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WO2012120779A1 - Recycled resin evaluation device and method for producing recycled article from recycled resin - Google Patents

Recycled resin evaluation device and method for producing recycled article from recycled resin Download PDF

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Publication number
WO2012120779A1
WO2012120779A1 PCT/JP2012/000816 JP2012000816W WO2012120779A1 WO 2012120779 A1 WO2012120779 A1 WO 2012120779A1 JP 2012000816 W JP2012000816 W JP 2012000816W WO 2012120779 A1 WO2012120779 A1 WO 2012120779A1
Authority
WO
WIPO (PCT)
Prior art keywords
recycled resin
thickness
recycled
determination
resin
Prior art date
Legal status (The legal status 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 status listed.)
Ceased
Application number
PCT/JP2012/000816
Other languages
French (fr)
Japanese (ja)
Inventor
禎章 太田
間瀬 健一郎
将稔 宮坂
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Panasonic Corp
Original Assignee
Panasonic Corp
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 Panasonic Corp filed Critical Panasonic Corp
Publication of WO2012120779A1 publication Critical patent/WO2012120779A1/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/02Separating plastics from other materials
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/25Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
    • G01N21/31Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
    • G01N21/35Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light
    • G01N21/3563Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light for analysing solids; Preparation of samples therefor
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/25Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
    • G01N21/31Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
    • G01N21/35Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light
    • G01N21/359Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light using near infrared light
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/02Separating plastics from other materials
    • B29B2017/0203Separating plastics from plastics
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/02Separating plastics from other materials
    • B29B2017/0213Specific separating techniques
    • B29B2017/0279Optical identification, e.g. cameras or spectroscopy
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N2201/00Features of devices classified in G01N21/00
    • G01N2201/06Illumination; Optics
    • G01N2201/061Sources
    • G01N2201/06166Line selective sources
    • G01N2201/0618Halogene sources
    • 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
    • Y02W30/62Plastics recycling; Rubber recycling

