substrate layer comprises a ceramic mix and the method comprises performing a plurality of annealing steps on the ceramic mix.
In one embodiment, the annealing steps elevate a temperature of the ceramic mix to an upper temperature.
In one embodiment, the annealing steps elevate the temperature of the ceramic mix from ambient to the upper temperature.
In one embodiment, the annealing steps elevate the temperature of the ceramic mix from ambient to the upper temperature one of continuously and discontinuously.
In one embodiment, each annealing step elevates the temperature of the ceramic mix to an elevated temperature for a first period and maintains the elevated temperature for a second period.
In one embodiment, the second period is longer than the first period.
In one embodiment, the method comprises controlling cooling of the ceramic mix following the plurality of annealing steps.
In one embodiment, the controlling cooling of the ceramic mix comprises reversing the annealing steps.
-7ln one embodiment, the controlling cooling cools the ceramic mix more slowly than the plurality of annealing steps heat the ceramic mix.
In one embodiment, a time taken to cool the ceramic mix is longer than a time taken to heat the ceramic mix.
In one embodiment, the method comprises mixing a ceramic with a fluid to form the ceramic mix.
In one embodiment, the fluid comprises water.
In one embodiment, the method comprises moulding the ceramic mix in a mould to form the reaction chamber.
In one embodiment, the method comprises agitating the ceramic mix within the mould to homogenise the ceramic mix.
In one embodiment, the method comprises agitating the ceramic mix within the mould to displace bubbles within the ceramic mix.
In one embodiment, the agitating comprises one of vibrating and rotating.
In one embodiment, the method comprises setting the ceramic mix within the mould.
In one embodiment, the method comprises removing the ceramic mix from the mould prior to performing the plurality of annealing steps.
Further particular and preferred aspects are set out in the accompanying independent and dependent claims. Features of the dependent claims may be combined with features of the independent claims as appropriate, and in combinations other than those explicitly set out in the claims.
-8Where an apparatus feature is described as being operable to provide a function, it will be appreciated that this includes an apparatus feature which provides that function or which is adapted or configured to provide that function.
BRIEF DESCRIPTION OF THE DRAWINGS
Embodiments of the present invention will now be described further, with reference to the accompanying drawings, in which:
Figures 1 and 2 illustrate components of a plasma torch abatement apparatus in cross-section according to one embodiment;
Figure 3 illustrates components of a plasma torch abatement apparatus of Figures 1 and 2 in perspective with the anode and cathode omitted to improve clarity; and
Figure 4 illustrates a cross-section through a reaction chamber according to one embodiment.
DESCRIPTION OF THE EMBODIMENTS
Before discussing the embodiments in any more detail, first an overview will be provided. Embodiments provide a multi-material reaction chamber. The reaction chamber is typically a tubular structure. An inner volume of the tubular structure defines a void within which plasma abatement occurs. A substrate is provided which forms the bulk of the reaction chamber wall. A layer of passivation material is provided on the inner surface of the reaction chamber, on top of the substrate material. The passivation material provides greater chemical resistance to reactants within the reaction chamber. Providing a comparatively thinner passivation layer compared to the substrate layer provides both a more cost effective reaction chamber and a reaction chamber with improved thermal properties compared to one formed solely from the passivation material, which tends to be more susceptible to damage during thermal cycling. A variety of different techniques may be employed to create the multi-material structure, such as physical or chemical deposition techniques, thermal baking, curing or annealing steps of both the passivation and the substrate material, providing a
-9separate passivation layer and fitting that together with the substrate layer. This arrangement helps to improve the life of the reaction chamber.
Plasma Torch Abatement Apparatus
Figures 1 and 2 illustrate components of a plasma torch abatement apparatus, generally 10, in cross-section according to one embodiment. Figure 3 illustrates components of the plasma torch abatement 10 in perspective. The plasma torch abatement apparatus 10 comprises a cathode 12 upstream of an opening of a generally tubular anode 14. A space is provided between the cathode 12 and the anode 14 through which a plasma source gas 16 (a neutral, inert gas such as, but not limited to argon or nitrogen) can flow. The cathode 12 and the anode 14 is electrically connected to a power supply (not shown) which is configured to apply a direct current between the cathode 12 and the anode 14 or an alternating current to either or both of the cathode 12 and the anode 14. The magnitude and frequency of the current required is generally determined and selected by reference to other process parameters, such as effluent stream or plasma source gas species and flow rate, the cathode-anode spacing, gas temperature, etc.
