WO2006115105A1 - Treatment apparatus for waste panel and method for treating waste panel - Google Patents

Treatment apparatus for waste panel and method for treating waste panel Download PDF

Info

Publication number
WO2006115105A1
WO2006115105A1 PCT/JP2006/308075 JP2006308075W WO2006115105A1 WO 2006115105 A1 WO2006115105 A1 WO 2006115105A1 JP 2006308075 W JP2006308075 W JP 2006308075W WO 2006115105 A1 WO2006115105 A1 WO 2006115105A1
Authority
WO
WIPO (PCT)
Prior art keywords
crushing
waste
liquid crystal
waste panel
panel
Prior art date
Application number
PCT/JP2006/308075
Other languages
French (fr)
Japanese (ja)
Inventor
Toshiaki Muratani
Takamichi Honma
Original Assignee
Sharp Kabushiki Kaisha
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 Sharp Kabushiki Kaisha filed Critical Sharp Kabushiki Kaisha
Publication of WO2006115105A1 publication Critical patent/WO2006115105A1/en

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B02CRUSHING, PULVERISING, OR DISINTEGRATING; PREPARATORY TREATMENT OF GRAIN FOR MILLING
    • B02CCRUSHING, PULVERISING, OR DISINTEGRATING IN GENERAL; MILLING GRAIN
    • B02C18/00Disintegrating by knives or other cutting or tearing members which chop material into fragments
    • B02C18/06Disintegrating by knives or other cutting or tearing members which chop material into fragments with rotating knives
    • B02C18/14Disintegrating by knives or other cutting or tearing members which chop material into fragments with rotating knives within horizontal containers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION 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
    • B03BSEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
    • B03B9/00General arrangement of separating plant, e.g. flow sheets
    • B03B9/06General arrangement of separating plant, e.g. flow sheets specially adapted for refuse
    • B03B9/061General arrangement of separating plant, e.g. flow sheets specially adapted for refuse the refuse being industrial
    • B03B9/062General arrangement of separating plant, e.g. flow sheets specially adapted for refuse the refuse being industrial the refuse being glass
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B58/00Obtaining gallium or indium
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/005Separation by a physical processing technique only, e.g. by mechanical breaking
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/52Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/60Glass recycling

