JP7684631B2 - Glass article manufacturing method and glass article manufacturing device - Google Patents
Glass article manufacturing method and glass article manufacturing device Download PDFInfo
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/0027—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours with additional separating or treating functions
- B01D46/0032—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours with additional separating or treating functions using electrostatic forces to remove particles, e.g. electret filters
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/0027—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours with additional separating or treating functions
- B01D46/0036—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours with additional separating or treating functions by adsorption or absorption
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/02—Particle separators, e.g. dust precipitators, having hollow filters made of flexible material
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/02—Particle separators, e.g. dust precipitators, having hollow filters made of flexible material
- B01D46/023—Pockets filters, i.e. multiple bag filters mounted on a common frame
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D47/00—Separating dispersed particles from gases, air or vapours by liquid as separating agent
- B01D47/06—Spray cleaning
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/54—Nitrogen compounds
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/75—Multi-step processes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/77—Liquid phase processes
- B01D53/78—Liquid phase processes with gas-liquid contact
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/02—Plant or installations having external electricity supply
- B03C3/16—Plant or installations having external electricity supply wet type
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- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03B—MANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
- C03B5/00—Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
- C03B5/16—Special features of the melting process; Auxiliary means specially adapted for glass-melting furnaces
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0241—Other waste gases from glass manufacture plants
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/50—Glass production, e.g. reusing waste heat during processing or shaping
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Description
本発明は、ガラス物品の製造方法及びガラス物品の製造装置の改良に関する。 The present invention relates to an improvement to a method for manufacturing glass articles and an apparatus for manufacturing glass articles.
ガラス溶融炉では、粉状又は粒状のガラス原料を、燃料(例えば天然ガス等の炭化水素ガス)を燃焼させるバーナや電極間の通電によって加熱することにより溶融ガラスを製造する。この溶融ガラスは、所定の成形工程を経て、ガラス板やガラス管、ガラス繊維などの種々のガラス物品になる In a glass melting furnace, powdered or granular glass raw material is heated by a burner that burns fuel (e.g., hydrocarbon gas such as natural gas) or by passing electricity between electrodes to produce molten glass. This molten glass goes through a specific forming process to become various glass products such as glass sheets, glass tubes, and glass fibers.
この際、ガラス溶融炉から発生する排ガス中には、ガラス原料中に含まれる成分の一部が気体又は微小固体の状態で含まれる。このため、排ガス中には、ガラス原料としてリサイクルできる成分も多く含まれている。したがって、排ガスからリサイクル原料を回収することができれば、ガラス原料の節約にも寄与し得る。また同時に環境にも配慮することができる。 At this time, the exhaust gas generated from the glass melting furnace contains some of the components contained in the glass raw materials in the form of gas or fine solids. For this reason, the exhaust gas also contains many components that can be recycled as glass raw materials. Therefore, if recycled raw materials can be recovered from the exhaust gas, it can contribute to saving glass raw materials. At the same time, it can also be environmentally friendly.
このような方法の一つとして、例えば、特許文献1では、ホウ素を含むガラス原料を溶融するガラス溶融炉の排ガスからホウ素を含むリサイクル原料を回収する技術が開示されている。詳細には、ガラス溶融炉から排出された排ガスをスプレー塔で冷却水の噴霧により冷却すると、排ガス中に気体として含まれるホウ素が固体(粉塵)として析出し、冷却水(捕集液)に捕集される。スプレー塔を通過したホウ素は湿式電気集塵機の水と接触し、その水(捕集液)に捕集される。このホウ素を含む捕集液に消石灰等の中和剤を加え、不純物除去等の処理を施すことにより、リサイクル原料としてホウ素が回収される(特許文献1参照)。 As one such method, for example, Patent Document 1 discloses a technology for recovering recycled materials containing boron from exhaust gas of a glass melting furnace that melts glass raw materials containing boron. In detail, when the exhaust gas discharged from the glass melting furnace is cooled by spraying cooling water in a spray tower, the boron contained as a gas in the exhaust gas precipitates as a solid (dust) and is collected in the cooling water (collection liquid). The boron that passes through the spray tower comes into contact with water from a wet electrostatic precipitator and is collected in the water (collection liquid). A neutralizing agent such as hydrated lime is added to this collection liquid containing boron, and processing such as removing impurities is performed, thereby recovering boron as a recycled material (see Patent Document 1).
しかしながら、スプレー塔や湿式電気集塵機を用いる湿式設備によりホウ素を回収する場合、大規模な排水処理設備が必要となり、消費電力の増加によりランニングコストが増加すると共にイニシャルコストが増加する。 However, when recovering boron using wet equipment that uses spray towers or wet electrostatic precipitators, large-scale wastewater treatment equipment is required, which increases power consumption, resulting in higher running costs and higher initial costs.
本発明は、ガラス溶融炉から排出される排ガスから粉塵を低コストで効率良く回収することを課題とする。 The objective of the present invention is to efficiently recover dust from exhaust gas discharged from a glass melting furnace at low cost.
溶融炉内でガラス原料を加熱して溶融ガラスを得る溶融工程と、前記溶融ガラスをガラス物品に成形する成形工程と、前記溶融炉内から排出される排ガスから粉塵を除去する排ガス処理工程と、を含むガラス物品の製造方法であって、前記溶融工程は、主に電極を用いる通電加熱により前記ガラス原料を溶融する通電加熱工程を含み、前記排ガス処理工程は、前記通電加熱工程を実行中の前記溶融炉内から排出される前記排ガスを処理する乾式捕集工程を含み、前記乾式捕集工程は、前記排ガスに冷却ガスを混合する乾式冷却工程と、前記乾式冷却工程を経た前記排ガスから乾式分離装置を用いて前記粉塵を分離する乾式分離工程と、を含むことを特徴とする。 A method for manufacturing a glass article, comprising a melting process for heating glass raw materials in a melting furnace to obtain molten glass, a forming process for forming the molten glass into a glass article, and an exhaust gas treatment process for removing dust from exhaust gas discharged from the melting furnace, wherein the melting process comprises an electric heating process for melting the glass raw materials by electric heating mainly using electrodes, the exhaust gas treatment process comprises a dry collection process for treating the exhaust gas discharged from the melting furnace during the electric heating process, and the dry collection process comprises a dry cooling process for mixing a cooling gas with the exhaust gas, and a dry separation process for separating the dust from the exhaust gas that has been subjected to the dry cooling process using a dry separation device.