The voltage magnitude of the plasma discharge is directly influenced by these parameters. In any event, an appropriate, initial high-voltage regime is one that causes the plasma source gas 16 to ionise and thereby form a plasma (in a process known as breakdown).
The cathode 12 is typically manufactured from a high-conductivity metal, such as copper. A downstream-facing end of the cathode 12 may provide a preferential electrical discharge site which is accomplished by selecting a different material for this portion than the main body of the cathode 12, i.e. the main body of the cathode 12 is typically formed of a conducting material with a higher thermal conductivity than that of the thermionic material of the downstream-facing portion. For example, it would be typical to use a copper cathode body and a hafnium or thoriated tungsten downstream-facing portion. The anode 14 can then be formed of a similar material to the main body of the cathode 12; for example, copper.
The plasma stream 18 is thus nucleated in the small region immediately below
- 10the cathode 12, guided by a frusto-conical portion of the anode 14 and exits as a jet from the anode 14.
In order to generate the plasma, the plasma source gas 16 (typically a moderately inert ionisable gas such as nitrogen or argon) is conveyed to the region between the cathode 12 and the anode 14. To initiate or start the plasma, a breakdown must first be generated between the cathode 12 and the anode 14. This is typically achieved by a high frequency, high voltage signal which may be provided by a generator associated with the power supply (not shown). The difference in thermal conductivity between the main body of the cathode 12 and the downstream-facing portion means that the cathode temperature will be higher and the electrons are preferably emitted from the downstream-facing portion. Therefore, when the signal is provided between the cathode 12 and the anode 14, an arc discharge is induced in the plasma source gas 16. The arc forms a current path between the anode 14 and the cathode 12, the plasma is then maintained by a controlled direct current between the anode 14 and the cathode
12. The plasma source gas 16 produces a high momentum plasma stream 18 of ionised plasma source gas 16.
Venturi Cone
Downstream of the anode 14 is a Venturi cone 20. The Venturi cone 20 comprises an inwardly-tapering, frusto-conical portion leading to a substantially parallel-sided throat portion. An annular space is provided between the anode 14 and the Venturi cone 20 through which an effluent gas stream 22 to be processed and a secondary gas stream 24 is provided. The secondary gas stream 24 may be compressed dry air or other gases and is typically used as a reagent to assist in the downstream reaction. The effect of the geometry of the Venturi cone 20 is to accelerate and compress the incoming gases to create a region of relatively high speed, relatively compressed gas in a region downstream of the anode 14 to assist with drawing in the effluent gas stream 22 and the secondary gas 24 and facilitate mixing with the plasma stream 18. The high speed of gas exiting from
- 11 the Venturi cone 20 can promote turbulence to enhance the mixing of the plasma stream 18, effluent gas stream 22 and secondary gas stream 24.
Reaction Chamber
Downstream of the Venturi cone 20 is provided a reaction chamber 26. The reaction chamber receives the plasma stream 18 mixed with the effluent gas stream 22 and secondary gas stream 24. The reaction chamber 26 is a cylindrical tube coaxially aligned with the cathode 12, anode 14 and the Venturi cone 20.
The reaction chamber 26 has an inner surface 26A which defines a cylindrical space within which the plasma stream 18, effluent gas stream 22 and secondary gas stream 24 are received. As will be appreciated, an intense heat is generated by the plasma stream 18 and this heat, together with reagents within the secondary gas stream 24, help to break down compounds within the effluent gas stream 22. An axial length of the reaction chamber 26 helps to increase the residence time of the effluent gas stream 22 within the reaction chamber 26 and improve its Destruction and Removal Efficiency (DRE). Most of the energy is confined inside the internal volume of the reaction chamber 26.