Definitions

  • the present invention relates to a waste panel processing apparatus and a waste panel processing method.
  • the present invention relates to a waste panel processing apparatus and a waste panel processing method capable of recovering materials used for liquid crystal panels such as liquid crystal and indium.
  • Patent Documents 1 and 2 disclose an economical method of treating a waste liquid crystal panel, which can be ideally recycled with little waste by collecting and reusing a glass substrate, liquid crystal, or the like. Is disclosed. Patent Document 3 discloses a method of recovering glass and indium by detoxifying and removing liquid crystals and organic substances (films) from a waste liquid crystal display device without using an organic solvent. Patent Document 4 discloses a liquid crystal panel that has been used and a method for recovering a liquid crystal composition safely and economically.
  • Patent Document 1 In the configurations of Patent Documents 1 and 2, first, a step of peeling the polarizing plate is performed. However, the polarizing plate is firmly bonded to the glass substrate, and it is very difficult to peel it off. This becomes more prominent as the display area of the liquid crystal panel increases.
  • Patent Document 1 a process of crushing the glass is performed after the process of peeling the polarizing plate. This is because it is difficult to crush the glass substrate on which the polarizing plate is provided. It is.
  • Patent Documents 1 and 2 have disadvantages in terms of feasibility and economical aspects that include processes that are difficult to realize and that have many processes for recovering liquid crystal materials and metal materials. Has a point.
  • Patent Document 3 the organic compound containing the liquid crystal compound is decomposed by bringing it into contact with a solid heat medium in an atmosphere below the melting point of the glass substrate and above the thermal decomposition temperature of the liquid crystal compound. The metal is separated. For this reason, facilities and energy for thermally decomposing organic compounds are required. This configuration also collects glass and indium. Recover the liquid crystal!
  • Patent Document 4 a circuit board or the like on which a polarizing plate or a driving IC is mounted is removed using a cutter or the like, and then the glass is cut and then heated to 80 ° C or higher.
  • the liquid crystal composition is separated and recovered by being immersed in water. For this reason, facilities and processes for cutting glass are required.
  • hot water at 80 ° C or higher is used, and energy is required to separate and recover the liquid crystal composition.
  • this configuration does not recover materials such as indium.
  • Patent Document 1 Japanese Patent Laid-Open No. 2001-305501 (published on October 31, 2001)
  • Patent Document 2 Japanese Patent Laid-Open No. 2001-337305 (published on December 7, 2001)
  • Patent Document 3 Japanese Patent Laid-Open No. 2001-137804 (published on May 22, 2001)
  • Patent Document 4 JP-A-2002-166259 (published on June 11, 2002)
  • the present invention has been made in view of the above-mentioned problems, and an object of the present invention is to provide a waste panel processing apparatus capable of crushing a glass substrate provided with a polarizing plate, a liquid crystal panel, and the like.
  • a waste panel processing apparatus capable of crushing a glass substrate provided with a polarizing plate, a liquid crystal panel, and the like.
  • the waste panel processing method is a medium comprising a pair of glass substrates and a medium that is sandwiched between the pair of glass substrates and optically modulates by applying a voltage.
  • An electrode disposed on the side facing the medium layer of at least one glass substrate, and a polarizing plate disposed on the side opposite to the surface facing the medium layer of at least one glass substrate.
  • a panel processing method comprising: a crushing process for crushing the waste panel; a medium recovery process for recovering the medium; an electrode material recovery process for recovering the material contained in the electrode; and the glass To perform the glass recovery process It is a feature.
  • the waste panel has a pair of glass substrates, a medium layer, an electrode, and a polarizing plate, and in the crushing step, the waste panel having these members is crushed. .
  • waste panels that have been discarded (with a polarizing plate) are crushed.
  • the medium adhering to the waste panel can be recovered.
  • the medium is sandwiched between a pair of glass substrates, and optically modulates according to a voltage applied between the glass substrates.
  • an electrode material recovery step is performed on the waste panel after the medium is recovered. Thereby, the electrode material adhering to the waste panel can be collected.
  • the electrode is disposed on the surface of at least one glass substrate facing the medium layer, and is for applying a voltage to the medium layer. It may be provided on one or both of the pair of glass substrates.
  • the electrode material is a material contained in this electrode, V, and the electrode is formed using this electrode material.
  • the glass to which the medium and the electrode material are not attached can be collected.
  • various materials used for the panel, which are the medium and the electrode material, are collected are collected.
  • each process also serves the purpose of facilitating the execution of subsequent processes, and it can be seen that this order is a natural flow. Therefore, each material contained in the waste panel can be recovered with less energy.
  • the present invention can be realized regardless of the panel size (display area). Large panels can easily be processed.
  • the waste panel can be easily treated, and the waste panel processing method can be realized with low environmental load when the energy is saved so that almost no waste is generated.
  • the waste panel processing method includes a pair of glass substrates and a medium sandwiched between the pair of glass substrates and optically modulated by applying a voltage.
  • An electrode disposed on the side facing the medium layer of at least one glass substrate, and a polarizing plate disposed on the side opposite to the surface facing the medium layer of at least one glass substrate.
  • the waste panel has a pair of glass substrates, a medium layer, an electrode, and a polarizing plate, and in the crushing step, the waste panel having these members is crushed. .
  • the crushing process waste panels that have been discarded are crushed.
  • the medium recovery process is performed to the waste panel crushed in the crushing process. From this, the medium adhering to the waste panel can be recovered.
  • the medium is sandwiched between a pair of glass substrates, and optically modulates according to the voltage applied between the glass substrates.
  • the treatment can be performed using the crushed pieces that do not require any processing on the waste panel, so that the treatment becomes easy. Also, because the waste panel does not need to be crushed and processed in the first place, the size of the panel ( This can be realized regardless of the display area, and even a panel having a large display area can be easily processed.
  • the waste panel treatment method is a medium comprising a pair of glass substrates and a medium that is sandwiched between the pair of glass substrates and optically modulates by applying a voltage.
  • An electrode disposed on the side facing the medium layer of at least one glass substrate, and a polarizing plate disposed on the side opposite to the surface facing the medium layer of at least one glass substrate.
  • a panel processing method characterized in that a crushing step of crushing the waste panel and an electrode material recovery step of recovering a material contained in the electrode are performed in this order.
  • the waste panel has a pair of glass substrates, a medium layer, an electrode, and a polarizing plate, and in the crushing step, the waste panel having these members is crushed. .
  • the electrode is disposed on the surface facing the medium layer of at least one glass substrate, and is for applying a voltage to the medium layer. It may be provided on one or both of the pair of glass substrates.
  • the electrode material is a material contained in this electrode, and the electrode is formed using this electrode material.
  • the processing can be performed using the crushed pieces that do not require any processing on the waste panel, so that the processing becomes easy. Also, since it is not necessary to crush the waste panel first and perform any processing, it can be realized regardless of the panel size (display area), and even a panel with a large display area is easy. Can be processed.
  • the waste panel processing apparatus is a waste panel processing apparatus including a rotary crushing means and a stationary crushing means, and the rotary crushing means includes: It has a plurality of flat crushing portions, and the plurality of crushing portions are arranged so that the planes of at least two rupture portions face different directions.
  • the rotary crushing means and the fixed crushing means are provided. By using these means, the waste panel can be crushed.
  • the rotary crushing means has a plurality of flat crushing parts, and these crushing parts are arranged so that the planes of at least two crushing parts face different directions. Waste panels can be crushed at different times.
  • the planes of the crushing parts are arranged in different directions means that the direction of the widest area in the planar crushing part and the direction perpendicular to the surface is different in each crushing part. It is in the state where it is arranged so that. That is, each crushing part is arranged so that the normal direction of each plane is different.
  • the waste panel can be crushed by a plurality of crushing portions arranged in various directions by one rotation of the rotary crushing means, and can be crushed at various timings. Therefore, the waste panel can be efficiently crushed.
  • FIG. 1 shows an embodiment of the present invention and is a diagram showing a flow of a method for treating a waste liquid crystal panel.
  • FIG. 2 showing an embodiment of the present invention, is a cross-sectional view showing a schematic configuration of a waste liquid crystal panel.
  • FIG. 3, showing an embodiment of the present invention is a cross-sectional view showing a schematic configuration of a crusher used in a crushing step.
  • FIG. 4 shows an embodiment of the present invention and is a cross-sectional view showing a schematic configuration of a crushing unit.
  • FIG. 5, showing an embodiment of the present invention is a diagram showing a liquid crystal recovery step.
  • FIG. 6, showing an embodiment of the present invention is a diagram illustrating an indium recovery step.
  • FIG. 7, showing an embodiment of the present invention is a diagram showing a schematic configuration of a crushing unit.
  • waste panel used in the waste panel processing method according to the present embodiment will be described.
  • a waste liquid crystal panel will be described as an example of a waste panel.
  • This waste liquid crystal panel is a liquid crystal panel to be discarded.
  • the above-mentioned waste liquid crystal panel refers to, for example, a liquid crystal panel discarded from a liquid crystal panel manufacturing factory, a liquid crystal panel discarded from a production factory such as an information display device and a video display device, and the market. Liquid crystal panels etc. discharged from the liquid crystal display device used in discarded information display devices and video display devices.
  • examples of the waste liquid crystal panel applicable to the present invention include a liquid crystal panel including an active element (not shown) such as a TFT (Thin Film Transistor), a TN (Twisted Nematic) liquid crystal panel, Examples include discarded liquid crystal panels such as STN (Super Twisted Nematic) liquid crystal panels.
  • an active element such as a TFT (Thin Film Transistor), a TN (Twisted Nematic) liquid crystal panel
  • examples include discarded liquid crystal panels such as STN (Super Twisted Nematic) liquid crystal panels.
  • FIG. 2 is a cross-sectional view showing a schematic configuration of the waste liquid crystal panel 30 (waste panel) according to the present embodiment.
  • the waste liquid crystal panel 30 is bonded to a pair of transparent glass substrates la and 1b via a seal member 2 arranged in a frame shape along the periphery of the glass substrates la and lb.
  • the liquid crystal layer (medium layer) 3 is filled with liquid crystal (medium) in the meantime. That is, the waste liquid crystal panel 30 has a configuration in which the liquid crystal layer 3 is sandwiched between a pair of glass substrates la and lb.
  • Polarizing plates 4a and 4b are bonded to the surfaces of the glass substrates la and lb opposite to the liquid crystal layer 3 by adhesives, respectively.
  • a transparent electrode (ITO (Indium Thin Oxide) film) with a color filter 5 mainly composed of an organic substance and a transparent film (ITO (Indium Thin Oxide) film) containing indium (In) (Electrode) 7 and an alignment film 8 having organic physical strength are laminated in this order.
  • an antireflection film 6 made of metallic chromium is formed in the gap between the color filters 5.
  • FIG. 1 is a diagram showing a flow of a processing method of the waste liquid crystal panel 30 according to the present invention. As shown in FIG.
  • the processing method of the waste liquid crystal panel 30 of the present invention includes a crushing process Sl, a liquid crystal recovery process (medium recovery process) S2, an indium recovery process (electrode material recovery process) S3, and a glass recovery process. S4 is performed in this order.
  • the waste liquid crystal panel 30 can be processed with energy saving, and the liquid crystal, indium, glass and other materials used in the waste liquid crystal panel 30 can be recovered. This will be specifically described below.
  • the crushing step S1 is performed.
  • the crushing step S1 is a step of crushing the waste liquid crystal panel 30 using a crusher. That is, it is a process of breaking the polarizing plates 4a and 4b and crushing the glass substrates la and lb.
  • FIG. 3 is a cross-sectional view showing a schematic configuration of the crusher 12 used in the crushing step S1. As shown in FIG. 3, the crusher 12 includes an input device 13, an input hopper 14, a crushing unit 15, a flexible container 16, a weigh scale 17, a dust collector 18, and a control panel 19.
  • the input device 13 is used to input the waste liquid crystal panel 30 to the input hopper 14. For example, when the charging hopper 14 is provided at a high place, the charging machine 13 transports the waste liquid crystal panel 30 from a low place to a high place and inputs it to the charging hopper 14. The waste liquid crystal panel 30 thrown into the throwing hopper 14 is thrown into the crushing unit 15.
  • the crushing unit 15 crushes the waste liquid crystal panel 30 that has been input. Details of the configuration of the crushing unit 15 and the method of crushing the waste liquid crystal panel 30 by the crushing unit 15 will be described later.
  • the waste liquid crystal panel 30 crushed to a predetermined size by the crushing unit 15 is collected by the flexible container 16 and calibrated by the weighing scale 17 and then discharged.
  • the dust collector 18 collects dust generated by crushing the waste liquid crystal panel 30 by the breaker unit 15. The control of these members is performed using the control panel 19.
  • FIG. 4 is a cross-sectional view showing a schematic configuration of the crushing unit 15.
  • the crushing unit 15 includes a crushing unit 20 that crushes the waste liquid crystal panel 30 that has been input, and an outlet 21 that discharges the crushed waste liquid crystal panel 30.
  • the crushing part 20 includes a side wall part 22, a screen 23, a rotary shaft 24, a rotor 25, a rotary blade (rotary type Crushing means) 26 and a fixed blade (fixed crushing means) 27.
  • the side wall portion 22 is a wall for forming a space for the crushing portion 20.
  • the inner surface of the side wall portion 22 may further include an inner surface plate 28 that has a stronger material force than the side wall portion 22.
  • the screen 23 is a so-called sieve having many holes of a predetermined size. Only the crushed pieces (cullet) of the waste liquid crystal panel 30 crushed to a size smaller than the size of the hole pass through the screen 23.
  • the rotor 25 is a member having a substantially triangular prism shape, and a rotating shaft 24 is integrally provided at a central portion thereof.
  • a plurality of rotary blades 26 are attached to each surface of the approximately triangular prism of the rotor 25 by fasteners such as bolts.
  • the fixed blade 27 is attached to the side wall portion 22 with a fastener such as a bolt.
  • At least tip portions of the rotary blade 26 and the fixed blade 27 are formed using a cemented carbide material or a ceramic material.
  • a cemented carbide material is a material having a Vickers hardness of at least 11.8 GPa, such as WC—Co alloy, WC—TiC Co alloy, WC—TiC—TaC (NbC) —Co alloy, etc. Materials can be mentioned.
  • the rotary blade 26 may be formed using a cemented carbide material, and the fixed blade 27 (tip end) may be formed using a ceramic material.
  • the blade 26 (tip portion) may be formed using a ceramic material, and the fixed blade 27 (tip portion) may be formed using a cemented carbide material.
  • FIG. 7 is a diagram showing a schematic configuration when the crushing unit 15 is viewed from above.
  • the rotary blade 26 provided on each surface of the rotor 25 has a plurality of crushing portions 29a, 29b and 29c. Is provided.
  • the plurality of crushing portions 29 a to 29 c have a planar blade force, and a plurality of crushing portions 29 a to 29 c are arranged in the rotation axis direction of the rotary blade 26 (the longitudinal direction of the rotor 25).
  • the crushing parts 29a to 29c are arranged so that the planes face in different directions.
  • each crushing portion 29a to 29c provided on the rotor 25 and arranged so that each plane faces in a different direction is set as one unit, a plurality of units are arranged. Yes. In each of these units, the crushing portions 29 a to 29 c are arranged along the rotation axis direction of the rotary blade 26.
  • each of the crushing portions 29a to 29c is arranged so as to be slightly shifted with respect to the rotation direction A shown in FIG.
  • the rotary blade 26 has the structure by which this crushing part 29a-29c was arrange
  • the arrangement direction (plane direction) of each of the crushing parts 29a to 29c can be set as appropriate according to the specifications as long as the inclination is a positional relationship that can crush the waste panel 30. it can.
  • the plurality of crushing portions 29a to 29c are arranged with the arrangement directions of the respective planes being different, and the waste panels 30 are arranged by continuously arranging them. It can be efficiently crushed. Further, with such a configuration, even when the waste panel 30 in a state where the polarizing plates 4a and 4b are provided on the glass substrates 1a and lb, the polarizing plates 4a and 4b are broken, It can be crushed by crushing the glass substrates la and lb.
  • the waste liquid crystal panel 30 can be crushed to a desired size, and crushed pieces of uniform size can be obtained.
  • the desired size is determined by the rotary blade 26 and the fixed blade 27. Can be set as appropriate by adjusting the interval.
  • lmn! can be ⁇ 5mm.
  • the crusher 12 As described above, by crushing the waste liquid crystal panel 30 using the crusher 12, it becomes possible to increase the reaction area for the chemical used in the subsequent process. Further, by using the crusher 12, the waste liquid crystal panel 30 in which the polarizing plates 4a and 4b are provided can be broken.
  • the liquid crystal recovery step S2 is a step of recovering the liquid crystal adhering to the crushed pieces of the waste liquid crystal panel 30 crushed in the crushing step S1.
  • the liquid crystal recovery step S2 is a step in which the liquid crystal is dissolved in the organic solvent and recovered by washing the crushed pieces with an organic solvent (solvent) that dissolves the liquid crystal. As a result, the liquid crystal can be easily and reliably collected.
  • FIG. 5 is a diagram showing a liquid crystal recovery step S2 according to the present embodiment.
  • the crushed pieces of the waste liquid crystal panel 30 crushed in the crushing step S1 are placed in a plurality of holes (a cullet container).
  • the cullet container should be sized so that the fragments will not pass through.
  • the cullet container containing the crushed pieces is immersed in a container (solvent container) containing an organic solvent that dissolves the liquid crystal to wash away the liquid crystal.
  • solvent container containing an organic solvent that dissolves the liquid crystal to wash away the liquid crystal.
  • the cullet container is also taken out of the solvent container force, so that the organic solvent in which the liquid crystal is dissolved remains in the solvent container.
  • the organic solvent containing the liquid crystal is distilled (evaporated) under reduced pressure to remove the organic solvent and obtain a liquid crystal as a residue.
  • Examples of the organic solvent for dissolving the liquid crystal include acetone.
  • usable organic solvents are not particularly limited as long as they can dissolve liquid crystals.
  • Liquid crystals have a sufficiently high boiling point compared to organic solvents such as acetone. Therefore, the organic solvent can be distilled at a temperature sufficiently lower than the boiling point of the liquid crystal. That is, by using the liquid crystal recovery step S2 according to this embodiment, the liquid crystal and the organic solvent can be easily separated.
  • liquid crystal recovery step S2 when the liquid crystal is dissolved in the organic solvent, part or all of other organic substances (for example, an alignment film, a polarizing plate, a color filter, etc.) are dissolved in the organic solvent.
  • other organic substances for example, an alignment film, a polarizing plate, a color filter, etc.
  • the crushed pieces are placed in a hollow hole, a container (cullet container), and immersed in a container (solvent container) containing an organic solvent.
  • a container cullet container
  • a container solvent container
  • the present invention is not limited to this. It is not a thing.
  • the crushed pieces may be directly put into a container containing an organic solvent and immersed in the organic solvent, and then the crushed pieces may be removed by filtration.
  • the liquid crystal attached to the crushed pieces can be removed and collected using ultrasonic waves.
  • the indium recovery step S3 is a step of recovering indium adhering to the crushed pieces from which organic substances have been removed in the liquid crystal recovery step S2. That is, this indium recovery step S3 is a step of recovering indium by dissolving it in the acid solution by washing the fragments using an acid solution in which indium is dissolved. As a result, high-purity indium can be easily and reliably recovered.
  • FIG. 6 is a diagram showing an indium recovery step S3 according to the present embodiment.
  • the crushed pieces from which organic substances have been removed in the liquid crystal recovery step S2 are placed in a container containing an acid solution and stirred.
  • the metal containing indium adhering to the fragments is dissolved in the acid solution.
  • the alignment films 4a and 4b provided on the transparent electrodes 7 and 10 containing the ink are removed ( Or partly peeled). For this reason, the acid solution is likely to come into contact with the transparent electrodes 7 and 10, and indium can be efficiently dissolved.
  • the acid solution used in this step is not particularly limited as long as it is an acid solution that dissolves indium.
  • an acid solution for example, a solution containing hydrochloric acid as a main component is preferably used, and a mixed solution of hydrochloric acid and nitric acid is particularly preferable.
  • a liquid for mixing hydrochloric acid and nitric acid is used, indium can be dissolved at room temperature.
  • Indium adhering to the debris dissolves in the acid solution as chloride (indium chloride).
  • the acid solution may be aluminum, titanium, molybdenum, for example. Then, the metal that adheres to the crushed pieces dissolves.
  • an acid solution force fragment in which a metal such as indium is dissolved is removed (solid-liquid separation). This can be done, for example, by filtration. As a result, the metal-containing acid solution remains in the container. Thereafter, the metal-containing acid solution from which the crushed pieces have been removed is passed through an indium ion-absorbing resin (resin).
  • This ion adsorption resin for indium is a resin that selectively adsorbs only indium. That is, indium in the acid solution is adsorbed by the ion adsorption resin for indium, and other metals pass through as they are. Therefore, indium and other metals can be separated by passing the metal-containing acid solution through the ion adsorption resin for indium (indium separation).
  • the metal-containing acid solution is passed through the ion adsorption resin for indium, and then water is passed through. That is, water is allowed to flow through an indium ion adsorption resin in which only indium is adsorbed. As a result, the indium adsorbed on the resin flows out as hydroxide (indium hydroxide).
  • indium hydroxide indium hydroxide
  • An indium sludge solid indium hydroxide
  • an alkali such as sodium hydroxide
  • the glass recovery step S4 is a step of recovering the crushed pieces after the metal is removed in the indium recovery step S3.
  • the glass recovered in this step is a crushed piece after the organic matter is removed in the liquid crystal recovery step S2 and the metal is removed in the indium recovery step S3, and it adheres to the waste liquid crystal panel 30. Glass with various materials removed.
  • the crushed pieces obtained after the solid-liquid separation in the indium recovery step S3 are recovered, and the crushed pieces are washed and dried.
  • the glass recovery step S4 the crushed pieces obtained after the solid-liquid separation in the indium recovery step S3 are recovered, and the crushed pieces are washed and dried.
  • various materials are not attached. That is, by simply performing the liquid crystal recovery step S2 and the indium recovery step S3 in this order, various materials can be adhered as a result! /, And a dark glass can be obtained. Further, the glass is washed and dried. Just to get a clean glass cullet. wear.
  • liquid crystal recovery step S2 in addition to recovering the liquid crystal, organic matter other than the liquid crystal may be recovered.
  • each organic substance can be efficiently recovered by performing fractional distillation using the difference in boiling point of each organic substance to be recovered.
  • indium recovery step S3 in addition to recovering indium, metals other than indium may be recovered. In this case, according to the type of metal to be recovered other than indium, it can be recovered by using an adsorption resin dedicated to that metal.
  • the present invention includes a pair of glass substrates, a liquid crystal layer sandwiched between the glass substrates, a transparent electrode provided on the facing surface side of the liquid crystal layer of each glass substrate, and the facing surface.
  • the crushing step, the liquid crystal recovery step, the indium recovery step, and the glass recovery step are performed in this order.
  • only the crushing step and the liquid crystal recovery step are performed. It can also be performed in this order, and only the crushing process and the indium recovery process can be performed in this order.
  • only the crushing step, the liquid crystal recovery step, and the glass recovery step can be performed in this order, and only the crushing step, the indium recovery step, and the glass recovery step can be performed in this order.
  • the glass recovery process may be started from the time when the individual liquid is separated in the indium recovery process.
  • the waste liquid crystal panel is not limited to the force described above as the waste panel.
  • the present invention can also be applied to discarded flat display panels such as plasma display panels, inorganic EL (Electro Luminescence) panels, and organic EL panels.
  • the present invention is not limited to the above-described embodiments, and various modifications can be made within the scope shown in the claims. In other words, embodiments obtained by combining technical means appropriately changed within the scope of the claims are also included in the technical scope of the present invention.
  • the waste panel processing method according to the present invention recovers the material contained in the electrode, the crushing step of crushing the waste panel, the medium recovery step of recovering the medium. Since the electrode material recovery process and the glass recovery process for recovering the glass are performed in this order, the waste panel can be easily processed and energy saving is achieved with almost no waste. There is an effect that the environmental load is small! / And the processing method of the waste panel can be realized.
  • the rotary crushing means has a plurality of flat crushing sections, and the plurality of crushing sections include at least two crushing sections. Since the plane of the crushing part is arranged in different directions, the waste panel can be efficiently crushed.
  • the crushing step it is preferable to crush the waste panel using a crusher having a rotary crushing means and a fixed crushing means arranged at regular intervals. . According to the above configuration, by using a crusher having a rotary crushing means and a fixed crushing means, it is possible to crush the waste panel with the polarizing plate attached.
  • the rotary crushing means rotates around a certain rotation axis, and a waste panel is inserted into a portion where the rotary crushing means and the stationary crushing means cross each other. Is to be crushed. As a result, it is not necessary to perform any processing on the waste panel to be processed, so that the waste panel can be easily processed.
  • the cutting edge means are arranged at a constant interval, the waste panel can be crushed to a desired size (a size that facilitates subsequent processing) by setting this interval as appropriate. Can do.
  • the crushing step it is preferable to break the polarizing plate and crush the glass substrate. According to said structure, even if it is a waste panel with the polarizing plate attached to the glass substrate, it can be reliably crushed.
  • the medium recovery step it is preferable to recover the medium using a solvent that dissolves the medium. According to the above configuration, the medium can be easily collected and can contribute to energy saving.
  • the electrode material recovery step it is preferable to recover the material contained in the electrode. According to the above configuration, the electrode material can be easily collected and can contribute to energy saving.
  • the electrode material recovery step it is preferable to recover the material contained in the electrode by dissolving it in an acid solution. According to the above configuration, the electrode material can be recovered at room temperature, so that it can be easily recovered and can contribute to energy saving.
  • the electrode material recovery step it is preferable to recover the material by using a resin that is contained in the electrode and adsorbs only the material. According to the above configuration, it is possible to reliably recover only the electrode material even when a substance different from the electrode material is present, and it is possible to easily recover the electrode material and to save energy. Can contribute.
  • the medium is preferably a liquid crystal.
  • liquid crystal that is an expensive material can be recovered, which is environmentally advantageous and economically advantageous.
  • the material contained in the electrode is preferably indium. According to the above configuration, indium, which is a rare metal, can be recovered, which is environmentally advantageous and economically advantageous.
  • the rotary crushing means includes a plurality of crushing units arranged so that the planes are in different directions as one unit. It is preferred to be placed repeatedly.
  • the plurality of crushing portions arranged so that the planes face in different directions are further provided in a plurality of units.
  • the above configuration is a configuration in which several crushing portions are arranged repeatedly so that the planes face in different directions.
  • the crushing part of the same inclination is the structure arrange
  • the plurality of crushing sections are preferably provided along the rotation axis direction of the rotary crushing means. According to the above configuration, since the plurality of crushing portions are provided along the rotation axis direction of the rotary crushing means, the interval between the rotary crushing means and the fixed crushing means is kept at an appropriate interval. And waste panels can be crushed more efficiently.
  • the waste panel has a pair of glass substrates and a polarizing plate disposed on the side opposite to the facing surface of at least one glass substrate. It is preferable that the polarizing plate is broken by the rotary crushing means and the fixed crushing means to crush the glass substrate. According to the above configuration, even a waste panel with a polarizing plate attached to a glass substrate can be reliably crushed.
  • the waste panel processing apparatus and waste panel processing method of the present invention can process waste panels with little energy consumption, for example, for televisions and the like. It can be widely applied as a processing method when disposing of image display devices such as personal computer monitors. Therefore, the present invention can be suitably used in an industrial field for manufacturing an image display device, an industrial field for processing waste, and the like.

