TW201350191A - Apparatus and method for processing gas - Google Patents

Apparatus and method for processing gas Download PDF

Info

Publication number
TW201350191A
TW201350191A TW102120172A TW102120172A TW201350191A TW 201350191 A TW201350191 A TW 201350191A TW 102120172 A TW102120172 A TW 102120172A TW 102120172 A TW102120172 A TW 102120172A TW 201350191 A TW201350191 A TW 201350191A
Authority
TW
Taiwan
Prior art keywords
gas
flow path
catalyst layer
catalyst
electric field
Prior art date
Application number
TW102120172A
Other languages
Chinese (zh)
Inventor
Yuki Sato
Masanori Ohyama
Original Assignee
Kyoritsu Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kyoritsu Co Ltd filed Critical Kyoritsu Co Ltd
Publication of TW201350191A publication Critical patent/TW201350191A/en

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/58Platinum group metals with alkali- or alkaline earth metals
    • 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8659Removing halogens or halogen compounds
    • B01D53/8662Organic halogen compounds
    • B01J35/33
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/40Alkaline earth metal or magnesium compounds
    • B01D2251/404Alkaline earth metal or magnesium compounds of calcium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/102Platinum group metals
    • B01D2255/1021Platinum
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20738Iron
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20746Cobalt
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20753Nickel
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20769Molybdenum
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/80Type of catalytic reaction
    • B01D2255/802Photocatalytic
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/80Type of catalytic reaction
    • B01D2255/806Electrocatalytic
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/20Halogens or halogen compounds
    • B01D2257/206Organic halogen compounds
    • B01D2257/2066Fluorine
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/55Compounds of silicon, phosphorus, germanium or arsenic
    • B01D2257/553Compounds comprising hydrogen, e.g. silanes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0216Other waste gases from CVD treatment or semi-conductor manufacturing
    • 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
    • B01D2259/804UV light
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/02Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the alkali- or alkaline earth metals or beryllium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/40Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals of the platinum group metals
    • B01J23/42Platinum
    • B01J35/19
    • B01J35/56
    • 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]

Abstract

Provided is an apparatus which is capable of processing a PFC gas and the like. This apparatus comprises: a channel in which at least some of a gas to be processed is exposed to a high-frequency electric field or ultraviolet irradiation; a catalyst layer to which the gas having passed through the channel is supplied; and a voltage supply unit which applies a bias voltage to the catalyst layer. By processing a gas to be processed, which has been converted into radicals by atmospheric pressure plasma formed by a high-frequency electric field, with the catalyst layer to which a bias voltage is applied, the gas to be processed can be processed at low temperature. The catalyst layer is a platinum catalyst having a porous structure, typically a honeycomb structure, and internally contains a layer that is filled with particulate slaked lime.

Description

氣體處理裝置及方法 Gas treatment device and method

本發明係有關對全氟碳化物(PFC)等之處理對象氣體所含有的分子進行分解處理之裝置及方法。 The present invention relates to an apparatus and method for decomposing molecules contained in a gas to be treated such as perfluorocarbon (PFC).

在日本國特開2005-7341號公報中記載:為提供以小型的裝置有效率地完全分解有機鹵素化合物的方法和裝置而提案一種有機鹵素化合物的分解方法,其特徵為,將PFC等之有機鹵素化合物與丙烷氣體等之可燃物質和氧或含氧氣體混合,使所獲得的混合物利用燃燒器進行火焰自由基反應,將反應中的混合物以熱電漿裝置一邊進行電漿處理一邊與活性氧化鋁或二氧化鈦等之觸媒層接觸而分解有機鹵素化合物。 Japanese Laid-Open Patent Publication No. 2005-7341 discloses a method for decomposing an organic halogen compound in order to provide a method and an apparatus for efficiently decomposing an organic halogen compound efficiently by a small device, which is characterized in that an organic solvent such as PFC is used. The halogen compound is mixed with a combustible substance such as propane gas and oxygen or an oxygen-containing gas, and the obtained mixture is subjected to a flame radical reaction by a burner, and the mixture in the reaction is subjected to plasma treatment with a hot plasma apparatus while being activated with alumina. The organic halogen compound is decomposed by contact with a catalyst layer such as titanium dioxide.

[先行技術文獻] [Advanced technical literature] [專利文獻] [Patent Literature]

【專利文獻1】日本國專利特開2005-7341號公報 [Patent Document 1] Japanese Patent Laid-Open Publication No. 2005-7341

對氣體進行改質或分解的製程以含有數100℃或其以上的高溫處理居多。用在半導體製造工場之蝕刻、清淨等的全氟碳化物氣體(以下稱為PFC)雖無反應性、毒性而穩定,但具有強力的溫室效應(地球暖化係數係CO2的6000至10,000倍程度)。PFC,考量其穩定性,一般是採用以高溫使之燃燒的除害方式。在除害過程所產生之酸性的氟氣(以下稱為F2)係溶於水而另外進行排水處理。以此種方式處理氣體的裝置,係因曝露在高溫的酸性氣體而易於腐蝕,運轉(running)成本高。又,為確保對多半處理可燃性氣體的半導體工場之安全性,高溫部分的斷熱、冷卻是必須的,成為加大溶有酸性氣體的水之處理設備及除害裝置的尺寸之要因。 The process of modifying or decomposing the gas is mostly carried out at a high temperature containing several hundred ° C or more. Perfluorocarbon gas (hereinafter referred to as PFC), which is etched and cleaned in a semiconductor manufacturing plant, is stable without toxicity and toxicity, but has a strong greenhouse effect (the global warming coefficient is 6000 to 10 of CO 2 , 000 times). PFC, considering its stability, generally uses a detoxification method that burns at high temperatures. The acidic fluorine gas (hereinafter referred to as F 2 ) generated during the detoxification process is dissolved in water and additionally subjected to drainage treatment. The apparatus for treating a gas in this manner is susceptible to corrosion due to exposure to a high-temperature acid gas, and the running cost is high. In addition, in order to ensure the safety of a semiconductor factory that processes a flammable gas, it is necessary to heat and cool the high temperature portion, and it is a factor for increasing the size of the processing equipment and the detoxification device for the water in which the acid gas is dissolved.

因此,在對PFC等之氣體進行分解、改質的處理裝置方面,企盼一種小型且能低溫化,並且運轉成本低的裝置。 Therefore, in the case of a processing apparatus that decomposes and reforms a gas such as PFC, a device that is small and can be cooled at a low temperature and has a low running cost is desired.

本發明的一態樣為一種處理裝置,其具有:流路,其處理對象的氣體之至少一部分被曝露在高頻電場或紫外線照射中;觸媒層,被供給已通過前述流路的氣體;及電壓供給單元,對前述觸媒層施加偏壓。透過施加偏壓(偏壓電場)於觸媒層可使觸媒活性化,能提升氣體的處理效率。再者,利用依高頻電場所生成之RF電漿或紫外線照射之反應,可在低溫且大氣壓下將處理對象氣體分子的至少一部分 自由基化並供予觸媒層。因此,能提供一種低溫且高效率藉觸媒層處理(分解或改質)氣體的處理裝置。因此,能提供一種可抑制因熱或酸性氣體使裝置的構成構件腐蝕,且以低運轉成本並對於周圍的安全性亦高的氣體處理裝置。 An aspect of the present invention is a processing apparatus having a flow path in which at least a part of a gas to be treated is exposed to a high-frequency electric field or ultraviolet ray; and a catalyst layer is supplied with a gas that has passed through the flow path; And a voltage supply unit that applies a bias voltage to the catalyst layer. By applying a bias voltage (biased electric field) to the catalyst layer, the catalyst can be activated, and the gas treatment efficiency can be improved. Furthermore, at least a part of the gas molecules to be treated can be treated at a low temperature and an atmospheric pressure by using a reaction of RF plasma or ultraviolet light generated by a high-frequency electric field. Free radicalization and supply to the catalyst layer. Therefore, it is possible to provide a treatment apparatus which treats (decomposes or reforms) a gas at a low temperature and with high efficiency by a catalyst layer. Therefore, it is possible to provide a gas processing apparatus capable of suppressing corrosion of constituent members of the apparatus due to heat or acid gas, and having high running cost and high safety to the surroundings.

施加於觸媒層的偏壓可為交流,直流亦可,但典型的是直流偏壓較佳。透過對觸媒表面賦予電荷或電洞,能以低消耗電力使觸媒活性化。因此,利用白金等之觸媒可期待像光觸媒那樣的效果。 The bias applied to the catalyst layer may be AC or DC, but DC bias is typically preferred. By imparting a charge or a hole to the surface of the catalyst, the catalyst can be activated with low power consumption. Therefore, effects such as photocatalyst can be expected by using a catalyst such as platinum.

紫外線照射,係攻撃處理對象氣體中的分子鍵結並予以切斷。在此同時,從空氣中的氧生成反應性高的氧自由基,藉以促進觸媒層中的處理。紫外線可以是近紫外線,亦可以是極紫外線,波長短能量高,而且較容易遮蔽的真空紫外線(波長200nm以下程度)較佳。處理裝置含有產生真空紫外線的紫外線源較佳。產生真空紫外線的紫外線源之一為準分子光照射單元。 Ultraviolet irradiation is a process of attacking and cutting off molecular bonds in the gas to be treated. At the same time, highly reactive oxygen radicals are generated from oxygen in the air to promote processing in the catalyst layer. The ultraviolet ray may be near ultraviolet ray, or may be extremely ultraviolet ray, and the wavelength is short and the energy is high, and vacuum ultraviolet rays (having a wavelength of 200 nm or less) which are easier to shield are preferable. The treatment device preferably contains an ultraviolet source that generates vacuum ultraviolet rays. One of the ultraviolet sources that generate vacuum ultraviolet rays is an excimer light irradiation unit.

使用高頻電源在處理對象氣體中生成RF電漿亦為有效。透過在處理對象氣體中生成RF電漿(大氣壓電漿),可減弱處理對象氣體的分子鍵結,促進氧自由基的生成。 It is also effective to generate RF plasma in the treatment target gas using a high frequency power source. By generating RF plasma (atmospheric piezoelectric slurry) in the gas to be processed, molecular bonding of the gas to be treated can be weakened, and generation of oxygen radicals can be promoted.

較佳為,處理裝置更具有:複數個電極,位在前述流路的兩側,形成高頻電場;及介電質層,配置成包夾前述複數個電極。複數個電極亦包含實質上作為電極發揮機能的外殼等構件。以處理對象氣體和載氣一起供給至處理裝置的情況居多。例如,氮比氬還難以電離,從經濟性的觀點,以將氮用作PFC的載氣的情況居多。為了在氮氣環境下形成 RF電漿而有必要施加高電場,容易從輝光放電轉換成電弧放電。然而,由於電弧放電易變高溫故加以回避較佳。透過將介電質層配置成被電極包夾而能利用介電質屏蔽放電,透過縮短放電週期可抑制轉換成電弧放電。 Preferably, the processing device further includes: a plurality of electrodes positioned on both sides of the flow path to form a high frequency electric field; and a dielectric layer disposed to sandwich the plurality of electrodes. The plurality of electrodes also include members such as a casing that functions substantially as an electrode. The processing gas and the carrier gas are supplied together to the processing apparatus. For example, nitrogen is more difficult to ionize than argon, and from the viewpoint of economy, nitrogen is used as a carrier gas for PFC. In order to form under a nitrogen atmosphere It is necessary to apply a high electric field to the RF plasma, and it is easy to convert from a glow discharge to an arc discharge. However, since the arc discharge is apt to become high temperature, it is preferable to avoid it. By disposing the dielectric layer so as to be sandwiched by the electrodes, it is possible to utilize the dielectric shield discharge, and it is possible to suppress the conversion into an arc discharge by shortening the discharge period.