A water jacket 28 concentrically surrounds the reaction chamber 26. An air gap 30 separates an inner wall 28A of the water jacket 28 from the reaction chamber
26. An outer wall 28B concentrically surrounds the inner wall 28A and defines a tubular void 28C which receives a coolant, such as water. The reaction chamber 26 is indirectly cooled by the coolant through radiative heat transfer across the air gap 30 and directly by thermal contact at either end of the reaction chamber 26. Most of the energy generated by the plasma stream 18 is confined inside the internal volume of the reaction chamber.
Typically, the reaction chamber 26 is formed from a cement such as a High Alumina Castable (HAC) cement. Such cements need to be able to withstand the high temperatures generated by the plasma stream 18, withstand the thermal
- 12shock caused by switching the plasma stream 18 on and off, and deal with the effects of the different gas streams.
Reaction Tube Casting
Embodiments provide a long-life reaction chamber 26 which is less prone to failure. Table 1 shows the main steps to manufacture the reaction chamber 26.
Step Process Description
S1 Preparation Cement HACT180S (93% AI2O3)
Preparation water Water 320 gram
Preparation outer mould Stainless steel 316L
Preparation inner mould Stainless steel
Mould support Steel
Ceramic powder into the bowl HACT-180S 2100 gram
Mix ceramic powder 1 minute, manual
Water into the bowl Water 320 gram
Mix ceramic powder and water 5 minutes, manual
S2 Mixed ceramic power with water into mould Remove bubbles with shaker
S3 Protect top of reaction tube with mould Steel
Fix inner mould with bolt
S4 Dry the complete tube+ cast assembly 24 hours
S5 Remove the inner mould Press
S6 Baking the reaction tube in oven see table 2/3
S7 Cooling down reaction tube 1 day min.
Table 1
- 13At step S1, a ceramic powder cement is mixed in a bowl with a mixing fluid such as water for a period of time by mechanical mixing.
At step S2, the mixed cement and fluid is poured in to a void created by an inner and outer mould for forming the reaction chamber 26. The mould is agitated in order to reduce the presence of any bubbles or voids within the cement and fluid mix. The mould may also be agitated in order to increase the homogeneity of the cement and fluid mix.
io
At step S3, the mould is closed and the inner mould is fixed with a bolt.
At step S4, the cement and fluid mix is allowed to set within the mould.
At step S5, a press is used to remove the inner mould and the outer mould is removed.
At step S6, the reaction tube 26 removed from the mould and is baked in an oven which follows a temperature profile to perform a sequence of one or more annealing steps. The temperature profile increases the temperature of the reaction chamber 26 in ramped steps and maintains that temperature for a period in order to perform iterative annealing. The most elevated annealing temperature is set to exceed the operating temperature of the reaction chamber 26. One embodiment follows the temperature profile shown in Table 2.
Step Temp range duration
1 ambient -180 °C ramp 60 minutes
2 180-360 °C ramp 60 minutes
3 360-540 °C ramp 60 minutes
4 540-720 °C ramp 60 minutes
5 720-900 °C ramp 60 minutes
6 900 °C steady plateau 60 mins
Total time: 6 hours
Table 2
Another embodiment follows the temperature profile shown in Table 3.
Step Temp range duration
1 Room Temp - 500°C 60 minutes (increase gradually)
2 500°C 10 minutes of maintenance
3 500 - 900 °C 60 minutes (increase gradually)
4 900 °C 180 minutes of maintenance
Table 3 io At step S7, the reaction tube undergoes controlled cooling. Typically, this involves allowing the reaction chamber to cool to ambient inside the oven. In one embodiment, the reaction chamber is cooled by following the temperature profile of the annealing steps but in reverse order.