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Metallurgy (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Organic Chemistry (AREA)
  • Geology (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Food Science & Technology (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

This invention provides a method for treating a waste panel that is low in environmental loading, that is, produce substantially no waste and can save energy. In the method for treating a waste panel, a waste panel comprising a glass substrate, a liquid crystal layer, an electrode, and a polarizing plate is treated. This method comprises carrying out the following steps in that order, that is, a crushing step (S1) of crushing a waste panel, a liquid crystal recovery step (S2) for recovering a liquid crystal, an indium recovery step (S3) for recovering indium as a material for an electrode, and a glass recovery step (S4) for recovering glass.

Description

明 細 書  Specification
廃パネルの処理装置および廃パネルの処理方法  Waste panel processing apparatus and waste panel processing method
技術分野  Technical field
[0001] 本発明は、廃パネルの処理装置および廃パネルの処理方法に関するものである。  The present invention relates to a waste panel processing apparatus and a waste panel processing method.
特に、液晶やインジウム等の液晶パネルに使用される材料を回収することが可能な 廃パネルの処理装置および廃パネルの処理方法に関するものである。  In particular, the present invention relates to a waste panel processing apparatus and a waste panel processing method capable of recovering materials used for liquid crystal panels such as liquid crystal and indium.
背景技術  Background art
[0002] 近年、一般廃棄物や産業廃棄物の量が増加しており、これら廃棄物の埋立地の残 余年数が心配される状況となっている。また、環境意識の高まりから、より環境に配慮 した産業活動が求められている。このような状況から、工場力も排出される産業廃棄 物、および、不要になった家電製品や情報機器等に関して、排出量の削減ゃリサイ クルの促進を要望する声が行政側力もも上がっている。このような要望は、液晶表示 装置や液晶パネルについても同様である。  [0002] In recent years, the amount of general waste and industrial waste has increased, and there is a concern about the remaining years of landfill of these wastes. In addition, with increasing environmental awareness, more environmentally conscious industrial activities are required. Under such circumstances, there is a growing demand from the government for the reduction of emissions of industrial waste that also emits factory power, and household appliances and information devices that are no longer needed, as well as requests for promoting recycling. . This is the same for liquid crystal display devices and liquid crystal panels.
[0003] 液晶パネルの製造工場力 排出される不良の廃液晶パネルは、大半が処分場に 埋め立てられている。また、家電製品や情報機器等の廃棄物に含まれる液晶表示装 置や液晶パネルは、廃棄物の量としては少ないこともあって、廃棄物の処理施設に て製品ごと粉砕された後、プラスチックを多量に含むシュレッダーダストと共に、埋め 立て処理或!、は焼却処理されて!、る。  [0003] The power of the manufacturing plant for liquid crystal panels Most of the defective liquid crystal panels that are discharged are buried in disposal sites. In addition, liquid crystal display devices and liquid crystal panels contained in waste such as home appliances and information equipment are small in amount of waste. Along with shredder dust containing a large amount of waste, it is either landfilled or incinerated!
[0004] ところが、近年、液晶ディスプレイは、省電力駆動および省資源が可能であることか ら、高度情報化社会の進展に伴い、国内海外ともにその需要が加速度的に拡大して いる。このように、液晶ディスプレイの生産量が急速に増大することにカ卩えて、表示面 積の大きな液晶パネルを用いた液晶ディスプレイが増加することが予測される。  [0004] However, in recent years, the demand for liquid crystal displays has been increasing rapidly both in Japan and overseas with the progress of an advanced information-oriented society because it can save power and save resources. In this way, it is predicted that the number of liquid crystal displays using a liquid crystal panel having a large display area will increase in view of the rapid increase in production volume of liquid crystal displays.
[0005] 従って、これら液晶ディスプレイが産業廃棄物となった場合には、廃液晶パネルの 量も急速に増大し、その処理量は極めて大きくなることが予想される。しかしながら、 これまでと同様に埋め立て処理や焼却処理による処理では対応できなくなることが確 実視されている。  [0005] Therefore, when these liquid crystal displays become industrial waste, the amount of waste liquid crystal panels is expected to increase rapidly, and the amount of treatment is expected to become extremely large. However, it has been confirmed that it cannot be handled by landfill or incineration as in the past.
[0006] また、液晶ディスプレイの生産量の増加に伴 、、その材料として使用されるインジゥ ムゃ液晶等の材料を大量に消費することとなる。この液晶は非常に高価な材料であり 、インジウムは稀少金属である。従って、これら材料の枯渴化が懸念されているため、 何らかの方法で液晶やインジウムを回収して再使用することが望まれて 、る。また、 液晶パネルの重量の大半を占めるガラスについても、資源を大切にする点力 再生 使用することが望ましい。 [0006] Further, as the production volume of liquid crystal displays increases, the indium used as a material for the liquid crystal displays is increased. A large amount of materials such as liquid crystals will be consumed. This liquid crystal is a very expensive material, and indium is a rare metal. Therefore, since there is a concern about the depletion of these materials, it is desired to recover and reuse the liquid crystal and indium by some method. It is also desirable to recycle and reuse glass, which accounts for the majority of the weight of LCD panels, as it saves resources.
[0007] 従って、大量の廃液晶パネルを効率的に処理すると共に、液晶パネルに使用され ている材料を回収することが可能な技術の確立が求められている。このような、廃液 晶パネルを処理する方法や液晶パネルに含まれる液晶等を回収する方法について は複数開示されている (例えば、特許文献 1〜4参照)。  Accordingly, there is a demand for establishment of a technique capable of efficiently processing a large amount of waste liquid crystal panels and collecting materials used in the liquid crystal panels. There are a plurality of disclosed methods for treating the waste liquid crystal panel and recovering the liquid crystal contained in the liquid crystal panel (see, for example, Patent Documents 1 to 4).
[0008] 特許文献 1および 2には、ガラス基板や液晶等を回収して再使用することによって、 殆ど廃棄物を出さない理想的なリサイクルが可能であり、経済的な廃液晶パネルの 処理方法が開示されている。特許文献 3には、廃液晶表示装置から、有機溶媒を用 いることなく液晶、有機物(フィルム類)を無害化して除去し、ガラス及びインジウムを 回収する方法が開示されている。また、特許文献 4には、使用済みとなった液晶パネ ルカ 安全かつ経済的に液晶組成物を回収する方法が開示されている。  [0008] Patent Documents 1 and 2 disclose an economical method of treating a waste liquid crystal panel, which can be ideally recycled with little waste by collecting and reusing a glass substrate, liquid crystal, or the like. Is disclosed. Patent Document 3 discloses a method of recovering glass and indium by detoxifying and removing liquid crystals and organic substances (films) from a waste liquid crystal display device without using an organic solvent. Patent Document 4 discloses a liquid crystal panel that has been used and a method for recovering a liquid crystal composition safely and economically.
[0009] 上記特許文献 1および 2の構成では、まず偏光板を剥離する工程を行っている。し カゝしながら、偏光板はガラス基板と強固に接着されており、これを剥離することは非常 に困難である。それは、液晶パネルの表示面積が大きくなるほど顕著なものとなる。ま た、特許文献 1では、偏光板を剥離する工程の後にガラスを破砕する工程を行って いるが、これは偏光板が設けられた状態のガラス基板を破砕することが困難であるこ とが原因である。 [0009] In the configurations of Patent Documents 1 and 2, first, a step of peeling the polarizing plate is performed. However, the polarizing plate is firmly bonded to the glass substrate, and it is very difficult to peel it off. This becomes more prominent as the display area of the liquid crystal panel increases. In Patent Document 1, a process of crushing the glass is performed after the process of peeling the polarizing plate. This is because it is difficult to crush the glass substrate on which the polarizing plate is provided. It is.
[0010] すなわち、特許文献 1および 2では、実現が困難な工程を含むと共に、液晶材料や 金属材料を回収するための工程が多ぐ実現性および経済的な面で不利であると ヽ う問題点を有している。  [0010] That is, Patent Documents 1 and 2 have disadvantages in terms of feasibility and economical aspects that include processes that are difficult to realize and that have many processes for recovering liquid crystal materials and metal materials. Has a point.
[0011] また、特許文献 3では、ガラス基板の融点以下で、かつ該液晶化合物の熱分解温 度以上の雰囲気で固体熱媒体と接触させ、該液晶化合物を含む有機化合物を分解 し、ガラスおよび金属を分離している。このため、有機化合物を熱分解するための設 備およびエネルギーが必要となる。また、この構成では、ガラスやインジウムは回収し て!ヽるものの液晶は回収して!/ヽな!、。 [0011] Further, in Patent Document 3, the organic compound containing the liquid crystal compound is decomposed by bringing it into contact with a solid heat medium in an atmosphere below the melting point of the glass substrate and above the thermal decomposition temperature of the liquid crystal compound. The metal is separated. For this reason, facilities and energy for thermally decomposing organic compounds are required. This configuration also collects glass and indium. Recover the liquid crystal!
[0012] また、特許文献 4では、偏光板や駆動用 ICが搭載されている回路基板などを、カツ ター等を用いて取り除 、た後にガラスを切断し、これを 80°C以上の熱水中に浸漬す ることによって液晶組成物を分離回収している。このため、ガラスを切断するための設 備および工程が必要となる。また、 80°C以上の熱水中を用いており、液晶組成物を 分離回収するためのエネルギーが必要となる。さらに、この構成ではインジウム等の 材料を回収していない。  [0012] In Patent Document 4, a circuit board or the like on which a polarizing plate or a driving IC is mounted is removed using a cutter or the like, and then the glass is cut and then heated to 80 ° C or higher. The liquid crystal composition is separated and recovered by being immersed in water. For this reason, facilities and processes for cutting glass are required. In addition, hot water at 80 ° C or higher is used, and energy is required to separate and recover the liquid crystal composition. Furthermore, this configuration does not recover materials such as indium.
[0013] すなわち、特許文献 3および 4にお ヽては、液晶材料および金属材料の全てを回 収できな!/、と!/、う問題点と、設備やエネルギーの点で経済的に不利であると!/、う問題 点とを有している。  [0013] That is, according to Patent Documents 3 and 4, it is impossible to collect all of the liquid crystal material and the metal material! /, And! /, Problems, as well as economical disadvantages in terms of equipment and energy. If so, there are problems.
特許文献 1:特開 2001— 305501号公報(2001年 10月 31日公開)  Patent Document 1: Japanese Patent Laid-Open No. 2001-305501 (published on October 31, 2001)
特許文献 2:特開 2001— 337305号公報(2001年 12月 7日公開)  Patent Document 2: Japanese Patent Laid-Open No. 2001-337305 (published on December 7, 2001)
特許文献 3:特開 2001— 137804号公報(2001年 5月 22日公開)  Patent Document 3: Japanese Patent Laid-Open No. 2001-137804 (published on May 22, 2001)
特許文献 4 :特開 2002— 166259号公報(2002年 6月 11日公開)  Patent Document 4: JP-A-2002-166259 (published on June 11, 2002)
発明の開示  Disclosure of the invention
[0014] 本発明は、上記の問題点に鑑みてなされたものであり、その目的は、偏光板が設け られた状態のガラス基板を破砕することが可能な廃パネルの処理装置や、液晶パネ ルに使用される液晶材料や金属材料を回収することによって、廃棄物を殆ど出さず に処理することが可能であって、該処理を行うためのエネルギーを必要とせずに (省 エネルギーで)、簡易な方法で処理することが可能な環境負荷の小さい廃パネルの 処理方法を実現することにある。  The present invention has been made in view of the above-mentioned problems, and an object of the present invention is to provide a waste panel processing apparatus capable of crushing a glass substrate provided with a polarizing plate, a liquid crystal panel, and the like. By collecting the liquid crystal material and metal material used in the tank, it is possible to process with almost no waste, and without requiring energy to perform the process (with energy saving), The purpose is to realize a method for processing waste panels with a low environmental impact that can be processed in a simple manner.
[0015] 本発明に係る廃パネルの処理方法は、上記課題を解決するために、一対のガラス 基板と、該一対のガラス基板間に挟持され、電圧の印加により光学変調する媒質か らなる媒質層と、少なくとも一方のガラス基板の媒質層との対向面側に配置された電 極と、少なくとも一方のガラス基板の媒質層との対向面とは反対側に配置された偏光 板とを有する廃パネルの処理方法であって、上記廃パネルを破砕する破砕工程と、 上記媒質を回収する媒質回収工程と、上記電極に含有されて!、る材料を回収する 電極材料回収工程と、上記ガラスを回収するガラス回収工程とをこの順で行うことを 特徴としている。 [0015] In order to solve the above problems, the waste panel processing method according to the present invention is a medium comprising a pair of glass substrates and a medium that is sandwiched between the pair of glass substrates and optically modulates by applying a voltage. An electrode disposed on the side facing the medium layer of at least one glass substrate, and a polarizing plate disposed on the side opposite to the surface facing the medium layer of at least one glass substrate. A panel processing method comprising: a crushing process for crushing the waste panel; a medium recovery process for recovering the medium; an electrode material recovery process for recovering the material contained in the electrode; and the glass To perform the glass recovery process It is a feature.
[0016] 上記の構成によれば、廃パネルは、一対のガラス基板と媒質層と電極と偏光板とを 有しており、破砕工程ではこれら各部材を有する状態の廃パネルを破砕している。す なわち、破砕工程では、廃棄された状態のままの (偏光板が設けられている状態の) 廃パネルを破砕している。  [0016] According to the above configuration, the waste panel has a pair of glass substrates, a medium layer, an electrode, and a polarizing plate, and in the crushing step, the waste panel having these members is crushed. . In other words, in the crushing process, waste panels that have been discarded (with a polarizing plate) are crushed.
[0017] そして、破砕工程にて破砕された廃パネルに対して、媒質回収工程を行って!/ヽる。  [0017] Then, perform a medium recovery process on the waste panel crushed in the crushing process! / Speak.
これにより、廃パネルに付着している媒質を回収することができる。ここで、媒質とは、 一対のガラス基板間に挟持されているものであり、ガラス基板間に印加された電圧に 応じて光学変調するものである。  Thereby, the medium adhering to the waste panel can be recovered. Here, the medium is sandwiched between a pair of glass substrates, and optically modulates according to a voltage applied between the glass substrates.
[0018] そして、媒質を回収した後の廃パネルに対して電極材料回収工程を行っている。こ れにより、廃パネルに付着している電極材料を回収することができる。ここで、電極と は、少なくとも一方のガラス基板の媒質層との対向面側に配置されているものであり、 媒質層に対して電圧を印加するためのものである。一対のガラス基板の一方に設け られていてもよぐ両方に設けられていてもよい。電極材料とは、この電極に含有して V、る材料のことであり、電極はこの電極材料を用いて形成されて 、る。  [0018] Then, an electrode material recovery step is performed on the waste panel after the medium is recovered. Thereby, the electrode material adhering to the waste panel can be collected. Here, the electrode is disposed on the surface of at least one glass substrate facing the medium layer, and is for applying a voltage to the medium layer. It may be provided on one or both of the pair of glass substrates. The electrode material is a material contained in this electrode, V, and the electrode is formed using this electrode material.