介電質層係以含有複數個凹凸構造者較佳。凸部比凹部還難引起放電。因而作成使小面積的電漿電極聚積的狀態,可加大放電面積的總和,可拉長氣體暴露在高頻電場的時間(距離)。 The dielectric layer is preferably one having a plurality of concavo-convex structures. The convex portion is harder to cause discharge than the concave portion. Therefore, in a state in which a small-area plasma electrode is accumulated, the sum of the discharge areas can be increased, and the time (distance) at which the gas is exposed to the high-frequency electric field can be elongated.

又,於流路的上游配置針電極是有效的。當於流路中流通大量的氣體時則流路內成為高壓的可能性高,在高壓下不易引起放電,當引起放電時則容易轉換成電弧放電。一方面,當加寬流路的寬度降低阻力時,則因電極間隔變大而變得不易引起放電。因此,將針電極設在流路的上游使之進行放電而將氣體分子的一部分電離,藉以在氣體中生成作為電子或電洞的載子之離子。因使氣體中的離子增加而變得在針電極的下游容易引起放電。因此,RF電漿的生成變容易,可拉長氣體通過RF電漿的時間(距離)。 Further, it is effective to arrange the needle electrode upstream of the flow path. When a large amount of gas flows through the flow path, there is a high possibility that the flow path becomes high pressure, and discharge is less likely to occur under high pressure, and when discharge occurs, it is easily converted into an arc discharge. On the other hand, when the width of the widened flow path is reduced, the discharge becomes less likely to cause discharge due to the increase in the electrode interval. Therefore, the needle electrode is provided upstream of the flow path to discharge it, and a part of the gas molecules are ionized, whereby ions as carriers of electrons or holes are generated in the gas. It becomes easy to cause discharge at the downstream of the needle electrode due to an increase in ions in the gas. Therefore, the generation of RF plasma becomes easy, and the time (distance) of the gas passing through the RF plasma can be elongated.

處理裝置更具有沿著流路斷續地配置的磁場生成單元者較佳。典型的磁場生成單元係永久磁鐵,電磁鐵亦可。透過沿著流路形成適當的磁場,可將電子關入流路而擴大放電區域,沿著流路順暢地引導含有自由基離子的氣體。 It is preferable that the processing apparatus further has a magnetic field generating unit that is intermittently arranged along the flow path. A typical magnetic field generating unit is a permanent magnet or an electromagnet. By forming an appropriate magnetic field along the flow path, electrons can be trapped in the flow path to expand the discharge region, and the gas containing the radical ions can be smoothly guided along the flow path.

在流路的兩側呈同心圓狀地配置複數個電極的處理裝置中,設置對外側的電極施加負電位的單元亦是有效。因電漿中的電子藉由負電位而跳回,可抑制電極表面中 之電子的損失。因此,可獲得關閉住電漿,促進電漿中之電離的效果(空心陰極效應),可促進自由基化。 In a processing apparatus in which a plurality of electrodes are arranged concentrically on both sides of a flow path, it is also effective to provide a means for applying a negative potential to the outer electrodes. Since the electrons in the plasma jump back by the negative potential, the surface of the electrode can be suppressed. The loss of electronics. Therefore, the effect of shutting off the plasma and promoting ionization in the plasma (hollow cathode effect) can be obtained, and radicalization can be promoted.

觸媒層,典型的是包含或擔持白金的載體。觸媒層係由鎳(Ni)、鉬(Mo)、鈷(Co)、白金(Pt)、鐵(Fe)等之金屬、包含鎳、鐵及鈷當中的至少2種的合金,或有機金屬等所構成。觸媒層亦可以是含有或擔持上述的金屬、合金或有機金屬的載體。 The catalyst layer is typically a carrier containing or supporting platinum. The catalyst layer is made of a metal such as nickel (Ni), molybdenum (Mo), cobalt (Co), platinum (Pt), iron (Fe), or an alloy containing at least two of nickel, iron, and cobalt, or an organic metal. And so on. The catalyst layer may also be a carrier containing or supporting the above metals, alloys or organometallics.

本發明的另一不同態樣之一為一種氣體的處理方法,包含以下的步驟。 Another aspect of the present invention is a method of treating a gas comprising the following steps.

1.使處理對象氣體的至少一部分通過被曝露在高頻電場或紫外線照射的流路。 1. At least a part of the gas to be treated is passed through a flow path that is exposed to a high-frequency electric field or ultraviolet light.

2.將已通過流路的氣體供予被施加偏壓的觸媒層。 2. The gas that has passed through the flow path is supplied to the biased catalyst layer.

以於流路的兩側包夾介電質層般地配置用以形成高頻電場的電極,作成可進行介電質屏蔽放電,較佳為,通過上述流路係包含使處理對象氣體通過生成介電質屏蔽放電的流路。利用藉介電質屏蔽放電所形成的RF電漿(大氣電漿),能以低溫有效率地將大量的處理對象氣體自由基化(自由基離子化),能利用觸媒反應以低溫將氣體有效率地分解或改質。 An electrode for forming a high-frequency electric field is disposed on both sides of the flow path so as to form a high-frequency electric field, and the dielectric shielding discharge can be performed. Preferably, the processing target gas is generated by the flow path system. The flow path of the dielectric shield discharge. By using RF plasma (atmospheric plasma) formed by dielectric shielding discharge, a large amount of gas to be treated can be radically (free radically ionized) at a low temperature, and a catalyst can be used to lower the gas by a catalyst reaction. Decompose or upgrade efficiently.

處理對象氣體之一為含有氟化碳者,典型的是PFC(全氟碳化物)氣體。利用上述的處理裝置及處理方法,透過將PFC氣體分解成二氧化碳和氟而能除害。在此場合,處理裝置的觸媒層以多孔構造且含有內部充填有消石灰(氫氧化鈣(Ca(OH)2))的層(第1層)者較佳。又,處理方 法係以包含將已通過流路的氣體供予充填有消石灰的層者較佳。觸媒層典型的是蜂窩結構,利用消石灰吸收在對處理對象氣體進行處理之際所產生的氟,可抑制因氟所致白金等之觸媒的不活性化(被毒化)。因此,可抑制處理裝置的處理效率降低。 One of the gas to be treated is a person containing carbon fluoride, typically a PFC (perfluorocarbon) gas. According to the above-described processing apparatus and processing method, the PFC gas can be decomposed into carbon dioxide and fluorine to be detoxified. In this case, the catalyst layer of the treatment apparatus is preferably a porous structure and contains a layer (first layer) in which slaked lime (calcium hydroxide (Ca(OH) 2 )) is filled. Further, it is preferable that the treatment method include a layer containing a gas having passed through the flow path and filled with slaked lime. The catalyst layer is typically a honeycomb structure, and the fluorine generated by the treatment of the gas to be treated is absorbed by the slaked lime, and the inactivation (detoxification) of the catalyst such as platinum due to fluorine can be suppressed. Therefore, it is possible to suppress a decrease in processing efficiency of the processing apparatus.

觸媒層以包含充填有粒狀的消石灰的層較佳。可抑制氣體在通過觸媒層時的阻力上昇,可抑制藉高頻電場而形成RF電漿的流路之壓力上昇。因此,容易維持易於生成RF電漿的條件。又,因為使消石灰和氟反應會生成氟石(CaF2),所以透過採用粒狀的消石灰,使的將氟回收予以再資源化亦變得容易。 The catalyst layer is preferably a layer containing hydrated hydrated lime. It is possible to suppress an increase in the resistance of the gas as it passes through the catalyst layer, and it is possible to suppress an increase in the pressure of the flow path in which the RF plasma is formed by the high-frequency electric field. Therefore, it is easy to maintain conditions in which RF plasma is easily generated. Further, since the slaked lime and the fluorine react to form fluorspar (CaF 2 ), it is easy to recycle the fluorine by recycling the granular slaked lime.

1‧‧‧PFC氣體 1‧‧‧PFC gas

2‧‧‧氧(空氣、或氧與氮之混合氣體) 2‧‧‧Oxygen (air, or a mixture of oxygen and nitrogen)

3‧‧‧混合氣體(氣體、處理對象氣體) 3‧‧‧ Mixed gas (gas, treatment target gas)

4‧‧‧混合氣體 4‧‧‧ mixed gas

5‧‧‧二氧化碳 5‧‧‧Carbon dioxide

5‧‧‧乾式泵 5‧‧‧Dry pump

6‧‧‧氟氣 6‧‧‧Fluorine gas

7‧‧‧氟石 7‧‧‧Fluorite

10‧‧‧處理方法(除害方法) 10‧‧‧Treatment method (detoxification method)

20‧‧‧紫外線照射單元 20‧‧‧UV irradiation unit

21‧‧‧真空紫外線源(真空紫外光源、準分子燈) 21‧‧‧Vacuum UV source (vacuum UV source, excimer lamp)

22‧‧‧紫外線(真空紫外線(VUV)) 22‧‧‧UV (Vacuum Ultraviolet (VUV))

23‧‧‧高頻電場 23‧‧‧High frequency electric field

24‧‧‧低溫大氣壓電漿(非平衡大氣壓電漿、RF電漿(大氣壓電漿)) 24‧‧‧Low-temperature atmospheric piezoelectric slurry (non-equilibrium atmospheric piezoelectric slurry, RF plasma (atmospheric piezoelectric slurry))

25‧‧‧大氣壓電漿產生裝置(高頻產生裝置) 25‧‧‧Atmospheric piezoelectric slurry generator (high frequency generator)

26‧‧‧大氣壓電漿 26‧‧‧Atmospheric piezoelectric paste

29‧‧‧流路 29‧‧‧Flow

31‧‧‧觸媒(觸媒層、白金觸媒) 31‧‧‧catalyst (catalyst layer, platinum catalyst)

33‧‧‧孔 33‧‧‧ hole

35‧‧‧電壓供給單元 35‧‧‧Voltage supply unit

41‧‧‧消石灰 41‧‧‧ slaked lime

50‧‧‧處理裝置 50‧‧‧Processing device

50a‧‧‧處理裝置 50a‧‧‧Processing device

50‧‧‧紫外線反應區域 50‧‧‧UV reaction area

51‧‧‧腔室(外殼) 51‧‧‧Case (outer casing)

52‧‧‧氣體供給單元 52‧‧‧ gas supply unit

53‧‧‧乾式泵 53‧‧‧dry pump

55‧‧‧觸媒反應區域 55‧‧‧catalytic reaction zone

56‧‧‧紫外線反應區域 56‧‧‧UV reaction area

57‧‧‧紫外線導入窗(壁) 57‧‧‧UV inlet window (wall)