Definitions

  • the present invention relates to a recycling apparatus for determining whether or not an object to be determined is a resin to be recycled, and a method for manufacturing a recycled resin recycled product.
  • a mixed plastic that is a mixture containing a plurality of resins such as polystyrene (hereinafter referred to as “PS”), polypropylene (hereinafter referred to as “PP”), acrylonitrile butadiene styrene (hereinafter referred to as ABS), and the like.
  • PS polystyrene
  • PP polypropylene
  • ABS acrylonitrile butadiene styrene
  • Recycled resin A technique for determining a resin to be recycled (hereinafter referred to as “recycled resin”) is disclosed in Patent Document 1. The conventional technique will be described with reference to FIG.
  • the determination apparatus 1 of the recycled resin which concerns on the prior art irradiates infrared light from the light source 4 with respect to the surface of the to-be-determined object 3 conveyed by the conveyance path 2, and is infrared from the surface of the to-be-determined object 3 Reflects light (hereinafter referred to as “infrared reflected light”).
  • the infrared reflected light reflected from the surface of the determination object 3 is imaged by the light receiving unit 7 via the mirror 5 and the polygon mirror 6.
  • the control device 8 compares the feature quantity of the infrared reflected light imaged by the light receiving unit 7 with the preset feature quantity of the recycled resin.
  • the recycled resin determination device 1 determines, for example, only PS as the recycled resin from the mixed plastic that is the determination target 3.
  • the recycled resin determination device when the object to be determined is a transparent resin, the recycled resin determination device according to the prior art also picks up the infrared reflected light from the conveyance path located below the object to be determined. In this case, the characteristic amount of the determination target acquired based on the captured infrared reflected light overlaps with the characteristic amount of the conveyance path as noise.
  • the present invention solves the above-described problems, and determines that the determination target, which is a transparent resin, is a recycling resin determination apparatus that determines whether the determination target resin is a recycling target resin, and a recycling target resin. It is an object of the present invention to provide a method for producing a recycled resin recycled product using an object to be determined.
  • the present invention is configured as follows in order to achieve the above object.
  • a transport device that transports a determination object that is a transparent resin; An infrared light source for irradiating the determination object with infrared light; An infrared light receiving unit that receives infrared reflected light from the object to be determined irradiated with the infrared light; and An absorption spectrum calculation unit for calculating an absorption spectrum of the object to be determined from the infrared reflected light received by the infrared light receiving unit; A thickness measuring unit for measuring a measurement thickness which is a thickness of the object to be determined; A storage unit that stores in advance reference data for different recycled resins for each thickness; Among the reference data, the reference data for the recycled resin having a thickness corresponding to the measured thickness measured by the thickness measurement unit is selected as selection reference data, and the selection reference data and the absorption spectrum calculation unit are calculated. And a determination unit that determines whether or not the determination target is the recycled resin based on the absorption spectrum.
  • the recycled resin determination device determines whether the determination object is the recycled resin.
  • a method for producing a recycled resin recycled product in which an article to be judged determined as the recycled resin is molded to produce a recycled resin recycled product.
  • the determination apparatus for recycled resin it is possible to determine whether or not the transparent resin is a resin to be recycled. Moreover, according to the manufacturing method of this recycled resin recycled product, it becomes possible to manufacture a recycled resin recycled product using the to-be-determined object determined to be a recycling target resin.
  • FIG. 1 is a schematic diagram of a recycled resin determination device according to the first embodiment.
  • FIG. 2 is a schematic diagram of a detection unit according to the first embodiment.
  • FIG. 3 is a diagram illustrating a graph of an absorption spectrum of a determination object having different thicknesses detected by the detection unit according to the first embodiment.
  • FIG. 4A is a block diagram illustrating an absorption spectrum calculation unit and a thickness measurement unit included in the detection unit and a storage unit and a determination unit included in the arithmetic processing unit in the recycled resin determination device according to the first embodiment. Yes, FIG.
  • FIG. 4B shows an absorption spectrum calculation unit and a thickness measurement unit included in the detection unit, and a reference data acquisition unit and a storage unit included in the arithmetic processing unit in the determination apparatus for recycled resin according to the modification of the first embodiment.
  • FIG. 5 is a flowchart showing a determination operation by the determination unit according to the first embodiment.
  • FIG. 6 is a graph showing an absorption spectrum obtained by subtracting noise detected when the thickness of the determination object is 2 mm or 3 mm from the absorption spectrum of the determination object having a thickness of 1 mm.
  • FIG. 7 is a graph showing an absorption spectrum obtained by subtracting noise detected when the thickness of the determination object is 1 mm from the absorption spectrum of the determination object having a thickness of 1.5 mm.
  • FIG. 8 is a flowchart showing the operation of the recycled resin determination apparatus according to the first embodiment.
  • FIG. 9 is a schematic diagram illustrating a first modification of the reference unit according to the first embodiment.
  • FIG. 10A is a block diagram showing a recycled resin recycled product manufacturing apparatus according to the second embodiment;
  • FIG. 10B is a cross-sectional view showing a manufacturing process of the manufacturing apparatus of the recycled resin recycled product according to the second embodiment.
  • FIG. 10C is a cross-sectional view showing the manufacturing process of the apparatus for manufacturing recycled resin recycled products according to the second embodiment, FIG.
  • FIG. 10D is a cross-sectional view illustrating the manufacturing process of the apparatus for manufacturing recycled resin recycled products according to the second embodiment
  • FIG. 10E is a perspective view showing a recycled molded product molded in the manufacturing process of the recycled resin recycled product manufacturing apparatus according to the second embodiment
  • FIG. 11 is a schematic diagram of a determination apparatus for recycled resin according to a conventional technique.
  • FIG. 1 is a schematic diagram of a recycled resin determination apparatus 100 according to the first embodiment.
  • a conveyor belt 101 which is an example of a transport device, is moving at a constant speed.
  • the determination object 103 is transported along the transport path in the longitudinal direction of the conveyor belt 101 from the input area 93A to the selection area 93C through the detection area 93B.
  • the determination target 103 is input.
  • the hopper 102 is an example of a loading unit that loads the determination target object 103 onto the conveyor belt 101.
  • a plurality of determination objects 103 stacked on the hopper 102 are sequentially input on the input region 93 ⁇ / b> A of the conveyor belt 101 with a certain interval.
  • the conveyor belt 101 is configured in black or a color close to black so that the light is not easily reflected even when the conveyor belt 101 is irradiated with light. Further, the conveyor belt 101 is made of a material (for example, vinyl chloride resin) different from the resin of the determination target 103 so that it can be easily distinguished from the determination target 103 at the time of determination.
  • a material for example, vinyl chloride resin
  • the conveyance speed of the object 103 to be determined by the conveyor belt 101 is 3 m / s, and the conveyance direction is the direction of arrow A shown in FIG.
  • the to-be-determined object 103 is a mixed plastic including a plurality of types of transparent resins, and includes a transparent recycled resin.
  • the determination target object 103 is, for example, a small piece having a side of about 5 mm to several tens of mm, and the thickness of each small piece is, for example, about 0.3 mm to 5.5 mm. That is, the determination target object 103 is a pulverized material and is composed of small pieces having a thickness that can be regarded as substantially constant.
  • the object 103 is irradiated with infrared light 105 ⁇ / b> A from the infrared light source 104, thereby reflecting infrared light that is a characteristic amount of each resin material as infrared reflected light 105.
  • the infrared light source 104 is disposed on both sides of the detection unit 106 disposed above the detection area 93 ⁇ / b> B of the conveyor belt 101 and in a space between the conveyor belt 101 and the detection unit 106.
  • a halogen lamp that irradiates infrared light (near infrared light) 105A in a broad wavelength band with a wavelength of 1360 to 2500 nm (a wavelength of 1360 nm to 2500 nm) is used.
  • the wavelength at which the light absorption phenomenon occurs varies depending on the type of resin, a feature amount is calculated based on the wavelength at which the light absorption phenomenon occurs, and an arithmetic processing unit determines whether the determination target 103 is a recycled resin using the calculated feature amount. The determination is made at 107.
  • the wavelength at which the light absorption phenomenon occurs can be obtained by the detection unit 106 from the absorption spectrum of the infrared reflected light 105 reflected by the determination target 103.
  • a laser light source may be used as the infrared light source 104 as an example.
  • the infrared reflected light 105 reflected by the determination object 103 is detected by the detection unit 106.
  • the detection result is converted into digital data by the detection unit 106 and then transferred from the detection unit 106 to the arithmetic processing unit 107.
  • the arithmetic processing unit 107 determines whether the determination target object 103 is a recycled resin based on the detection result of the detection unit 106.
  • a pulsed air nozzle 108 which is an example of a sorting unit that blows air onto an object 103 to be judged to be recycled resin (hereinafter referred to as “recycled resin 103a”) above a terminal portion that is a sorting region 93C of the conveyor belt 101.
  • an air supply source 95 are arranged. Based on an instruction from the arithmetic processing unit 107 or the control unit 97, the air supply source 95 is driven, air corresponding to the driving amount is blown out from the pulse air nozzle 108, and the recycled resin 103a is blown out.
  • the recycled resin 103a is stored in the recycling box 109.
  • a recycling resin 103a is stored in the recycling box 109.
  • the determination object 103 determined not to be recycled resin (hereinafter referred to as “non-recycled resin 103 b”) is stored in the non-recycle box 110 without being blown off by the pulse air nozzle 108.
  • the non-recycle box 110 is disposed adjacent to the recycle box 109. In this case, the non-recycle box 110 is disposed below the end portion of the conveyor belt 101 and at a position where the non-recycle resin 103b freely falls.
  • the position information of the determination object 103 is specified by a position calculation unit 94 connected to the control unit 97.
  • FIG. 2 is a diagram showing the detection unit 106 from the X-axis direction of FIG.
  • the detection unit 106 includes a thickness measurement unit 106a and an absorption spectrum calculation unit 106b.
  • the thickness measuring unit 106 a measures the thickness of the determination target object 103.
  • the absorption spectrum calculation unit 106 b calculates an absorption spectrum as a feature amount of the infrared reflected light 105 reflected by the determination target object 103.
  • the detection unit 106 irradiates the reference unit 112 and the object to be determined 103 with measurement light from the light source 111 for thickness measurement, and reflects from the light.
  • a function as an optical interferometer for measuring the thickness of the determination target object 103 is provided.
  • a Michelson interferometer configuration is used as the optical interferometer.
  • the thickness measurement light source 111 for example, a wavelength scanning optical coherence tomography device (hereinafter referred to as “SS-OCT”) is used.
  • SS-OCT wavelength scanning optical coherence tomography device
  • a silicon avalanche photodiode is used for the light receiving element 113 that receives light
  • light having a wavelength of 780 to 860 nm (wavelength of 780 nm or more and 860 nm or less) with which the light receiving element 113 is sensitive is measured by the light source 111 for thickness measurement.
  • Adopt for light.
  • the wavelength of the measurement light may be any wavelength other than the wavelength 1360 to 2500 nm irradiated by the infrared light source 104 shown in FIG.
  • the thickness may not be accurately measured with visible light (light with a wavelength of 380 or more and less than 780 nm) or light with a short wavelength (light with a wavelength of less than 380 nm). For these reasons, it is preferable to use light having a wavelength of 780 or more and less than 1360 nm as measurement light from the light source 111.
  • the measurement light emitted from the light source 111 for thickness measurement passes through the narrow band filter 114 and is divided into two lights described later by the beam splitter 115.
  • the narrow band filter 114 transmits light having a wavelength of 780 to 860 nm.
  • the light L ⁇ b> 1 (hereinafter referred to as “object light”) L ⁇ b> 1 irradiated to the object 103 or the conveyor belt 101 is reflected by the polygon mirror 116.
  • the object light L1 reflected by the polygon mirror 116 is irradiated to the determination target object 103 through the telecentric f ⁇ lens 117 and the wavelength filter 132.
  • the polygon mirror 116 enables scanning in the width direction (Y-axis direction) of the conveyor belt 101 by rotating itself. This scan enables detection of the object light L1 reflected from each scan point on the conveyor belt 101 (position where the object light L1 is irradiated).
  • the telecentric f ⁇ lens 117 has an f ⁇ function that equalizes the difference in scanning speed between the center and the periphery of the polygon mirror 116. In this case, a telecentric optical system is established between the telecentric f ⁇ lens 117 and the conveyor belt 101.
  • the telecentric f ⁇ lens 117 is thinned from the center to both ends on the conveyor belt 101 side.
  • a glass body (not shown) is installed. The glass body is based on the refractive index of the glass body so that the object light L1 reflected by the polygon mirror 116 is irradiated on the conveyor belt 101 with the same optical path length no matter what angle the light enters the telecentric f ⁇ lens 117.
  • the shape is designed.
  • the wavelength filter 132 may be configured so that the thickness thereof decreases from the center to both ends.
  • the object light L1 irradiated from the beam splitter 115 through the polygon mirror 116, the telecentric f ⁇ lens 117, and the wavelength filter 132 to the object to be determined 103 is reflected on the surface of the object to be determined 103, and travels backward on the same path. It enters the beam splitter 115 again.
  • reference light light different from the object light L ⁇ b> 1 (hereinafter referred to as “reference light”) L ⁇ b> 2 enters the reference unit 112 via the narrowband filter 118 and the condenser lens 119.
  • the narrow band filter 118 transmits light having a wavelength of 780 to 860 nm.
  • the reference unit 112 reflects the incident reference light L ⁇ b> 2 inside and then emits it again from the reference unit 112. Details of the reference unit 112 will be described later.
  • the object light L1 reflected from the surface of the determination object 103 and the reference light L2 emitted from the reference unit 112 are again incident on the beam splitter 115, and are combined into one light beam (that is, interference light). L3).
  • the interference light L3 is emitted from the beam splitter 115, reflected and diffracted by the diffraction grating 122, and dispersed at different angles for each wavelength.
  • the split interference light L3 is incident on the light receiving surface of the light receiving element 113 via the interference light condensing lens 123 and the narrow band filter 124.
  • the narrow band filter 124 transmits light having a wavelength of 780 to 860 nm.
  • the light receiving element 113 has a plurality of light receiving surfaces, and the interference light L3 dispersed by wavelength by the diffraction grating 122 is incident on each light receiving surface.
  • the light receiving element 113 photoelectrically converts the interference light L3 incident on each light receiving surface into a current.
  • the analog data converted into current is converted into digital data by the optical gain current-voltage conversion amplifier 125 and the high-speed AD conversion circuit 126.
  • the converted digital data is sent to the thickness measuring unit 106a.
  • the thickness of the determination target object 103 is measured by the thickness measurement unit 106a based on the wavelength of the light whose intensity is increased by the interference. In the following description, the measured thickness of the determination target object 103 is referred to as “measured thickness”.
  • Information on the measured thickness measured by the thickness measuring unit 106 a is sent to the arithmetic processing unit 107.
  • the narrow-band filters 114, 118, and 124 are installed to prevent light having a wavelength of 1360 to 2500 nm used for calculating an absorption spectrum from being incident as noise on light having a wavelength of 780 to 860 nm used for thickness measurement. Yes.
  • the infrared reflected light 105 reflected by the determination target object 103 enters the beam splitter 115 through the same path as the object light L1.
  • the infrared reflected light 105 incident on the beam splitter 115 enters the diffraction grating 122 through the same path as the interference light L3.
  • the diffraction grating 122 reflects and diffracts the incident interference light L3 and the infrared reflected light 105 at different angles for each wavelength.
  • the light having a wavelength of 780 to 860 nm, which is the interference light L3 enters the interference light condensing lens 123
  • the light having the wavelength of 1360 to 2500 nm, which is the infrared reflected light 105 enters the condensing lens 127 for the infrared light.
  • a diffraction grating 122, a condensing lens for interference light 123, and a condensing lens for infrared light 127 are arranged.
  • the infrared reflected light 105 incident on the infrared light condenser lens 127 passes through the infrared light narrowband filter 128 and enters the light receiving surface of the infrared light receiving unit 129.
  • the infrared narrowband filter 128 transmits light having a wavelength of 1360 to 2500 nm.
  • the infrared light receiving unit 129 has a plurality of light receiving surfaces, and the infrared reflected light 105 that is spectrally separated by the diffraction grating 122 for each wavelength is incident on each light receiving surface.
  • the infrared light receiving unit 129 photoelectrically converts the received infrared reflected light 105 into a current.
  • the analog data converted into current is converted into digital data by the optical gain current-voltage conversion amplifier 130 and the high-speed AD conversion circuit 131.
  • the converted digital data is sent to the absorption spectrum calculation unit 106b. At this time, the light intensity varies depending on the wavelength due to the light absorption phenomenon of the determination target object 103.
  • the absorption spectrum calculation unit 106b obtains the intensity distribution of the infrared reflected light 105 for each wavelength of the determination target object 103, and calculates the absorption spectrum. Information on the absorption spectrum calculated by the absorption spectrum calculation unit 106 b is sent to the arithmetic processing unit 107.
  • the wavelength filter 132 is disposed between the conveyor belt 101 and the telecentric f ⁇ lens 117, and shields light having a wavelength of less than 780 nm. This is because light having a wavelength other than 780 to 2500 nm used for thickness measurement or absorption spectrum calculation becomes noise. However, light exceeding a wavelength of 2500 nm has a large transmission loss in a general optical system made of resin or glass and is naturally filtered. Therefore, it is sufficient to shield light having a wavelength of less than 780 nm.
  • FIG. 3 shows, as an example, the measurement result of the absorption spectrum of the transparent PS object 103 having a thickness of 1 mm, 2 mm, and 3 mm.
  • the vertical axis represents absorbance and the horizontal axis represents wavelength ( ⁇ m).
  • These absorption spectra are calculated by an absorption spectrum calculation unit 106b provided in the detection unit 106 shown in FIG.
  • the absorption spectrum of the non-transparent PS object 103 is shown as a reference absorption spectrum (referred to as “reference” in FIG. 3). From FIG. 3, it can be seen that the transparent PS determination object 103 and the non-transparent PS determination object 103 show different absorption spectra.
  • the transparent PS has an absorption spectrum that changes depending on the thickness of the determination target object 103.
  • the reference absorption spectrum is constant regardless of the thickness of the resin.
  • the reference absorption spectrum is an absorption spectrum of a resin that does not transmit white light, and specifically means an absorbance obtained with a white resin with respect to a standard diffusion plate.
  • the infrared reflected light 105 reflected by the object 103 is conveyed below the object 103.
  • Infrared reflected light 105C reflected by the path (conveyor belt 101) overlaps. Therefore, when the infrared reflected light 105 reflected by the determination target 103 is received, the infrared reflected light 105C reflected from the conveyance path (conveyor belt 101) is also received.