[0019] そして、電極材料を回収した後の廃パネルに対してガラス回収工程を行っている。  [0019] Then, a glass recovery process is performed on the waste panel after the electrode material is recovered.
これにより、媒質および電極材料が付着していないガラスを回収することができる。す なわち、媒質および電極材料と ヽつたパネルに用いられて ヽる各種材料が回収され た状態のガラスを得ることができる。  Thereby, the glass to which the medium and the electrode material are not attached can be collected. In other words, it is possible to obtain a glass in which various materials used for the panel, which are the medium and the electrode material, are collected.
[0020] このように、破砕工程、媒質回収工程、電極材料回収工程およびガラス回収工程を この順で行っていることにより、廃棄物が殆ど出ることのない処理を実現することが可 能になる。すなわち、各工程にて媒質や電極材料等の廃パネルに含まれている各材 料を回収しているため廃棄物を少なくすることができる。  [0020] As described above, by performing the crushing step, the medium recovery step, the electrode material recovery step, and the glass recovery step in this order, it is possible to realize a process with almost no waste. . That is, since each material contained in the waste panel such as a medium and electrode material is collected in each process, waste can be reduced.
[0021] また、上記各工程を上記の順で行うことにより、省エネルギーに貢献することが可能 になる。すなわち、最初に廃パネルを破砕しているため、廃パネルに何らかの加工を 施す必要がなぐ破砕片を用いて処理を行うことができるため処理が容易になる。さら に、媒質回収工程および電極材料回収工程の順で行うことにより、ガラス基板に対し て遠い側に設けられた部材力 順に回収している。つまり、露出している部分から回 収することとなり、媒質や電極材料を、無駄なエネルギーを使うことなく容易に回収す ることが可能になる。 [0021] Further, it is possible to contribute to energy saving by performing the above steps in the order described above. In other words, since the waste panel is first crushed, the processing can be performed easily by using a crushed piece that does not require any processing on the waste panel. Furthermore, by performing the medium recovery step and the electrode material recovery step in this order, the members are recovered in the order of the member force provided on the side farther from the glass substrate. In other words, from the exposed part Therefore, the medium and the electrode material can be easily recovered without using wasted energy.
[0022] さらに、これら各材料を回収した後にはガラスが残ることとなるため、ガラスをも容易 に回収することができること〖こなる。つまり、各工程が後工程の実行を容易にする目 的も兼ねることとなり、この順番が自然な流れであることが分かる。それゆえ、少ない エネルギーで廃パネルに含まれる各材料を回収することができる。  [0022] Furthermore, since the glass remains after each of these materials is recovered, the glass can be easily recovered. In other words, each process also serves the purpose of facilitating the execution of subsequent processes, and it can be seen that this order is a natural flow. Therefore, each material contained in the waste panel can be recovered with less energy.
[0023] また、最初に廃パネルを破砕し、何らかの加工を施す必要がな 、ことから、本発明 は、パネルの大きさ(表示面積)に関係無く実現することが可能であり、表示面積の大 き 、パネルであっても容易に処理することが可能になる。  [0023] In addition, since it is not necessary to first crush the waste panel and perform some processing, the present invention can be realized regardless of the panel size (display area). Large panels can easily be processed.
[0024] 以上により、廃パネルの処理を容易に行うことができると共に、廃棄物が殆ど出るこ となぐ省エネルギーであると 、つた環境負荷の小さ 、廃パネルの処理方法を実現 することができる。  [0024] As described above, the waste panel can be easily treated, and the waste panel processing method can be realized with low environmental load when the energy is saved so that almost no waste is generated.
[0025] 本発明に係る廃パネルの処理方法は、上記課題を解決するために、一対のガラス 基板と、該一対のガラス基板間に挟持され、電圧の印加により光学変調する媒質か らなる媒質層と、少なくとも一方のガラス基板の媒質層との対向面側に配置された電 極と、少なくとも一方のガラス基板の媒質層との対向面とは反対側に配置された偏光 板とを有する廃パネルの処理方法であって、上記廃パネルを破砕する破砕工程と、 上記媒質を回収する媒質回収工程とをこの順で行うことを特徴としている。  In order to solve the above problems, the waste panel processing method according to the present invention includes a pair of glass substrates and a medium sandwiched between the pair of glass substrates and optically modulated by applying a voltage. An electrode disposed on the side facing the medium layer of at least one glass substrate, and a polarizing plate disposed on the side opposite to the surface facing the medium layer of at least one glass substrate. A panel processing method, wherein a crushing step of crushing the waste panel and a medium recovery step of recovering the medium are performed in this order.
[0026] 上記の構成によれば、廃パネルは、一対のガラス基板と媒質層と電極と偏光板とを 有しており、破砕工程ではこれら各部材を有する状態の廃パネルを破砕している。す なわち、破砕工程では、廃棄された状態のままの廃パネルを破砕している。そして、 破砕工程にて破砕された廃パネルに対して、媒質回収工程を行っている。これ〖こより 、廃パネルに付着している媒質を回収することができる。ここで、媒質とは、一対のガ ラス基板間に挟持されているものであり、ガラス基板間に印加された電圧に応じて光 学変調するものである。  [0026] According to the above configuration, the waste panel has a pair of glass substrates, a medium layer, an electrode, and a polarizing plate, and in the crushing step, the waste panel having these members is crushed. . In other words, in the crushing process, waste panels that have been discarded are crushed. And the medium recovery process is performed to the waste panel crushed in the crushing process. From this, the medium adhering to the waste panel can be recovered. Here, the medium is sandwiched between a pair of glass substrates, and optically modulates according to the voltage applied between the glass substrates.
[0027] このように、最初に廃パネルを破砕しているため、廃パネルに何らかの加工を施す 必要がなぐ破砕片を用いて処理を行うことができるため処理が容易になる。また、最 初に廃パネルを破砕し、何らかの加工を施す必要がないことから、パネルの大きさ( 表示面積)に関係無く実現することが可能であり、表示面積の大きいパネルであって も容易に処理することが可能になる。 [0027] In this manner, since the waste panel is first crushed, the treatment can be performed using the crushed pieces that do not require any processing on the waste panel, so that the treatment becomes easy. Also, because the waste panel does not need to be crushed and processed in the first place, the size of the panel ( This can be realized regardless of the display area, and even a panel having a large display area can be easily processed.
[0028] 本発明に係る廃パネルの処理方法は、上記課題を解決するために、一対のガラス 基板と、該一対のガラス基板間に挟持され、電圧の印加により光学変調する媒質か らなる媒質層と、少なくとも一方のガラス基板の媒質層との対向面側に配置された電 極と、少なくとも一方のガラス基板の媒質層との対向面とは反対側に配置された偏光 板とを有する廃パネルの処理方法であって、上記廃パネルを破砕する破砕工程と、 上記電極に含有されている材料を回収する電極材料回収工程とをこの順で行うこと を特徴としている。  [0028] In order to solve the above problems, the waste panel treatment method according to the present invention is a medium comprising a pair of glass substrates and a medium that is sandwiched between the pair of glass substrates and optically modulates by applying a voltage. An electrode disposed on the side facing the medium layer of at least one glass substrate, and a polarizing plate disposed on the side opposite to the surface facing the medium layer of at least one glass substrate. A panel processing method, characterized in that a crushing step of crushing the waste panel and an electrode material recovery step of recovering a material contained in the electrode are performed in this order.
[0029] 上記の構成によれば、廃パネルは、一対のガラス基板と媒質層と電極と偏光板とを 有しており、破砕工程ではこれら各部材を有する状態の廃パネルを破砕している。す なわち、破砕工程では、廃棄された状態のままの廃パネルを破砕している。そして、 破砕工程にて破砕された廃パネルに対して電極材料回収工程を行って 、る。これに より、廃パネルに付着している電極材料を回収することができる。ここで、電極とは、 少なくとも一方のガラス基板の媒質層との対向面側に配置されているものであり、媒 質層に対して電圧を印加するためのものである。一対のガラス基板の一方に設けら れていてもよぐ両方に設けられていてもよい。電極材料とは、この電極に含有してい る材料のことであり、電極はこの電極材料を用いて形成されて 、る。  [0029] According to the above configuration, the waste panel has a pair of glass substrates, a medium layer, an electrode, and a polarizing plate, and in the crushing step, the waste panel having these members is crushed. . In other words, in the crushing process, waste panels that have been discarded are crushed. Then, an electrode material recovery process is performed on the waste panel crushed in the crushing process. As a result, the electrode material adhering to the waste panel can be recovered. Here, the electrode is disposed on the surface facing the medium layer of at least one glass substrate, and is for applying a voltage to the medium layer. It may be provided on one or both of the pair of glass substrates. The electrode material is a material contained in this electrode, and the electrode is formed using this electrode material.
[0030] このように、最初に廃パネルを破砕しているため、廃パネルに何らかの加工を施す 必要がなぐ破砕片を用いて処理を行うことができるため処理が容易になる。また、最 初に廃パネルを破砕し、何らかの加工を施す必要がないことから、パネルの大きさ( 表示面積)に関係無く実現することが可能であり、表示面積の大きいパネルであって も容易に処理することが可能になる。  [0030] As described above, since the waste panel is first crushed, the processing can be performed using the crushed pieces that do not require any processing on the waste panel, so that the processing becomes easy. Also, since it is not necessary to crush the waste panel first and perform any processing, it can be realized regardless of the panel size (display area), and even a panel with a large display area is easy. Can be processed.
[0031] 本発明に係る廃パネルの処理装置は、上記課題を解決するために、回転式破砕 手段と固定式破砕手段とを備えた廃パネルの処理装置であって、上記回転式破砕 手段は、平面状の破砕部を複数有しており、上記複数の破砕部は、少なくとも 2つの 破碎部の平面が異なる方向を向くように配置されて 、ることを特徴として 、る。 [0031] In order to solve the above problems, the waste panel processing apparatus according to the present invention is a waste panel processing apparatus including a rotary crushing means and a stationary crushing means, and the rotary crushing means includes: It has a plurality of flat crushing portions, and the plurality of crushing portions are arranged so that the planes of at least two rupture portions face different directions.
[0032] 上記の構成によれば、回転式破砕手段と固定式破砕手段とを備えているため、こ れら各手段を用いることにより廃パネルを破砕することができる。また、回転式破砕手 段は、平面状の複数の破砕部を有しており、これら複数の破砕部は、少なくとも 2つ の破砕部の平面が異なる方向を向くように配置されているため、廃パネルを異なるタ イミングで破砕することが可能になる。 [0032] According to the above configuration, the rotary crushing means and the fixed crushing means are provided. By using these means, the waste panel can be crushed. In addition, the rotary crushing means has a plurality of flat crushing parts, and these crushing parts are arranged so that the planes of at least two crushing parts face different directions. Waste panels can be crushed at different times.
[0033] なお、破砕部の平面が異なる方向を向くように配置されているとは、平面状の破砕 部における最も面積の広 、面に対して垂直な方向が、各破砕部にて異なる方向とな るように配置されている状態である。すなわち、各破砕部は、各平面の法線の方向が 異なる方向となるように配置されて 、る。 [0033] It should be noted that the planes of the crushing parts are arranged in different directions means that the direction of the widest area in the planar crushing part and the direction perpendicular to the surface is different in each crushing part. It is in the state where it is arranged so that. That is, each crushing part is arranged so that the normal direction of each plane is different.
[0034] これにより、回転式破砕手段の一度の回転にて、廃パネルを種々の方向に配置さ れた複数の破砕部にて破砕することができると共に、種々のタイミングで破砕すること ができるため、廃パネルを効率的に破砕することができる。 [0034] With this, the waste panel can be crushed by a plurality of crushing portions arranged in various directions by one rotation of the rotary crushing means, and can be crushed at various timings. Therefore, the waste panel can be efficiently crushed.
[0035] 本発明のさらに他の目的、特徴、および優れた点は、以下に示す記載によって十 分わかるであろう。 [0035] Still other objects, features, and advantages of the present invention will be fully understood from the following description.
図面の簡単な説明  Brief Description of Drawings
[0036] [図 1]本発明の実施の一形態を示すものであり、廃液晶パネルの処理方法のフロー を示す図である。  FIG. 1 shows an embodiment of the present invention and is a diagram showing a flow of a method for treating a waste liquid crystal panel.
[図 2]本発明の実施の一形態を示すものであり、廃液晶パネルの概略構成を示す断 面図である。  FIG. 2, showing an embodiment of the present invention, is a cross-sectional view showing a schematic configuration of a waste liquid crystal panel.
[図 3]本発明の実施の一形態を示すものであり、破砕工程にて用いる破砕機の概略 構成を示す断面図である。  FIG. 3, showing an embodiment of the present invention, is a cross-sectional view showing a schematic configuration of a crusher used in a crushing step.
[図 4]本発明の実施の一形態を示すものであり、破砕ユニットの概略構成を示す断面 図である。  FIG. 4 shows an embodiment of the present invention and is a cross-sectional view showing a schematic configuration of a crushing unit.
[図 5]本発明の実施の一形態を示すものであり、液晶回収工程を示す図である。  FIG. 5, showing an embodiment of the present invention, is a diagram showing a liquid crystal recovery step.
[図 6]本発明の実施の一形態を示すものであり、インジウム回収工程を示す図である  FIG. 6, showing an embodiment of the present invention, is a diagram illustrating an indium recovery step.
[図 7]本発明の実施の一形態を示すものであり、破砕ユニットの概略構成を示す図で ある。 FIG. 7, showing an embodiment of the present invention, is a diagram showing a schematic configuration of a crushing unit.
発明を実施するための最良の形態 [0037] 本発明の実施の一形態について図 1ないし図 7に基づいて説明すると以下の通り である。 BEST MODE FOR CARRYING OUT THE INVENTION [0037] An embodiment of the present invention will be described with reference to Figs. 1 to 7 as follows.
[0038] まず、本実施の形態に係る廃パネルの処理方法に用いられる廃パネルにっ 、て説 明する。本実施の形態では、廃パネルとして廃液晶パネルを例に挙げて説明する。 この廃液晶パネルとは、廃棄処分される液晶パネルのことである。  First, the waste panel used in the waste panel processing method according to the present embodiment will be described. In the present embodiment, a waste liquid crystal panel will be described as an example of a waste panel. This waste liquid crystal panel is a liquid crystal panel to be discarded.
[0039] なお、上記廃液晶パネルとは、例えば、液晶パネルの製造工場にぉ 、て廃棄され る液晶パネル、情報表示装置や映像表示装置等の生産工場から廃棄される液晶パ ネル、市場にて廃棄された情報表示装置や映像表示装置等に用いられた液晶表示 装置カゝら排出される液晶パネル等を含む。  [0039] The above-mentioned waste liquid crystal panel refers to, for example, a liquid crystal panel discarded from a liquid crystal panel manufacturing factory, a liquid crystal panel discarded from a production factory such as an information display device and a video display device, and the market. Liquid crystal panels etc. discharged from the liquid crystal display device used in discarded information display devices and video display devices.