58‧‧‧反射鏡 58‧‧‧Mirror

60‧‧‧處理裝置 60‧‧‧Processing device

61‧‧‧第1單元 61‧‧‧Unit 1

62‧‧‧第2單元 62‧‧‧Unit 2

63、64‧‧‧電極 63, 64‧‧‧ electrodes

63a‧‧‧帽緣狀或凸緣狀的部分 63a‧‧‧Front or flanged part

63b‧‧‧針電極(針狀電極) 63b‧‧‧needle electrode (needle electrode)

64‧‧‧外側電極(圓筒電極、外周的電極) 64‧‧‧Outer electrode (cylinder electrode, peripheral electrode)

65、66‧‧‧介電質層 65, 66‧‧‧ dielectric layer

67‧‧‧磁鐵 67‧‧‧ Magnet

68‧‧‧外殼 68‧‧‧Shell

68a‧‧‧結合裝置 68a‧‧‧ Combined device

69‧‧‧外殼 69‧‧‧Shell

70‧‧‧電力供給單元 70‧‧‧Power supply unit

71‧‧‧交流電源(高頻電源、RF電源) 71‧‧‧AC power supply (high frequency power supply, RF power supply)

72‧‧‧匹配器(MB) 72‧‧‧matcher (MB)

73‧‧‧線路 73‧‧‧ lines

74‧‧‧DC電源 74‧‧‧DC power supply

80‧‧‧處理裝置 80‧‧‧Processing device

80‧‧‧除害裝置 80‧‧‧Injury device

80‧‧‧外殼 80‧‧‧ Shell

81‧‧‧第1單元 81‧‧‧Unit 1

82‧‧‧第2單元 82‧‧‧Unit 2

83、84‧‧‧電極 83, 84‧‧‧ electrodes

85、86‧‧‧介電質層 85, 86‧‧‧ dielectric layer

87‧‧‧單元(磁鐵) 87‧‧‧unit (magnet)

88‧‧‧針電極 88‧‧‧needle electrode

89‧‧‧外殼 89‧‧‧ Shell

89a‧‧‧外殼 89a‧‧‧ Shell

89b‧‧‧外殼 89b‧‧‧ Shell

90‧‧‧凹凸構造 90‧‧‧Concave structure

91‧‧‧介電質的凸部分 91‧‧‧The convex part of the dielectric

95‧‧‧放電(微電漿、毫電漿) 95‧‧‧discharge (microplasma, milliplasma)

圖1係顯示處理方法的圖。 Fig. 1 is a diagram showing a processing method.

圖2(a)係顯示根據紫外線的反應的圖,(b)係顯示根據觸媒的反應的圖。 Fig. 2(a) is a view showing a reaction according to ultraviolet rays, and (b) is a view showing a reaction according to a catalyst.

圖3係顯示處理裝置之概略構成的方塊圖。 Fig. 3 is a block diagram showing a schematic configuration of a processing apparatus.

圖4係顯示處理裝置的不同例之概略構成的方塊圖。 Fig. 4 is a block diagram showing a schematic configuration of a different example of the processing device.

圖5係顯示處理裝置的另一不同例之概略構成的方塊圖。 Fig. 5 is a block diagram showing a schematic configuration of another different example of the processing apparatus.

圖6係顯示處理裝置的另一不同例之概略構成的方塊圖。 Fig. 6 is a block diagram showing a schematic configuration of another different example of the processing apparatus.

圖1中,關於本發明的一例,係顯示對半導體製 造、FPD(平板顯示器)製造步驟的蝕刻、洗淨所使用的四氟化碳(CF4)等之PFC(全氟碳化物)氣體進行除害的處理方法。關於該處理,係利用紫外線或RF電漿提高氣體分子的反應性,使之與藉由DC偏壓電位而被高度地活性化的觸媒接觸,藉由使氣體氧化而無害化。 In an example of the present invention, PFC (perfluorocarbon) gas such as carbon tetrafluoride (CF 4 ) used for etching and cleaning of a semiconductor manufacturing or FPD (flat panel display) manufacturing step is shown in FIG. The treatment method of detoxification. In this treatment, the reactivity of the gas molecules is increased by ultraviolet rays or RF plasma, and is brought into contact with a catalyst which is highly activated by a DC bias potential, and is detoxified by oxidizing the gas.

PFC係指碳化氫CxHy的氫全被氟置換者(CxFy)。PFC的地球暖化係數(GWP)係CO2的6000倍至10000倍且對暖化的影響遠大於CO2。而且,在大氣中的壽命亦有1萬年那麼長,對環境的不良影響強。在以下所示的例子中,目標在於對PFC進行處理並排出CO2進行PFC的除害處理。 PFC means that the hydrogen of the hydrocarbon CxHy is completely replaced by fluorine (CxFy). The global warming coefficient (GWP) of PFC is 6000 to 10,000 times that of CO 2 and has a much greater impact on warming than CO 2 . Moreover, the life in the atmosphere is as long as 10,000 years, and the adverse effects on the environment are strong. In the example shown below, the objective is to treat the PFC and discharge the CO 2 to perform the PFC detoxification treatment.

以往,PFC除害處理係採用高溫,代表方式有燃燒型、電氣加熱分解型、觸媒型及電漿燃燒器型。均利用熱切斷PFC之分子內的鍵結,在和氧反應後進行濕式處理。依濕式處理所產生的氟系排水係有必要另外處理。燃燒型係使氫或化石燃料等燃燒而在1600℃程度的高溫環境下分解PFC。除害效率雖有95%程度,但需要大量的燃料。而且,依處理所產生之氟化氫(HF)等的酸曝露在高溫環境使除害裝置產生腐蝕、運轉成本高。且裝置尺寸成為數立方公尺程度,在既存的半導體工場內難以確保設置場所。 In the past, the PFC decontamination treatment system used high temperatures, and the representative methods were combustion type, electric heating decomposition type, catalytic type and plasma burner type. The bonds in the molecules of the PFC are cut off by heat, and are subjected to a wet treatment after reacting with oxygen. It is necessary to additionally treat the fluorine-based drainage system produced by the wet treatment. The combustion type burns hydrogen or fossil fuels and decomposes the PFC in a high temperature environment of about 1600 °C. Although the efficiency of decontamination is 95%, it requires a lot of fuel. Further, the acid such as hydrogen fluoride (HF) generated by the treatment is exposed to a high temperature environment to cause corrosion of the detoxification device and high running cost. Moreover, the size of the device is several cubic meters, and it is difficult to secure the installation place in the existing semiconductor factory.

電氣加熱分解型係藉電爐將PFC加熱成800℃程度並予以分解。溫度比燃燒型還低,其份量少有腐蝕的疑慮。然而,除害效率係40%程度。觸媒型係使用從650℃加熱至800℃的溫度的觸媒以乾式對PFC進行除害。除害效率係98 %程度,亦少有腐蝕的疑慮。然而,處理流量為80LPM乃係其他方式的1/3程度。 The electric heating decomposition type heats the PFC to 800 ° C by an electric furnace and decomposes it. The temperature is lower than that of the combustion type, and the amount of the coating is less likely to be corroded. However, the efficiency of detoxification is 40%. The catalyst type uses a catalyst heated from 650 ° C to 800 ° C to dry out the PFC in a dry manner. Detoxification efficiency system 98 % degree, there are few doubts about corrosion. However, the processing flow rate of 80 LPM is 1/3 of the other way.

電漿燃燒器型係對排放氣體施加電力,透過電弧放電形成熱電漿化而將PFC加熱分解。因為要形成熱電漿故電力消耗大,且在分解過程所生成的氟化氫於高溫下具有腐蝕性,當成為形成氫氟酸(氟酸)的狀況時則腐蝕會加劇。 The plasma burner type applies electric power to the exhaust gas, and forms a thermal plasma by arc discharge to thermally decompose the PFC. Since the thermoelectricity is to be formed, the power consumption is large, and the hydrogen fluoride generated in the decomposition process is corrosive at a high temperature, and the corrosion is intensified when the hydrofluoric acid (fluoric acid) is formed.

關於圖1所示的處理方法(除害方法)10,係根據紫外線或RF電漿的氣體分子之自由基化與藉DC偏壓電位而成為高度活性化的觸媒型之組合,藉以在低溫,例如200℃以下抑制消耗電力並抑制腐蝕以改善運轉成本,實現和以往的觸媒型同程度的除害效率。更透過在觸媒中配置消石灰,將反應過程所生成的氟氣以消石灰吸附,以實現維持觸媒活性與氟的乾式除害及再資源化。 The treatment method (decontamination method) 10 shown in FIG. 1 is based on a combination of radicalization of gas molecules of ultraviolet or RF plasma and a catalyst type which is highly activated by a DC bias potential. At a low temperature, for example, 200 ° C or less suppresses power consumption and suppresses corrosion to improve running cost, and achieves the same degree of decontamination efficiency as the conventional catalyst type. Further, by disposing slaked lime in the catalyst, the fluorine gas generated in the reaction process is adsorbed by slaked lime to achieve dry detoxification and re-recycling of the catalyst activity and fluorine.

就此處理方法(除害方法)10而言,在步驟11生成混合PFC氣體1和氧(空氣、或氧與氮之混合氣體)2的混合氣體3。PFC氣體1以氮為載氣被稀釋成2000ppm程度並從半導體製程排出。因此,以下將以對大量的氮氣中所含的PFC氣體1進行除害的方法及裝置為例作說明。 In this treatment method (decontamination method) 10, a mixed gas 3 in which PFC gas 1 and oxygen (air, or a mixed gas of oxygen and nitrogen) 2 are mixed is generated in step 11. The PFC gas 1 is diluted to about 2000 ppm with nitrogen as a carrier gas and is discharged from the semiconductor process. Therefore, a method and apparatus for detoxifying a large amount of PFC gas 1 contained in nitrogen gas will be described below as an example.

在步驟12,將混合氣體3導入於被照射從真空紫外線源(真空紫外光源)21供給的紫外線22之流路29,對混合氣體3照射紫外線22使混合氣體3自由基化。或對流路29施加高頻電場23而形成低溫大氣壓電漿(非平衡大氣壓電漿)24,使通過流路29的混合氣體3自由基化。在提高PFC的反應性的激發源方面,光及電子比熱還易於控制能量,將 在高頻電場23生成的RF電漿24以低溫大氣壓電漿的範圍作控制使PFC1自由基化。藉此使反應低溫化,實現低運轉成本。 In step 12, the mixed gas 3 is introduced into the flow path 29 of the ultraviolet ray 22 supplied from the vacuum ultraviolet source (vacuum ultraviolet light source) 21, and the mixed gas 3 is irradiated with the ultraviolet ray 22 to radicalize the mixed gas 3. The high-frequency electric field 23 is applied to the flow path 29 to form a low-temperature atmospheric piezoelectric slurry (non-equilibrium atmospheric piezoelectric slurry) 24, and the mixed gas 3 passing through the flow path 29 is radicalized. In terms of excitation sources that increase the reactivity of PFC, light and electron specific heat are also easier to control energy, The RF plasma 24 generated in the high-frequency electric field 23 is controlled by the range of the low-temperature atmospheric piezoelectric slurry to radically PFC1. Thereby, the reaction is lowered in temperature to achieve low running costs.