- 15Passivation Layer
In one embodiment, the reaction chamber 26 has a passivation layer, as shown in Figure 4. The passivation layer improves the chemical inertness of the inner surface 26A of the reaction chamber 26 when in contact with halogen radicals generated during the plasma phase of the abatement. The passivation layer is formed by one or more materials which are halogen resistant (for example, fluorine) at high temperatures. Suitable materials include: AL=ALumina, AM=Alumina Mullite (corundum), ZR= ZiRconia, YSZ=Yttria-Stabilized Zirconia (fully stabilized), ZTA = Zirconia Toughened Alumina, FQ = Fused Quartz (Silica), io YR=Yttria, HF=Hafnia, AS= aluminosilicate (sillimanite) and/or LaB6 =
Lanthanum Hexaboride.
The passivation layer 26B is typically provided as a layer deposited on at least the inner surface 26A of the reaction chamber 26. The passivation layer may also be deposited to extend on to one or more of the annular ends of the reaction chamber 26.
Providing a comparatively thin passivation layer 26B compared to the thickness of the reaction chamber 26 reduces the thermal shock experienced by the passivation layer 26B when the plasma stream 18 is started and stopped, while still providing chemical protection to the underlying structure of the reaction chamber 26.
A variety of different techniques may be employed to deposit the passivation layer 26B on the reaction chamber 26. These techniques are shown in Table 4:
Main Techniques Available materials Additional processes
AL AM ZR YSZ SC ZTA FQ YR HF AS LaB6
Refractory paint X X X X X Curing the paint with an additional baking step
Sputter coating X X X X X X X X Heating of substrate, annealing of coating
Sleeve/tiles insert X X X X X X X X X X Insert tiles or sleeve on fresh cement (after step S2 of Table 1)
It will be appreciated that additional techniques, such as physical vapour deposition and chemical vapour deposition may also be utilised.
Accordingly, embodiments increase the ceramic reaction tube lifetime employed in plasma abatement systems. Embodiments create a passivation layer in order to improve the chemical inertness of its internal wall when in contact with halogen radicals generated during the plasma phase of the abatement.
Embodiments utilise a hollow cylinder named “ceramic reaction tube” in the socalled reaction section of a plasma system. The internal volume encompassed by the tube is the area where the main reaction takes place. Here converge the thermal plasma generated by the DC-arc torch, the process gas and the reagent respectively after being mixed by crossing a coned orifice called “Venturi cone”.
- 17Compressed dried air (CDA) is typically used as a reagent returning a dry reaction possible free from corrosion from acid such as HF, HCI.
The reaction tube is indirectly cooled by cooling water (PCW) through radiative heat transfer across the air gap and directly by the thermal contact at the bottom of the reaction section. Most of the torch energy has to be confined inside the internal volume of the tube (hence the choice of the cooling design and the insulating ceramic material for the tube). The tube can be elongate in order to increase the residence time of the effluent gas to be treated. All of these features improve the Destruction and Removal Efficiency (DRE) of the system.
In embodiments, the tube is formed by employing “High Alumina Castable” (HAC) cement between an internal mould and an external shell (a stainless steel tube of appropriate dimension. The recipe to prepare the tube is described above. Tube life time is a function of the erosion rate of the HAC cement. The hightemperature can change the chemical state of AI2O3 enabling the halogens to attack it. Experiments have shown that HAC cement with >90% of AI2O3 content and a baking/annealing temperature of up to 900°C are required for an acceptable part lifetime.
Other key factors to improve the tube lifetime are the increases of both the Venturi cone aperture and of the tube bore itself. Both result in an increase the space between the tube and plasma plume but they have an impact on DRE.
The tube preparation described above deals with techniques to prepare the tube cement free from defect (inhomogeneous density, trapped bubbles etc.). The temperature profiles mentioned illustrate in detail the steps to anneal the HAC cement to allow a partial sintering of its particles. This makes the tube less permeable to erosion.
The HAC reaction tube is fit for the purpose due its excellent thermo-mechanical (T-M) properties. Experimental data shows HAC tubes sitting under the “hot”
- 18plasma plume for some weeks without loss of material, while tests with a similar tube made of pure alumina cracks in minutes due the T-M stress.