[0040] また、本発明に適用可能な廃液晶パネルとしては、例えば、 TFT(Thin Film Transi stor)等のアクティブ素子(図示せず)を備えた液晶パネルや、 TN (Twisted Nematic) 液晶パネル、 STN (Super Twisted Nematic)液晶パネル等の廃棄処分された廃液晶 パネルを挙げることができる。  [0040] In addition, examples of the waste liquid crystal panel applicable to the present invention include a liquid crystal panel including an active element (not shown) such as a TFT (Thin Film Transistor), a TN (Twisted Nematic) liquid crystal panel, Examples include discarded liquid crystal panels such as STN (Super Twisted Nematic) liquid crystal panels.
[0041] 図 2は、本実施の形態に係る廃液晶パネル 30 (廃パネル)の概略構成を示す断面 図である。図 2に示すように、廃液晶パネル 30は、一対の透明なガラス基板 la及び 1 bを、当該ガラス基板 la及び lbの周縁に沿って額縁状に配置したシール部材 2を介 して貼り合わせ、その間に液晶 (媒質)を充填させて液晶層 (媒質層) 3とした構成を 有している。すなわち、廃液晶パネル 30は、一対のガラス基板 la及び lbで液晶層 3 を挟持した構成となって 、る。  FIG. 2 is a cross-sectional view showing a schematic configuration of the waste liquid crystal panel 30 (waste panel) according to the present embodiment. As shown in FIG. 2, the waste liquid crystal panel 30 is bonded to a pair of transparent glass substrates la and 1b via a seal member 2 arranged in a frame shape along the periphery of the glass substrates la and lb. The liquid crystal layer (medium layer) 3 is filled with liquid crystal (medium) in the meantime. That is, the waste liquid crystal panel 30 has a configuration in which the liquid crystal layer 3 is sandwiched between a pair of glass substrates la and lb.
[0042] ガラス基板 la及び lbにおける液晶層 3とは反対側の面には、各々偏光板 4a及び 4 bが粘着剤によって貼り合わされている。また、ガラス基板 laの液晶層 3側の面には、 有機物を主体としたカラーフィルタ 5、インジウム (In;電極材料)を含む透明な膜 (IT O (Indium Thin Oxide)膜)力もなる透明電極 (電極) 7、有機物力もなる配向膜 8がこ の順で積層されている。なお、カラーフィルタ 5の隙間には、金属クロムからなる反射 防止膜 6が形成されている。  [0042] Polarizing plates 4a and 4b are bonded to the surfaces of the glass substrates la and lb opposite to the liquid crystal layer 3 by adhesives, respectively. In addition, on the surface of the glass substrate la on the liquid crystal layer 3 side, a transparent electrode (ITO (Indium Thin Oxide) film) with a color filter 5 mainly composed of an organic substance and a transparent film (ITO (Indium Thin Oxide) film) containing indium (In) (Electrode) 7 and an alignment film 8 having organic physical strength are laminated in this order. In addition, an antireflection film 6 made of metallic chromium is formed in the gap between the color filters 5.
[0043] 一方、ガラス基板 lbの液晶層 3側の面には、タンタル、アルミニウム、チタン等の金 属膜からなるバス電極 9、インジウムを含む透明な膜 (ITO膜)カゝらなる画素電極 10、 有機物からなる配向膜 11がこの順で積層されている。 [0044] 次に、上記構成を有する廃液晶パネル 30を処理する方法について説明する。図 1 は、本発明に係る廃液晶パネル 30の処理方法のフローを示す図である。図 1に示す ように、本発明の廃液晶パネル 30の処理方法は、破砕工程 Sl、液晶回収工程 (媒 質回収工程) S2、インジウム回収工程 (電極材料回収工程) S3、およびガラス回収ェ 程 S4をこの順で行うものである。これにより、廃液晶パネル 30の処理を省エネルギー で行うことが可能になると共に、廃液晶パネル 30に使用されている液晶やインジウム 、ガラス等の材料を回収することが可能になる。以下、具体的に説明する。 On the other hand, on the surface of the glass substrate lb on the liquid crystal layer 3 side, a bus electrode 9 made of a metal film such as tantalum, aluminum or titanium, a pixel electrode made of a transparent film (ITO film) containing indium 10. An alignment film 11 made of an organic material is laminated in this order. Next, a method for treating the waste liquid crystal panel 30 having the above configuration will be described. FIG. 1 is a diagram showing a flow of a processing method of the waste liquid crystal panel 30 according to the present invention. As shown in FIG. 1, the processing method of the waste liquid crystal panel 30 of the present invention includes a crushing process Sl, a liquid crystal recovery process (medium recovery process) S2, an indium recovery process (electrode material recovery process) S3, and a glass recovery process. S4 is performed in this order. As a result, the waste liquid crystal panel 30 can be processed with energy saving, and the liquid crystal, indium, glass and other materials used in the waste liquid crystal panel 30 can be recovered. This will be specifically described below.
[0045] 本発明に係る廃液晶パネル 30を処理する方法としては、まず破砕工程 S 1を行う。  [0045] As a method for treating the waste liquid crystal panel 30 according to the present invention, first, the crushing step S1 is performed.
破砕工程 S1とは、破砕機を用いて廃液晶パネル 30を破砕する工程である。すなわ ち、偏光板 4a及び 4bを破り、ガラス基板 la及び lbを砕く工程である。図 3は、破砕ェ 程 S1にて用いる破砕機 12の概略構成を示す断面図である。図 3に示すように、破砕 機 12は、投入機 13、投入ホッパー 14、破砕ユニット 15、フレコン 16、重量計 17、集 塵機 18、制御盤 19を備えている。  The crushing step S1 is a step of crushing the waste liquid crystal panel 30 using a crusher. That is, it is a process of breaking the polarizing plates 4a and 4b and crushing the glass substrates la and lb. FIG. 3 is a cross-sectional view showing a schematic configuration of the crusher 12 used in the crushing step S1. As shown in FIG. 3, the crusher 12 includes an input device 13, an input hopper 14, a crushing unit 15, a flexible container 16, a weigh scale 17, a dust collector 18, and a control panel 19.
[0046] 投入機 13は、廃液晶パネル 30を投入ホッパー 14に投入するためのものである。例 えば、投入ホッパー 14が高所に設けられている場合に、投入機 13は、廃液晶パネ ル 30を低所から高所へと運搬して投入ホッパー 14に投入するようになっている。投 入ホッパー 14に投入された廃液晶パネル 30は、破砕ユニット 15へと投入される。  The input device 13 is used to input the waste liquid crystal panel 30 to the input hopper 14. For example, when the charging hopper 14 is provided at a high place, the charging machine 13 transports the waste liquid crystal panel 30 from a low place to a high place and inputs it to the charging hopper 14. The waste liquid crystal panel 30 thrown into the throwing hopper 14 is thrown into the crushing unit 15.
[0047] 破砕ユニット 15は、投入された廃液晶パネル 30を破砕するものである。破砕ュ-ッ ト 15の構成や破砕ユニット 15にて廃液晶パネル 30を破砕する方法の詳細につ 、て は後述する。破砕ユニット 15にて所定の大きさに破砕された廃液晶パネル 30は、フ レコン 16にて回収され、重量計 17で検量された後に排出される。なお、集塵機 18は 、破枠ユニット 15にて廃液晶パネル 30を破砕することにより発生する粉塵を回収す るものである。また、これら各部材の制御は、制御盤 19を用いて行われる。  The crushing unit 15 crushes the waste liquid crystal panel 30 that has been input. Details of the configuration of the crushing unit 15 and the method of crushing the waste liquid crystal panel 30 by the crushing unit 15 will be described later. The waste liquid crystal panel 30 crushed to a predetermined size by the crushing unit 15 is collected by the flexible container 16 and calibrated by the weighing scale 17 and then discharged. The dust collector 18 collects dust generated by crushing the waste liquid crystal panel 30 by the breaker unit 15. The control of these members is performed using the control panel 19.
[0048] 次に、破砕ユニット 15の構成について具体的に説明する。図 4は、破砕ユニット 15 の概略構成を示す断面図である。図 4に示すように、破砕ユニット 15は、投入された 廃液晶パネル 30を破砕する破砕部 20と、破砕された廃液晶パネル 30を排出する排 出口 21とを備えている。  [0048] Next, the configuration of the crushing unit 15 will be specifically described. FIG. 4 is a cross-sectional view showing a schematic configuration of the crushing unit 15. As shown in FIG. 4, the crushing unit 15 includes a crushing unit 20 that crushes the waste liquid crystal panel 30 that has been input, and an outlet 21 that discharges the crushed waste liquid crystal panel 30.
[0049] 破砕部 20は、側壁部 22、スクリーン 23、回転軸 24、ローター 25、回転刃(回転式 破砕手段) 26、固定刃(固定式破砕手段) 27を備えている。側壁部 22は、破砕部 20 の空間を形成するための壁である。なお、側壁部 22の内面には、側壁部 22よりも強 固な材質力もなる内面板 28をさらに備えていてもよい。スクリーン 23は、所定の大き さの穴を多数有する、いわゆる篩いである。この穴の大きさよりも小さい大きさに破砕 された廃液晶パネル 30の破砕片 (カレット)だけが、スクリーン 23を通過することとな る。 [0049] The crushing part 20 includes a side wall part 22, a screen 23, a rotary shaft 24, a rotor 25, a rotary blade (rotary type Crushing means) 26 and a fixed blade (fixed crushing means) 27. The side wall portion 22 is a wall for forming a space for the crushing portion 20. The inner surface of the side wall portion 22 may further include an inner surface plate 28 that has a stronger material force than the side wall portion 22. The screen 23 is a so-called sieve having many holes of a predetermined size. Only the crushed pieces (cullet) of the waste liquid crystal panel 30 crushed to a size smaller than the size of the hole pass through the screen 23.
[0050] ローター 25は略三角柱の形状を有する部材であり、その中心部分に回転軸 24が 一体的に設けられている。ローター 25の略三角柱の各面には、ボルトなどの留具に て回転刃 26 (ロータリーカッター)が複数取り付けられている。また、固定刃 27は、側 壁部 22にボルトなどの留具にて取り付けられている。  [0050] The rotor 25 is a member having a substantially triangular prism shape, and a rotating shaft 24 is integrally provided at a central portion thereof. A plurality of rotary blades 26 (rotary cutters) are attached to each surface of the approximately triangular prism of the rotor 25 by fasteners such as bolts. The fixed blade 27 is attached to the side wall portion 22 with a fastener such as a bolt.
[0051] 上記回転刃 26および固定刃 27は、少なくとも先端部が超硬合金材料またはセラミ ック材料を用いて形成されている。超硬合金材料とは、ビッカース硬度で少なくとも 1 1. 8GPa以上の硬度を有する材料であり、例えば、 WC— Co合金、 WC— TiC Co 合金、 WC— TiC— TaC (NbC)—Co合金等の材料を挙げることができる。  [0051] At least tip portions of the rotary blade 26 and the fixed blade 27 are formed using a cemented carbide material or a ceramic material. A cemented carbide material is a material having a Vickers hardness of at least 11.8 GPa, such as WC—Co alloy, WC—TiC Co alloy, WC—TiC—TaC (NbC) —Co alloy, etc. Materials can be mentioned.
[0052] なお、上記回転刃 26 (の先端部)が超硬合金材料を用いて形成され、固定刃 27 ( の先端部)がセラミック材料を用いて形成されていてもよぐあるいは、上記回転刃 26 (の先端部)がセラミック材料を用いて形成され、固定刃 27 (の先端部)が超硬合金材 料を用いて形成されて 、てもよ 、。  [0052] The rotary blade 26 (tip end) may be formed using a cemented carbide material, and the fixed blade 27 (tip end) may be formed using a ceramic material. The blade 26 (tip portion) may be formed using a ceramic material, and the fixed blade 27 (tip portion) may be formed using a cemented carbide material.
[0053] 上記回転軸 24の回転に伴い、ローター 25および回転刃 26が回転するようになつ ており、回転刃 26と固定刃 27とが一定の間隔を保った状態で交錯するようになって いる。具体的には、駆動モータ(図示せず)等によって回転軸 24とローター 25とが図 4中矢印 Aの方向に回転すると、ローター 25に設けられた回転刃 26も回転する。そ して、破砕部 20の上方カゝら投入された廃液晶パネル 30は、回転刃 26と固定刃 27と が一定の間隔を保った状態で交錯する部分を通過し、これら各刃 26及び 27によつ て破枠される。  [0053] As the rotary shaft 24 rotates, the rotor 25 and the rotary blade 26 rotate, and the rotary blade 26 and the fixed blade 27 come to intersect with each other at a constant interval. Yes. Specifically, when the rotary shaft 24 and the rotor 25 are rotated in the direction of arrow A in FIG. 4 by a drive motor (not shown) or the like, the rotary blade 26 provided on the rotor 25 is also rotated. Then, the waste liquid crystal panel 30 thrown into the upper part of the crushing section 20 passes through a portion where the rotary blade 26 and the fixed blade 27 intersect with each other at a constant interval. 27.
[0054] ここで、回転刃 26の構成について図 7に基づいて具体的に説明する。図 7は、破砕 ユニット 15を上方から見た場合の概略構成を示す図である。図 7に示すように、ロー ター 25の各面上には設けられた回転刃 26は、複数の破砕部 29a、 29b及び 29cが 設けられている。これら複数の破砕部 29a〜29cは平面状の刃力 なっており、回転 刃 26の回転軸方向(ローター 25の長手方向)に複数配置されている。また、各破砕 部 29a〜29cは、各平面が異なる方向を向くように配置されて 、る。 Here, the configuration of the rotary blade 26 will be specifically described with reference to FIG. FIG. 7 is a diagram showing a schematic configuration when the crushing unit 15 is viewed from above. As shown in FIG. 7, the rotary blade 26 provided on each surface of the rotor 25 has a plurality of crushing portions 29a, 29b and 29c. Is provided. The plurality of crushing portions 29 a to 29 c have a planar blade force, and a plurality of crushing portions 29 a to 29 c are arranged in the rotation axis direction of the rotary blade 26 (the longitudinal direction of the rotor 25). The crushing parts 29a to 29c are arranged so that the planes face in different directions.
[0055] 上記「破砕部 29a〜29cの各平面が異なる方向を向くように配置されている」とは、 各破砕部 29a〜29cの最も面積の広い面に対して垂直な方向力 各々の破砕部 29 a〜29cにて異なる方向となっている構成を指す。すなわち、破砕部 29a〜29cの各 平面の法線の方向が異なる方向となっている構成である。  [0055] The above-mentioned "arranged so that the flat surfaces of the crushing portions 29a to 29c face different directions" means that the directional force perpendicular to the widest surface of the crushing portions 29a to 29c This refers to a configuration that is different in the sections 29a to 29c. That is, the normal direction of each plane of the crushing portions 29a to 29c is different.
[0056] また、本実施の形態では、ローター 25上に設けられ、各平面が異なる方向を向くよ うに配置された各破砕部 29a〜29cを 1単位とした場合に、これが複数単位配置され ている。これら各単位は、破砕部 29a〜29cが回転刃 26の回転軸方向に沿って配置 されている。  [0056] Further, in the present embodiment, when each crushing portion 29a to 29c provided on the rotor 25 and arranged so that each plane faces in a different direction is set as one unit, a plurality of units are arranged. Yes. In each of these units, the crushing portions 29 a to 29 c are arranged along the rotation axis direction of the rotary blade 26.
[0057] すなわち、破砕部 29a〜29cの各々力 図 7中に示す回転方向 Aに対して多少ずら した状態となるように配置されている。そして、本実施の形態では、回転刃 26は、この 破砕部 29a〜29cが連続して配置された構成を有している。なお、これら各破砕部 2 9a〜29cの配置方向(平面の向き)は、廃パネル 30を破砕することが可能な位置関 係となる傾きとすればよぐ仕様に応じて適宜設定することができる。  That is, the force of each of the crushing portions 29a to 29c is arranged so as to be slightly shifted with respect to the rotation direction A shown in FIG. And in this Embodiment, the rotary blade 26 has the structure by which this crushing part 29a-29c was arrange | positioned continuously. The arrangement direction (plane direction) of each of the crushing parts 29a to 29c can be set as appropriate according to the specifications as long as the inclination is a positional relationship that can crush the waste panel 30. it can.
[0058] このように、回転刃 26として、複数の破砕部 29a〜29cを、各々の平面の配置方向 を異ならせて配置し、かつ、それらを連続的に配置することにより、廃パネル 30を効 率よく破砕することが可能になる。また、このような構成とすることにより、ガラス基板 1 a及び lbに偏光板 4a及び 4bが設けられている状態の廃パネル 30を処理する場合に おいても、偏光板 4a及び 4bを破り、ガラス基板 la及び lbを砕くことによって破砕する ことができる。  [0058] In this manner, as the rotary blade 26, the plurality of crushing portions 29a to 29c are arranged with the arrangement directions of the respective planes being different, and the waste panels 30 are arranged by continuously arranging them. It can be efficiently crushed. Further, with such a configuration, even when the waste panel 30 in a state where the polarizing plates 4a and 4b are provided on the glass substrates 1a and lb, the polarizing plates 4a and 4b are broken, It can be crushed by crushing the glass substrates la and lb.