在步驟13,將已自由基化的混合氣體4供予已被施加偏壓的白金觸媒31使之氧化反應,將PFC氣體1分解成二氧化碳5和氟氣6(氧化、化學變化、改質)。由於步驟12主要是進行到在低溫下的自由基化,所以在步驟13併用觸媒,俾即便在低溫仍可獲得充分處理速度。再者,透過對此觸媒施加DC偏壓,而從已通過電漿的化學種抽出電子,並促進化學種朝觸媒表面之吸附、擴散,以低溫使PFC氧化反應而無害化。 In step 13, the radicalized mixed gas 4 is supplied to the platinum catalyst 31 which has been biased to cause oxidation reaction, and the PFC gas 1 is decomposed into carbon dioxide 5 and fluorine gas 6 (oxidation, chemical change, modification). ). Since step 12 is mainly carried out to radicalization at a low temperature, in step 13 and using a catalyst, a sufficient treatment speed can be obtained even at a low temperature. Further, by applying a DC bias to the catalyst, electrons are extracted from the chemical species that have passed through the plasma, and the adsorption and diffusion of the chemical species toward the catalyst surface are promoted, and the PFC is oxidized at a low temperature to be harmless.

如圖2(a)所示,在步驟12中,PFC氣體1(混合氣體3)的CF鍵結是依真空紫外光22的照射或RF電漿24而被切斷。又,如圖2(b)所示,於步驟13,在依直流偏壓而帯正電之觸媒31的表面的電洞與已自由基化的PFC氣體1的電子之間進行電荷之授受,促進PFC氣體1的氧化還元。亦即,已自由基化的混合氣體4的碳自由基係因與白金觸媒31之接觸而被氧化成二氧化碳。 As shown in Fig. 2(a), in step 12, the CF bond of the PFC gas 1 (mixed gas 3) is cut by the irradiation of the vacuum ultraviolet light 22 or the RF plasma 24. Further, as shown in Fig. 2(b), in step 13, the charge is exchanged between the hole on the surface of the catalyst 31 which is positively charged by the DC bias voltage and the electron of the radicalized PFC gas 1. Promote oxidation of PFC gas 1. That is, the carbon radical of the radicalized mixed gas 4 is oxidized to carbon dioxide due to contact with the platinum catalyst 31.

關於此處理方法10,在氧化反應的步驟13生成的二氧化碳係利用乾式泵等排氣。在氧化反應的步驟13生成的氟氣6係在觸媒31中且於步驟14被消石灰(氫氧化鈣、Ca(OH)2)所捕獲而生成氟化鈣(氟石、螢石、CaF2)。因此,氟係以氟石7形態被固定而被安全地捕獲及回收。觸媒31係多孔構造,例如蜂窩結構且內部充填有粒狀的消石灰41,通過流路29之已自由基化的混合氣體4係被供予充填有 消石灰41的觸媒層31。氟石7有作為熔劑、光學素材等之用途,且成為氟的儲藏源。因此,透過設置步驟14,可進行氟的回收及資源化。再者,透過將生石灰(氧化鈣、CaCO3)連同消石灰一起預先充填於觸媒層31,利用生石灰捕獲在氟石(氟化鈣)7被生成之際的水分,可進行消石灰(氫氧化鈣)41的生成。 In the treatment method 10, the carbon dioxide generated in the step 13 of the oxidation reaction is exhausted by a dry pump or the like. The fluorine gas 6 generated in the step 13 of the oxidation reaction is in the catalyst 31 and is captured by slaked lime (calcium hydroxide, Ca(OH) 2 ) in step 14 to form calcium fluoride (fluorite, fluorite, CaF 2 ). ). Therefore, the fluorine is fixed in the form of fluorite 7 and is safely captured and recovered. The catalyst 31 has a porous structure, for example, a honeycomb structure, and is filled with granular slaked lime 41 inside, and the radicalized mixed gas 4 passing through the flow path 29 is supplied with the catalyst layer 31 filled with the slaked lime 41. Fluorite 7 is used as a flux, an optical material, etc., and is a storage source of fluorine. Therefore, through the setting step 14, recovery and recycling of fluorine can be performed. Further, slaked lime (calcium hydroxide) can be obtained by preliminarily charging quicklime (calcium oxide, CaCO 3 ) together with hydrated lime to the catalyst layer 31, and capturing the water at the time when fluorite (calcium fluoride) 7 is formed by using quicklime. ) 41 generation.

圖3顯示PFC氣體的處理裝置(除害裝置)之一例。此處理裝置60包含:筒型的第1單元61,其使被氮稀釋的PFC氣體1與氧或空氣2之混合氣體3通過RF電漿生成區域而自由基化;筒型的第2單元62,其收納白金觸媒31且供已自由基化的混合氣體4通過白金觸媒31並氧化;氣體供給單元52,其將混合氣體3供予上游的第1單元61;及乾式泵53,其從下游的第2單元62排出所生成的二氧化碳5。 Fig. 3 shows an example of a processing device (abuse device) for PFC gas. The processing apparatus 60 includes a cylindrical first unit 61 that radicalizes the mixed gas 3 of the PFC gas 1 diluted with nitrogen and oxygen or air 2 through the RF plasma generation region; the second unit 62 of the cylindrical type And storing the platinum catalyst 31 and supplying the radicalized mixed gas 4 through the platinum catalyst 31 and oxidizing; the gas supply unit 52 supplying the mixed gas 3 to the upstream first unit 61; and the dry pump 53, The generated carbon dioxide 5 is discharged from the second unit 62 downstream.

就此處理裝置60而言,在第1單元61,進行使混合氣體1(3?)自由基化的步驟12。收納於第2單元62的觸媒層31係擔持白金之多孔性的陶瓷製觸媒體,具體來說是具備蜂窩結構。且於觸媒層31的蜂窩結構的孔33中充填有顆粒狀的消石灰41。因此,在第2單元62同時或並行地進行氧化還元的步驟13和使氟氣6穩定成氟石的步驟14。 In the processing device 60, the first unit 61 performs a step 12 of radically activating the mixed gas 1 (3?). The catalyst layer 31 accommodated in the second unit 62 is a ceramic contact medium that is porous in platinum, and specifically has a honeycomb structure. The pores 33 of the honeycomb structure of the catalyst layer 31 are filled with granular slaked lime 41. Therefore, the step 13 of oxidizing the reductive unit and the step 14 of stabilizing the fluorine gas 6 into the fluorspar are performed simultaneously or in parallel in the second unit 62.

第1單元61係包含圓筒狀的不鏽鋼製的外殼69、和在外殼69的內部呈同心圓狀配置的2個電極63及64、及以覆蓋各個電極63及64般設有間隙作配置的介電質層65及66,介電質層65及66間成為供處理對象的混合氣體3通過的流路29。適合於介電質層65及66之材料的一例為PTFE (聚四氟乙烯)。 The first unit 61 includes a cylindrical stainless steel outer casing 69, two electrodes 63 and 64 which are concentrically arranged inside the outer casing 69, and a gap between the electrodes 63 and 64. The dielectric layers 65 and 66 and the dielectric layers 65 and 66 serve as a flow path 29 through which the mixed gas 3 to be processed passes. An example of a material suitable for the dielectric layers 65 and 66 is PTFE. (polytetrafluoroethylene).

內側的電極63,係為靠近於氣體供給單元52的混合氣體3的流入口側擴展成帽緣狀之棒狀的電極,複數個針狀電極63b以面向外側的電極64的方向設在擴展成帽緣狀的部分63a。外側的電極64係圓筒狀的電極,複數個磁鐵67在其內側沿著軸向斷續地配置。 The inner electrode 63 is a rod-shaped electrode that is expanded toward the inlet side of the mixed gas 3 of the gas supply unit 52, and the plurality of needle electrodes 63b are expanded in the direction of the electrode 64 facing the outer side. A brim-like portion 63a. The outer electrode 64 is a cylindrical electrode, and a plurality of magnets 67 are intermittently arranged along the axial direction inside.

處理裝置60包含電力供給單元70,其用以對第1單元61的電極63及64供給高頻電壓,在流路29形成高頻電場而生成RF電漿。電力供給單元70包含交流電源(高頻電源、RF電源)71及匹配器(MB)72,經由匹配器72將高頻電力供予內側的電極63。電力供給單元70更包含將外殼69接地的線路73與賦予外側電極64負電位的DC電源74。 The processing device 60 includes a power supply unit 70 for supplying a high-frequency voltage to the electrodes 63 and 64 of the first unit 61, and a high-frequency electric field to be formed in the flow path 29 to generate RF plasma. The power supply unit 70 includes an AC power source (high-frequency power source, RF power source) 71 and a matcher (MB) 72, and supplies the high-frequency power to the inner electrode 63 via the matching unit 72. The power supply unit 70 further includes a line 73 that grounds the outer casing 69 and a DC power source 74 that gives a negative potential to the outer electrode 64.

如先前所說明,PFC的稀釋採用氮(N2)氣。因此,第1單元61中,在考量實用性時以近於大氣壓的壓力生成低溫的電漿者較佳。欲獲得低溫的電漿時是需要引起輝光放電或流光放電的,且必須回避易形成高溫的電弧放電。在電離方面,N2氣比Ar氣還需要高電場,當以接近大氣壓的壓力施加高電場時,則變得容易轉換成電弧放電。於是,在第1單元61中採用包夾介電質65及66般地配置電極63及64的介電質屏蔽放電電極構造和針電極63b,藉由針電極63b一邊實現高電場一邊引起輝光放電並使用介電質屏蔽放電以提升除害效率。 As explained previously, the dilution of the PFC uses nitrogen (N 2 ) gas. Therefore, in the first unit 61, it is preferable to generate a low-temperature plasma at a pressure close to atmospheric pressure when considering practicality. In order to obtain a low-temperature plasma, it is necessary to cause a glow discharge or a streamer discharge, and it is necessary to avoid an arc discharge which is liable to form a high temperature. In terms of ionization, the N 2 gas requires a high electric field than the Ar gas, and when a high electric field is applied at a pressure close to atmospheric pressure, it becomes easy to convert into an arc discharge. Then, in the first unit 61, the dielectric shield discharge electrode structure and the needle electrode 63b of the electrodes 63 and 64 are arranged in the same manner as the sandwich dielectrics 65 and 66, and the glow discharge is caused by the high electric field while the needle electrode 63b is realized. Dielectric shielding discharge is used to improve the efficiency of decontamination.

就介電質屏蔽放電而言,透過如PTFE或石英之類的介電質阻礙來自RF電源71的電場施加,在高電場未被 長時間施加之下極性逆轉。因此,能將放電時間限制成短時間,可防止形成於電極間的電漿變高溫。就此例而言,因分解PFC之際產生的氟容易浸蝕石英,故石英(玻璃)不適於作為介電質。進行其他氣體的分解或改質處理的裝置,在考慮成本、強度等點時,適合將石英作為介電質。 In the case of dielectric barrier discharge, the application of an electric field from the RF power source 71 is hindered by a dielectric such as PTFE or quartz, which is not in the high electric field. The polarity is reversed under long time application. Therefore, the discharge time can be limited to a short time, and the plasma formed between the electrodes can be prevented from becoming high in temperature. In this case, since fluorine generated by the decomposition of the PFC easily etches quartz, quartz (glass) is not suitable as a dielectric. A device for performing decomposition or modification of other gases is suitable for using quartz as a dielectric when considering cost, strength, and the like.