  • the inventors have found that the influence of the infrared reflected light 105 ⁇ / b> C reflected from the conveyor belt 101 changes depending on the thickness of the determination target object 103. This can be understood from the results of FIG. That is, as a result of experiments by the inventors, it has become clear that the absorption spectrum of a transparent recycled resin changes depending on its thickness.
  • absorption spectra corresponding to each thickness are stored as reference data in the storage unit 107a of the arithmetic processing unit 107 in FIG. 4A described later.
  • the reference data of the recycled resin having a thickness corresponding to the measured thickness of the determination target object 103 is selected by the determination unit 107b of the arithmetic processing unit 107 described later.
  • the selected reference data is referred to as “selection reference data”.
  • the determination unit 107b can determine whether the determination target 103 is a recycled resin.
  • FIG. 4A shows a block diagram of the detection unit 106 and the arithmetic processing unit 107.
  • the arithmetic processing unit 107 includes a storage unit 107a and a determination unit 107b.
  • the storage unit 107a stores in advance a plurality of types of absorption spectra for each thickness of the transparent recycled resin as reference data.
  • the storage unit 107a also has a function as a reference data acquisition unit that acquires reference data.
  • the determination unit 107b determines whether the determination target 103 is a recycled resin. Do.
  • the measured thickness and absorption spectrum of the determination object 103 are respectively calculated by the thickness measurement unit 106a and the absorption spectrum calculation unit 106b provided in the detection unit 106, and input to the determination unit 107b.
  • reference data (selection reference data) for a recycled resin having a thickness equal to the measured thickness of the determination target object 103 input from the detection unit 106 is determined from a plurality of reference data stored in the storage unit 107a. The selection is made by the unit 107b (step S1). When there is no selection reference data having a thickness equal to the measured thickness of the object 103 to be determined, an allowable range is determined in advance, and thickness selection reference data that falls within the allowable range with respect to the measured thickness of the object 103 to be determined. You may make it select as selection reference data in the recycled resin of the thickness corresponding to the measured thickness of the to-be-determined object 103. FIG. This will be described later.
  • the determination unit 107b compares the absorption spectrum of the determination target 103 input from the detection unit 106 with the selection reference data, and the determination unit 107b determines the absorption spectrum of the determination target 103 (step S2). ). At this time, after the gain of the input absorption spectrum is adjusted by the determination unit 107b, spectrum leveling is performed by the determination unit 107b.
  • the determination unit 107b determines whether the determination object 103 is a recycled resin (step S3).
  • the determination unit 107b uses a chemometric technique that extracts necessary information from the feature amount of the absorption spectrum.
  • the chemometrics method is a method for estimating an effective result by an optimal processing method using a mathematical method or a statistical method from calculated multivariate data and multivariate data.
  • a linear multiple regression analysis method, a principal component analysis method, a PLS (Partial Last Squires) regression analysis method, or the like may be used in the determination unit 107b.
  • cluster analysis may be used, and among them, the Mahalanobis distance or the asymmetric Mahalanobis distance may be used in the determination unit 107b.
  • the recycled resin determination device 100 determines whether or not the determination target object 103 is recycled resin.
  • step S1 a case is described in which the reference data for the recycled resin having the same thickness as the measured thickness is selected as the selection reference data from among a plurality of reference data stored in the storage unit 107a.
  • the determination object 103 constituting the mixed plastic includes the determination objects 103 having various thicknesses. That is, in order to select reference data having a thickness equal to the measured thickness, a huge amount of reference data must be stored in the storage unit 107a in advance. If the amount of reference data to be handled becomes enormous, a burden is imposed on the determination unit 107b that selects specific reference data from among them. For this reason, the processing speed of the determination unit 107b may be reduced.
  • the inventors may select the selection criterion data by the determination unit 107b so that the difference between the thickness corresponding to the selection criterion data and the measured thickness of the determination target object 103 is 0.5 mm or less.
  • the difference between the thickness corresponding to the selection criterion data and the measured thickness of the determination target object 103 is 0.5 mm or less.
  • the inventors have found. This will be described based on experimental data.
  • the reference data is data including a reference absorption spectrum and noise corresponding to the thickness.
  • the noise refers to an absorption spectrum caused by reflected light (infrared reflected light 105) from the conveyance path (conveyor belt 101).
  • the noise changes due to the thickness. That is, if noise corresponding to the thickness of the resin is subtracted from the absorption spectrum of the resin whose thickness has been calculated, determination based only on the reference absorption spectrum that does not depend on the thickness becomes possible.
  • FIG. 6 shows an absorption spectrum obtained by subtracting noise corresponding to PS having a thickness of 2 mm and 3 mm from an absorption spectrum calculated for PS having a thickness of 1 mm, and a reference absorption spectrum of PS, respectively.
  • the vertical axis represents absorbance and the horizontal axis represents wavelength ( ⁇ m).
  • a peak is shown in a wavelength band of 1.763 ⁇ m.
  • the P1 region in FIG. 6 is where the peak of the PS absorption spectrum appears.
  • the absorption spectrum obtained by subtracting noise corresponding to PS having a thickness of 2 mm or 3 mm has a variation from the reference absorption spectrum, and therefore, the recycled resin cannot be accurately determined. From this, it can be understood that when there is a difference of 1 mm or more between the measured thickness of the determination target object 103 and the thickness corresponding to the noise included in the selection reference data, the determination cannot be performed with high accuracy.
  • FIG. 7 shows an absorption spectrum obtained by subtracting noise corresponding to PS having a thickness of 1 mm from the absorption spectrum calculated for PS having a thickness of 1.5 mm, and a reference absorption spectrum of PS, respectively.
  • the vertical axis represents absorbance and the horizontal axis represents wavelength ( ⁇ m).
  • the P2 region in FIG. 7 is where the peak of the PS absorption spectrum appears.
  • the inventors used the reference data in the recycled resin having a thickness within 0.5 mm as a difference from the measured thickness of the determination target object 103 as the selection reference data. The inventors have found that it is possible to determine whether the object 103 is a recycled resin.
  • the storage unit 107a in FIG. 4A may store reference data for recycled resin having a thickness of 1 mm. This is because the maximum difference between the thickness of the selection reference data and the measured thickness is 0.5 mm. Thereby, it is possible to reduce the amount of reference data to be stored in advance in the storage unit 107a. In addition, by providing an allowable range of 0.5 mm for the difference between the thickness of the selection reference data and the measured thickness in this way, the determination unit 107b also reduces the amount of reference data to be selected, so that it can process at high speed. Can be done.
  • the order of measuring the thickness of the object 103 to be determined may be 1 mm intervals. This is because if the thickness (measurement thickness) of the object to be determined 103 is measured at intervals of 1 mm, the difference between the measured thickness and the actual thickness of the object to be determined 103 is 0.5 mm or less.
  • the reference data for the recycled resin having a thickness corresponding to the measurement interval may be stored in the storage unit 107a.
  • a reference unit 112 shown in FIG. 2 will be described as means for measuring the measured thickness of the determination target object 103 at intervals of 1 mm.
  • the reference unit 112 includes a fiber type optical demultiplexer 120 and a reflection mirror group 121.
  • the fiber type optical demultiplexer 120 demultiplexes the incident reference light L2 for each wavelength.
  • the reflection mirror group 121 includes a plurality of mirrors 121a to 121e that reflect the reference light L2 demultiplexed by the fiber-type optical demultiplexer 120 so as to have different optical path lengths. Since the wavelength of the light included in the reference light L2 is set to 780 to 860 nm, here, the reference light L2 is converted into light having wavelengths of 780 nm, 800 nm, 820 nm, 840 nm, and 860 nm, respectively. Spectroscopy.
  • the mirrors 121a to 121e constituting the reflecting mirror group 121 are arranged so as to give different optical path length differences for each wavelength at intervals of 1 mm.
  • the mirror 121a that reflects light having a wavelength of 780 nm is arranged so that the optical path length of light having a wavelength of 780 nm included in the reference light L2 is 1 mm shorter than the optical path length of object light L1 reflected by the conveyor belt 101. Has been placed.
  • a mirror 121b that reflects light having a wavelength of 800 nm is disposed so that the optical path length of light having a wavelength of 800 nm included in the reference light L2 is 2 mm shorter than the optical path length of object light L1 reflected from the conveyor belt 101.
  • the mirror 121c that reflects light with a wavelength of 820 nm, the mirror 121d that reflects light with a wavelength of 840 nm, and the mirror 121e that reflects light with a wavelength of 860 nm have an optical path length difference between the object light L1 and the reference light L2.
  • the surface of the determination object 103 is positioned 1 mm from the conveyor belt 101. You can see that it is at (height). Since the determination object 103 is crushed into small pieces as a mixed plastic, the position (height) of the surface of the determination object 103 from the conveyor belt 101 can be regarded as the thickness of the determination object 103. Therefore, the thickness of the determination target object 103 can be measured by measuring the optical path length of the object light L1.
  • the reference light L2 having a wavelength corresponding to the thickness of 1 mm (780 nm) and the reference light L2 having a wavelength corresponding to the thickness of 2 mm (800 nm) interfere with the object light L1.
  • interference by the reference light L2 having a wavelength (780 nm) corresponding to the thickness of 1 mm is stronger than interference by the reference light L2 having a wavelength (800 nm) corresponding to the thickness of 2 mm. ) Is measured as 1 mm.
  • determination is performed using the reference data (selection reference data) for the recycled resin having a thickness of 1 mm with respect to the determination target object 103 having a measured thickness of 1.0 mm and an actual thickness of 1.2 mm.
  • the measured thickness is measured at intervals of 1 mm, the difference from the actual thickness is 0.5 mm or less, so it is possible to use reference data prepared at intervals of 1 mm. Thereby, the number of reference data to be prepared in advance can be reduced. Furthermore, since the thickness is measured at intervals of 1 mm, the load on the arithmetic processing unit 107 can be reduced. In this case, it is necessary to prepare reference data in which the thickness interval to be measured is matched with the corresponding thickness.
  • the determination target 103 having a thickness of about 0.3 to 5.5 mm is assumed. Therefore, the number of mirrors in the reflection mirror group 121 in the reference unit 112 is five, and preparation is performed.
  • the reference data to be used are also five types corresponding to thicknesses from 1 mm to 1 mm at intervals of 1 mm. If the thickness variation of the determination target 103 changes, the number of mirrors may be set to 6 or more and 4 or less, and the type or number of reference data may be changed. Furthermore, the wavelength of the measurement light emitted from the light source 111 may be changed in a range of 780 or more and less than 1360 nm.
  • the coherence distance of the light source 111 is set to 1 mm or more. Furthermore, it is desirable that the coherence distance is less than 2 mm so that the reference light L2 having three or more types of wavelengths does not interfere simultaneously.
  • the thickness of the determination object 103 can be measured with an accuracy of 0.1 mm or less from the ratio of the intensity of the interference light of each wavelength.
  • the interference intensity of the reference light L2 having a wavelength corresponding to 1 mm (780 nm) and a wavelength corresponding to 2 mm (800 nm) ) Is different from the interference intensity of the reference light L2. Therefore, by measuring the difference in interference intensity in advance, the measurement thickness can be measured with an accuracy of 0.1 mm or less.
  • the determination object 103 can be accurately determined by subtracting the correction data corresponding to the thickness (noise corresponding to the thickness) from the calculated absorption spectrum.
  • correction data corresponding to each type of resin it is possible to determine the resin with higher accuracy. This is because if the thickness of the resin is increased, the resin is affected by absorption by the resin itself, and the correction data corresponding to the thickness may be different for each type of resin due to this.
  • the absorption spectrum (conveyance path absorption spectrum) of the conveyance path (conveyor belt 101) may be used as the correction data.
  • the reference absorption spectrum is different for each type of resin, it is necessary to prepare or acquire a different reference absorption spectrum for each type of resin in the storage unit 107a. Therefore, it is preferable to store different reference data for each type of resin in the storage unit 107a. This is because the reference data includes a reference absorption spectrum and noise (correction data) corresponding to the thickness.
  • the determination unit 107b determines the determination target 103 using the absorption spectrum of the determination target 103 and the selection reference data, the absorption spectrum of the determination target 103 obtained by subtracting noise, the reference absorption spectrum, and the like.
  • the determination object 103 may be determined based on the above. Further, the determination of the determination target object 103 may be performed based on the reference absorption spectrum added with noise and the absorption spectrum of the determination target object 103. Further, a plurality of types of reference absorption spectra to which noise has been added are prepared in advance as reference data for each thickness, and based on the selection reference data selected from the reference data and the absorption spectrum of the determination target 103, the determination target 103 The determination may be made.
  • the determination object 103 arranged on the upper part is dropped to an arbitrary place in the input area 93A on the conveyor belt 101 (step S21).
  • the object 103 is conveyed to the detection area 93B below the detection unit 106 by the flow.
  • the measured thickness and the absorption spectrum are measured by the thickness measuring unit 106a and the absorption spectrum calculating unit 106b of the detection unit 106 for the determination target 103 carried to the detection region 93B (step S22). .
  • the determination unit 107b determines whether the determination target 103 is a recycled resin based on the measured thickness of the determination target 103 and the absorption spectrum.
  • the determination means is as shown in the flow of FIG. 5 (step S23).
  • to-be-determined object 103 (recycled resin 103a) determined to be recycled resin is blown out by pulse air nozzle 108 under the control of control unit 97 and stored in recycling box 109 (step S24).
  • the to-be-determined object 103 (non-recycled resin 103 b) determined not to be recycled resin is not blown out by the pulse air nozzle 108 under the control of the control unit 97, and the non-recycled box 110 is caused by free fall from the conveyor belt 101. (Step S25).
  • sorting such as PP and PS can be performed.
  • the thickness measurement unit 106a and the absorption spectrum calculation unit 106b provided in the detection unit 106 are operated in synchronization with an external clock, basically, the measurement thickness data and the absorption spectrum data are measured at the same measurement point. Are calculated at once.
  • a resin having a total light transmittance of 70% or more is described as a transparent resin.
  • reference data may be acquired as necessary from a reference data acquisition unit 107c provided separately from the storage unit 107a. Further, the reference data may be acquired by the reference data acquisition unit 107c as needed from the external database 107e via the communication line 107d.
  • FIG. 9 shows a reference unit 133 that is a modification of the reference unit 112 of the first embodiment.
  • the size of the fiber-type optical demultiplexer 120 is a problem, and it is difficult to reduce the size. Therefore, in the reference unit 133 of the first modified example in FIG. 9, the diffraction grating 134 is used instead of the fiber type optical demultiplexer 120 to reduce the size.
  • the reference unit 133 includes a diffraction grating 134, a condensing lens group 135 composed of a plurality (five in FIG. 9) of condensing lenses, and a reflection composed of a plurality of (five in FIG. 9) reflecting mirrors. And a mirror group 136.
  • the reference light L2 incident on the reference unit 133 is split by the diffraction grating 134 into wavelengths of 780 nm, 800 nm, 820 nm, 840 nm, and 860 nm.
  • the split reference light L2 is reflected by the respective reflecting mirrors of the reflecting mirror group 136 through the respective condensing lenses of the condensing lens group 135.
  • the reference light L2 reflected by the respective reflecting mirrors of the reflecting mirror group 136 is emitted from the reference unit 133 via the respective condensing lenses of the condensing lens group 135 so as to travel backward in the optical path.
  • the diffraction grating 134, the condenser lens group 135, and the reflection mirror group 136 are arranged so that different optical path lengths are given to the reference light L2 of each wavelength at intervals of 1 mm.
  • the reference unit 133 of the first modification can achieve the same effect as the reference unit 112 while reducing the size of the apparatus.
  • the thickness measuring unit 106a in FIG. 2 has been described as measuring the measured thickness using an optical interferometer (optical interferometry) that uses measurement light different from the infrared light 105.
  • the thickness measuring unit 106a may measure the measured thickness using a triangulation instrument (triangulation method).
  • triangulation method triangulation method
  • the recycled resin recycled product manufacturing apparatus 141 includes the recycled resin determination apparatus 100 according to the first embodiment and a recycled resin molding apparatus 142.
  • the recycled resin recycled product manufacturing apparatus 141 is the recycled resin recycled product manufacturing apparatus 141 using the determination target article 103 (recycled resin 103a) determined as the recycled resin by the recycled resin determining apparatus 100 according to the first embodiment.
  • Manufactures recycled plastic products As such a recycled resin molding apparatus 142, a molding apparatus capable of performing the steps described in JP-A-2001-205632 can be used.
  • the determination step of determining whether or not the determination target object 103 is the recycled resin by the recycled resin determination device 100 according to the first embodiment A manufacturing step of manufacturing a recycled resin recycled product using the recycled resin recycled product manufacturing apparatus 141 using the determination target product 103 (recycled resin 103a) determined to be recycled resin in the step. Has been.
  • a mixed raw material 82 in which metal powder is mixed with a pulverized product of resin waste (recycled resin 103a in FIG. 1) determined as a recycled resin is formed into a concave portion of a lower mold 83 as shown in FIG. 10B. Put in 83b. Then, the pulverized product 81 obtained by pulverizing only the resin waste as shown in FIG. 10C is put on the mixed raw material 82. Thereafter, as shown in FIG. 10D, the upper mold 83 a is lowered and pressure-molded with the lower mold 83.
  • a recycled molded product 84 (recycled resin recycled product) as shown in FIG. 10E can be manufactured.
  • the regenerated molded product 84 thus obtained has a two-layer structure in which the surface layer 84a and the backing layer 84b are integrated. Since the surface layer 84a is formed of the mixed raw material 82 of the pulverized resin waste and the metal powder, the surface finish is metallic. For this reason, a high-class feeling can be improved.
  • Such a recycled molded product 84 can be applied to various products such as a decorative panel used as a building material as a recycled resin recycled product.
  • the recycled resin recycled product manufacturing apparatus 141 according to the second embodiment is recycled using the to-be-determined product 103 (recycled resin 103a) determined as the recycled resin by the recycled resin determining apparatus 100 according to the first embodiment.
  • the manufacturing method of the recycled resin recycled product which manufactures a resin recycled product can be implemented. For this reason, it is possible to save resources.
  • this invention is not limited to the said embodiment or modification, It can implement in another various aspect.
  • this invention is not limited to the said embodiment or modification, It can implement in another various aspect.
  • a desired recycled resin can be determined from a crushed mixed plastic for recycling from waste home appliances and the like.
  • the recycled resin recycled product manufacturing apparatus it is possible to manufacture a recycled resin recycled product by using a determination target determined as a resin to be recycled.