[0059] 破砕された廃液晶パネル 30の破砕片力 スクリーン 23に設けられた穴よりも小さい 場合にはこの穴を通って排出口 21から排出される。一方、破砕された廃液晶パネル 30の破砕片力 スクリーン 23に設けられた穴よりも大きい場合には、この穴よりも小さ くなるまで繰り返し破砕されるようになって!/、る。  [0059] When the crushed piece force of the crushed waste liquid crystal panel 30 is smaller than the hole provided in the screen 23, it is discharged from the discharge port 21 through this hole. On the other hand, if it is larger than the crushing force of the crushed waste liquid crystal panel 30 than the hole provided in the screen 23, it will be repeatedly crushed until it becomes smaller than this hole!
[0060] これにより、廃液晶パネル 30を所望の大きさに破砕することが可能となり、均一な大 きさの破砕片を得ることができる。なお、上記所望の大きさは、回転刃 26と固定刃 27 との間隔を調整することにより適宜設定することができる。本発明の処理方法に適し た破砕片の大きさとしては、例えば lmn!〜 5mmとすることができる。 [0060] Thereby, the waste liquid crystal panel 30 can be crushed to a desired size, and crushed pieces of uniform size can be obtained. The desired size is determined by the rotary blade 26 and the fixed blade 27. Can be set as appropriate by adjusting the interval. As a size of the fragment suitable for the treatment method of the present invention, for example, lmn! Can be ~ 5mm.
[0061] このように、上記破砕機 12を用いて廃液晶パネル 30を破砕することにより、後工程 で使用する薬品に対する反応面積を大きくすることが可能になる。また、上記破砕機 12を用いることにより、偏光板 4a及び 4bが設けられている状態の廃液晶パネル 30を 破枠することができる。 As described above, by crushing the waste liquid crystal panel 30 using the crusher 12, it becomes possible to increase the reaction area for the chemical used in the subsequent process. Further, by using the crusher 12, the waste liquid crystal panel 30 in which the polarizing plates 4a and 4b are provided can be broken.
[0062] 次に、液晶回収工程 S2を行う。液晶回収工程 S2は、上記破砕工程 S1にて破砕さ れた廃液晶パネル 30の破砕片に付着して ヽる液晶を回収する工程である。すなわ ち、この液晶回収工程 S2は、液晶を溶解する有機溶剤 (溶剤)などを用いて破砕片 を洗浄することにより、液晶を有機溶剤に溶解させて回収する工程である。これ〖こより 、液晶を簡単かつ確実に回収することができるものとなっている。  [0062] Next, a liquid crystal recovery step S2 is performed. The liquid crystal recovery step S2 is a step of recovering the liquid crystal adhering to the crushed pieces of the waste liquid crystal panel 30 crushed in the crushing step S1. In other words, the liquid crystal recovery step S2 is a step in which the liquid crystal is dissolved in the organic solvent and recovered by washing the crushed pieces with an organic solvent (solvent) that dissolves the liquid crystal. As a result, the liquid crystal can be easily and reliably collected.
[0063] 図 5は、本実施の形態に係る液晶回収工程 S2を示す図である。図 5に示すように、 まず、破砕工程 S1で破砕された廃液晶パネル 30の破砕片を複数の穴の空 、た容 器 (カレット容器)に入れる。このカレット容器の穴は、破砕片が通り抜けることのない 程度の大きさの穴とする。次いで、液晶を溶解する有機溶剤が入れられた容器 (溶剤 容器)に、破砕片の入ったカレット容器を浸漬させて液晶を洗い流す。これにより、破 砕片に付着した液晶がカレット容器の穴を介して有機溶剤に溶解する。  FIG. 5 is a diagram showing a liquid crystal recovery step S2 according to the present embodiment. As shown in FIG. 5, first, the crushed pieces of the waste liquid crystal panel 30 crushed in the crushing step S1 are placed in a plurality of holes (a cullet container). The cullet container should be sized so that the fragments will not pass through. Next, the cullet container containing the crushed pieces is immersed in a container (solvent container) containing an organic solvent that dissolves the liquid crystal to wash away the liquid crystal. As a result, the liquid crystal adhering to the debris is dissolved in the organic solvent through the hole in the cullet container.
[0064] その後、カレット容器を溶剤容器力も取り出すことにより、溶剤容器内には、液晶が 溶解した有機溶剤が残る。そして、この液晶を含む有機溶剤を減圧下で蒸留 (留去) することによって有機溶剤が除去され残留物として液晶を得ることができる。  [0064] Thereafter, the cullet container is also taken out of the solvent container force, so that the organic solvent in which the liquid crystal is dissolved remains in the solvent container. The organic solvent containing the liquid crystal is distilled (evaporated) under reduced pressure to remove the organic solvent and obtain a liquid crystal as a residue.
[0065] なお、上記液晶を溶解させる有機溶剤としては、例えばアセトンを挙げることができ る。ただし、使用可能な有機溶剤としては、液晶を溶解させることができるものであれ ばよく特に限定されるものではない。また、液晶はアセトン等の有機溶剤と比較して、 沸点が充分に高い。従って、液晶の沸点よりも充分に低い温度にて有機溶剤を蒸留 することができる。すなわち、本実施の形態に係る液晶回収工程 S2とすることにより、 液晶と有機溶剤とを簡単に分離することができる。  [0065] Examples of the organic solvent for dissolving the liquid crystal include acetone. However, usable organic solvents are not particularly limited as long as they can dissolve liquid crystals. Liquid crystals have a sufficiently high boiling point compared to organic solvents such as acetone. Therefore, the organic solvent can be distilled at a temperature sufficiently lower than the boiling point of the liquid crystal. That is, by using the liquid crystal recovery step S2 according to this embodiment, the liquid crystal and the organic solvent can be easily separated.
[0066] また、液晶回収工程 S2では、有機溶剤に液晶を溶解させる際に、他の有機物 (例 えば、配向膜や偏光板、カラーフィルタ等)の一部または全部が有機溶剤に溶解す る。ただし、この場合であっても、液晶と他の有機物との沸点の違いを利用して分留 することにより、液晶だけを容易に回収することができる。 [0066] Further, in the liquid crystal recovery step S2, when the liquid crystal is dissolved in the organic solvent, part or all of other organic substances (for example, an alignment film, a polarizing plate, a color filter, etc.) are dissolved in the organic solvent. The However, even in this case, only the liquid crystal can be easily recovered by fractional distillation using the difference in boiling point between the liquid crystal and other organic substances.
[0067] なお、上記説明では、破砕片を穴の空!、た容器 (カレット容器)に入れて、有機溶 剤の入った容器 (溶剤容器)に浸漬しているが、これに限定されるものではない。例え ば、破砕片を有機溶剤の入った容器に直接入れて有機溶剤に浸した後に、破砕片 を濾過により取り除いてもよい。また、破砕片に付着した液晶を、超音波を用いて除 去し回収することちでさる。  [0067] In the above description, the crushed pieces are placed in a hollow hole, a container (cullet container), and immersed in a container (solvent container) containing an organic solvent. However, the present invention is not limited to this. It is not a thing. For example, the crushed pieces may be directly put into a container containing an organic solvent and immersed in the organic solvent, and then the crushed pieces may be removed by filtration. In addition, the liquid crystal attached to the crushed pieces can be removed and collected using ultrasonic waves.
[0068] 次に、インジウム回収工程 S3を行う。インジウム回収工程 S3は、上記液晶回収ェ 程 S2にて有機物が除去された破砕片に付着しているインジウムを回収する工程であ る。すなわち、このインジウム回収工程 S3は、インジウムを溶解する酸溶液を用いて 破砕片を洗浄することにより、インジウムを酸溶液に溶解させて回収する工程である。 これにより、高純度のインジウムを簡単かつ確実に回収することができるものとなって いる。  [0068] Next, an indium recovery step S3 is performed. The indium recovery step S3 is a step of recovering indium adhering to the crushed pieces from which organic substances have been removed in the liquid crystal recovery step S2. That is, this indium recovery step S3 is a step of recovering indium by dissolving it in the acid solution by washing the fragments using an acid solution in which indium is dissolved. As a result, high-purity indium can be easily and reliably recovered.
[0069] 図 6は、本実施の形態に係るインジウム回収工程 S3を示す図である。図 6に示すよ うに、まず、液晶回収工程 S2で有機物が除去された破砕片を酸溶液の入った容器 に入れ攪拌する。これにより、破砕片に付着したインジウムを含む金属が酸溶液に溶 解する。特に、本実施の形態では、上記液晶回収工程 S2を先に行っているため、ィ ンジゥムが含有されている透明電極 7及び 10上に設けられている配向膜 4a及び 4b が除去されている(または一部剥離している)。このため、酸溶液が透明電極 7及び 1 0に接触しやすくなつており、効率的にインジウムを溶解させることが可能になってい る。  FIG. 6 is a diagram showing an indium recovery step S3 according to the present embodiment. As shown in Fig. 6, first, the crushed pieces from which organic substances have been removed in the liquid crystal recovery step S2 are placed in a container containing an acid solution and stirred. As a result, the metal containing indium adhering to the fragments is dissolved in the acid solution. In particular, in the present embodiment, since the liquid crystal recovery step S2 is performed first, the alignment films 4a and 4b provided on the transparent electrodes 7 and 10 containing the ink are removed ( Or partly peeled). For this reason, the acid solution is likely to come into contact with the transparent electrodes 7 and 10, and indium can be efficiently dissolved.
[0070] なお、この工程で使用する酸溶液は、インジウムを溶解する酸溶液であればよく特 に限定されるものではない。このような酸溶液としては、例えば、塩酸を主成分とする 溶液を用いることが好ましく、特に塩酸と硝酸との混合溶液を用いることが好まし 、。 塩酸と硝酸との混合用液を用いた場合には、インジウムの溶解を室温で行うことがで きる。  [0070] The acid solution used in this step is not particularly limited as long as it is an acid solution that dissolves indium. As such an acid solution, for example, a solution containing hydrochloric acid as a main component is preferably used, and a mixed solution of hydrochloric acid and nitric acid is particularly preferable. When a liquid for mixing hydrochloric acid and nitric acid is used, indium can be dissolved at room temperature.
[0071] 破碎片に付着して!/、たインジウムは、酸溶液に塩化物 (塩化インジウム)として溶解 する。また、酸溶液には、インジウムの他にも、例えばアルミニウム、チタン、モリブデ ンと 、つた破砕片に付着して 、る金属が溶解する。 [0071] Indium adhering to the debris dissolves in the acid solution as chloride (indium chloride). In addition to indium, the acid solution may be aluminum, titanium, molybdenum, for example. Then, the metal that adheres to the crushed pieces dissolves.
[0072] 次いで、インジウム等の金属が溶解した酸溶液力 破砕片を除去する(固液分離) 。これは、例えば濾過によって行うことができる。これにより、容器内には金属含有酸 溶液が残る。その後、破砕片が除去された金属含有酸溶液を、インジウム用イオン吸 着榭脂 (榭脂)に通過させる。このインジウム用イオン吸着樹脂とは、インジウムだけを 選択的に吸着する榭脂である。すなわち、酸溶液中のインジウムは、インジウム用ィ オン吸着樹脂に吸着され、他の金属はそのまま通過することとなる。従って、金属含 有酸溶液をインジウム用イオン吸着樹脂に通過させることにより、インジウムと他の金 属とを分離することができる (インジウム分離)。  [0072] Next, an acid solution force fragment in which a metal such as indium is dissolved is removed (solid-liquid separation). This can be done, for example, by filtration. As a result, the metal-containing acid solution remains in the container. Thereafter, the metal-containing acid solution from which the crushed pieces have been removed is passed through an indium ion-absorbing resin (resin). This ion adsorption resin for indium is a resin that selectively adsorbs only indium. That is, indium in the acid solution is adsorbed by the ion adsorption resin for indium, and other metals pass through as they are. Therefore, indium and other metals can be separated by passing the metal-containing acid solution through the ion adsorption resin for indium (indium separation).
[0073] そして、インジウム用イオン吸着榭脂に金属含有酸溶液を通過させた後に水を通 過させる。すなわち、インジウムのみが吸着されたインジウム用イオン吸着樹脂に水 を流す。これにより、榭脂に吸着されていたインジウムが水酸ィ匕物 (水酸化インジウム )として流出する。この流出液を回収することにより、インジウムが溶解した溶液 (イン ジゥム回収液)を回収することができる。このインジウム回収液に水酸ィ匕ナトリウム等の アルカリを添加して中和し(中和溶液)、無水硫酸ナトリウム等で脱水することにより、 インジウムスラッジ(固形の水酸化インジウム)を得ることができる。  [0073] Then, the metal-containing acid solution is passed through the ion adsorption resin for indium, and then water is passed through. That is, water is allowed to flow through an indium ion adsorption resin in which only indium is adsorbed. As a result, the indium adsorbed on the resin flows out as hydroxide (indium hydroxide). By collecting the effluent, a solution in which indium is dissolved (indium recovery solution) can be recovered. An indium sludge (solid indium hydroxide) can be obtained by adding an alkali such as sodium hydroxide to the indium recovery solution to neutralize it (neutralizing solution) and dehydrating with anhydrous sodium sulfate or the like. .
[0074] この方法によれば、破砕片力ゝら酸溶液に溶解したインジウムを濃縮することができる と共に、高純度のインジウムを回収することができる。  [0074] According to this method, it is possible to concentrate indium dissolved in the acid solution from the crushed piece, and to collect high-purity indium.
[0075] 次に、ガラス回収工程 S4を行う。ガラス回収工程 S4は、インジウム回収工程 S3に て金属が除去された後の破砕片を回収する工程である。すなわち、この工程で回収 されるガラスは、液晶回収工程 S2にて有機物が除去され、インジウム回収工程 S3に て金属が除去された後の破砕片であり、廃液晶パネル 30に付着して ヽた各種材料 が取り除かれた状態のガラスである。  [0075] Next, a glass recovery step S4 is performed. The glass recovery step S4 is a step of recovering the crushed pieces after the metal is removed in the indium recovery step S3. In other words, the glass recovered in this step is a crushed piece after the organic matter is removed in the liquid crystal recovery step S2 and the metal is removed in the indium recovery step S3, and it adheres to the waste liquid crystal panel 30. Glass with various materials removed.
[0076] ガラス回収工程 S4では、上記インジウム回収工程 S3にて固液分離した際の破砕 片を回収し、破砕片を洗浄し乾燥する。これにより、各種材料の付着していないガラ スを得ることができる。すなわち、上記液晶回収工程 S2およびインジウム回収工程 S 3をこの順で行うだけで、結果物として各種材料の付着して!/、な ヽガラスを得ることが でき、さらに、このガラスを洗浄し乾燥するだけで清浄なガラスカレットを得ることがで きる。 [0076] In the glass recovery step S4, the crushed pieces obtained after the solid-liquid separation in the indium recovery step S3 are recovered, and the crushed pieces are washed and dried. As a result, it is possible to obtain glass to which various materials are not attached. That is, by simply performing the liquid crystal recovery step S2 and the indium recovery step S3 in this order, various materials can be adhered as a result! /, And a dark glass can be obtained. Further, the glass is washed and dried. Just to get a clean glass cullet. wear.
[0077] なお、上記液晶回収工程 S2では、液晶の回収を行うことに加えて、液晶以外の有 機物の回収を行ってもよい。この場合、回収すべき有機物毎の沸点の違いを利用し た分留を行うことで各有機物を効率的に回収することができる。また、インジウム回収 工程 S3では、インジウムの回収を行うことに加えて、インジウム以外の金属の回収を 行ってもよい。この場合には、インジウム以外の回収する金属の種類に応じて、その 金属専用の吸着榭脂を用いることによって回収することができる。  [0077] In the liquid crystal recovery step S2, in addition to recovering the liquid crystal, organic matter other than the liquid crystal may be recovered. In this case, each organic substance can be efficiently recovered by performing fractional distillation using the difference in boiling point of each organic substance to be recovered. In addition, in the indium recovery step S3, in addition to recovering indium, metals other than indium may be recovered. In this case, according to the type of metal to be recovered other than indium, it can be recovered by using an adsorption resin dedicated to that metal.