再者,第1單元61中,因為在中心的電極63設置帽緣或凸緣狀的部分63a,在混合氣體3之流路29的氣體導入口附近電極間隔變窄,形成容易引起氣體3電離的構造。然後,在氣體導入口附近配置針電極63b。利用該等構造在氣體導入口附近一度進行輝光放電使氣體分子的一部分電離形成離子而成為電子的載子。因此,在那之後,變得容易在流路29的內部形成電漿,即使是放電區域寬廣的電極形狀亦變得容易形成電漿。 Further, in the first unit 61, since the cap electrode or the flange-shaped portion 63a is provided in the center electrode 63, the electrode interval is narrowed in the vicinity of the gas introduction port of the flow path 29 of the mixed gas 3, and the gas 3 is easily ionized. Construction. Then, the needle electrode 63b is placed in the vicinity of the gas introduction port. With these structures, a glow discharge is once performed in the vicinity of the gas introduction port to ionize a part of the gas molecules to form ions and become electron carriers. Therefore, after that, it becomes easy to form a plasma inside the flow path 29, and even a shape of an electrode having a wide discharge area becomes easy to form a plasma.

在第1單元61中賦予外周的圓筒電極64負的電位而作成空心陰極。透過將外周的電極64形成空心陰極,因電漿中的電子藉由負電位跳回抑制了電極表面的電子之損失而關閉住電子,可獲得促進電漿中之電離的效果(空心陰極效應)。 In the first unit 61, a negative potential is applied to the outer cylindrical electrode 64 to form a hollow cathode. By forming the outer peripheral electrode 64 into a hollow cathode, the electrons in the plasma are prevented from being trapped by the negative potential to suppress the loss of electrons on the surface of the electrode, and the effect of promoting ionization in the plasma can be obtained (hollow cathode effect). .

再者,於圓筒電極64的內部沿著軸向斷續地配置圓盤狀的磁鐵67,關閉住的電子因沿著磁鐵67所產生的外部磁場作迴旋加速運動而一邊在圓筒電極64的直徑方向移動,一邊連同自由基及/或自由基離子一起朝氣體的下游方向流動。藉由此種機構擴大流路29內部的放電區域,促進混合氣體3的自由基化。外部磁場的方向可為周向或亦可為軸向, 只要能獲得關閉住電子的效果即可。 Further, a disk-shaped magnet 67 is intermittently arranged in the axial direction inside the cylindrical electrode 64, and the closed electrons are subjected to a cyclotron acceleration motion along the external magnetic field generated by the magnet 67 while being on the cylindrical electrode 64. The diametrical movement moves along with the free radicals and/or radical ions in the downstream direction of the gas. By such a mechanism, the discharge region inside the flow path 29 is enlarged, and the radicalization of the mixed gas 3 is promoted. The direction of the external magnetic field may be circumferential or axial. As long as you can get the effect of turning off the electronic.

照這樣,在第1單元61中於流路29以約大氣壓的狀態且200℃以下的低溫形成電漿(RF電漿或大氣壓電漿)。於實驗階段使用傅立葉轉換紅外分光光度計(FT-IR)測定除害效率後,獲得氮流量大者電漿可穩定地形成,且氧和PFC的流量比是達1:1或3:2程度,氧的比率大者則除害效率佳那樣的結果。可認為氮流量大者電極溫度穩定而放電穩定。 In this manner, in the first unit 61, plasma (RF plasma or atmospheric piezoelectric slurry) is formed in the flow path 29 at a low atmospheric pressure and at a low temperature of 200 ° C or lower. After the determination of the abatement efficiency by the Fourier transform infrared spectrophotometer (FT-IR) in the experimental stage, the plasma with a large nitrogen flow rate can be stably formed, and the flow ratio of oxygen to PFC is 1:1 or 3:2. The ratio of oxygen is large, and the result of good detoxification is good. It can be considered that the electrode having a large nitrogen flow rate is stable in temperature and stable in discharge.

傅立葉轉換紅外分光光度計,係對測定對象照射紅外線,由於所吸收的紅外線之各波長的能量在物質中的鍵合是固有,故能評價存在於對象內的分子及其濃度。係適合於評價PFC除害裝置的特性之方法的測定裝置。 The Fourier transform infrared spectrophotometer irradiates infrared rays to the measurement target, and since the energy of each wavelength of the absorbed infrared rays is inherent in the substance, it is possible to evaluate the molecules present in the object and their concentrations. A measuring device suitable for a method for evaluating characteristics of a PFC detoxification device.

關於處理裝置60,第1單元61中已自由基化的混合氣體4係被供給至形成觸媒反應區域的第2單元62。第2單元62包含圓筒狀的不鏽鋼製的外殼68及設置在其內部的觸媒層31。就第2單元62而言,已自由基化的混合氣體4係通過觸媒層31的孔33與觸媒層31接觸而被氧化還元、分解。經氧化還元所生成的氟氣6係與充填於蜂窩結構的孔33的消石灰41反應,以氟石7的形態固定。因此,在處理裝置60中,混合氣體3中的PFC1被分解,所生成的氟氣6固定於觸媒層31的內部,二氧化碳5係藉由乾式泵53從處理裝置60被排氣。 In the processing device 60, the mixed gas 4 that has been radicalized in the first unit 61 is supplied to the second unit 62 that forms the catalyst reaction region. The second unit 62 includes a cylindrical stainless steel outer casing 68 and a catalyst layer 31 provided inside. In the second unit 62, the radicalized mixed gas 4 is oxidized and decomposed by contact with the catalyst layer 31 through the pores 33 of the catalyst layer 31. The fluorine gas 6 formed by the oxidation unit reacts with the slaked lime 41 filled in the pores 33 of the honeycomb structure, and is fixed in the form of the fluorite 7. Therefore, in the processing device 60, the PFC 1 in the mixed gas 3 is decomposed, the generated fluorine gas 6 is fixed inside the catalyst layer 31, and the carbon dioxide 5 is exhausted from the processing device 60 by the dry pump 53.

處理裝置60更包含對觸媒層31施加電位的電壓供給單元35。電壓供給單元35將直流電壓(直流電場)供予 觸媒層31,俾觸媒層31的表面相對於接地的外殼68被施加正偏壓(高電位)。透過將觸媒層31的表面施加正偏壓,可對已自由基化的混合氣體4所接觸之觸媒層31的表面強制地賦予正的電荷。因此,在與藉自由基化而被負離子化(自由基離子化)的混合氣體4之間容易進行電荷的授受。因此,更促進在觸媒層31中的PFC1之分解。藉直流偏壓電場將觸媒層31活性化,可擬似地賦予和光觸媒的效果同等之效果。 The processing device 60 further includes a voltage supply unit 35 that applies a potential to the catalyst layer 31. The voltage supply unit 35 supplies a DC voltage (DC electric field) The catalyst layer 31, the surface of the germanium catalyst layer 31 is applied with a positive bias (high potential) with respect to the grounded outer casing 68. By applying a positive bias to the surface of the catalyst layer 31, a positive charge can be forcibly imparted to the surface of the catalyst layer 31 to which the radicalized mixed gas 4 is in contact. Therefore, charge is easily transferred between the mixed gas 4 which is negatively ionized (radical ionized) by radicalization. Therefore, the decomposition of PFC1 in the catalyst layer 31 is further promoted. The catalyst layer 31 is activated by a DC bias electric field, and the effects equivalent to those of the photocatalyst can be similarly applied.

充填於觸媒層31的多孔33之消石灰41的充填量越多越容易將氟除去。然而,通過觸媒層31的氣體之電導下降,差壓變大。因此,上游的第1單元61之流路29內部的壓力上昇,有可能使電漿不穩定。因此,消石灰41的充填量,係評價氟除去量和除害效率而選定可一邊保持目標的高除害效率例如95%一邊呈現最高的氟除去量的充填量。 The more the amount of the slaked lime 41 filled in the porous body 33 of the catalyst layer 31, the more easily the fluorine is removed. However, the conductance of the gas passing through the catalyst layer 31 is lowered, and the differential pressure is increased. Therefore, the pressure inside the flow path 29 of the upstream first unit 61 rises, and the plasma may be unstable. Therefore, the filling amount of the slaked lime 41 is selected to evaluate the amount of fluorine removal and the efficiency of the detoxification, and it is possible to select a filling amount which is the highest fluorine removal amount while maintaining the high decontamination efficiency of the target, for example, 95%.

第1單元61的外殼69和第2單元62的外殼68係利用凸緣型的結合裝置68a以可裝卸的方式連接。因此,在經過所定的處理時間後,卸下第2單元62,補充觸媒層31的消石灰41,可從消石灰41中回收氟石7。被回收的氟石7係當作氟資源使用。如此,在處理裝置60中氟的除去及再資源化能以乾式處理方式實現。 The outer casing 69 of the first unit 61 and the outer casing 68 of the second unit 62 are detachably connected by a flange type coupling device 68a. Therefore, after a predetermined processing time elapses, the second unit 62 is removed, and the slaked lime 41 of the catalyst layer 31 is replenished, whereby the fluorite 7 can be recovered from the slaked lime 41. The recovered fluorspar 7 is used as a fluorine resource. Thus, the removal and re-recycling of fluorine in the processing device 60 can be achieved in a dry process.

圖4顯示PFC氣體的處理裝置(除害裝置)的不同例。此處理裝置80亦包含:利用RF電漿將含有PFC的混合氣體3自由基化的第1單元81;利用白金觸媒31將已自由基化的混合氣體4氧化的第2單元82;供給混合氣體3的氣體供給單元52;及排出二氧化碳5的乾式泵53。 Fig. 4 shows a different example of a processing device (abatement device) of PFC gas. The processing device 80 further includes: a first unit 81 that radicalizes the mixed gas containing PFC by RF plasma; and a second unit 82 that oxidizes the radicalized mixed gas 4 by the platinum catalyst 31; A gas supply unit 52 for the gas 3; and a dry pump 53 for discharging the carbon dioxide 5.

第1單元81包含:箱型的不鏽鋼製的外殼89;以於外殼89的內部形成Z字狀的流路29之方式平行地交互配置的平板型的電極83及84;及覆蓋各個電極83及84的介電質層85及86。具有平行平板型的電極之處理裝置80適合於處理大流量的混合氣體3。因為處理對象氣體3成為大流量,使得荷電粒子穿過施加有電場的氣體流路之速度也變快。因此,對電子、離子加速的時間變短,變得難以引起放電。 The first unit 81 includes a box-shaped stainless steel case 89; flat-type electrodes 83 and 84 that are alternately arranged in parallel so as to form a zigzag channel 29 inside the case 89; and cover each electrode 83 and The dielectric layers 85 and 86 of 84. The processing device 80 having electrodes of parallel plate type is suitable for processing a large flow of the mixed gas 3. Since the processing target gas 3 becomes a large flow rate, the speed at which the charged particles pass through the gas flow path to which the electric field is applied also becomes faster. Therefore, the time for accelerating electrons and ions becomes short, and it becomes difficult to cause discharge.