溶融炉内でガラス原料を溶融するための加熱手段としては、通電加熱と燃焼加熱が用いられる。通電加熱は、溶融ガラスに浸漬させた電極間に通電することにより溶融ガラスを加熱する方法である。燃焼加熱は、溶融炉内で燃料を燃焼させることによりガラス原料及び溶融ガラスを加熱する方法である。通電加熱により発生する排ガスは燃焼加熱により発生する排ガスと比較して、含まれる水蒸気の割合が低い。排ガスに含まれる水蒸気の割合が高いと、バグフィルタ等の乾式分離装置で目詰まりが発生しやすくなり、メンテナンスコストが増加するおそれがある。したがって、主に電極を用いる通電加熱によりガラス原料を溶融する通電加熱工程であれば、排ガスに含まれる水蒸気の割合が低くなることから、目詰まりを抑制でき、メンテナンスコストを低減できる。また、スプレー塔や湿式電気集塵機、排水処理設備、中和剤等の薬品を用いることなく排ガス処理が可能であり、排ガスから粉塵を低コストで効率良く回収することができる。 Electric heating and combustion heating are used as heating means for melting glass raw materials in a melting furnace. Electric heating is a method of heating molten glass by passing electricity between electrodes immersed in molten glass. Combustion heating is a method of heating glass raw materials and molten glass by burning fuel in a melting furnace. The exhaust gas generated by electric heating contains a lower proportion of water vapor than the exhaust gas generated by combustion heating. If the proportion of water vapor in the exhaust gas is high, clogging is likely to occur in dry separation devices such as bag filters, and maintenance costs may increase. Therefore, if the electric heating process melts glass raw materials mainly by electric heating using electrodes, the proportion of water vapor in the exhaust gas is low, so clogging can be suppressed and maintenance costs can be reduced. In addition, exhaust gas treatment is possible without using spray towers, wet electric dust collectors, wastewater treatment equipment, or chemicals such as neutralizing agents, and dust can be efficiently collected from the exhaust gas at low cost.
上記の構成において、前記乾式分離装置は、バグフィルタであることが好ましい。このような構成によれば、排ガスから粉塵をより低コストで回収することができる。 In the above configuration, the dry separation device is preferably a bag filter. With this configuration, dust can be collected from the exhaust gas at a lower cost.
上記の構成において、前記溶融工程は、少なくとも、バーナを用いる燃焼加熱によって前記ガラス原料を溶融する燃焼加熱工程を含み、前記排ガス処理工程は、前記燃焼加熱工程を実行中の前記溶融炉内から排出される排ガスを処理する湿式捕集工程を含み、前記湿式捕集工程は、前記排ガスに冷却液を散布する湿式冷却工程を含むことが好ましい。燃焼加熱工程を行う溶融炉から排出される排ガスは、含まれる水蒸気の割合が高い。湿式捕集工程は、含まれる水蒸気の割合が高い排ガスを支障なく処理可能である。このため、燃焼加熱を行う際は、湿式捕集工程を行うことにより、効率良く排ガス処理を行うことができる。燃焼加熱工程及び湿式捕集工程は、例えば溶融炉の立ち上げ時等に一時的に実施され、特許文献1のようにスプレー塔等を常時使用するものではない。このため、スプレー塔等を他の溶融炉等と共用したり、小型化したりすることが可能となり、ランニングコスト及びイニシャルコストを削減できる。 In the above configuration, the melting process includes at least a combustion heating process for melting the glass raw material by combustion heating using a burner, and the exhaust gas treatment process includes a wet collection process for treating the exhaust gas discharged from the melting furnace during the combustion heating process, and the wet collection process preferably includes a wet cooling process for spraying a cooling liquid into the exhaust gas. The exhaust gas discharged from the melting furnace performing the combustion heating process contains a high proportion of water vapor. The wet collection process can treat exhaust gas containing a high proportion of water vapor without any problems. Therefore, when performing combustion heating, the wet collection process can be performed to efficiently treat the exhaust gas. The combustion heating process and the wet collection process are performed temporarily, for example, when the melting furnace is started up, and the spray tower or the like is not used all the time as in Patent Document 1. Therefore, it is possible to share the spray tower or the like with other melting furnaces or to reduce its size, thereby reducing running costs and initial costs.
上記の構成において、前記湿式捕集工程は、前記湿式冷却工程を経た前記排ガスから湿式分離装置を用いて前記粉塵を分離する湿式分離工程を含むことが好ましい。このような構成によれば、排ガスから粉塵をより確実に回収することができる。 In the above configuration, it is preferable that the wet collection process includes a wet separation process in which the dust is separated from the exhaust gas that has been subjected to the wet cooling process using a wet separation device. With this configuration, dust can be more reliably collected from the exhaust gas.
上記の構成において、前記湿式分離装置は、湿式電気集塵機であることが好ましい。このような構成によれば、排ガスから粉塵をより確実に、より低コストで回収することができる。 In the above configuration, the wet separation device is preferably a wet electrostatic precipitator. With this configuration, dust can be collected from the exhaust gas more reliably and at lower cost.
上記の構成において、前記乾式冷却工程を経た前記排ガスの温度は、60℃以下であることが好ましい。このような構成によれば、排ガス中に気体状態で含まれる成分を固体として析出させ、乾式分離工程において回収することができる。 In the above configuration, it is preferable that the temperature of the exhaust gas after the dry cooling process is 60°C or less. With this configuration, components contained in the exhaust gas in a gaseous state can be precipitated as solids and recovered in the dry separation process.
上記の構成において、前記通電加熱工程を実行中の前記溶融炉から排出された排ガス中に含まれる水蒸気の体積分率が10%以下であることが好ましい。このような構成によれば、乾式冷却工程を経ても排ガス中に含まれる水蒸気が結露せず、乾式捕集工程を効率良く行うことができる。 In the above configuration, it is preferable that the volume fraction of water vapor contained in the exhaust gas discharged from the melting furnace during the electrical heating process is 10% or less. With this configuration, the water vapor contained in the exhaust gas does not condense even after the dry cooling process, and the dry collection process can be carried out efficiently.