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Abstract

This recycled resin evaluation device is provided with the following: a conveyance device (101) that conveys an evaluation sample (103) of transparent resin; an infrared light source (104) that illuminates the evaluation sample with infrared light; an infrared photoreceptor (129) that receives infrared light reflected from the evaluation sample illuminated with infrared light; an absorption spectrum calculating unit (106b) that calculates the absorption spectrum of the evaluation sample from the reflected infrared light; a thickness measuring unit (106a) that measures the thickness of the evaluation sample; a memory unit (107a) that pre -stores reference data which varies by the thickness of recycled resin; and an evaluation unit (107b) that selects from among the stored reference data the reference data for a recycled resin having a thickness matching the measured thickness, designates the same as selected reference data, and then evaluates whether or not the evaluation sample is the recycled resin on the basis of the absorption spectrum and the selected reference data.

Description

リサイクル樹脂の判定装置、及び、リサイクル樹脂再生品の製造方法Recycled resin judgment device and method for producing recycled resin recycled product

 本発明は、被判定物がリサイクル対象の樹脂であるか否かを判定するリサイクル樹脂の判定装置、及び、リサイクル樹脂再生品の製造方法に関する。 The present invention relates to a recycling apparatus for determining whether or not an object to be determined is a resin to be recycled, and a method for manufacturing a recycled resin recycled product.

 ポリスチレン(以下、「PS」とする。)、ポリプロピレン(以下、「PP」とする。)、アクリロニトリル・ブタジエン・スチレン(以下、ABSとする。)等の複数の樹脂を含む混合物であるミックスプラスチックから、リサイクル対象の樹脂(以下、「リサイクル樹脂」とする。)を判定する技術が、特許文献1に開示されている。図11を用いて、従来の技術について説明する。 From a mixed plastic that is a mixture containing a plurality of resins such as polystyrene (hereinafter referred to as “PS”), polypropylene (hereinafter referred to as “PP”), acrylonitrile butadiene styrene (hereinafter referred to as ABS), and the like. A technique for determining a resin to be recycled (hereinafter referred to as “recycled resin”) is disclosed in Patent Document 1. The conventional technique will be described with reference to FIG.

 従来の技術に係るリサイクル樹脂の判定装置1は、搬送路2によって搬送される被判定物3の表面に対し、光源4から赤外光を照射することで、被判定物3の表面から赤外光(以下、「赤外反射光」とする。)を反射させる。被判定物3の表面から反射した赤外反射光を、ミラー5、ポリゴンミラー6を介して受光部7で撮像する。このとき、制御装置8は、受光部7で撮像した赤外反射光の特徴量と、予め設定したリサイクル樹脂の特徴量とを比較する。制御装置8による比較の結果、被判定物3の特徴量と予め設定したリサイクル樹脂の特徴量とが一致した場合、被判定物3をリサイクル樹脂として判定する。このようにして、従来の技術に係るリサイクル樹脂の判定装置1は、被判定物3であるミックスプラスチックの中から、リサイクル樹脂として、例えばPSのみを判定している。 The determination apparatus 1 of the recycled resin which concerns on the prior art irradiates infrared light from the light source 4 with respect to the surface of the to-be-determined object 3 conveyed by the conveyance path 2, and is infrared from the surface of the to-be-determined object 3 Reflects light (hereinafter referred to as “infrared reflected light”). The infrared reflected light reflected from the surface of the determination object 3 is imaged by the light receiving unit 7 via the mirror 5 and the polygon mirror 6. At this time, the control device 8 compares the feature quantity of the infrared reflected light imaged by the light receiving unit 7 with the preset feature quantity of the recycled resin. As a result of comparison by the control device 8, when the feature amount of the determination target object 3 matches a preset feature amount of the recycled resin, the determination target component 3 is determined as the recycled resin. In this manner, the recycled resin determination device 1 according to the related art determines, for example, only PS as the recycled resin from the mixed plastic that is the determination target 3.