就第1單元81而言,首先,和上述的處理裝置60同樣地,將電極83及84配置成包夾介電質層85及86,以產生介電質屏蔽放電。藉此,透過使電極間狹窄並相對地加大電場強度而容易產生輝光放電,同時縮放電時間以阻止從輝光放電轉換成電弧放電。再者,於流路29的氣體導入口側設置針電極88,在局部產生更高的電場使流路29的上游側更確實地產生放電。依此,生成氣體中的電荷的載子(離子),在流路29全體中成為容易生成電漿。又,因為容易引起放電,故可降低要施加的電壓,能減低消耗電力,能在低溫生成電漿。 In the first unit 81, first, in the same manner as the above-described processing apparatus 60, the electrodes 83 and 84 are placed to sandwich the dielectric layers 85 and 86 to generate dielectric shield discharge. Thereby, the glow discharge is easily generated by narrowing the electrodes and relatively increasing the electric field intensity, and the electric time is scaled to prevent the conversion from the glow discharge to the arc discharge. Further, the needle electrode 88 is provided on the gas introduction port side of the flow path 29, and a higher electric field is locally generated to cause discharge to be more reliably generated on the upstream side of the flow path 29. Accordingly, carriers (ions) that generate electric charges in the gas are likely to generate plasma in the entire flow path 29. Further, since the discharge is likely to occur, the voltage to be applied can be lowered, power consumption can be reduced, and plasma can be generated at a low temperature.

在此裝置80中,外殼89和電極84接地,在連接於RF電源71的電極83和外殼89及/或電極84之間放電而生成電漿。針電極88可設在電極83、84或外殼89中任一處,但本例中是在外殼89設置成朝電極83突出。針電極88只要是可產生不平衡電場者即可,可以未必是前端尖鋭的針狀,亦可以是棒狀或適當之形狀的凸部。 In this device 80, the outer casing 89 and the electrode 84 are grounded, and are discharged between the electrode 83 connected to the RF power source 71 and the outer casing 89 and/or the electrode 84 to generate plasma. The needle electrode 88 may be provided at any of the electrodes 83, 84 or the outer casing 89, but in this example, the outer casing 89 is disposed to protrude toward the electrode 83. The needle electrode 88 may be any needle-shaped cusp, and may be a rod-shaped or appropriately shaped convex portion as long as it can generate an unbalanced electric field.

再就第1單元81而言,係將平板狀的電極83及84交互排列,俾在外殼89的內部形成Z字的流路29。透過將施加電場的氣體流路29的寬度加寬、加長,作成即便是被供給大流量的混合氣體3之場合也能確保用以加速的時間,即便是相同電場也能保持大的動能。 Further, in the first unit 81, the flat electrodes 83 and 84 are alternately arranged, and a zigzag flow path 29 is formed inside the outer casing 89. By widening and lengthening the width of the gas flow path 29 to which the electric field is applied, it is possible to ensure the time for acceleration even when the mixed gas 3 having a large flow rate is supplied, and it is possible to maintain a large kinetic energy even with the same electric field.

流路29成為Z字或蛇行者,在流路29會產生曲率大的彎曲部分,在該彎曲部分會因為急劇加速的方向變化而引發荷電粒子減速。因此,利用磁場防止荷電粒子減速。具體言之,將用以形成磁場的單元(磁鐵)87配置於電極83及84的前端,沿著磁場調整氣體中的自由基離子的軌道以輔助自由基離子的移動。藉此,可防止氣體中之荷電粒子減速,且可抑制和電極或外殼之衝撞而導致荷電粒子消滅。 The flow path 29 is a zigzag or a snakewalker, and a curved portion having a large curvature is generated in the flow path 29, and the charged portion is decelerated due to a change in the direction of rapid acceleration. Therefore, the magnetic field is prevented from decelerating by the magnetic field. Specifically, a unit (magnet) 87 for forming a magnetic field is disposed at the tips of the electrodes 83 and 84, and the orbit of the radical ions in the gas is adjusted along the magnetic field to assist the movement of the radical ions. Thereby, the charged particles in the gas can be prevented from decelerating, and the collision with the electrode or the outer casing can be suppressed to cause the charged particles to be destroyed.

當流通大流量的氣體使容器內(流路內)成為高壓時,則變得不易引起放電,即便是引起放電,轉換成電弧放電的風險變大。電弧放電係容易伴隨著高熱的電漿,成為消耗電力變大的原因。欲避免容器內形成高壓時,加大氣體的電導是有效的,以加大氣體流路29的斷面積者較佳。再者,因將電極間隔取大會使放電變困難,故欲使除害裝置80省電力化時,加大電極的面積者較為有效。另一方面,加大電極面積時,則會產生所謂大氣壓電漿的大面積化之課題,放電部位的分散變困難。 When a large flow rate of gas is caused to cause a high pressure in the inside of the container (in the flow path), discharge is less likely to occur, and even if discharge is caused, the risk of switching to arc discharge becomes large. The arc discharge system is easily accompanied by high-heat plasma, which causes a large power consumption. In order to avoid the formation of a high pressure in the container, it is effective to increase the conductance of the gas, so that it is preferable to increase the sectional area of the gas flow path 29. Further, since it is difficult to discharge the electrode by taking the interval therebetween, it is effective to increase the area of the electrode when the abatement device 80 is required to be electrically operated. On the other hand, when the electrode area is increased, the problem of a large area of the atmospheric piezoelectric slurry is caused, and dispersion of the discharge portion becomes difficult.

在處理裝置80中,係賦予介電質層85及86複數個微小的凹凸構造90。在介電質的凸部分91難以引起放電,原理上作成聚積小面積的電漿電極的狀態。藉此,在電 極全體產生許多微小的放電(微電漿、毫電漿)95,可使混合氣體3有效率地自由基化。導入微小的凹凸構造90的一方法為,預先對形成介電質層85及86的介電質薄片進行壓花加工。 In the processing apparatus 80, a plurality of minute concavo-convex structures 90 are provided to the dielectric layers 85 and 86. In the convex portion 91 of the dielectric material, it is difficult to cause discharge, and in principle, a state in which a small-area plasma electrode is accumulated is formed. In this way, in electricity A large number of minute discharges (microplasma, milliplasma) 95 are generated in the entirety, and the mixed gas 3 can be freely radicalized. One method of introducing the minute uneven structure 90 is to emboss the dielectric sheets forming the dielectric layers 85 and 86 in advance.

就此處理裝置80的第1單元81而言,經由匹配器72連接於RF電源71的複數個電極83與接地的複數個電極84係相互組合而形成氣體3的流路29。第1單元81的外殼89包含有複數個電極83呈梳齒狀安裝而成的右半部的外殼89a及複數個電極84呈梳齒狀安裝而成的左半部的外殼89b,藉由組合該等的外殼89a及89b而構成第1單元81。 In the first unit 81 of the processing device 80, a plurality of electrodes 83 connected to the RF power source 71 via the matching unit 72 and a plurality of ground electrodes 84 are combined with each other to form a flow path 29 of the gas 3. The outer casing 89 of the first unit 81 includes a casing 89a of a right half in which a plurality of electrodes 83 are comb-shaped, and a casing 89b of a left half in which a plurality of electrodes 84 are attached in a comb shape. The first casings 81 are formed by the outer casings 89a and 89b.

除了被供給依第1單元81而已自由基化的氣體4之第2單元82係具備和第1單元81的形狀一致的外形以外,其餘具有和上述的處理裝置60的第2單元62共通的構成。此處理裝置80的第2單元82亦被安裝成可對第1單元81裝卸,成為可容易地進行消石灰41之補充與氟石7之回收。 The second unit 82 that is supplied with the gas 4 that has been radicalized by the first unit 81 has a configuration that is identical to the shape of the first unit 81, and has a configuration common to the second unit 62 of the processing device 60 described above. . The second unit 82 of the processing apparatus 80 is also attached to the first unit 81 so that the slaked lime 41 can be easily replenished and the fluorite 7 can be easily recovered.

圖5顯示PFC氣體的處理裝置(除害裝置)的另一不同例。此處理裝置50係可使上述的自由基化之步驟12、藉觸媒進行氧化還元之步驟13、及使氟氣6穩定化成氟石的步驟14在一個腔室51的內部,同時或並行地進行。亦可為同時或並行地進行在腔室51中混合PFC氣體1和氧(空氣)2的步驟11。 Fig. 5 shows another different example of the processing device (abuse device) of the PFC gas. The processing device 50 is configured to perform the above-described radicalization step 12, the step 13 of oxidizing the catalyst by the catalyst, and the step 14 of stabilizing the fluorine gas 6 into the fluorspar inside the chamber 51, simultaneously or in parallel. get on. The step 11 of mixing the PFC gas 1 and the oxygen (air) 2 in the chamber 51 may also be performed simultaneously or in parallel.

處理裝置50包含:腔室(外殼)51,其收納白金觸媒31且形成供混合氣體3通過白金觸媒31並有效率地接觸的路徑;氣體供給單元52,對腔室51供給PFC氣體1 和氧2混合成的混合氣體3;及乾式泵53,其從腔室51排出所生成的二氧化碳5。腔室51包含:觸媒反應區域55,其收納有觸媒(觸媒層)31;及紫外線反應區域56,設置在觸媒反應區域55的上部(上游)。在腔室51的紫外線反應區域56之外壁的一部分,例如腔室51的上面(上壁)係成為相對於紫外線(真空紫外線)呈透明(透過性)的壁(紫外線導入窗)57。例如,紫外線導入窗57係短波長光的透過性高的氟化鈣製。 The processing apparatus 50 includes a chamber (outer casing) 51 that houses the platinum catalyst 31 and forms a path for the mixed gas 3 to pass through the platinum catalyst 31 and efficiently contacts the gas supply unit 52, and supplies the PFC gas to the chamber 51. a mixed gas 3 mixed with oxygen 2; and a dry pump 53 that discharges the generated carbon dioxide 5 from the chamber 51. The chamber 51 includes a catalyst reaction region 55 in which a catalyst (catalyst layer) 31 and an ultraviolet reaction region 56 are provided, and is disposed at an upper portion (upstream) of the catalyst reaction region 55. A part of the outer wall of the ultraviolet ray reaction region 56 of the chamber 51, for example, the upper surface (upper wall) of the chamber 51 is a wall (ultraviolet introduction window) 57 which is transparent (transparent) with respect to ultraviolet rays (vacuum ultraviolet rays). For example, the ultraviolet light introduction window 57 is made of calcium fluoride having high transmittance of short-wavelength light.

處理裝置50更包含配置在面向紫外線導入窗57的位置之紫外線照射單元20。本例的紫外線照射單元20包含作為紫外線源21的準分子燈。準分子燈21係能有效率地輸出波長是180nm以下程度的真空紫外線(VUV)22之紫外線源,可經由紫外線導入窗57對腔室51的紫外線反應區域56有效率地供給真空紫外線22。 The processing apparatus 50 further includes an ultraviolet irradiation unit 20 disposed at a position facing the ultraviolet light introduction window 57. The ultraviolet irradiation unit 20 of this example includes an excimer lamp as the ultraviolet source 21. The excimer lamp 21 can efficiently output an ultraviolet light source of a vacuum ultraviolet ray (VUV) 22 having a wavelength of about 180 nm or less, and can efficiently supply the vacuum ultraviolet ray 22 to the ultraviolet ray reaction region 56 of the chamber 51 via the ultraviolet ray introduction window 57.