上記の構成において、前記ガラス原料はホウ素を含み、前記排ガス処理工程は、前記粉塵からホウ素を回収する回収工程を含むことが好ましい。このような構成によれば、回収したホウ素をガラス原料として再利用することができる。なお、ここでいう「ホウ素」は、酸化ホウ素やホウ酸などのホウ素化合物を含むものとする(以下、同様)。 In the above configuration, it is preferable that the glass raw material contains boron, and the exhaust gas treatment process includes a recovery process for recovering boron from the dust. With such a configuration, the recovered boron can be reused as a glass raw material. Note that "boron" here includes boron compounds such as boron oxide and boric acid (the same applies below).
上記の構成において、前記排ガス処理工程は、前記乾式捕集工程又は前記湿式捕集工程を経た排ガスに脱硝処理を施す脱硝工程を含むことが好ましい。このような構成によれば、排ガス中に含まれる窒素酸化物が環境中に流出する量を減らすことができる。 In the above configuration, it is preferable that the exhaust gas treatment process includes a denitrification process in which the exhaust gas that has passed through the dry capture process or the wet capture process is subjected to a denitrification process. With this configuration, it is possible to reduce the amount of nitrogen oxides contained in the exhaust gas that flow into the environment.
上記の構成において、前記冷却ガスの温度は、15℃以上であることが好ましい。このような構成によれば、排ガス中に気体状態で含まれる成分を固体として析出させることができる。また、乾式冷却工程を経た排ガスが必要以上に冷却されることが無く、排ガス中に含まれる水蒸気の結露を防止することができる。これにより、乾式分離装置の目詰まりや、設備の腐食を防止することができる。 In the above configuration, the temperature of the cooling gas is preferably 15°C or higher. With this configuration, the components contained in the exhaust gas in a gaseous state can be precipitated as solids. In addition, the exhaust gas that has been through the dry cooling process is not cooled more than necessary, and condensation of water vapor contained in the exhaust gas can be prevented. This makes it possible to prevent clogging of the dry separation device and corrosion of the equipment.
上記の構成において、前記冷却ガスは、前記溶融炉からの排熱により加熱されることが好ましい。外気温が15℃以上の場合は、冷却ガスとして外気を直接利用できる。一方で外気温が15℃未満の場合は、排ガス中に含まれる水蒸気の結露を防止するため、15℃以上まで昇温することで冷却ガスとして使用できる。外気を昇温するに際して、溶融炉からの排熱を使用することで、使用するエネルギーを削減することができる。 In the above configuration, it is preferable that the cooling gas is heated by exhaust heat from the melting furnace. When the outside air temperature is 15°C or higher, the outside air can be used directly as the cooling gas. On the other hand, when the outside air temperature is less than 15°C, the outside air can be used as the cooling gas by heating it to 15°C or higher to prevent condensation of the water vapor contained in the exhaust gas. By using the exhaust heat from the melting furnace to heat the outside air, the amount of energy used can be reduced.
また、本発明に係るガラス物品の製造装置は、ガラス原料を加熱し溶融ガラスを得る溶融炉と、前記溶融ガラスをガラス物品に成形する成形装置と、前記溶融炉内から排出される排ガスから粉塵を除去する排ガス処理設備と、を備えるガラス物品の製造装置であって、前記溶融炉では、主に電極を用いる通電加熱により前記ガラス原料を溶融する通電加熱工程を行い、前記排ガス処理設備は、乾式捕集設備を備え、前記乾式捕集設備は、前記排ガスに冷却ガスを混合する乾式冷却装置と、バグフィルタを用いて前記排ガスから前記粉塵を分離する乾式分離装置と、を含み、前記乾式捕集設備では、前記通電加熱工程を実行中の前記溶融炉内から排出される排ガスを処理することを特徴とする。このような構成によれば、ガラス溶融炉から排出される排ガスから粉塵を低コストで効率良く回収することができる。 The glass article manufacturing apparatus according to the present invention is an apparatus for manufacturing glass articles, comprising a melting furnace for heating glass raw materials to obtain molten glass, a forming device for forming the molten glass into a glass article, and an exhaust gas treatment facility for removing dust from exhaust gas discharged from the melting furnace, wherein the melting furnace performs an electric heating process for melting the glass raw materials mainly by electric heating using electrodes, and the exhaust gas treatment facility includes a dry collection facility, which includes a dry cooling device for mixing a cooling gas with the exhaust gas and a dry separation device for separating the dust from the exhaust gas using a bag filter, and the dry collection facility treats the exhaust gas discharged from the melting furnace during the electric heating process. With this configuration, dust can be efficiently collected from the exhaust gas discharged from the glass melting furnace at low cost.
本発明によれば、ガラス溶融炉から排出される排ガスから粉塵を低コストで効率良く回収することができる。 According to the present invention, dust can be efficiently recovered from exhaust gas discharged from a glass melting furnace at low cost.
以下、添付図面に従って、本発明に係るガラス物品の製造方法の一実施形態について説明する。 Below, one embodiment of the method for manufacturing a glass article according to the present invention will be described with reference to the attached drawings.
図1及び図2に示すように、本実施形態に係るガラス物品の製造方法は、溶融工程S1、成形工程S2、及び排ガス処理工程S3を含む。 As shown in Figures 1 and 2, the method for manufacturing a glass article according to this embodiment includes a melting process S1, a forming process S2, and an exhaust gas treatment process S3.
溶融工程S1では、所定の成分比に調整されたガラス原料Grが、原料投入装置11を用いて溶融炉1へ供給される。原料投入装置11としては、例えばスクリュフィーダを使用することができる。溶融炉1では、ガラス原料Grを加熱して溶融ガラスGmを得る。溶融炉1からは、ガラス原料Gr及び溶融ガラスGmの加熱に伴い、排ガスGsが排出される。溶融工程S1は、通電加熱工程S11と燃焼加熱工程S12とを含む。 In the melting step S1, glass frit Gr adjusted to a predetermined component ratio is supplied to the melting furnace 1 using a raw material input device 11. For example, a screw feeder can be used as the raw material input device 11. In the melting furnace 1, the glass frit Gr is heated to obtain molten glass Gm. As the glass frit Gr and molten glass Gm are heated, exhaust gas Gs is discharged from the melting furnace 1. The melting step S1 includes an electrical heating step S11 and a combustion heating step S12.