特表2002-540397号公報Japanese translation of PCT publication No. 2002-540397

 しかしながら、被判定物が透明な樹脂の場合、従来の技術に係るリサイクル樹脂の判定装置では、被判定物の下部に位置する搬送路からの赤外反射光も、一緒に撮像してしまう。この場合、撮像した赤外反射光に基づいて取得した被判定物の特徴量には、搬送路の特徴量がノイズとして重なる。 However, when the object to be determined is a transparent resin, the recycled resin determination device according to the prior art also picks up the infrared reflected light from the conveyance path located below the object to be determined. In this case, the characteristic amount of the determination target acquired based on the captured infrared reflected light overlaps with the characteristic amount of the conveyance path as noise.

 このようなノイズの影響を含んだ特徴量を用いると、被判定物の種類がリサイクル樹脂であるか否かを判定することができない。 If such a feature amount including the influence of noise is used, it cannot be determined whether or not the type of the object to be determined is a recycled resin.

 つまり、従来の技術に係るリサイクル樹脂の判定装置では、被判定物が透明な樹脂である場合、被判定物がリサイクル樹脂であるか否かを判定することができない課題を有していた。 That is, in the conventional determination apparatus for recycled resin, when the determination target is a transparent resin, it is impossible to determine whether the determination target is a recycled resin.

 そこで、本発明は、上述の課題を解決し、透明な樹脂である被判定物が、リサイクル対象の樹脂であるか否かを判定するリサイクル樹脂の判定装置、及び、リサイクル対象の樹脂と判定した被判定物を用いるリサイクル樹脂再生品の製造方法を提供することを目的とする。 Therefore, the present invention solves the above-described problems, and determines that the determination target, which is a transparent resin, is a recycling resin determination apparatus that determines whether the determination target resin is a recycling target resin, and a recycling target resin. It is an object of the present invention to provide a method for producing a recycled resin recycled product using an object to be determined.

 本発明は、前記目的を達成するため、以下のように構成されている。 The present invention is configured as follows in order to achieve the above object.

 本発明の1つの態様によれば、透明な樹脂である被判定物を搬送する搬送装置と、
 前記被判定物に赤外光を照射する赤外光源と、
 前記赤外光が照射された前記被判定物からの赤外反射光を受光する赤外受光部と、
 前記赤外受光部で受光された前記赤外反射光から前記被判定物の吸収スペクトルを算出する吸収スペクトル算出部と、
 前記被判定物の厚みである測定厚みを測定する厚み測定部と、
 厚み毎に異なるリサイクル樹脂の基準データを予め記憶する記憶部と、
 前記基準データのうち、前記厚み測定部で測定された前記測定厚みに対応する厚みの前記リサイクル樹脂における基準データを選択基準データとして選択し、この選択基準データと、前記吸収スペクトル算出部で算出された前記吸収スペクトルとに基づいて、前記被判定物が前記リサイクル樹脂か否かを判定する判定部と、を備えるリサイクル樹脂の判定装置を提供する。
According to one aspect of the present invention, a transport device that transports a determination object that is a transparent resin;
An infrared light source for irradiating the determination object with infrared light;
An infrared light receiving unit that receives infrared reflected light from the object to be determined irradiated with the infrared light; and
An absorption spectrum calculation unit for calculating an absorption spectrum of the object to be determined from the infrared reflected light received by the infrared light receiving unit;
A thickness measuring unit for measuring a measurement thickness which is a thickness of the object to be determined;
A storage unit that stores in advance reference data for different recycled resins for each thickness;
Among the reference data, the reference data for the recycled resin having a thickness corresponding to the measured thickness measured by the thickness measurement unit is selected as selection reference data, and the selection reference data and the absorption spectrum calculation unit are calculated. And a determination unit that determines whether or not the determination target is the recycled resin based on the absorption spectrum.

 また、前記のリサイクル樹脂の判定装置によって前記被判定物が前記リサイクル樹脂か否かを判定し、
 前記リサイクル樹脂と判定された被判定物を成形してリサイクル樹脂再生品を製造するリサイクル樹脂再生品の製造方法を提供する。
Further, it is determined by the recycled resin determination device whether the determination object is the recycled resin,
Provided is a method for producing a recycled resin recycled product, in which an article to be judged determined as the recycled resin is molded to produce a recycled resin recycled product.

 本リサイクル樹脂の判定装置によれば、透明な樹脂が、リサイクル対象の樹脂であるか否かを判定することが可能である。また、本リサイクル樹脂再生品の製造方法によれば、リサイクル対象の樹脂と判定した被判定物を用いてリサイクル樹脂再生品を製造することが可能となる。 According to the determination apparatus for recycled resin, it is possible to determine whether or not the transparent resin is a resin to be recycled. Moreover, according to the manufacturing method of this recycled resin recycled product, it becomes possible to manufacture a recycled resin recycled product using the to-be-determined object determined to be a recycling target resin.

 本発明のこれらと他の目的と特徴は、添付された図面についての実施形態に関連した次の記述から明らかになる。この図面においては、
図1は、第1実施形態に係るリサイクル樹脂の判定装置の模式図であり、 図2は、第1実施形態に係る検出ユニットの模式図であり、 図3は、第1実施形態に係る検出ユニットで検出した異なる厚みの被判定物の吸収スペクトルのグラフを示す図であり、 図4Aは、第1実施形態に係るリサイクル樹脂の判定装置において、検出ユニットに備わる吸収スペクトル算出部と厚み測定部とを示すとともに、演算処理部に備わる記憶部と判定部とを示すブロック図であり、 図4Bは、第1実施形態の変形例に係るリサイクル樹脂の判定装置において、検出ユニットに備わる吸収スペクトル算出部と厚み測定部とを示すとともに、演算処理部に備わる基準データ取得部と記憶部と判定部とを示すブロック図であり、 図5は、第1実施形態に係る判定部による判定の動作を示すフローチャートであり、 図6は、厚みが1mmの被判定物の吸収スペクトルから、被判定物の厚みが2mm、3mmの場合に検出されるノイズを減算した吸収スペクトルのグラフを示す図であり、 図7は、厚みが1.5mmの被判定物の吸収スペクトルから、被判定物の厚みが1mmの場合に検出されるノイズを減算した吸収スペクトルのグラフを示す図であり、 図8は、第1実施形態に係るリサイクル樹脂の判定装置の動作を表すフローチャートであり、 図9は、第1実施形態に係る参照ユニットの第1変形例を示す模式図であり、 図10Aは、第2実施形態に係るリサイクル樹脂再生品の製造装置を示すブロック図であり、 図10Bは、第2実施形態に係るリサイクル樹脂再生品の製造装置の製造工程を示す断面図であり、 図10Cは、第2実施形態に係るリサイクル樹脂再生品の製造装置の製造工程を示す断面図であり、 図10Dは、第2実施形態に係るリサイクル樹脂再生品の製造装置の製造工程を示す断面図であり、 図10Eは、第2実施形態に係るリサイクル樹脂再生品の製造装置の製造工程で成形された再生成形品を示す斜視図であり、 図11は、従来の技術に係るリサイクル樹脂の判定装置の模式図である。
These and other objects and features of the invention will become apparent from the following description taken in conjunction with the embodiments with reference to the accompanying drawings. In this drawing,
FIG. 1 is a schematic diagram of a recycled resin determination device according to the first embodiment. FIG. 2 is a schematic diagram of a detection unit according to the first embodiment. FIG. 3 is a diagram illustrating a graph of an absorption spectrum of a determination object having different thicknesses detected by the detection unit according to the first embodiment. FIG. 4A is a block diagram illustrating an absorption spectrum calculation unit and a thickness measurement unit included in the detection unit and a storage unit and a determination unit included in the arithmetic processing unit in the recycled resin determination device according to the first embodiment. Yes, FIG. 4B shows an absorption spectrum calculation unit and a thickness measurement unit included in the detection unit, and a reference data acquisition unit and a storage unit included in the arithmetic processing unit in the determination apparatus for recycled resin according to the modification of the first embodiment. It is a block diagram showing a determination unit, FIG. 5 is a flowchart showing a determination operation by the determination unit according to the first embodiment. FIG. 6 is a graph showing an absorption spectrum obtained by subtracting noise detected when the thickness of the determination object is 2 mm or 3 mm from the absorption spectrum of the determination object having a thickness of 1 mm. FIG. 7 is a graph showing an absorption spectrum obtained by subtracting noise detected when the thickness of the determination object is 1 mm from the absorption spectrum of the determination object having a thickness of 1.5 mm. FIG. 8 is a flowchart showing the operation of the recycled resin determination apparatus according to the first embodiment. FIG. 9 is a schematic diagram illustrating a first modification of the reference unit according to the first embodiment. FIG. 10A is a block diagram showing a recycled resin recycled product manufacturing apparatus according to the second embodiment; FIG. 10B is a cross-sectional view showing a manufacturing process of the manufacturing apparatus of the recycled resin recycled product according to the second embodiment. FIG. 10C is a cross-sectional view showing the manufacturing process of the apparatus for manufacturing recycled resin recycled products according to the second embodiment, FIG. 10D is a cross-sectional view illustrating the manufacturing process of the apparatus for manufacturing recycled resin recycled products according to the second embodiment; FIG. 10E is a perspective view showing a recycled molded product molded in the manufacturing process of the recycled resin recycled product manufacturing apparatus according to the second embodiment; FIG. 11 is a schematic diagram of a determination apparatus for recycled resin according to a conventional technique.

 以下、本発明の実施形態について、図面を参照しながら説明する。なお、以下の説明において、同一構成には同一符号を付して説明を省略する。 Hereinafter, embodiments of the present invention will be described with reference to the drawings. In the following description, the same components are denoted by the same reference numerals and description thereof is omitted.

 (第1実施形態)
 図1は、第1実施形態に係るリサイクル樹脂の判定装置100の模式図である。
(First embodiment)
FIG. 1 is a schematic diagram of a recycled resin determination apparatus 100 according to the first embodiment.