[0078] 以上により、液晶パネルを廃棄処分する際においても、この廃液晶パネルに残され た各種材料 (液晶等の有機物、インジウム等の金属、ガラス)を回収することが可能に なり、廃棄物を殆ど出すことのない処理方法を実現することができる。  [0078] As described above, even when the liquid crystal panel is disposed of, various materials (organic substances such as liquid crystal, metals such as indium and glass) remaining on the waste liquid crystal panel can be recovered, and the waste Can be realized.
[0079] なお、本発明は、一対のガラス基板と、該ガラス基板間に挟持された液晶層と、各 ガラス基板の液晶層との対向面側に設けられた透明電極と、対向面とは反対側に設 けられた偏光板とを有する廃液晶パネルの処理方法であって、上記廃液晶パネルを 破砕する破砕工程と、破砕された廃液晶パネルに含まれる液層を回収する液晶回収 工程と、破砕された廃液晶パネルに含まれるインジウムを回収するインジウム回収ェ 程と、液晶およびインジウムを回収した後の廃液晶パネルに含まれるガラスを回収す るガラス回収工程とをこの順で行う廃液晶パネルの処理方法と表現することもできる。  [0079] It should be noted that the present invention includes a pair of glass substrates, a liquid crystal layer sandwiched between the glass substrates, a transparent electrode provided on the facing surface side of the liquid crystal layer of each glass substrate, and the facing surface. A method for treating a waste liquid crystal panel having a polarizing plate provided on the opposite side, the crushing step for crushing the waste liquid crystal panel, and the liquid crystal recovery step for collecting a liquid layer contained in the crushed waste liquid crystal panel And an indium recovery process for recovering indium contained in the crushed waste liquid crystal panel, and a glass recovery process for recovering liquid crystal and glass contained in the waste liquid crystal panel after recovering indium in this order. It can also be expressed as a liquid crystal panel processing method.
[0080] また、本実施の形態では、破砕工程、液晶回収工程、インジウム回収工程およびガ ラス回収工程をこの順で行っているが、本発明は、例えば、破砕工程および液晶回 収工程のみをこの順で行うこともでき、破砕工程およびインジウム回収工程のみをこ の順で行うこともできる。さらに、破砕工程、液晶回収工程およびガラス回収工程のみ をこの順で行うこともでき、破砕工程、インジウム回収工程およびガラス回収工程のみ をこの順で行うこともできる。また、ガラス回収工程を、インジウム回収工程で個液分 離した時点から開始してもよ 、。  [0080] In the present embodiment, the crushing step, the liquid crystal recovery step, the indium recovery step, and the glass recovery step are performed in this order. However, in the present invention, for example, only the crushing step and the liquid crystal recovery step are performed. It can also be performed in this order, and only the crushing process and the indium recovery process can be performed in this order. Furthermore, only the crushing step, the liquid crystal recovery step, and the glass recovery step can be performed in this order, and only the crushing step, the indium recovery step, and the glass recovery step can be performed in this order. In addition, the glass recovery process may be started from the time when the individual liquid is separated in the indium recovery process.
[0081] また、本実施の形態では、廃パネルとして廃液晶パネルにっ 、て説明した力 れに 限定されるものではない。本発明は、例えば、プラズマディスプレイパネル、無機 EL ( Electro Luminescence)パネル、有機 ELパネル等の廃棄処分された廃フラットデイス プレイパネルにも適用することができる。 [0082] 本発明は上述した実施形態に限定されるものではなぐ請求の範囲に示した範囲 で種々の変更が可能である。すなわち、請求の範囲に示した範囲で適宜変更した技 術的手段を組み合わせて得られる実施形態についても本発明の技術的範囲に含ま れる。 In the present embodiment, the waste liquid crystal panel is not limited to the force described above as the waste panel. The present invention can also be applied to discarded flat display panels such as plasma display panels, inorganic EL (Electro Luminescence) panels, and organic EL panels. The present invention is not limited to the above-described embodiments, and various modifications can be made within the scope shown in the claims. In other words, embodiments obtained by combining technical means appropriately changed within the scope of the claims are also included in the technical scope of the present invention.
[0083] 本発明に係る廃パネルの処理方法は、以上のように、廃パネルを破砕する破砕ェ 程と、上記媒質を回収する媒質回収工程と、上記電極に含有されている材料を回収 する電極材料回収工程と、上記ガラスを回収するガラス回収工程とをこの順で行うの で、廃パネルの処理を容易に行うことができると共に、廃棄物が殆ど出ることなぐ省 エネルギーであると 、つた環境負荷の小さ!/、廃パネルの処理方法を実現することが できるという効果を奏する。  [0083] The waste panel processing method according to the present invention, as described above, recovers the material contained in the electrode, the crushing step of crushing the waste panel, the medium recovery step of recovering the medium. Since the electrode material recovery process and the glass recovery process for recovering the glass are performed in this order, the waste panel can be easily processed and energy saving is achieved with almost no waste. There is an effect that the environmental load is small! / And the processing method of the waste panel can be realized.
[0084] また、本発明に係る廃パネルの処理装置は、以上のように、回転式破砕手段は、平 面状の破砕部を複数有しており、上記複数の破砕部は、少なくとも 2つの破砕部の平 面が異なる方向を向くように配置されているので、廃パネルを効率的に破砕すること ができる。  [0084] Further, in the waste panel processing apparatus according to the present invention, as described above, the rotary crushing means has a plurality of flat crushing sections, and the plurality of crushing sections include at least two crushing sections. Since the plane of the crushing part is arranged in different directions, the waste panel can be efficiently crushed.
[0085] 本発明に係る廃パネルの処理方法では、上記破砕工程では、一定の間隔で配置 された回転式破砕手段および固定式破砕手段を有する破砕機を用いて廃パネルを 破砕することが好ましい。上記の構成によれば、回転式破砕手段と固定式破砕手段 とを有する破砕機を用いることにより、偏光板の付 、た状態の廃パネルを破砕するこ とがでさる。  In the waste panel processing method according to the present invention, in the crushing step, it is preferable to crush the waste panel using a crusher having a rotary crushing means and a fixed crushing means arranged at regular intervals. . According to the above configuration, by using a crusher having a rotary crushing means and a fixed crushing means, it is possible to crush the waste panel with the polarizing plate attached.
[0086] なお、回転式破砕手段は、ある回転軸を中心にして回転しており、この回転式破砕 手段と固定式破砕手段とが交錯する部分に廃パネルを投入することによって、廃パ ネルが破砕されるようになっている。これにより、処理すべき廃パネルに対して何らか の加工を施す必要がないため、廃パネルの処理が容易になる。また、各刃際手段が 一定の間隔で配置されているため、この間隔を適宜設定することにより、廃パネルを 所望の大きさ (後工程での処理が容易となる大きさ)に破砕することができる。  [0086] Note that the rotary crushing means rotates around a certain rotation axis, and a waste panel is inserted into a portion where the rotary crushing means and the stationary crushing means cross each other. Is to be crushed. As a result, it is not necessary to perform any processing on the waste panel to be processed, so that the waste panel can be easily processed. In addition, since the cutting edge means are arranged at a constant interval, the waste panel can be crushed to a desired size (a size that facilitates subsequent processing) by setting this interval as appropriate. Can do.
[0087] 本発明に係る廃パネルの処理方法では、上記破砕工程では、偏光板を破り、ガラ ス基板を砕くことが好ましい。上記の構成によれば、偏光板がガラス基板に付いた状 態の廃パネルであっても確実に破砕することが可能になる。 [0088] 本発明に係る廃パネルの処理方法では、上記媒質回収工程では、上記媒質を溶 解させる溶剤を用いて該媒質を回収することが好ましい。上記の構成によれば、媒質 の回収を容易に行うことができると共に、省エネルギーに貢献することができる。 In the waste panel treatment method according to the present invention, in the crushing step, it is preferable to break the polarizing plate and crush the glass substrate. According to said structure, even if it is a waste panel with the polarizing plate attached to the glass substrate, it can be reliably crushed. In the waste panel treatment method according to the present invention, in the medium recovery step, it is preferable to recover the medium using a solvent that dissolves the medium. According to the above configuration, the medium can be easily collected and can contribute to energy saving.
[0089] 本発明に係る廃パネルの処理方法では、上記電極材料回収工程では、上記電極 に含有されている材料をィ匕学的に回収することが好ましい。上記の構成によれば、電 極材料の回収を容易に行うことができると共に、省エネルギーに貢献することができ る。  [0089] In the waste panel treatment method according to the present invention, in the electrode material recovery step, it is preferable to recover the material contained in the electrode. According to the above configuration, the electrode material can be easily collected and can contribute to energy saving.
[0090] 本発明に係る廃パネルの処理方法では、上記電極材料回収工程では、上記電極 に含有されて 、る材料を酸溶液に溶解させて回収することが好ま ヽ。上記の構成 によれば、常温で電極材料の回収を行うことができるため、容易に回収することがで きると共に、省エネルギーに貢献することができる。  In the waste panel treatment method according to the present invention, in the electrode material recovery step, it is preferable to recover the material contained in the electrode by dissolving it in an acid solution. According to the above configuration, the electrode material can be recovered at room temperature, so that it can be easily recovered and can contribute to energy saving.
[0091] 本発明に係る廃パネルの処理方法では、上記電極材料回収工程では、上記電極 に含有されて 、る材料のみを吸着する榭脂を用いて該材料を回収することが好まし い。上記の構成によれば、電極材料とは異なる物質が存在する場合であっても電極 材料だけを確実に回収することが可能になり、電極材料の回収を容易に行うことがで きると共に、省エネルギーに貢献することができる。  In the waste panel treatment method according to the present invention, in the electrode material recovery step, it is preferable to recover the material by using a resin that is contained in the electrode and adsorbs only the material. According to the above configuration, it is possible to reliably recover only the electrode material even when a substance different from the electrode material is present, and it is possible to easily recover the electrode material and to save energy. Can contribute.
[0092] 本発明に係る廃パネルの処理方法では、上記媒質が液晶であることが好ましい。  In the waste panel processing method according to the present invention, the medium is preferably a liquid crystal.
上記の構成によれば、高価な材料である液晶を回収することができるため、環境的に 有利になると共に、経済的にも有利となる。  According to the above configuration, liquid crystal that is an expensive material can be recovered, which is environmentally advantageous and economically advantageous.
[0093] 本発明に係る廃パネルの処理方法では、上記電極に含有されている材料がインジ ゥムであることが好ましい。上記の構成によれば、稀少金属であるインジウムを回収す ることができるため、環境的に有利になると共に、経済的にも有利となる。  [0093] In the method for treating a waste panel according to the present invention, the material contained in the electrode is preferably indium. According to the above configuration, indium, which is a rare metal, can be recovered, which is environmentally advantageous and economically advantageous.
[0094] 本発明に係る廃パネルの処理装置では、上記回転式破砕手段は、上記平面が異 なる方向となるように配置された複数の破砕部を 1単位とすると、複数単位の破砕部 が繰り返し配置されて 、ることが好まし 、。  [0094] In the waste panel processing apparatus according to the present invention, the rotary crushing means includes a plurality of crushing units arranged so that the planes are in different directions as one unit. It is preferred to be placed repeatedly.
[0095] 上記の構成によれば、上記平面が異なる方向を向くように配置された複数の破砕 部が、さらに複数単位で設けられている。すなわち、上記の構成は、平面が異なる方 向を向くように配置された、いくつかの破砕部が繰り返し設けられている構成となって おり、同じ傾きの破砕部が一定の間隔で繰り返し配置されている構成である。これに より、廃パネルをより効率的に破砕することができる。 [0095] According to the above configuration, the plurality of crushing portions arranged so that the planes face in different directions are further provided in a plurality of units. In other words, the above configuration is a configuration in which several crushing portions are arranged repeatedly so that the planes face in different directions. And the crushing part of the same inclination is the structure arrange | positioned repeatedly by the fixed space | interval. As a result, the waste panel can be crushed more efficiently.
[0096] 本発明に係る廃パネルの処理装置では、上記複数の破砕部は、回転式破砕手段 の回転軸方向に沿って設けられていることが好ましい。上記の構成によれば、これら 複数の破砕部が回転式破砕手段の回転軸方向に沿って設けられていることから、回 転式破砕手段と固定式破砕手段との間隔を適切な間隔に保つことが可能になり、廃 パネルをより効率的に破砕することができる。  [0096] In the waste panel processing apparatus according to the present invention, the plurality of crushing sections are preferably provided along the rotation axis direction of the rotary crushing means. According to the above configuration, since the plurality of crushing portions are provided along the rotation axis direction of the rotary crushing means, the interval between the rotary crushing means and the fixed crushing means is kept at an appropriate interval. And waste panels can be crushed more efficiently.
[0097] 本発明に係る廃パネルの処理装置では、上記廃パネルは、一対のガラス基板と、 少なくとも一方のガラス基板の対向面とは反対側に配置された偏光板とを有しており 、上記回転式破砕手段と固定式破砕手段とによって偏光板を破り、ガラス基板を砕く ことが好ましい。上記の構成によれば、偏光板がガラス基板に付いた状態の廃パネ ルであっても確実に破砕することが可能になる。  [0097] In the waste panel processing apparatus according to the present invention, the waste panel has a pair of glass substrates and a polarizing plate disposed on the side opposite to the facing surface of at least one glass substrate. It is preferable that the polarizing plate is broken by the rotary crushing means and the fixed crushing means to crush the glass substrate. According to the above configuration, even a waste panel with a polarizing plate attached to a glass substrate can be reliably crushed.
[0098] 尚、発明を実施するための最良の形態の項においてなした具体的な実施態様また は実施例は、あくまでも、本発明の技術内容を明らかにするものであって、そのような 具体例にのみ限定して狭義に解釈されるべきものではなぐ本発明の精神と次に記 載する特許請求の範囲内で、いろいろと変更して実施することができるものである。 産業上の利用の可能性  [0098] It should be noted that the specific embodiments or examples made in the section of the best mode for carrying out the invention are merely to clarify the technical contents of the present invention. Various modifications can be made within the spirit of the present invention and the following claims, which should not be construed as narrowly limited to only examples. Industrial applicability
[0099] 以上のように、本発明の廃パネルの処理装置および廃パネルの処理方法は、廃棄 物を殆ど出すことなく省エネルギーで廃パネルを処理することができるものであり、例 えば、テレビやパソコンのモニタ等の画像表示装置を廃棄する際に処理する方法とし て広く適用することができる。従って、本発明は、画像表示装置を製造する産業分野 や、廃棄物を処理する産業分野等に好適に用いることができる。 [0099] As described above, the waste panel processing apparatus and waste panel processing method of the present invention can process waste panels with little energy consumption, for example, for televisions and the like. It can be widely applied as a processing method when disposing of image display devices such as personal computer monitors. Therefore, the present invention can be suitably used in an industrial field for manufacturing an image display device, an industrial field for processing waste, and the like.