通電加熱工程S11は、主に図示しない電極を用いる通電加熱によりガラス原料Grを加熱する工程である。通電加熱工程S11では、補助的に燃焼加熱を用いても良いが、燃焼加熱を用いることなく、通電加熱のみでガラス原料Grを加熱することが好ましい。補助的に燃焼加熱を用いる場合、排ガスGs中に含まれる水蒸気の体積分率を、好ましくは10%以下、より好ましくは8%以下、さらに好ましくは5%以下にする観点から、燃焼加熱による発熱量と通電加熱による発熱量の合計発熱量に対して通電加熱による発熱量が占める割合が90%以上であることが好ましい。本実施形態の通電加熱工程S11は、操業中に実行され、ガラス原料Grが溶融炉1に連続的に供給されると共に、溶融炉1から溶融ガラスGmが連続的に排出される。 The electric heating step S11 is a step of heating the glass frit Gr mainly by electric heating using electrodes not shown. In the electric heating step S11, combustion heating may be used as an auxiliary, but it is preferable to heat the glass frit Gr only by electric heating without using combustion heating. When combustion heating is used as an auxiliary, it is preferable that the ratio of the heat generated by electric heating to the total heat generated by the heat generated by combustion heating and the heat generated by electric heating is 90% or more, from the viewpoint of making the volume fraction of water vapor contained in the exhaust gas Gs preferably 10% or less, more preferably 8% or less, and even more preferably 5% or less. The electric heating step S11 of this embodiment is performed during operation, and the glass frit Gr is continuously supplied to the melting furnace 1, and the molten glass Gm is continuously discharged from the melting furnace 1.
燃焼加熱工程S12は、少なくともバーナを用いる燃焼加熱によりガラス原料Grを加熱する工程である。燃焼加熱工程S12では、燃焼加熱のみでガラス原料Grを加熱しても良く、補助的に通電加熱を用いてガラス原料Grを加熱しても良い。本実施形態の燃焼加熱工程S12は、操業前の立ち上げ時に実行される。この場合、ガラス原料Grが溶融炉1に連続的又は断続的に供給される。 The combustion heating step S12 is a step of heating the glass frit Gr by combustion heating using at least a burner. In the combustion heating step S12, the glass frit Gr may be heated only by combustion heating, or the glass frit Gr may be heated supplementarily by electrical heating. The combustion heating step S12 of this embodiment is performed at the start-up before operation. In this case, the glass frit Gr is supplied to the melting furnace 1 continuously or intermittently.
溶融炉1から排出される排ガスGsは、バーナの燃焼ガスと、ガラス原料Gr及び溶融ガラスGmからの揮発物とを含む。燃焼ガスは、二酸化炭素と、水蒸気と、窒素酸化物と、硫黄酸化物と、を含む。揮発物は、ホウ素を含む。 The exhaust gas Gs discharged from the melting furnace 1 contains burner combustion gas and volatile matter from the glass raw material Gr and molten glass Gm. The combustion gas contains carbon dioxide, water vapor, nitrogen oxides, and sulfur oxides. The volatile matter contains boron.
通電加熱では、溶融ガラスGmに浸漬した電極間に通電することによって、溶融ガラスGmが加熱される。通電加熱のみによってガラス原料Grを加熱する場合、排ガスGsは燃焼ガスを含まない。 In electrical heating, the molten glass Gm is heated by passing electricity between electrodes immersed in the molten glass Gm. When glass raw material Gr is heated only by electrical heating, the exhaust gas Gs does not contain combustion gas.
燃焼加熱には、空気燃焼バーナや酸素燃焼バーナ等のバーナが用いられる。加熱効率が高く、排ガスGsの量が少ないことから、酸素燃焼バーナを使用することが好ましい。バーナの燃料としては、天然ガス等の気体燃料が用いられる。気体燃料は、硫黄化合物の含有量が少ないことが好ましい。これにより、後述の排ガス処理工程S3において硫黄酸化物の除去工程を省略できると共に、亜硫酸や硫酸の発生による排ガス処理設備3の劣化を防止することができる。 For the combustion heating, burners such as air combustion burners and oxygen combustion burners are used. It is preferable to use oxygen combustion burners because they have high heating efficiency and produce a small amount of exhaust gas Gs. As fuel for the burners, gaseous fuels such as natural gas are used. It is preferable that the gaseous fuel contains a small amount of sulfur compounds. This makes it possible to omit the sulfur oxide removal process in the exhaust gas treatment process S3 described below, and prevents deterioration of the exhaust gas treatment equipment 3 due to the generation of sulfurous acid and sulfuric acid.
通電加熱には、排ガスGsの量が少ない、排ガスGs中に含まれる水蒸気の割合が少ない、溶融ガラスGmの加熱効率が良い、という利点がある。しかしながら、ガラス原料Grや固化したガラスには電流が流れ難いため、溶融炉1の立ち上げ時や、溶融炉1を一時的に停止した後の再立ち上げ時には、通電加熱によって溶融ガラスGmを得ることは困難である。このため、溶融炉1の立ち上げ時及び再立ち上げ時には、初めは燃焼加熱のみによって溶融ガラスGmを得て、順次通電加熱の割合を増加させる方法が用いられる。 Electrical heating has the advantages of a small amount of exhaust gas Gs, a small proportion of water vapor contained in the exhaust gas Gs, and good heating efficiency for molten glass Gm. However, because it is difficult for electric current to flow through glass raw material Gr and solidified glass, it is difficult to obtain molten glass Gm by electrical heating when starting up the melting furnace 1 or when restarting the melting furnace 1 after it has been temporarily stopped. For this reason, when starting up and restarting the melting furnace 1, a method is used in which molten glass Gm is obtained initially only by combustion heating, and the proportion of electrical heating is gradually increased.
溶融工程S1で得られた溶融ガラスGmは、成形装置2へ送られ、成形工程S2が行われる。成形工程S2では、溶融ガラスGmをガラス板や管ガラス、ガラス繊維等の所定の形状のガラス物品Gpに成形する。例えばガラス板に成形する場合は、フロート法やオーバーフローダウンドロー法、スロットダウンドロー法、ロールアウト法等が用いられる。 The molten glass Gm obtained in the melting step S1 is sent to a forming device 2, where the forming step S2 is carried out. In the forming step S2, the molten glass Gm is formed into a glass product Gp of a predetermined shape, such as a glass plate, a glass tube, or glass fiber. For example, when forming into a glass plate, the float method, the overflow downdraw method, the slot downdraw method, the roll-out method, or the like is used.