 搬送装置の一例であるコンベアベルト101は、一定の速度で移動している。このコンベアベルト101により、被判定物103が、コンベアベルト101の長手方向の搬送路に沿って、投入領域93Aから検出領域93Bを経て選別領域93Cまで搬送される。コンベアベルト101による搬送路の始端部に配置されたホッパー102が振動又は揺動することで、被判定物103が投入される。ホッパー102は、コンベアベルト101上に被判定物103を投入する投入部の一例である。ホッパー102上に積載された複数の被判定物103は、コンベアベルト101の投入領域93A上へ一定の間隔を開けて順次投入される。コンベアベルト101は、コンベアベルト101に光を照射しても光が反射しにくいように黒色又は黒に近い色で構成される。また、コンベアベルト101は、判定の際に被判定物103と区別を付け易いように、被判定物103の樹脂とは異なる材料(例えば、塩化ビニル樹脂)で構成されている。 A conveyor belt 101, which is an example of a transport device, is moving at a constant speed. By the conveyor belt 101, the determination object 103 is transported along the transport path in the longitudinal direction of the conveyor belt 101 from the input area 93A to the selection area 93C through the detection area 93B. When the hopper 102 disposed at the start end of the conveyance path by the conveyor belt 101 vibrates or swings, the determination target 103 is input. The hopper 102 is an example of a loading unit that loads the determination target object 103 onto the conveyor belt 101. A plurality of determination objects 103 stacked on the hopper 102 are sequentially input on the input region 93 </ b> A of the conveyor belt 101 with a certain interval. The conveyor belt 101 is configured in black or a color close to black so that the light is not easily reflected even when the conveyor belt 101 is irradiated with light. Further, the conveyor belt 101 is made of a material (for example, vinyl chloride resin) different from the resin of the determination target 103 so that it can be easily distinguished from the determination target 103 at the time of determination.

 コンベアベルト101による被判定物103の搬送速度を、3m/sとし、搬送方向は、図1に示す矢印Aの方向とする。 The conveyance speed of the object 103 to be determined by the conveyor belt 101 is 3 m / s, and the conveyance direction is the direction of arrow A shown in FIG.

 被判定物103は、複数種類の透明樹脂を含むミックスプラスチックであり、この中に、透明なリサイクル樹脂を含んでいる。被判定物103は、一例として、一辺5mm~数10mm程度の小片からなり、各小片の厚みは、一例として、0.3mm~5.5mm程度である。すなわち、被判定物103は、粉砕物で、厚みがほぼ一定とみなせる程度の小片で構成されている。 The to-be-determined object 103 is a mixed plastic including a plurality of types of transparent resins, and includes a transparent recycled resin. The determination target object 103 is, for example, a small piece having a side of about 5 mm to several tens of mm, and the thickness of each small piece is, for example, about 0.3 mm to 5.5 mm. That is, the determination target object 103 is a pulverized material and is composed of small pieces having a thickness that can be regarded as substantially constant.

 被判定物103は、赤外光源104によって赤外光105Aを照射されることで、それぞれの樹脂材料の特徴量となる赤外光を赤外反射光105として反射する。 The object 103 is irradiated with infrared light 105 </ b> A from the infrared light source 104, thereby reflecting infrared light that is a characteristic amount of each resin material as infrared reflected light 105.

 赤外光源104は、コンベアベルト101の検出領域93Bの上方に配置される検出ユニット106の両側で、かつ、コンベアベルト101と検出ユニット106との間の空間に配置されている。赤外光源104には、一例として、波長1360~2500nm(波長1360nm以上2500nm以下)のブロードな波長帯域の赤外光(近赤外光)105Aを照射するハロゲンランプを用いる。吸光現象が生じる波長は樹脂の種類によって異なるため、この吸光現象の生じた波長に基づいて特徴量を算出し、算出した特徴量を用いて被判定物103がリサイクル樹脂か否かを演算処理部107で判定する。吸光現象の生じた波長は、被判定物103で反射した赤外反射光105の吸収スペクトルから検出ユニット106で求めることが可能である。なお、赤外光源104には、一例として、レーザ光源を用いてもよい。 The infrared light source 104 is disposed on both sides of the detection unit 106 disposed above the detection area 93 </ b> B of the conveyor belt 101 and in a space between the conveyor belt 101 and the detection unit 106. As an example of the infrared light source 104, a halogen lamp that irradiates infrared light (near infrared light) 105A in a broad wavelength band with a wavelength of 1360 to 2500 nm (a wavelength of 1360 nm to 2500 nm) is used. Since the wavelength at which the light absorption phenomenon occurs varies depending on the type of resin, a feature amount is calculated based on the wavelength at which the light absorption phenomenon occurs, and an arithmetic processing unit determines whether the determination target 103 is a recycled resin using the calculated feature amount. The determination is made at 107. The wavelength at which the light absorption phenomenon occurs can be obtained by the detection unit 106 from the absorption spectrum of the infrared reflected light 105 reflected by the determination target 103. Note that a laser light source may be used as the infrared light source 104 as an example.

 被判定物103で反射した赤外反射光105は、検出ユニット106により検出される。この検出結果は、検出ユニット106でデジタルデータに変換された後に、検出ユニット106から演算処理部107へと転送される。 The infrared reflected light 105 reflected by the determination object 103 is detected by the detection unit 106. The detection result is converted into digital data by the detection unit 106 and then transferred from the detection unit 106 to the arithmetic processing unit 107.

 演算処理部107は、検出ユニット106での検出結果を基に、被判定物103がリサイクル樹脂であるか否かを判定する。 The arithmetic processing unit 107 determines whether the determination target object 103 is a recycled resin based on the detection result of the detection unit 106.

 検出ユニット106及び演算処理部107の詳細な説明は、後述する。 Details of the detection unit 106 and the arithmetic processing unit 107 will be described later.

 コンベアベルト101の選別領域93Cである終端部の上方に、リサイクル樹脂と判定された被判定物103(以下、「リサイクル樹脂103a」とする。)にエアを吹き付ける選別部の一例であるパルスエアノズル108とエア供給源95とが配置される。演算処理部107又は制御部97からの指示に基づき、エア供給源95が駆動され、駆動量に応じたエアをパルスエアノズル108から吹き出して、リサイクル樹脂103aを吹き飛ばす。このパルスエアノズル108からのエアによる吹き飛ばしにより、自由落下の軌跡を外れるように強制的に落下させられて、リサイクル樹脂103aがリサイクルボックス109に収納される。リサイクルボックス109には、リサイクル樹脂103aが収納される。一方、リサイクル樹脂でないと判定された被判定物103(以下、「非リサイクル樹脂103b」とする。)は、パルスエアノズル108による吹き飛ばしが行われずに、非リサイクルボックス110に収納される。非リサイクルボックス110は、リサイクルボックス109に隣接して配置されている。この場合、非リサイクルボックス110は、コンベアベルト101の終端部の下方であって、非リサイクル樹脂103bが、自由落下する位置に配置される。被判定物103の位置情報は、制御部97に接続された位置演算部94で特定される。具体的には、制御部97により制御されるコンベアベルト101の駆動モータ90に取り付けられたエンコーダ検出器91からの値と、検出ユニット106のスキャン位置とから、被判定物103のコンベアベルト101上の位置が位置演算部94で特定される。これにより、複数の被判定物103の中から、リサイクル樹脂103aのみを選別することができる。 A pulsed air nozzle 108, which is an example of a sorting unit that blows air onto an object 103 to be judged to be recycled resin (hereinafter referred to as “recycled resin 103a”) above a terminal portion that is a sorting region 93C of the conveyor belt 101. And an air supply source 95 are arranged. Based on an instruction from the arithmetic processing unit 107 or the control unit 97, the air supply source 95 is driven, air corresponding to the driving amount is blown out from the pulse air nozzle 108, and the recycled resin 103a is blown out. By blowing off the air from the pulse air nozzle 108, the resin is forced to fall off the locus of free fall, and the recycled resin 103 a is stored in the recycling box 109. A recycling resin 103a is stored in the recycling box 109. On the other hand, the determination object 103 determined not to be recycled resin (hereinafter referred to as “non-recycled resin 103 b”) is stored in the non-recycle box 110 without being blown off by the pulse air nozzle 108. The non-recycle box 110 is disposed adjacent to the recycle box 109. In this case, the non-recycle box 110 is disposed below the end portion of the conveyor belt 101 and at a position where the non-recycle resin 103b freely falls. The position information of the determination object 103 is specified by a position calculation unit 94 connected to the control unit 97. Specifically, on the conveyor belt 101 of the object 103 to be determined from the value from the encoder detector 91 attached to the drive motor 90 of the conveyor belt 101 controlled by the control unit 97 and the scan position of the detection unit 106. Is determined by the position calculation unit 94. Thus, only the recycled resin 103a can be selected from the plurality of determination objects 103.

 次に、図2を用いて検出ユニット106の説明を行う。図2は、検出ユニット106を図1のX軸方向から表した図である。検出ユニット106は、厚み測定部106aと吸収スペクトル算出部106bとを備えて構成されている。厚み測定部106aは、被判定物103の厚みを測定する。吸収スペクトル算出部106bでは、被判定物103で反射した赤外反射光105の特徴量としての吸収スペクトルを算出する。 Next, the detection unit 106 will be described with reference to FIG. FIG. 2 is a diagram showing the detection unit 106 from the X-axis direction of FIG. The detection unit 106 includes a thickness measurement unit 106a and an absorption spectrum calculation unit 106b. The thickness measuring unit 106 a measures the thickness of the determination target object 103. The absorption spectrum calculation unit 106 b calculates an absorption spectrum as a feature amount of the infrared reflected light 105 reflected by the determination target object 103.

 最初に、検出ユニット106による被判定物103の厚みの測定の動作について説明する。 First, the operation of measuring the thickness of the determination target object 103 by the detection unit 106 will be described.

 検出ユニット106は、厚み測定部106aで被判定物103の厚みを測定するために、厚み測定用の光源111からの測定光を参照ユニット112と被判定物103とにそれぞれ照射し、これらから反射した光を干渉させることで、被判定物103の厚みを測定する光干渉計としての機能を備える。ここでは、光干渉計として、マイケルソン干渉計の構成を用いる。 In order for the thickness measurement unit 106a to measure the thickness of the object to be determined 103, the detection unit 106 irradiates the reference unit 112 and the object to be determined 103 with measurement light from the light source 111 for thickness measurement, and reflects from the light. By interfering with the received light, a function as an optical interferometer for measuring the thickness of the determination target object 103 is provided. Here, a Michelson interferometer configuration is used as the optical interferometer.