Embodiments passivate the tube internal wall with a purer material with improved 5 chemical resistance. This layer is made thin so that the T-M properties of the bulk material (HAC cement) are retained. This allows also to use a small amount of exotic materials in this layer while minimizing the part cost. This layer can be made a high purity Alumina (AL), Alumina Mullite (corundum - AM), Zirconia (ZR), Yttria-Stabilized Zirconia (fully stabilized - YSZ), Zirconia Toughened
Alumina (ZTA), Fused Quartz (Silica - ZTA FQ),Yttria (YR), Hafnia (HF), aluminosilicate (sillimanite - AS). With regard to the techniques to build this passivation layer one can use the following:
a) Some materials are available as refractory paint allowing the layer to be applied with a brush and then cured in oven in a further thermal step;.
b) Thermal plasma spray coating; this technique allows a layer with excellent quality to be deposited onto the tube wall.
c) Tile or sleeve insert; a sleeve or some tiles are typically applied to the internal wall while the HAC cement is still wet; these tiles (or the sleeve) can stay attached to the tube internal wall due to the cement cohesion forces.
Although illustrative embodiments of the invention have been disclosed in detail herein, with reference to the accompanying drawings, it is understood that the invention is not limited to the precise embodiment and that various changes and modifications can be effected therein by one skilled in the art without departing from the scope of the invention as defined by the appended claims and their equivalents.
- 19REFERENCE SIGNS
plasma torch abatement apparatus 10
cathode 12
anode 14
plasma source gas 16
plasma stream 18
venturi cone 20
effluent gas stream 22
secondary gas stream 24
reaction chamber 26
inner surface 26a
passivation layer 26b
water jacket 28
inner wall 28a
outer wall 28b
tubular void 28c
air gap 30

Claims (17)

1. A plasma torch abatement apparatus for treatment of an effluent stream from a processing tool with a plasma stream, comprising:
5 a reaction chamber defined by a reaction chamber wall for receiving said effluent stream and said plasma stream, said reaction chamber wall comprising a composite structure having a passivation layer facing said effluent stream and said plasma stream, said passivation layer being formed from a passivation material, said composite structure having a io substrate layer formed from a substrate material surrounding said passivation layer, said passivation material being less chemically reactive to said effluent stream and said plasma stream than said substrate material.
15
2. The plasma torch abatement apparatus of claim 1, wherein said substrate layer is more resistant to thermal fracture than said passivation layer.
3. The plasma torch abatement apparatus of claim 1 or 2, wherein said passivation layer is thinner than said substrate layer.
4. The plasma torch abatement apparatus of any preceding claim, wherein said passivation material comprises at least one of: Alumina, Alumina Mullite, Zirconia, Yttria-Stabilized Zirconia, Zirconia Toughened Alumina, Fused Quartz, Yttria, Hafnia and Aluminosilicate and Lanthanum
25 Hexaboride.
5. The plasma torch abatement apparatus of any preceding claim, wherein said passivation layer is at least one of painted, phyiscal deposited, chemical vapour deposited and sprayed onto said substrate layer.
-21
6. The plasma torch abatement apparatus of any preceding claim, wherein said passivation layer comprises at least one of a sleeve and tiles fixed onto said substrate layer.
7. The plasma torch abatement apparatus of any preceding claim, wherein said substrate material comprises a high alumina castable cement.
8. A method of manufacturing a reaction chamber of a plasma torch io abatement apparatus for treatment of an effluent stream from a processing tool with a plasma stream, comprising:
forming a reaction chamber wall from a composite structure having a passivation layer formed from a passivation material and a substrate layer formed from a substrate material, said passivation layer facing said
15 effluent stream and plasma stream and said passivation material being less chemically reactive to said effluent stream and plasma stream than said substrate material.
9. The method of manufacturing of claim 8, wherein said substrate layer is
20 more resistant to thermal fracture than said passivation layer.
10. The method of manufacturing of claim 8 or 9, wherein said substrate layer comprises a ceramic mix and said method comprises performing at least one annealing step on said ceramic mix.
11. The method of manufacturing of any one of claims 8 to 10, wherein said annealing steps elevate a temperature of said ceramic mix to an upper temperature.
-2212. The method of manufacturing of claims 10 or 11, comprising controlling cooling of said ceramic mix following said annealing steps.