溶融炉1から排出される排ガスGsは、排ガス処理設備3へ導入され、排ガス処理工程S3が行われる。排ガス処理設備3は、乾式捕集設備31と、湿式捕集設備32と、脱硝設備33と、回収設備34と、を備える。また、排ガス処理工程S3は、乾式捕集工程S31と、湿式捕集工程S32と、脱硝工程S33と、回収工程S34と、を含む。 The exhaust gas Gs discharged from the melting furnace 1 is introduced into the exhaust gas treatment equipment 3, where the exhaust gas treatment process S3 is carried out. The exhaust gas treatment equipment 3 includes a dry capture equipment 31, a wet capture equipment 32, a denitrification equipment 33, and a recovery equipment 34. The exhaust gas treatment process S3 also includes a dry capture equipment S31, a wet capture equipment S32, a denitrification equipment S33, and a recovery process S34.
通電加熱工程S11を行う溶融炉1から排出される排ガスGs11は、乾式捕集設備31へと導入され、乾式捕集工程S31が行われる。乾式捕集設備31は、乾式冷却装置311と、乾式分離装置312と、を備える。また、乾式捕集工程S31は、乾式冷却工程S311と、乾式分離工程S312とを含む。 The exhaust gas Gs11 discharged from the melting furnace 1 performing the electrical heating process S11 is introduced into the dry collection equipment 31, where the dry collection process S31 is performed. The dry collection equipment 31 includes a dry cooling device 311 and a dry separation device 312. The dry collection process S31 also includes a dry cooling process S311 and a dry separation process S312.
乾式捕集設備31へ導入された排ガスGs11は、初めに乾式冷却装置311へ導入され、乾式冷却工程S311が行われる。乾式冷却工程S311では、80℃~300℃程度の排ガスGs11に冷却ガスGcを混合し、温度を低下させる。混合する冷却ガスGcの温度は、15℃以上であることが好ましく、20℃以上であることがより好ましい。冷却された排ガスGs12の温度は、15℃以上60℃以下であることが好ましく、20℃以上40℃以下であることがより好ましい。冷却された排ガスGs12の温度が低すぎると、排ガスGs12中に含まれる水蒸気が結露し、水滴が発生する。発生した水滴は、後述のバグフィルタの目詰まりや、配管の腐食等の悪影響を与える。一方で排ガスGs12の温度が高すぎると、排ガスGs中に気体状態で含まれるホウ素を固体として析出させることができないため、後述の乾式分離工程S312においてホウ素を回収することができず、大気中に流出する。また、外気の温度が15℃以上である場合は、冷却ガスGcとして外気を導入して使用することが好ましい。外気の温度が15℃未満である場合は、外気を溶融炉1からの排熱を利用して加熱し、冷却ガスGcとして使用することが好ましい。溶融炉1からの排熱を利用することで、冷却ガスGcを最適な温度に維持するためのエネルギーを節約することができる。 The exhaust gas Gs11 introduced into the dry collection equipment 31 is first introduced into the dry cooling device 311, where the dry cooling process S311 is performed. In the dry cooling process S311, the exhaust gas Gs11 at about 80°C to 300°C is mixed with cooling gas Gc to lower the temperature. The temperature of the mixed cooling gas Gc is preferably 15°C or higher, more preferably 20°C or higher. The temperature of the cooled exhaust gas Gs12 is preferably 15°C or higher and 60°C or lower, more preferably 20°C or higher and 40°C or lower. If the temperature of the cooled exhaust gas Gs12 is too low, the water vapor contained in the exhaust gas Gs12 condenses and water droplets are generated. The generated water droplets have adverse effects such as clogging of the bag filter and corrosion of the piping, which will be described later. On the other hand, if the temperature of the exhaust gas Gs12 is too high, the boron contained in the exhaust gas Gs in a gaseous state cannot be precipitated as a solid, and therefore the boron cannot be recovered in the dry separation step S312 described below, and flows out into the atmosphere. Also, when the temperature of the outside air is 15°C or higher, it is preferable to introduce and use the outside air as the cooling gas Gc. When the temperature of the outside air is less than 15°C, it is preferable to heat the outside air using the exhaust heat from the melting furnace 1 and use it as the cooling gas Gc. By using the exhaust heat from the melting furnace 1, it is possible to save energy for maintaining the cooling gas Gc at an optimal temperature.
乾式冷却工程S311を経た排ガスGs12は、乾式分離装置312へ導入され、乾式分離工程S312が行われる。乾式分離工程S312では、排ガスGs12が乾式分離装置312を通過する際に、固体状態のホウ素を含む粉塵が排ガスGs12から分離される。乾式分離装置312としては、低コストで運用可能であるバグフィルタを用いることが好ましい。 The exhaust gas Gs12 that has passed through the dry cooling process S311 is introduced into the dry separation device 312, where the dry separation process S312 is carried out. In the dry separation process S312, as the exhaust gas Gs12 passes through the dry separation device 312, dust containing solid boron is separated from the exhaust gas Gs12. As the dry separation device 312, it is preferable to use a bag filter, which can be operated at low cost.
燃焼加熱工程S12を行う溶融炉1から排出される排ガスGs21は、湿式捕集設備32へと導入され、湿式捕集工程S32が行われる。湿式捕集設備32は、湿式冷却装置321と、湿式分離装置322と、を備える。また、湿式捕集工程S32は、湿式冷却工程S321と、湿式分離工程S322とを含む。燃焼加熱工程S12が行われる溶融炉1から排出される排ガスGsは、含まれる水蒸気の割合が高いため、冷却すると水蒸気が結露しやすい。このため、バグフィルタ等のフィルタを用いた分離工程を行うと、容易に目詰まりを起こし、メンテナンスコストが増加する。コストを抑えつつ、結露に影響を受けずに排ガスGsからホウ素を含む粉塵を分離するためには、湿式捕集工程S32を行うことが好ましい。 The exhaust gas Gs21 discharged from the melting furnace 1 performing the combustion heating process S12 is introduced into the wet collection equipment 32, where the wet collection process S32 is performed. The wet collection equipment 32 includes a wet cooling device 321 and a wet separation device 322. The wet collection process S32 also includes a wet cooling process S321 and a wet separation process S322. The exhaust gas Gs discharged from the melting furnace 1 performing the combustion heating process S12 contains a high proportion of water vapor, so the water vapor is likely to condense when cooled. For this reason, if a separation process is performed using a filter such as a bag filter, clogging easily occurs, and maintenance costs increase. In order to separate dust containing boron from the exhaust gas Gs while suppressing costs and without being affected by condensation, it is preferable to perform the wet collection process S32.