 厚み測定用の光源111には、一例として波長走査型光干渉断層画像装置(Swept Source Optical Coherence Tomography:以下、「SS-OCT」とする。)を用いる。ここでは、光を受光する受光素子113にシリコンのアバランシェフォトダイオードを用いるため、受光素子113が感度を有する波長780~860nm(波長780nm以上860nm以下)の光を、厚み測定用の光源111の測定光に採用する。なお、測定光の波長は、赤外光源104から被判定物103で反射した赤外反射光105と区別するため、図1に示す赤外光源104で照射する波長1360~2500nm以外であればよい。しかし、可視光(波長380以上780nm未満の光)又は短波長の光(波長380nm未満の光)では、精度良く厚みを測定できない場合がある。これらのことから、光源111からの測定光には、波長780以上1360nm未満の光を用いることが好ましい。 As the thickness measurement light source 111, for example, a wavelength scanning optical coherence tomography device (hereinafter referred to as “SS-OCT”) is used. Here, since a silicon avalanche photodiode is used for the light receiving element 113 that receives light, light having a wavelength of 780 to 860 nm (wavelength of 780 nm or more and 860 nm or less) with which the light receiving element 113 is sensitive is measured by the light source 111 for thickness measurement. Adopt for light. Note that the wavelength of the measurement light may be any wavelength other than the wavelength 1360 to 2500 nm irradiated by the infrared light source 104 shown in FIG. 1 in order to distinguish it from the infrared reflected light 105 reflected by the determination target 103 from the infrared light source 104. . However, the thickness may not be accurately measured with visible light (light with a wavelength of 380 or more and less than 780 nm) or light with a short wavelength (light with a wavelength of less than 380 nm). For these reasons, it is preferable to use light having a wavelength of 780 or more and less than 1360 nm as measurement light from the light source 111.

 厚み測定用の光源111から出射した測定光は、狭帯域フィルタ114を通過して、ビームスプリッタ115によって、後述する2つの光に分けられる。狭帯域フィルタ114は、波長780~860nmの光を透過させる。 The measurement light emitted from the light source 111 for thickness measurement passes through the narrow band filter 114 and is divided into two lights described later by the beam splitter 115. The narrow band filter 114 transmits light having a wavelength of 780 to 860 nm.

 ビームスプリッタ115で分けられた光のうち、被判定物103またはコンベアベルト101に照射される光(以下、「物体光」とする。)L1は、ポリゴンミラー116によって反射される。ポリゴンミラー116で反射した物体光L1はテレセントリックfθレンズ117及び波長フィルタ132を通して、被判定物103に照射される。ポリゴンミラー116は、自身が回転することにより、コンベアベルト101の幅方向(Y軸方向)のスキャンを可能とする。このスキャンにより、コンベアベルト101上の各スキャンポイント(物体光L1が照射される位置)から反射した物体光L1の検出を可能とする。 Of the light split by the beam splitter 115, the light L <b> 1 (hereinafter referred to as “object light”) L <b> 1 irradiated to the object 103 or the conveyor belt 101 is reflected by the polygon mirror 116. The object light L1 reflected by the polygon mirror 116 is irradiated to the determination target object 103 through the telecentric fθ lens 117 and the wavelength filter 132. The polygon mirror 116 enables scanning in the width direction (Y-axis direction) of the conveyor belt 101 by rotating itself. This scan enables detection of the object light L1 reflected from each scan point on the conveyor belt 101 (position where the object light L1 is irradiated).

 テレセントリックfθレンズ117は、ポリゴンミラー116の中央と周辺とのスキャン速度の差を均一化するfθ機能を持つ。この場合、テレセントリックfθレンズ117は、コンベアベルト101との間に、テレセントリック光学系が成立させる。 The telecentric fθ lens 117 has an fθ function that equalizes the difference in scanning speed between the center and the periphery of the polygon mirror 116. In this case, a telecentric optical system is established between the telecentric fθ lens 117 and the conveyor belt 101.

 ポリゴンミラー116の回転により、テレセントリックfθレンズ117に入射する角度に依存する物体光L1の光路長の差を補正するために、テレセントリックfθレンズ117のコンベアベルト101側に、中心から両端にかけて薄くなるようなガラス体(図示しない)を設置する。ガラス体は、ポリゴンミラー116で反射した物体光L1が、どの角度からテレセントリックfθレンズ117に入射しても、同じ光路長でコンベアベルト101に照射されるように、ガラス体の屈折率に基づいて、形状が設計される。ガラス体の代わりに、波長フィルタ132の厚みを中心から両端にかけて薄くなるように構成してもよい。 In order to correct the difference in the optical path length of the object light L1 depending on the angle incident on the telecentric fθ lens 117 by the rotation of the polygon mirror 116, the telecentric fθ lens 117 is thinned from the center to both ends on the conveyor belt 101 side. A glass body (not shown) is installed. The glass body is based on the refractive index of the glass body so that the object light L1 reflected by the polygon mirror 116 is irradiated on the conveyor belt 101 with the same optical path length no matter what angle the light enters the telecentric fθ lens 117. The shape is designed. Instead of the glass body, the wavelength filter 132 may be configured so that the thickness thereof decreases from the center to both ends.

 ビームスプリッタ115からポリゴンミラー116及びテレセントリックfθレンズ117及び波長フィルタ132を介して被判定物103に照射された物体光L1は、被判定物103の表面で反射され、同一の経路を逆進し、再度、ビームスプリッタ115に入射する。 The object light L1 irradiated from the beam splitter 115 through the polygon mirror 116, the telecentric fθ lens 117, and the wavelength filter 132 to the object to be determined 103 is reflected on the surface of the object to be determined 103, and travels backward on the same path. It enters the beam splitter 115 again.

 ビームスプリッタ115で分けられた光のうち、物体光L1と異なる光(以下、「参照光」とする。)L2は、狭帯域フィルタ118及び集光レンズ119を介して、参照ユニット112に入射する。狭帯域フィルタ118は、波長780~860nmの光を透過させる。 Of the light split by the beam splitter 115, light different from the object light L <b> 1 (hereinafter referred to as “reference light”) L <b> 2 enters the reference unit 112 via the narrowband filter 118 and the condenser lens 119. . The narrow band filter 118 transmits light having a wavelength of 780 to 860 nm.

 参照ユニット112は、入射した参照光L2を内部で反射した後に、再度、参照ユニット112から出射させる。参照ユニット112の詳細は後述する。 The reference unit 112 reflects the incident reference light L <b> 2 inside and then emits it again from the reference unit 112. Details of the reference unit 112 will be described later.

 被判定物103の表面で反射した物体光L1と、参照ユニット112を出射した参照光L2は、再び、ビームスプリッタ115にそれぞれ入射することで、1つの光束に合波される(すなわち、干渉光L3となる。)。 The object light L1 reflected from the surface of the determination object 103 and the reference light L2 emitted from the reference unit 112 are again incident on the beam splitter 115, and are combined into one light beam (that is, interference light). L3).

 干渉光L3は、ビームスプリッタ115から出射して、回折格子122で反射回折されて、波長毎にそれぞれ異なる角度で分光される。 The interference light L3 is emitted from the beam splitter 115, reflected and diffracted by the diffraction grating 122, and dispersed at different angles for each wavelength.

 分光された干渉光L3は、干渉光用集光レンズ123及び狭帯域フィルタ124を介して、受光素子113の受光面に入射する。狭帯域フィルタ124は、波長780~860nmの光を透過させる。 The split interference light L3 is incident on the light receiving surface of the light receiving element 113 via the interference light condensing lens 123 and the narrow band filter 124. The narrow band filter 124 transmits light having a wavelength of 780 to 860 nm.

 受光素子113は、複数の受光面を有し、各受光面には、回折格子122で波長毎に分光された干渉光L3がそれぞれ入射する。また、受光素子113は、各受光面に入射した干渉光L3を電流に光電変換する。電流に変換されたアナログデータは、光ゲイン電流電圧変換アンプ125と高速AD変換回路126とによりデジタルデータに変換される。変換されたデジタルデータは、厚み測定部106aに送られる。このとき、干渉によって強度が強くなった光の波長に基づいて、厚み測定部106aにより被判定物103の厚みが計算により測定される。以下の説明では、測定した被判定物103の厚みを「測定厚み」と記載する。厚み測定部106aで測定された測定厚みの情報は、演算処理部107に送られる。 The light receiving element 113 has a plurality of light receiving surfaces, and the interference light L3 dispersed by wavelength by the diffraction grating 122 is incident on each light receiving surface. The light receiving element 113 photoelectrically converts the interference light L3 incident on each light receiving surface into a current. The analog data converted into current is converted into digital data by the optical gain current-voltage conversion amplifier 125 and the high-speed AD conversion circuit 126. The converted digital data is sent to the thickness measuring unit 106a. At this time, the thickness of the determination target object 103 is measured by the thickness measurement unit 106a based on the wavelength of the light whose intensity is increased by the interference. In the following description, the measured thickness of the determination target object 103 is referred to as “measured thickness”. Information on the measured thickness measured by the thickness measuring unit 106 a is sent to the arithmetic processing unit 107.

 なお、狭帯域フィルタ114、118、および124は、厚み測定に用いる波長780~860nmの光に、吸収スペクトル算出に用いる波長1360~2500nmの光がノイズとして入射するのを防止するために設置されている。 The narrow-band filters 114, 118, and 124 are installed to prevent light having a wavelength of 1360 to 2500 nm used for calculating an absorption spectrum from being incident as noise on light having a wavelength of 780 to 860 nm used for thickness measurement. Yes.

 次に、検出ユニット106を用いて被判定物103で反射した赤外反射光105の吸収スペクトルを算出する動作について説明する。 Next, an operation for calculating the absorption spectrum of the infrared reflected light 105 reflected by the determination target object 103 using the detection unit 106 will be described.

 被判定物103で反射した赤外反射光105は、物体光L1と同一の経路を通って、ビームスプリッタ115に入射する。 The infrared reflected light 105 reflected by the determination target object 103 enters the beam splitter 115 through the same path as the object light L1.

 ビームスプリッタ115に入射した赤外反射光105は、干渉光L3と同一の経路を通って、回折格子122に入射する。回折格子122は、入射した干渉光L3と赤外反射光105とを波長毎に異なる角度で反射、回折させる。このとき、干渉光L3である波長780~860nmの光は干渉光用集光レンズ123に入射し、赤外反射光105である波長1360~2500nmの光は赤外光用集光レンズ127に入射するように、回折格子122と、干渉光用集光レンズ123と、赤外光用集光レンズ127とが配置されている。 The infrared reflected light 105 incident on the beam splitter 115 enters the diffraction grating 122 through the same path as the interference light L3. The diffraction grating 122 reflects and diffracts the incident interference light L3 and the infrared reflected light 105 at different angles for each wavelength. At this time, the light having a wavelength of 780 to 860 nm, which is the interference light L3, enters the interference light condensing lens 123, and the light having the wavelength of 1360 to 2500 nm, which is the infrared reflected light 105, enters the condensing lens 127 for the infrared light. As shown, a diffraction grating 122, a condensing lens for interference light 123, and a condensing lens for infrared light 127 are arranged.