Claims

請求の範囲 The scope of the claims
[1] 一対のガラス基板と、該一対のガラス基板間に挟持され、電圧の印加により光学変 調する媒質力 なる媒質層と、少なくとも一方のガラス基板の媒質層との対向面側に 配置された電極と、少なくとも一方のガラス基板の媒質層との対向面とは反対側に配 置された偏光板とを有する廃パネルの処理方法であって、  [1] A pair of glass substrates, a medium layer that is sandwiched between the pair of glass substrates and optically modulates by applying a voltage, and is disposed on a surface facing the medium layer of at least one glass substrate. And a polarizing plate disposed on the opposite side of the surface facing the medium layer of at least one glass substrate,
上記廃パネルを破砕する破砕工程と、  Crushing step of crushing the waste panel;
上記媒質を回収する媒質回収工程と、  A medium recovery step for recovering the medium;
上記電極に含有されている材料を回収する電極材料回収工程と、  An electrode material recovery step of recovering the material contained in the electrode;
上記ガラスを回収するガラス回収工程とをこの順で行うことを特徴とする廃パネルの 処理方法。  A method for treating a waste panel, wherein the glass collecting step for collecting the glass is performed in this order.
[2] 上記破砕工程では、一定の間隔で配置された回転式破砕手段および固定式破砕 手段を有する破砕機を用いて廃パネルを破砕することを特徴とする請求の範囲 1に 記載の廃パネルの処理方法。  [2] The waste panel according to claim 1, wherein in the crushing step, the waste panel is crushed using a crusher having a rotary crushing means and a fixed crushing means arranged at regular intervals. Processing method.
[3] 上記破砕工程では、偏光板を破り、ガラス基板を砕くことを特徴とする請求の範囲 2 に記載の廃パネルの処理方法。 [3] The method for treating a waste panel according to claim 2, wherein, in the crushing step, the polarizing plate is broken to crush the glass substrate.
[4] 上記媒質回収工程では、上記媒質を溶解させる溶剤を用いて該媒質を回収するこ とを特徴とする請求の範囲 1ないし 3のいずれか 1項に記載の廃パネルの処理方法。 [4] The method for treating a waste panel according to any one of claims 1 to 3, wherein, in the medium recovery step, the medium is recovered using a solvent that dissolves the medium.
[5] 上記電極材料回収工程では、上記電極に含有されている材料を化学的に回収す ることを特徴とする請求の範囲 1ないし 4のいずれか 1項に記載の廃パネルの処理方 法。 [5] The method for treating a waste panel according to any one of claims 1 to 4, wherein in the electrode material recovery step, the material contained in the electrode is chemically recovered. .
[6] 上記電極材料回収工程では、上記電極に含有されている材料を酸溶液に溶解さ せて回収することを特徴とする請求の範囲 1ないし 5のいずれか 1項に記載の廃パネ ルの処理方法。  [6] The waste panel according to any one of claims 1 to 5, wherein in the electrode material recovery step, the material contained in the electrode is recovered by being dissolved in an acid solution. Processing method.
[7] 上記電極材料回収工程では、上記電極に含有されている材料のみを吸着する榭 脂を用いて該材料を回収することを特徴とする請求の範囲 1ないし 6のいずれか 1項 に記載の廃パネルの処理方法。  [7] The electrode material recovery step according to any one of claims 1 to 6, wherein the material is recovered using a resin that adsorbs only the material contained in the electrode. Of disposing of waste panels.
[8] 上記媒質が液晶であることを特徴とする請求の範囲 1ないし 7のいずれか 1項に記 載の廃パネルの処理方法。 [8] The method for treating a waste panel according to any one of claims 1 to 7, wherein the medium is a liquid crystal.
[9] 上記電極に含有されて!、る材料力インジウムであることを特徴とする請求の範囲 1 な!、し 8の!、ずれか 1項に記載の廃パネルの処理方法。 [9] It is contained in the electrode !, and the material strength is indium. The waste panel processing method described in 1 above.
[10] 一対のガラス基板と、該一対のガラス基板間に挟持され、電圧の印加により光学変 調する媒質力 なる媒質層と、少なくとも一方のガラス基板の媒質層との対向面側に 配置された電極と、少なくとも一方のガラス基板の媒質層との対向面とは反対側に配 置された偏光板とを有する廃パネルの処理方法であって、 [10] A pair of glass substrates, a medium layer that is sandwiched between the pair of glass substrates and optically modulates by applying a voltage, and is disposed on the opposite surface side of the medium layer of at least one glass substrate. And a polarizing plate disposed on the opposite side of the surface facing the medium layer of at least one glass substrate,
上記廃パネルを破砕する破砕工程と、  Crushing step of crushing the waste panel;
上記媒質を回収する媒質回収工程とをこの順で行うことを特徴とする廃パネルの処 理方法。  A waste panel processing method comprising performing a medium recovery step of recovering the medium in this order.
[11] 一対のガラス基板と、該一対のガラス基板間に挟持され、電圧の印加により光学変 調する媒質力 なる媒質層と、少なくとも一方のガラス基板の媒質層との対向面側に 配置された電極と、少なくとも一方のガラス基板の媒質層との対向面とは反対側に配 置された偏光板とを有する廃パネルの処理方法であって、  [11] A pair of glass substrates, a medium layer that is sandwiched between the pair of glass substrates and optically modulates by applying a voltage, and is disposed on the opposite surface side of the medium layer of at least one glass substrate. And a polarizing plate disposed on the opposite side of the surface facing the medium layer of at least one glass substrate,
上記廃パネルを破砕する破砕工程と、  Crushing step of crushing the waste panel;
上記電極に含有されている材料を回収する電極材料回収工程とをこの順で行うこと を特徴とする廃パネルの処理方法。  A method for treating a waste panel, comprising performing an electrode material recovery step of recovering a material contained in the electrode in this order.
[12] 回転式破砕手段と固定式破砕手段とを備えた廃パネルの処理装置であって、 上記回転式破砕手段は、平面状の破砕部を複数有しており、 [12] A waste panel processing apparatus comprising a rotary crushing means and a fixed crushing means, wherein the rotary crushing means has a plurality of flat crushing portions,
上記複数の破砕部は、少なくとも 2つの破砕部の平面が異なる方向を向くように配 置されて!ヽることを特徴とする廃パネルの処理装置。  The waste panel processing apparatus, wherein the plurality of crushing parts are arranged such that at least two crushing parts have different planes.
[13] 上記回転式破砕手段は、上記平面が異なる方向を向くように配置された複数の破 砕部を 1単位とすると、複数単位の破砕部が繰り返し配置されて ヽることを特徴とする 請求の範囲 12に記載の廃パネルの処理装置。 [13] The rotary crushing means is characterized in that a plurality of crushing parts are repeatedly arranged when the plurality of crushing parts arranged so that the planes face in different directions are one unit. The waste panel processing apparatus according to claim 12.
[14] 上記複数の破砕部は、回転式破砕手段の回転軸方向に沿って設けられていること を特徴とする請求の範囲 12または 13に記載の廃パネルの処理装置。 14. The waste panel processing apparatus according to claim 12, wherein the plurality of crushing portions are provided along a rotation axis direction of the rotary crushing means.
[15] 上記廃パネルは、一対のガラス基板と、少なくとも一方のガラス基板の対向面とは 反対側に配置された偏光板とを有しており、 [15] The waste panel includes a pair of glass substrates and a polarizing plate disposed on the side opposite to the facing surface of at least one glass substrate,
上記回転式破砕手段と固定式破砕手段とによって偏光板を破り、ガラス基板を砕く :とを特徴とする請求の範囲 12ないし 14のいずれ力 1項に記載の廃パネルの処理 The polarizing plate is broken by the rotary crushing means and the fixed crushing means, and the glass substrate is broken. The processing of the waste panel according to any one of claims 12 to 14, characterized by:
PCT/JP2006/308075 2005-04-25 2006-04-17 Treatment apparatus for waste panel and method for treating waste panel WO2006115105A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP2005-127130 2005-04-25
JP2005127130 2005-04-25

Publications (1)

Publication Number Publication Date
WO2006115105A1 true WO2006115105A1 (en) 2006-11-02

Family

ID=37214726

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/JP2006/308075 WO2006115105A1 (en) 2005-04-25 2006-04-17 Treatment apparatus for waste panel and method for treating waste panel

Country Status (1)

Country Link
WO (1) WO2006115105A1 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010089075A (en) * 2008-08-11 2010-04-22 Ind Technol Res Inst Method of recovering liquid crystal from waste lcd panel
JP2012125693A (en) * 2010-12-15 2012-07-05 Sharp Corp Separation recovery apparatus and recycling method of liquid crystal panel

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002254059A (en) * 2001-02-28 2002-09-10 Mitsubishi Materials Corp Material recovery method from liquid crystal display panel

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002254059A (en) * 2001-02-28 2002-09-10 Mitsubishi Materials Corp Material recovery method from liquid crystal display panel

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010089075A (en) * 2008-08-11 2010-04-22 Ind Technol Res Inst Method of recovering liquid crystal from waste lcd panel
JP2012125693A (en) * 2010-12-15 2012-07-05 Sharp Corp Separation recovery apparatus and recycling method of liquid crystal panel

Similar Documents

Publication Publication Date Title
JP4651506B2 (en) Liquid crystal panel processing method and processing apparatus
JP2012125693A (en) Separation recovery apparatus and recycling method of liquid crystal panel
Götze et al. Challenges for the recovery of critical metals from waste electronic equipment-A case study of indium in LCD panels
JP3589937B2 (en) Waste LCD panel treatment method
JP5100156B2 (en) Method for recovering glass substrates of waste liquid crystal panels
JP2011245379A (en) Method for recycling of liquid crystal panel
TW200537169A (en) Use of liquid-crystal displays, and processes for the recycling thereof
WO2006115105A1 (en) Treatment apparatus for waste panel and method for treating waste panel
CN114798693A (en) Waste photovoltaic module recovery method based on supercritical fluid
JP4918839B2 (en) Disposal of display panel waste
Chinnam et al. Leaching indium from discarded LCD glass: A rapid and environmentally friendly process
JP6000617B2 (en) Flat panel recycling method
JP3506217B2 (en) LCD panel disposal
JP3589936B2 (en) Waste LCD panel treatment method
JP3381234B2 (en) Detoxification and recycling of LCD equipment products
JP4374772B2 (en) Liquid crystal recovery method
JP3205732B2 (en) Harmless Recycling and Harmless Disposal of Flat Panel Displays
JP2011224475A (en) Method of recycling liquid crystal panel and apparatus for separating and recovering glass
JP3516864B2 (en) Waste LCD panel treatment method
JP4374770B2 (en) Recycling method of liquid crystal panel
JP2001235718A (en) Method for recycling treatment of liquid crystal panel and system for recycling treatment
JP2002239833A (en) Disposing device of waste liquid crystal panel and its disposing method using it
JP2012239974A (en) Method for recycling glass formed with film
JP2001296508A (en) Method for processing waste liquid crystal panel
CN111633002A (en) Method and device for recovering glass substrate and polarizing film in waste liquid crystal display

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application
NENP Non-entry into the national phase

Ref country code: DE

NENP Non-entry into the national phase

Ref country code: RU

122 Ep: pct application non-entry in european phase

Ref document number: 06732004

Country of ref document: EP

Kind code of ref document: A1

NENP Non-entry into the national phase

Ref country code: JP