湿式捕集設備32へ導入された排ガスGs21は、初めに湿式冷却装置321(例えばスプレー塔)へ導入され、湿式冷却工程S321が行われる。湿式冷却工程S321では、排ガスGs21に冷却液Lcを散布し、温度を低下させる。冷却された排ガスGs22の温度は、60℃以上70℃以下であることが好ましい。このように排ガスGs22の温度を低下させれば、排ガスGs中に気体状態で含まれるホウ素の大部分を固体として析出させ、回収することができる。冷却液Lcとしては、水を用いても良く、石灰水を用いても良い。また、後述の湿式分離装置322でホウ素を捕集した液体を用いても良い。排ガスGs21が冷却液Lcと接触するのに伴い、排ガスGs21から固体(粉塵)状態又は気体状態のホウ素が冷却液Lcに捕集される。 The exhaust gas Gs21 introduced into the wet collection equipment 32 is first introduced into a wet cooling device 321 (e.g., a spray tower) and a wet cooling process S321 is performed. In the wet cooling process S321, the exhaust gas Gs21 is sprayed with a cooling liquid Lc to lower the temperature. The temperature of the cooled exhaust gas Gs22 is preferably 60°C or higher and 70°C or lower. By lowering the temperature of the exhaust gas Gs22 in this manner, most of the boron contained in the exhaust gas Gs in a gaseous state can be precipitated as a solid and recovered. As the cooling liquid Lc, water or lime water may be used. In addition, a liquid that has captured boron in the wet separation device 322 described later may be used. As the exhaust gas Gs21 comes into contact with the cooling liquid Lc, boron in a solid (dust) state or gaseous state is captured from the exhaust gas Gs21 by the cooling liquid Lc.
湿式冷却工程S321を経た排ガスGs22は、湿式分離装置322へ導入され、湿式分離工程S322が行われることが好ましい。湿式分離工程S322では、排ガスGs22が湿式分離装置322を通過する際に、排ガスGs22から固体(粉塵)状態又は気体状態のホウ素が液体(例えば水)と接触することで液体に捕集される。湿式分離装置322としては、排ガスGs22からの粉塵及び液滴の分離性能の高さから、湿式電気集塵機を使用することが好ましい。 The exhaust gas Gs22 that has passed through the wet cooling step S321 is preferably introduced into the wet separation device 322, where the wet separation step S322 is performed. In the wet separation step S322, as the exhaust gas Gs22 passes through the wet separation device 322, boron in a solid (dust) state or gaseous state from the exhaust gas Gs22 comes into contact with the liquid (e.g., water) and is collected in the liquid. As the wet separation device 322, it is preferable to use a wet electrostatic precipitator because of its high performance in separating dust and liquid droplets from the exhaust gas Gs22.
乾式捕集工程S31を経た排ガスGs13、及び湿式捕集工程S32を経た排ガスGs23は、脱硝設備33へ導入され、脱硝工程S33が行われることが好ましい。脱硝工程S33では、排ガスGs13及び排ガスGs23に還元剤としてアンモニアを混合した後、触媒と接触させることで、排ガスGs13及び排ガスGs23中に含まれる窒素酸化物を還元する。脱硝工程S33を経た排ガスGs3は、煙突を介して大気中へ放出される。 The exhaust gas Gs13 that has passed through the dry capture process S31, and the exhaust gas Gs23 that has passed through the wet capture process S32 are preferably introduced into the denitration equipment 33, where the denitration process S33 is carried out. In the denitration process S33, the exhaust gas Gs13 and the exhaust gas Gs23 are mixed with ammonia as a reducing agent, and then brought into contact with a catalyst to reduce the nitrogen oxides contained in the exhaust gas Gs13 and the exhaust gas Gs23. The exhaust gas Gs3 that has passed through the denitration process S33 is released into the atmosphere via a chimney.
乾式分離工程S312及び湿式分離工程S322に続いて、回収工程S34が行われる。また、回収工程S34は、乾式分離装置312からホウ素を含むダストDを回収する乾式回収工程S341と、ホウ素が捕集された液体からホウ素を回収する湿式回収工程S342と、を含む。回収設備34は、固液分離装置3421と、乾燥機3422と、を備える。 The recovery process S34 is carried out following the dry separation process S312 and the wet separation process S322. The recovery process S34 also includes a dry recovery process S341 for recovering dust D containing boron from the dry separation device 312, and a wet recovery process S342 for recovering boron from the liquid in which boron has been collected. The recovery facility 34 includes a solid-liquid separator 3421 and a dryer 3422.
乾式回収工程S341では、例えば、バグフィルタに堆積したダストDを払い落とし、乾式分離装置312の下部に設けた図示しない取り出し口から回収する。ダストDを払い落とす際は、バグフィルタに振動を与える振動式や、逆気流を与える逆洗式、圧縮空気を瞬間的に噴射するパルスジェット式等の方法を用いることができる。また、これらの方法を組み合わせても良い。回収されたダストDは、ホウ素を含む。 In the dry recovery step S341, for example, dust D accumulated on a bag filter is brushed off and collected from an outlet (not shown) provided at the bottom of the dry separation device 312. When brushing off the dust D, a vibration method that applies vibrations to the bag filter, a backwash method that applies a reverse airflow, a pulse jet method that instantly sprays compressed air, or other methods can be used. These methods may also be combined. The collected dust D contains boron.