腔室51係在和紫外線導入窗57對峙的位置,例如腔室51的底面設置用以反射紫外線的反射鏡58。於此腔室51中,觸媒反應區域55被紫外線導入窗57和反射鏡58包夾,由紫外線導入窗57所供給的真空紫外線(紫外光)22藉反射鏡58反射而往復於紫外線反應區域56及觸媒反應區域55,使得腔室51內的真空紫外線22之衰減受抑制。因此,不僅是紫外線反應區域56,在觸媒反應區域55中的混合氣體3和真空紫外線22亦進行反應而促進混合氣體3的自由基化。 The chamber 51 is disposed at a position facing the ultraviolet ray introduction window 57. For example, a mirror 58 for reflecting ultraviolet rays is provided on the bottom surface of the chamber 51. In the chamber 51, the catalyst reaction region 55 is sandwiched by the ultraviolet ray introduction window 57 and the mirror 58, and the vacuum ultraviolet ray (ultraviolet light) 22 supplied from the ultraviolet ray introduction window 57 is reflected by the mirror 58 to reciprocate in the ultraviolet ray reaction region. 56 and the catalyst reaction zone 55 are such that the attenuation of the vacuum ultraviolet rays 22 in the chamber 51 is suppressed. Therefore, not only the ultraviolet ray reaction region 56, but also the mixed gas 3 and the vacuum ultraviolet ray 22 in the catalyst reaction region 55 react to promote radicalization of the mixed gas 3.

處理裝置50係和上述的處理裝置60及80同樣地包含對觸媒層31施加正(高電位)偏壓的電壓供給單元35, 本例的觸媒層31也是擔持白金的多孔性陶瓷製觸媒體,蜂窩結構的孔33充填有顆粒狀的消石灰41。 Similarly to the processing devices 60 and 80 described above, the processing device 50 includes a voltage supply unit 35 that applies a positive (high potential) bias voltage to the catalyst layer 31. The catalyst layer 31 of this example is also a porous ceramic contact medium in which platinum is supported, and the pores 33 of the honeycomb structure are filled with granular slaked lime 41.

於此處理裝置50,紫外線反應區域56及觸媒反應區域55係在一個腔室51的內部連續地形成,在觸媒反應區域55的出口側設反射鏡58使真空紫外光22被反射於觸媒反應區域55。因此,於此處理裝置50,在觸媒反應區域55中,根據紫外線22的自由基化和根據觸媒31的氧化還元反應係同時地、並列地進行。因此,紫外線照射等而自由基化的混合氣體4再結合、已自由基化的氧穩定化前和觸媒31接觸且因觸媒31的作用而被氧化。因此,能效率地分解PFC1。 In the processing device 50, the ultraviolet ray reaction region 56 and the catalyst reaction region 55 are continuously formed inside one chamber 51, and a mirror 58 is provided on the outlet side of the catalyst reaction region 55 to cause the vacuum ultraviolet light 22 to be reflected. Media reaction area 55. Therefore, in the catalyst reaction region 55, the radical reaction of the ultraviolet rays 22 and the oxidation-reduction reaction according to the catalyst 31 are simultaneously and in parallel in the catalyst reaction region 55. Therefore, the mixed gas 4 which is radicalized by ultraviolet irradiation or the like is recombined, and the radicalized oxygen is brought into contact with the catalyst 31 before being stabilized by oxidation, and is oxidized by the action of the catalyst 31. Therefore, PFC1 can be efficiently decomposed.

圖6顯示PFC氣體的處理裝置(除害裝置)的另一不同例。就此處理裝置50a而言,在作為紫外線源的腔室51的紫外線反應區域56生成RF電漿(大氣壓電漿)24。處理裝置50包含將高頻電壓施加於被導入紫外線反應區域56的混合氣體3之大氣壓電漿產生裝置(高頻產生裝置)25。亦可在紫外線反應區域56生成大氣壓電漿26,並將源自於準分子燈21等的紫外線源之真空紫外線22照射於紫外線反應區域56。此處理裝置50a的其他構成係和圖5所示的處理裝置50共通。 Fig. 6 shows another different example of the processing device (abuse device) of the PFC gas. In this processing apparatus 50a, RF plasma (atmospheric piezoelectric slurry) 24 is generated in the ultraviolet reaction region 56 of the chamber 51 as an ultraviolet source. The processing device 50 includes an atmospheric piezoelectric slurry generating device (high-frequency generating device) 25 that applies a high-frequency voltage to the mixed gas 3 introduced into the ultraviolet-ray reaction region 56. The atmospheric piezoelectric slurry 26 may be generated in the ultraviolet ray reaction region 56, and the vacuum ultraviolet ray 22 derived from the ultraviolet ray source of the excimer lamp 21 or the like may be irradiated to the ultraviolet ray reaction region 56. The other configuration of the processing device 50a is common to the processing device 50 shown in FIG.

就此處理裝置50a而言,在紫外線反應區域50生成大氣壓電漿26。因此,依電漿的電離作用而更加促進混合氣體3的自由基化。因此,能更有效率地進行PFC氣體1的分解。 In this processing apparatus 50a, the atmospheric piezoelectric slurry 26 is generated in the ultraviolet ray reaction region 50. Therefore, the radicalization of the mixed gas 3 is further promoted by the ionization of the plasma. Therefore, the decomposition of the PFC gas 1 can be performed more efficiently.

如以上所說明,就本發明的氣體處理裝置而言, 係將藉紫外線照射或RF電漿且在大氣壓或接近大氣壓的壓力下以低溫將處理對象氣體自由基化的處理與之後使已自由基化的氣體與和被施加高電位偏壓的觸媒層反應的處理作組合,進行將氣體無害化或改質的處理。因此,依據本發明的處理裝置,能於大氣壓下且低溫下實現例如對PFC氣體進行無害化的處理。再者,本說明書中係揭示在處理對象氣體是大流量,例如被以數百LPM作供給那樣的場合下以低溫形成大氣壓電漿的條件及構成。透過在低溫下確實地生成大氣壓電漿(非平衡電漿),可將處理裝置的消耗電力抑制在10幾kW程度或其以下,可提供省電力型處理裝置。 As explained above, with the gas treatment device of the present invention, A process of radically treating a gas to be treated at a low temperature by ultraviolet irradiation or RF plasma and at a pressure of atmospheric pressure or near atmospheric pressure, and then a radicalized gas and a catalyst layer to which a high potential bias is applied The treatment of the reaction is combined to carry out a treatment for detoxifying or upgrading the gas. Therefore, according to the processing apparatus of the present invention, for example, the treatment of detoxifying the PFC gas can be realized under atmospheric pressure and at a low temperature. In the present specification, the conditions and configuration for forming the atmospheric piezoelectric slurry at a low temperature when the processing target gas is a large flow rate, for example, when it is supplied in a few hundred LPMs, is disclosed. By reliably generating atmospheric piezoelectric slurry (unbalanced plasma) at a low temperature, the power consumption of the processing apparatus can be suppressed to about 10 kW or less, and a power saving type processing apparatus can be provided.

又,關於PFC的除害處理,在處理中當氟等腐蝕性的氣體產生並成為高溫時,則因酸而導致的腐蝕顯著,維修頻度高。於本發明的處理裝置,因為能以低溫進行氣體的處理,故可提供一種可抑制腐蝕等之產生、保修頻度低的經濟的處理裝置。再者,就半導體工場等、處理對象氣體的產生源而言,大多使用可燃性氣體的場所並不少。從火災的危險性等考量,要在那樣的場所設置會成為高溫的裝置是有困難的。若為本發明的處理裝置,則設置於那樣的場所亦容易,可在處理對象氣體的產生源或其附近進行氣體處理。由於這點亦可削減積存或輸送處理對象氣體之設備及費用,所以本發明的處理裝置是經濟的。 Further, in the decontamination treatment of the PFC, when a corrosive gas such as fluorine is generated during the treatment and becomes a high temperature, the corrosion due to the acid is remarkable, and the maintenance frequency is high. In the processing apparatus of the present invention, since the gas can be treated at a low temperature, it is possible to provide an economical processing apparatus capable of suppressing generation of corrosion and the like and having a low warranty frequency. In addition, as for the source of the processing target gas such as a semiconductor factory, there are many places where flammable gas is often used. From the viewpoint of the risk of fire, etc., it is difficult to install a device that becomes high in such a place. In the case of the processing apparatus of the present invention, it is easy to install in such a place, and gas treatment can be performed at or near the source of the processing target gas. Since this also reduces the equipment and cost of accumulating or transporting the gas to be processed, the processing apparatus of the present invention is economical.

依PFC的無害化處理而產生的氟溶於水中所作成的氟酸會使裝置腐蝕。且成為需要放置進行氟系的水處理用的槽、池子的空間。就吸附方式、觸媒方式而言,留下所 謂如何處理既使用過的吸附劑、觸媒的課題。本發明的處理裝置及方法係包含採用多孔性的觸媒,於該孔中充填粒狀的消石灰,俾將氟以氟石的形態回收。由於氟的回收處理被乾式化,故必要設備全體變簡易。又,因為可一邊保護觸媒一邊使氟再資源化,所以透過可抑制處理裝置之性能的劣化並使氟再資源化,可提供更經濟的處理裝置。 The fluorine acid produced by dissolving fluorine in water according to the detoxification treatment of PFC causes corrosion of the device. Further, it is a space in which a tank or a tank for performing fluorine-based water treatment needs to be placed. In terms of adsorption mode and catalyst mode, It is said that how to deal with the problems of adsorbents and catalysts that have been used. The treatment apparatus and method of the present invention comprise a porous catalyst, and the pores are filled with granular slaked lime, and the fluorine is recovered in the form of fluorite. Since the fluorine recovery process is dried, it is necessary to make the entire equipment simple. Further, since the fluorine can be re-resourced while protecting the catalyst, the transmission can suppress deterioration of the performance of the processing apparatus and recycle the fluorine, thereby providing a more economical processing apparatus.

再者,由於本發明的處理裝置能以低溫進行氣體的處理,故花費在斷熱材等之保護機能上的費用及空間少,可避免處理對象氣體膨脹而增加處理體積那樣的事態。本發明的處理裝置係與處理流量相依,縱橫高度分別可收在1m~2m程度的尺寸,即便是設置空間有限的小型半導體工場也能充分設置。 Further, since the processing apparatus of the present invention can perform gas treatment at a low temperature, it takes a small amount of cost and space for the protection function of the heat-insulating material or the like, and it is possible to avoid a situation in which the processing target gas expands and the processing volume is increased. The processing apparatus of the present invention is dependent on the processing flow rate, and can have a vertical and horizontal height of about 1 m to 2 m, and can be sufficiently provided even in a small semiconductor factory having a limited installation space.

因本發明所包含的PFC氣體的除害裝置係小型化,故可獲得所謂在不對現今的半導體、FPD生產線變更佈局之下予以導入的效果。且能使PFC氣體的除害處理低能量化,因而可減低環境負荷,在對暖化氣體進行除害時所使用的化石燃料可減低到極限。又,因為低消耗電力化而削減溫室效應氣體的排出,故可提供更省電力的製品。再者,即便此處理裝置50之單體的分解率是70%程度,透過多段地組合,還是能將最終的PFC氣體的分解率提升至99%程度。 Since the detoxification device of the PFC gas included in the present invention is downsized, it is possible to obtain an effect of introducing the semiconductor semiconductor or the FPD production line without changing the layout. Moreover, the decontamination treatment of the PFC gas can be reduced, so that the environmental load can be reduced, and the fossil fuel used for detoxification of the warming gas can be reduced to the limit. Moreover, since the discharge of the greenhouse gas is reduced by the low power consumption, it is possible to provide a more power-saving product. Further, even if the decomposition rate of the monomer of the treatment apparatus 50 is about 70%, the decomposition rate of the final PFC gas can be increased to about 99% by combining in multiple stages.