13. The method of manufacturing of any one of claims 10 to 12, comprising
5 mixing a ceramic with a fluid to form said ceramic mix.
14. The method of manufacturing of any one of claims 8 to 10, wherein said forming comprises moulding said ceramic mix in a mould to form said reaction chamber.
io
15. The method of manufacturing of claim 14, comprising agitating said ceramic mix within said mould to homogenise said ceramic mix.
16. The method of manufacturing of claim 14 or 15, comprising agitating said
15 ceramic mix within said mould to displace bubbles within said ceramic mix.
17. A plasma torch abatement apparatus or method of manufacturing as hereinbefore described with reference to the accompanying drawings.
Intellectual
Property
Office
-23Application No: GB1616286.9 Examiner: Dr Rhys Williams
GB1616286.9A 2016-09-26 2016-09-26 Plasma abatement Withdrawn GB2554406A (en)

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GB1616286.9A GB2554406A (en) 2016-09-26 2016-09-26 Plasma abatement
TW106213595U TWM561683U (en) 2016-09-26 2017-09-13 Plasma torch abatement apparatus for treatment of an effluent stream from a processing tool with a plasma stream
KR2020170004992U KR20180000936U (en) 2016-09-26 2017-09-22 Plasma abatement
CN201721240822.2U CN207868157U (en) 2016-09-26 2017-09-26 Plasma torch cancellation element

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Publication number Priority date Publication date Assignee Title
GB2165827A (en) * 1984-10-23 1986-04-23 Skf Steel Eng Ab Cleaning waste gases
JPH06287095A (en) * 1993-04-02 1994-10-11 Toshiba Corp Heat-resistant ceramic and its production
WO2003095072A1 (en) * 2002-05-08 2003-11-20 Lau, Edmund, Kin, On Hazardous waste treatment method and apparatus
US20050115674A1 (en) * 2002-02-14 2005-06-02 Hiroyasu Taguchi Method for treating exhaust gas
CN1644992A (en) * 2005-01-24 2005-07-27 真一(上海)集成电路设备有限公司 Combustion chamber structure of waste gas treating system
EP1865255A2 (en) * 2006-06-07 2007-12-12 Global Standard Technology Co., Ltd. Apparatus for treating a waste gas using plasma torch
KR20130023795A (en) * 2011-08-30 2013-03-08 주식회사 아이지티 Waste gas treatment apparatus using plasma and waste gas treating method using the same
KR20140104848A (en) * 2013-02-21 2014-08-29 주식회사 지앤비에스엔지니어링 Combustible gas scrubber
CN204063061U (en) * 2014-08-29 2014-12-31 河南中易环保科技有限公司 A kind of plasma furnace for the treatment of domestic waste incineration flue gas

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2165827A (en) * 1984-10-23 1986-04-23 Skf Steel Eng Ab Cleaning waste gases
JPH06287095A (en) * 1993-04-02 1994-10-11 Toshiba Corp Heat-resistant ceramic and its production
US20050115674A1 (en) * 2002-02-14 2005-06-02 Hiroyasu Taguchi Method for treating exhaust gas
WO2003095072A1 (en) * 2002-05-08 2003-11-20 Lau, Edmund, Kin, On Hazardous waste treatment method and apparatus
CN1644992A (en) * 2005-01-24 2005-07-27 真一(上海)集成电路设备有限公司 Combustion chamber structure of waste gas treating system
EP1865255A2 (en) * 2006-06-07 2007-12-12 Global Standard Technology Co., Ltd. Apparatus for treating a waste gas using plasma torch
KR20130023795A (en) * 2011-08-30 2013-03-08 주식회사 아이지티 Waste gas treatment apparatus using plasma and waste gas treating method using the same
KR20140104848A (en) * 2013-02-21 2014-08-29 주식회사 지앤비에스엔지니어링 Combustible gas scrubber
CN204063061U (en) * 2014-08-29 2014-12-31 河南中易环保科技有限公司 A kind of plasma furnace for the treatment of domestic waste incineration flue gas

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CN207868157U (en) 2018-09-14
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TWM561683U (en) 2018-06-11

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