湿式回収工程S342では、湿式冷却装置321でホウ素を捕集した冷却液Lc及び湿式分離装置322でホウ素を捕集した液体からホウ素を回収する。以下では、湿式冷却装置321でホウ素を捕集した冷却液Lc及び湿式分離装置322でホウ素を捕集した液体を総称して捕集液Ltという。捕集液Ltを、固液分離装置3421へ導入し、抽出固体Seと廃液Lwに分離する。固液分離装置3421としては、フィルタプレス、遠心分離、減圧濾過など、が挙げられるが、その種類は特に限定されない。抽出固体Seは乾燥機3422へ導入され、所定の水分含有量となるまで乾燥される。乾燥機3422としては、減圧乾燥機、ロータリードライヤ、バンド乾燥機、スプレードライヤなど、が挙げられるが、その種類は特に限定されない。乾燥された抽出固体Seは、ホウ素を含む。廃液Lwは、図示しない廃液処理設備により処理され、排出される。 In the wet recovery process S342, boron is recovered from the cooling liquid Lc from which boron has been collected in the wet cooling device 321 and the liquid from which boron has been collected in the wet separation device 322. Hereinafter, the cooling liquid Lc from which boron has been collected in the wet cooling device 321 and the liquid from which boron has been collected in the wet separation device 322 are collectively referred to as the collected liquid Lt. The collected liquid Lt is introduced into the solid-liquid separation device 3421 and separated into the extracted solid Se and the waste liquid Lw. Examples of the solid-liquid separation device 3421 include a filter press, a centrifugal separator, a vacuum filtration, and the like, but the type is not particularly limited. The extracted solid Se is introduced into the dryer 3422 and dried until it has a predetermined moisture content. Examples of the dryer 3422 include a vacuum dryer, a rotary dryer, a band dryer, a spray dryer, and the like, but the type is not particularly limited. The dried extracted solid Se contains boron. The waste liquid Lw is treated and discharged using waste liquid treatment equipment (not shown).
乾式回収工程S341及び湿式回収工程S342では、ダストD又は抽出固体Seから不純物を除去してホウ素を抽出することが好ましい。例えばダストD又は抽出固体Seを高濃度ホウ素溶液と混合すれば、抽出固体Seに含まれる不純物が高濃度ホウ素溶液に溶解し、抽出固体Seに含まれるホウ素が未溶解物として残存する(抽出される)。このように回収されたホウ素は、ガラス原料Grのホウ素源として利用される。 In the dry recovery step S341 and the wet recovery step S342, it is preferable to remove impurities from the dust D or the extracted solid Se to extract boron. For example, if the dust D or the extracted solid Se is mixed with a high-concentration boron solution, the impurities contained in the extracted solid Se will dissolve in the high-concentration boron solution, and the boron contained in the extracted solid Se will remain as undissolved (extracted). The boron thus recovered is used as a boron source for the glass raw material Gr.
以上のようなガラス物品の製造方法は、乾式捕集工程S31を含み、ガラス物品の製造装置は、乾式捕集設備31を含む。このため、本実施形態のガラス物品の製造方法及び製造装置は、通電加熱工程S11が行われているガラス溶融炉1から排出される排ガスGsから粉塵を低コストで効率良く回収することができる。また、通電加熱工程S11が行われている際は乾式捕集工程S31を、燃焼加熱工程S12が行われている際は湿式捕集工程S32を行うことで、燃焼加熱工程S12が行われているガラス溶融炉1から排出される、含まれる水蒸気の割合が高い排ガスGsを支障なく処理可能である。また、例えば操業中は通電加熱工程S11及び乾式捕集工程S31を実行し、溶融炉1の立ち上げ時等に一時的に燃焼加熱工程S12及び湿式捕集工程S32を実行すれば、特許文献1のようにスプレー塔等を常時使用する必要がない。このため、スプレー塔等を他の溶融炉等と共用したり、小型化したりすることが可能となり、ランニングコスト及びイニシャルコストを削減できる。 The above-mentioned manufacturing method of a glass article includes a dry collection step S31, and the manufacturing apparatus of a glass article includes a dry collection facility 31. Therefore, the manufacturing method and manufacturing apparatus of a glass article of this embodiment can efficiently recover dust from the exhaust gas Gs discharged from the glass melting furnace 1 in which the electric heating step S11 is performed at low cost. In addition, by performing the dry collection step S31 when the electric heating step S11 is performed and the wet collection step S32 when the combustion heating step S12 is performed, it is possible to treat the exhaust gas Gs containing a high proportion of water vapor discharged from the glass melting furnace 1 in which the combustion heating step S12 is performed without any problems. In addition, for example, if the electric heating step S11 and the dry collection step S31 are performed during operation and the combustion heating step S12 and the wet collection step S32 are temporarily performed when the melting furnace 1 is started up, there is no need to use a spray tower or the like all the time as in Patent Document 1. Therefore, it is possible to share the spray tower with other melting furnaces or the like or to reduce the size, thereby reducing running costs and initial costs.
なお、本発明は、上記実施形態の構成に限定されるものではなく、上記した作用効果に限定されるものでもない。本発明は、本発明の要旨を逸脱しない範囲で種々の変更が可能である。 The present invention is not limited to the configuration of the above embodiment, nor is it limited to the above-mentioned effects. Various modifications of the present invention are possible without departing from the gist of the present invention.
上記実施形態では、スクリュフィーダを用いて溶融炉へガラス原料を供給していたが、これに限定されない。振動フィーダやプッシャを用いても良い。また、1台ではなく、複数台用いても良い。 In the above embodiment, the glass raw material is supplied to the melting furnace using a screw feeder, but this is not limited to this. A vibration feeder or a pusher may also be used. Also, multiple units may be used instead of one unit.
上記実施形態では、乾式分離装置としてバグフィルタを使用していたが、これに限定されない。バグフィルタの替わりに乾式電気集塵機やセラミックフィルタを使用しても良い。 In the above embodiment, a bag filter was used as the dry separation device, but this is not limited to this. A dry electrostatic precipitator or a ceramic filter may be used instead of the bag filter.
上記実施形態では、湿式冷却工程の後に湿式分離工程を行ったが、これに限定されない。湿式冷却工程において、冷却液の散布量が少ない場合、排ガス中に散布された冷却液は全て気化する。一方で冷却液の散布量が十分に多い場合、冷却液の一部は気化することなく液滴として残存し、ホウ素を含んだ粉塵を液滴中に捕集することができる。この場合、湿式分離工程を行うことなく、排ガス中から粉塵を回収することができる。 In the above embodiment, the wet separation process is performed after the wet cooling process, but this is not limited to the above. If the amount of cooling liquid sprayed in the wet cooling process is small, all of the cooling liquid sprayed into the exhaust gas will evaporate. On the other hand, if the amount of cooling liquid sprayed is sufficiently large, some of the cooling liquid will not evaporate but will remain as droplets, and dust containing boron can be collected in the droplets. In this case, dust can be collected from the exhaust gas without performing the wet separation process.
上記実施形態では、排ガス処理工程において脱硝工程を含んでいたが、これに限定されない。排ガス中に含まれる窒素酸化物濃度が低い場合には、脱硝工程を行わなくても良い。 In the above embodiment, the exhaust gas treatment process includes a denitrification process, but is not limited to this. If the concentration of nitrogen oxides contained in the exhaust gas is low, the denitrification process does not need to be performed.