此外,上述係藉由PFC氣體的除害裝置說明本發明的處理裝置,惟此處理裝置不限於PFC氣體,也可使用在對依半導體製程所產生的其他暖化氣體之處理或HFC(氫氟碳化合物)、SF6(六氟化硫)、SiH4(矽烷)等之其他氣體的 處理。再者,也可與SiH4的處理裝置連結而構築含有PFC氣體的氣體處理系統。 Further, the above-described processing apparatus of the present invention is described by a PFC gas detoxification apparatus, but the processing apparatus is not limited to PFC gas, and may be used for treatment of other warming gases or HFC (hydrogen fluoride) generated by a semiconductor process. Treatment of other gases such as carbon compounds), SF 6 (sulfur hexafluoride), and SiH 4 (decane). Further, a gas processing system containing PFC gas may be constructed by being connected to a processing device of SiH 4 .

再者,即使著眼於PFC氣體的除害裝置,亦不僅有助於半導體、液晶製造工場的暖化對策,亦能在將以PFC用作消火劑的船舶機器工場和船舶、航空器引擎工場和機場保修場、大型化學聯合工場等作為暖化氣體減低的除害裝置中發揮效果。且也可適用在各種醫療福祉施設之醫療機器‧器具‧用具類等之殺菌‧洗淨領域。 In addition, even if you focus on the PFC gas decontamination device, it will not only help the heating measures of semiconductor and liquid crystal manufacturing plants, but also ship equipment workshops and ships, aircraft engine workshops and airports that use PFC as a fire extinguishing agent. Warranty fields, large-scale chemical joint laboratories, etc. are effective as detoxification devices for reducing warm gas. It can also be applied to the fields of sterilization and cleaning of medical equipment, utensils, and utensils, which are used in various medical facilities.

1‧‧‧PFC氣體 1‧‧‧PFC gas

3‧‧‧混合氣體 3‧‧‧ mixed gas

4‧‧‧混合氣體 4‧‧‧ mixed gas

22‧‧‧真空紫外光 22‧‧‧vacuum ultraviolet light

24‧‧‧RF電漿 24‧‧‧RF plasma

31‧‧‧白金觸媒 31‧‧‧ Platinum Catalyst

Claims (11)

一種處理裝置,具有:流路,其處理對象的氣體之至少一部分被曝露在高頻電場或紫外線照射中;觸媒層,被供給已通過前述流路的氣體;及電壓供給單元,對前述觸媒層施加偏壓。 A processing device having a flow path in which at least a part of a gas to be treated is exposed to a high-frequency electric field or ultraviolet light; a catalyst layer supplied with a gas that has passed through the flow path; and a voltage supply unit that touches the aforementioned The dielectric layer applies a bias voltage. 如申請專利專利範圍第1項之處理裝置,其中更具有:複數個電極,位在前述流路的兩側,形成高頻電場;及介電質層,配置成包夾前述複數個電極。 The processing device of claim 1, further comprising: a plurality of electrodes positioned on both sides of the flow path to form a high frequency electric field; and a dielectric layer disposed to sandwich the plurality of electrodes. 如申請專利專利範圍第2項之處理裝置,其中前述介電質層係包含複數個凹凸構造。 The processing device of claim 2, wherein the dielectric layer comprises a plurality of concavo-convex structures. 如申請專利專利範圍第2或3項之處理裝置,其中更具有:針電極,配置在前述流路的上游。 A processing apparatus according to claim 2 or 3, further comprising: a needle electrode disposed upstream of the flow path. 如申請專利專利範圍第2至4項中任一項之處理裝置,其中更具有:磁場生成單元,沿著前述流路斷續地配置。 The processing apparatus according to any one of claims 2 to 4, further comprising: a magnetic field generating unit that is intermittently arranged along the flow path. 如申請專利專利範圍第2至5項中任一項之處理裝置,其中前述複數個電極具有:以位在前述流路的兩側般呈同心圓狀配置的複數個電極;及 對前述同心圓狀配置之複數個電極的外側的電極施加負電位的單元。 The processing device according to any one of claims 2 to 5, wherein the plurality of electrodes have: a plurality of electrodes arranged concentrically on both sides of the flow path; A unit of a negative potential is applied to the electrodes on the outer side of the plurality of electrodes arranged concentrically. 如申請專利專利範圍第1至6項中任一項之處理裝置,其中前述觸媒層,係多孔構造且包含內部充填有消石灰的層。 The processing apparatus according to any one of claims 1 to 6, wherein the catalyst layer is of a porous structure and comprises a layer filled with slaked lime inside. 如申請專利專利範圍第1至6項中任一項之處理裝置,其中前述觸媒層,係多孔構造且包含內部充填有粒狀消石灰的層。 The processing apparatus according to any one of claims 1 to 6, wherein the catalyst layer is a porous structure and includes a layer filled with granular slaked lime. 一種氣體的處理方法,包含:使處理對象氣體的至少一部分通過被曝露在高頻電場或紫外線照射的流路,及將已通過前述流路的氣體供予被施加偏壓的觸媒層。 A method for treating a gas includes: passing at least a part of a gas to be processed through a flow path exposed to a high-frequency electric field or ultraviolet rays, and supplying a gas having passed through the flow path to a catalyst layer to which a bias is applied. 如申請專利專利範圍第9項之氣體的處理方法,其中以於前述流路的兩側包夾介電質層般地配置用以形成高頻電場的電極,通過前述流路,係包含使前述處理對象氣體通過生成介電質屏蔽放電的前述流路。 The method for treating a gas according to the ninth aspect of the invention, wherein an electrode for forming a high-frequency electric field is disposed in a manner of sandwiching a dielectric layer on both sides of the flow path, and the flow path includes The treatment target gas passes through the aforementioned flow path for generating a dielectric shield discharge. 如申請專利專利範圍第9或10項之氣體的處理方法,其中前述觸媒層,係多孔構造且包含內部充填有消石灰的層,前述供給,係包含將已通過前述流路的氣體供予充填有前述消石灰的層。 The method for treating a gas according to claim 9 or 10, wherein the catalyst layer is a porous structure and includes a layer filled with slaked lime inside, and the supplying comprises supplying a gas that has passed through the flow path. There is a layer of the aforementioned slaked lime.
TW102120172A 2012-06-06 2013-06-06 Apparatus and method for processing gas TW201350191A (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2012129053A JP2015157230A (en) 2012-06-06 2012-06-06 Treatment apparatus and method

Publications (1)

Publication Number Publication Date
TW201350191A true TW201350191A (en) 2013-12-16

Family

ID=49711706

Family Applications (1)

Application Number Title Priority Date Filing Date
TW102120172A TW201350191A (en) 2012-06-06 2013-06-06 Apparatus and method for processing gas

Country Status (3)

Country Link
JP (1) JP2015157230A (en)
TW (1) TW201350191A (en)
WO (1) WO2013183300A1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105381693A (en) * 2014-09-04 2016-03-09 苏州鼎德电环保科技有限公司 Explosion-proof plasma

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP6373035B2 (en) * 2014-03-31 2018-08-15 株式会社Nbcメッシュテック Gas processing equipment
DE102020120582A1 (en) * 2020-08-04 2022-02-10 Cinogy Gmbh Gas cleaning device and method for cleaning a gas

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001054721A (en) * 1999-06-04 2001-02-27 Kashiyama Kogyo Kk Method and device for decomposing fluorocarbons
JP4006998B2 (en) * 2001-12-21 2007-11-14 ダイキン工業株式会社 Deodorizing device
JP4679315B2 (en) * 2005-09-15 2011-04-27 株式会社東芝 High temperature photocatalytic reactor
JP2007250478A (en) * 2006-03-18 2007-09-27 Nano Electronics & Micro System Technologies Inc Plasma processing system
US20090246524A1 (en) * 2006-06-02 2009-10-01 National University Corporation Tohoku University Porous calcium oxide particulate and porous calcium hydroxide particulate
JP5495219B2 (en) * 2007-03-30 2014-05-21 国立大学法人豊橋技術科学大学 Exhaust gas purification device
JP5437715B2 (en) * 2009-07-06 2014-03-12 東芝三菱電機産業システム株式会社 Active gas generating apparatus and remote plasma type film forming apparatus
JP5423594B2 (en) * 2010-06-23 2014-02-19 セントラル硝子株式会社 Method for removing fluorine-containing compound gas

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105381693A (en) * 2014-09-04 2016-03-09 苏州鼎德电环保科技有限公司 Explosion-proof plasma
WO2016034155A3 (en) * 2014-09-04 2016-04-28 苏州鼎德电环保科技有限公司 Anti-explosion purification device using plasma
CN105381693B (en) * 2014-09-04 2019-12-31 苏州鼎德电环保科技有限公司 Explosion-proof plasma

Also Published As

Publication number Publication date
WO2013183300A1 (en) 2013-12-12
JP2015157230A (en) 2015-09-03

Similar Documents

Publication Publication Date Title
Chu et al. Low temperature plasma technology: methods and applications
AU2006310457B2 (en) Combined treatment of gaseous effluents by cold plasma and photocatalysis
US7407635B2 (en) Processes and apparatuses for treating halogen-containing gases
Liu et al. Kinetic model of NO removal from SO2-containing simulated flue gas by wet UV/H2O2 advanced oxidation process
JP2009240862A (en) Gas purifying apparatus
Urashima et al. Removal of C/sub 2/F/sub 6/from a semiconductor process flue gas by a ferroelectric packed-bed barrier discharge reactor with an adsorber
Radoiu Studies on atmospheric plasma abatement of PFCs
US20020111045A1 (en) Atmospheric pressure plasma enhanced abatement of semiconductor process effluent species
He et al. Role of O3 in the removal of HCHO using a DC streamer plasma
TW201350191A (en) Apparatus and method for processing gas
CN206444423U (en) A kind of UV photoions waste gas purification apparatus
JPWO2008072392A1 (en) Exhaust gas treatment method and apparatus
US7220396B2 (en) Processes for treating halogen-containing gases
Qi et al. Simultaneous removal of NO and SO2 from dry gas stream using non-thermal plasma
KR100365368B1 (en) Method for treating toxic compounds using non-thermal plasma
Shi et al. Recent advances in degradation of the most potent industrial greenhouse gas sulfur hexafluoride
Hong et al. Decomposition of phosgene by microwave plasma-torch generated at atmospheric pressure
JPH07256056A (en) Treatment of waste substance
JP2001054721A (en) Method and device for decomposing fluorocarbons
JP2011110446A (en) Treatment apparatus of organic waste liquid, and treatment method of organic waste liquid
Zhang et al. Removal dynamics of nitric oxide (NO) pollutant gas by pulse-discharged plasma technique
WO2014207906A1 (en) Method for treating soil-contaminating water using photocatalytic material
Machmud et al. Review on Applying Plasma and Catalysis for Abating the Emissions of Fluorinated Compounds
JP2002336650A (en) Method of treating waste combustion gas
JP2007209897A (en) Apparatus and method for decomposing and removing nitrogen oxide in combustion exhaust gas