上記実施形態では、脱硝工程において、還元剤としてアンモニアを使用していたが、これに限定されない。アンモニアの替わりにアンモニア水や尿素を使用しても良い。 In the above embodiment, ammonia was used as the reducing agent in the denitrification process, but this is not limited to this. Ammonia water or urea may be used instead of ammonia.
本発明は、ガラス溶融炉から排出される排ガスから粉塵を低コストで効率良く回収することに好適に使用することができる。 The present invention can be suitably used to recover dust from exhaust gas discharged from a glass melting furnace efficiently and at low cost.
1 溶融炉
2 成形装置
3 排ガス処理設備
31 乾式捕集設備
311 乾式冷却装置
312 乾式分離装置
322 湿式分離装置
Gp ガラス物品
Gm 溶融ガラス
Gr ガラス原料
Gs 排ガス
Gc 冷却ガス
Lc 冷却液
S1 溶融工程
S11 通電加熱工程
S12 燃焼加熱工程
S2 成形工程
S3 排ガス処理工程
S31 乾式捕集工程
S311乾式冷却工程
S312乾式分離工程
S32 湿式捕集工程
S321湿式冷却工程
S322湿式分離工程
S33 脱硝工程
S34 回収工程
1 Melting furnace 2 Molding device 3 Exhaust gas treatment equipment 31 Dry collection equipment 311 Dry cooling device 312 Dry separation device 322 Wet separation device Gp Glass article Gm Molten glass Gr Glass raw material Gs Exhaust gas Gc Cooling gas Lc Cooling liquid S1 Melting process S11 Electric heating process S12 Combustion heating process S2 Molding process S3 Exhaust gas treatment process S31 Dry collection process S311 Dry cooling process S312 Dry separation process S32 Wet collection process S321 Wet cooling process S322 Wet separation process S33 Denitrification process S34 Recovery process
Claims (11)
前記溶融ガラスをガラス物品に成形する成形工程と、
前記溶融炉内から排出される排ガスから粉塵を除去する排ガス処理工程と、を含むガラス物品の製造方法であって、
前記溶融工程は、主に電極を用いる通電加熱により前記ガラス原料を溶融する通電加熱工程を含み、
前記排ガス処理工程は、前記通電加熱工程を実行中の前記溶融炉内から排出される前記排ガスを処理する乾式捕集工程を含み、
前記乾式捕集工程は、前記排ガスに冷却ガスを混合する乾式冷却工程と、前記乾式冷却工程を経た前記排ガスから乾式分離装置を用いて前記粉塵を分離する乾式分離工程と、を含み、
前記溶融工程は、少なくとも、バーナを用いる燃焼加熱によって前記ガラス原料を溶融する燃焼加熱工程を含み、
前記排ガス処理工程は、前記燃焼加熱工程を実行中の前記溶融炉内から排出される排ガスを処理する湿式捕集工程を含み、
前記湿式捕集工程は、前記排ガスに冷却液を散布する湿式冷却工程を含むことを特徴とするガラス物品の製造方法。 A melting step of heating glass raw materials in a melting furnace to obtain molten glass;
forming the molten glass into a glass article;
and an exhaust gas treatment step for removing dust from the exhaust gas discharged from the melting furnace,
The melting step includes an electric heating step of melting the glass raw material by electric heating mainly using electrodes,
The exhaust gas treatment process includes a dry collection process for treating the exhaust gas discharged from the melting furnace during the electric heating process,
The dry collection step includes a dry cooling step of mixing a cooling gas with the exhaust gas, and a dry separation step of separating the dust from the exhaust gas that has been subjected to the dry cooling step by using a dry separation device,
The melting step includes at least a combustion heating step of melting the glass frit by combustion heating using a burner,
The exhaust gas treatment process includes a wet collection process for treating exhaust gas discharged from the melting furnace during the combustion heating process,
The method for manufacturing a glass article , wherein the wet collection step includes a wet cooling step of spraying a cooling liquid into the exhaust gas .
前記排ガス処理工程は、前記粉塵からホウ素を回収する回収工程を含むことを特徴とする請求項1~6のいずれかに記載のガラス物品の製造方法。 The glass frit contains boron,
7. The method for manufacturing a glass article according to claim 1, wherein the exhaust gas treatment step includes a recovery step of recovering boron from the dust.
前記溶融ガラスをガラス物品に成形する成形装置と、
前記溶融炉内から排出される排ガスから粉塵を除去する排ガス処理設備と、を備えるガラス物品の製造装置であって、
前記排ガス処理設備は、前記溶融炉で主に電極を用いる通電加熱により前記ガラス原料を溶融する通電加熱工程を実行中の前記溶融炉内から排出される排ガスを処理するための乾式捕集設備と、前記溶融炉で少なくともバーナを用いる燃焼加熱によって前記ガラス原料を溶融する燃焼加熱工程を実行中の前記溶融炉内から排出される排ガスを処理するための湿式捕集設備とを備え、
前記乾式捕集設備は、前記排ガスに冷却ガスを混合する乾式冷却装置と、バグフィルタを用いて前記排ガスから前記粉塵を分離する乾式分離装置と、を含み、
前記湿式捕集設備は、前記排ガスに冷却液を散布する湿式冷却装置を含むことを特徴とするガラス物品の製造装置。 a melting furnace for heating glass raw materials to obtain molten glass;
a forming device for forming the molten glass into a glass article;
and an exhaust gas treatment facility for removing dust from the exhaust gas discharged from the melting furnace,
The exhaust gas treatment equipment includes a dry collection equipment for treating exhaust gas discharged from the melting furnace during an electric heating process for melting the glass frit mainly by electric heating using electrodes in the melting furnace , and a wet collection equipment for treating exhaust gas discharged from the melting furnace during a combustion heating process for melting the glass frit by combustion heating using at least a burner in the melting furnace ,
The dry collection equipment includes a dry cooling device that mixes a cooling gas with the exhaust gas, and a dry separation device that separates the dust from the exhaust gas using a bag filter,
The apparatus for manufacturing a glass article , wherein the wet collection equipment includes a wet cooling device that sprays a cooling liquid into the exhaust gas .
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| JP2010077470A (en) * | 2008-09-25 | 2010-04-08 | Dowa Metals & Mining Co Ltd | Method for treating material to be treated, containing platinum group element, rhenium and/or arsenic |
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