 赤外光用集光レンズ127に入射した赤外反射光105は、赤外光用狭帯域フィルタ128を透過して、赤外受光部129の受光面に入射する。赤外光用狭帯域フィルタ128は、波長1360~2500nmの光を透過させる。 The infrared reflected light 105 incident on the infrared light condenser lens 127 passes through the infrared light narrowband filter 128 and enters the light receiving surface of the infrared light receiving unit 129. The infrared narrowband filter 128 transmits light having a wavelength of 1360 to 2500 nm.

 赤外受光部129は、複数の受光面を有し、各受光面には、回折格子122で波長毎に分光された赤外反射光105が入射する。また、赤外受光部129は、受光した赤外反射光105を電流に光電変換する。電流に変換されたアナログデータは、光ゲイン電流電圧変換アンプ130と高速AD変換回路131とによりデジタルデータに変換される。変換されたデジタルデータは、吸収スペクトル算出部106bに送られる。このとき、被判定物103の吸光現象により、波長毎に光の強度が異なる。このため、吸収スペクトル算出部106bにて、被判定物103の波長毎の赤外反射光105の強度分布が求められ、吸収スペクトルが算出される。吸収スペクトル算出部106bで算出された吸収スペクトルの情報は、演算処理部107に送られる。 The infrared light receiving unit 129 has a plurality of light receiving surfaces, and the infrared reflected light 105 that is spectrally separated by the diffraction grating 122 for each wavelength is incident on each light receiving surface. The infrared light receiving unit 129 photoelectrically converts the received infrared reflected light 105 into a current. The analog data converted into current is converted into digital data by the optical gain current-voltage conversion amplifier 130 and the high-speed AD conversion circuit 131. The converted digital data is sent to the absorption spectrum calculation unit 106b. At this time, the light intensity varies depending on the wavelength due to the light absorption phenomenon of the determination target object 103. Therefore, the absorption spectrum calculation unit 106b obtains the intensity distribution of the infrared reflected light 105 for each wavelength of the determination target object 103, and calculates the absorption spectrum. Information on the absorption spectrum calculated by the absorption spectrum calculation unit 106 b is sent to the arithmetic processing unit 107.

 なお、波長フィルタ132は、コンベアベルト101と、テレセントリックfθレンズ117との間に配置されており、波長780nm未満の光を遮光する。厚み測定又は吸収スペクトル算出に用いる波長780~2500nm以外の光は、ノイズとなるからである。ただし、波長2500nmを超える光は、樹脂又はガラスで構成される一般的な光学系では透過損失が大きく、自然にフィルタリングされるため、波長780nm未満の光を遮光すれば十分である。 The wavelength filter 132 is disposed between the conveyor belt 101 and the telecentric fθ lens 117, and shields light having a wavelength of less than 780 nm. This is because light having a wavelength other than 780 to 2500 nm used for thickness measurement or absorption spectrum calculation becomes noise. However, light exceeding a wavelength of 2500 nm has a large transmission loss in a general optical system made of resin or glass and is naturally filtered. Therefore, it is sufficient to shield light having a wavelength of less than 780 nm.

 次に、被判定物103がリサイクル樹脂であるか否かを判定する具体的な方法について説明する。 Next, a specific method for determining whether the determination target object 103 is a recycled resin will be described.

 図3に、一例として、それぞれの厚みが1mm、2mm、3mmの透明なPSの被判定物103の吸収スペクトルの測定結果を示す。図3では、縦軸に吸光度を示し、横軸に波長(μm)を示す。これらの吸収スペクトルは、図2に示す検出ユニット106に備えられた吸収スペクトル算出部106bによって算出する。また、透明でないPSの被判定物103の吸収スペクトルを基準吸収スペクトル(図3中では「基準」と記載する。)として示す。図3から、透明なPSの被判定物103と透明でないPSの被判定物103とで、異なる吸収スペクトルを示すことがわかる。また、透明なPSは、被判定物103の厚みにより吸収スペクトルが変化することもわかる。なお、基準吸収スペクトルは、樹脂の厚みによらず、一定である。基準吸収スペクトルとは、白色光が透過しない樹脂の吸収スペクトルであって、詳しくは、標準拡散板に対して、白色の樹脂で取得した吸光度を意味する。 FIG. 3 shows, as an example, the measurement result of the absorption spectrum of the transparent PS object 103 having a thickness of 1 mm, 2 mm, and 3 mm. In FIG. 3, the vertical axis represents absorbance and the horizontal axis represents wavelength (μm). These absorption spectra are calculated by an absorption spectrum calculation unit 106b provided in the detection unit 106 shown in FIG. The absorption spectrum of the non-transparent PS object 103 is shown as a reference absorption spectrum (referred to as “reference” in FIG. 3). From FIG. 3, it can be seen that the transparent PS determination object 103 and the non-transparent PS determination object 103 show different absorption spectra. It can also be seen that the transparent PS has an absorption spectrum that changes depending on the thickness of the determination target object 103. The reference absorption spectrum is constant regardless of the thickness of the resin. The reference absorption spectrum is an absorption spectrum of a resin that does not transmit white light, and specifically means an absorbance obtained with a white resin with respect to a standard diffusion plate.

 図1に示す被判定物103に、赤外光源104から赤外光105Aを照射した場合、この被判定物103で反射する赤外反射光105には、被判定物103の下部に位置する搬送路(コンベアベルト101)で反射した赤外反射光105Cが重なる。従って、被判定物103で反射した赤外反射光105を受光すると、搬送路(コンベアベルト101)から反射した赤外反射光105Cも受光する。 When the object 103 shown in FIG. 1 is irradiated with the infrared light 105A from the infrared light source 104, the infrared reflected light 105 reflected by the object 103 is conveyed below the object 103. Infrared reflected light 105C reflected by the path (conveyor belt 101) overlaps. Therefore, when the infrared reflected light 105 reflected by the determination target 103 is received, the infrared reflected light 105C reflected from the conveyance path (conveyor belt 101) is also received.

 このとき、コンベアベルト101から反射した赤外反射光105Cの影響は、被判定物103の厚みに依存して変化することを発明者らは見出した。このことは、図3の結果から理解できる。すなわち、透明なリサイクル樹脂の吸収スペクトルは、その厚みに依存して変化することが、発明者らによる実験の結果、明らかとなった。 At this time, the inventors have found that the influence of the infrared reflected light 105 </ b> C reflected from the conveyor belt 101 changes depending on the thickness of the determination target object 103. This can be understood from the results of FIG. That is, as a result of experiments by the inventors, it has become clear that the absorption spectrum of a transparent recycled resin changes depending on its thickness.

 そこで、詳しくは後述するが、厚みの条件のみが異なる複数の透明なリサイクル樹脂に関して、それぞれの厚みに対応した吸収スペクトルを、基準データとして、後述する図4Aの演算処理部107の記憶部107aに予め準備しておく。次いで、準備した基準データのうち、被判定物103の測定厚みに対応する厚みのリサイクル樹脂の基準データを、後述する演算処理部107の判定部107bで選択する。以下、選択した基準データを「選択基準データ」とする。次いで、この選択基準データと被判定物103の吸収スペクトルとを比較することで、被判定物103がリサイクル樹脂であるか否かを判定部107bで判定できる。 Therefore, as will be described in detail later, with respect to a plurality of transparent recycled resins that differ only in thickness conditions, absorption spectra corresponding to each thickness are stored as reference data in the storage unit 107a of the arithmetic processing unit 107 in FIG. 4A described later. Prepare in advance. Next, of the prepared reference data, the reference data of the recycled resin having a thickness corresponding to the measured thickness of the determination target object 103 is selected by the determination unit 107b of the arithmetic processing unit 107 described later. Hereinafter, the selected reference data is referred to as “selection reference data”. Next, by comparing the selection reference data with the absorption spectrum of the determination target 103, the determination unit 107b can determine whether the determination target 103 is a recycled resin.

 演算処理部107による、判定の処理手法について説明する。図4Aに、検出ユニット106と、演算処理部107とのブロック図を示す。 The processing method of determination by the arithmetic processing unit 107 will be described. FIG. 4A shows a block diagram of the detection unit 106 and the arithmetic processing unit 107.

 演算処理部107は、記憶部107aと、判定部107bとを備えて構成される。 The arithmetic processing unit 107 includes a storage unit 107a and a determination unit 107b.

 記憶部107aは、基準データとして、透明なリサイクル樹脂の厚み毎の複数種類の吸収スペクトルを予め記憶している。この場合、記憶部107aは、基準データを取得する基準データ取得部としての機能も有する。 The storage unit 107a stores in advance a plurality of types of absorption spectra for each thickness of the transparent recycled resin as reference data. In this case, the storage unit 107a also has a function as a reference data acquisition unit that acquires reference data.

 判定部107bは、被判定物103の測定厚み及び吸収スペクトル、並びに、記憶部107aに記憶されている複数の基準データに基づいて、被判定物103がリサイクル樹脂であるか否かの判定処理を行う。被判定物103の測定厚み及び吸収スペクトルは、検出ユニット106に備わる厚み測定部106a及び吸収スペクトル算出部106bによりそれぞれ算出されて、判定部107bへと入力される。 Based on the measured thickness and absorption spectrum of the determination target 103 and a plurality of reference data stored in the storage unit 107a, the determination unit 107b determines whether the determination target 103 is a recycled resin. Do. The measured thickness and absorption spectrum of the determination object 103 are respectively calculated by the thickness measurement unit 106a and the absorption spectrum calculation unit 106b provided in the detection unit 106, and input to the determination unit 107b.

 判定部107bによる判定処理の方法について、図2及び図4A、並びに図5に示すフローチャートを用いて説明する。 The method of the determination process by the determination unit 107b will be described with reference to FIGS. 2 and 4A and the flowchart shown in FIG.

 最初に、検出ユニット106から入力された、被判定物103の測定厚みと等しい厚みのリサイクル樹脂における基準データ(選択基準データ)を、記憶部107aに記憶されている複数の基準データの中から判定部107bで選択する(ステップS1)。被判定物103の測定厚みと等しい厚みの選択基準データが無い場合には、許容範囲を予め決めておき、被判定物103の測定厚みに対して許容範囲内に入る厚みの選択基準データを、被判定物103の測定厚みに対応する厚みのリサイクル樹脂における選択基準データとして、選択するようにしてもよい。これについては、後述する。 First, reference data (selection reference data) for a recycled resin having a thickness equal to the measured thickness of the determination target object 103 input from the detection unit 106 is determined from a plurality of reference data stored in the storage unit 107a. The selection is made by the unit 107b (step S1). When there is no selection reference data having a thickness equal to the measured thickness of the object 103 to be determined, an allowable range is determined in advance, and thickness selection reference data that falls within the allowable range with respect to the measured thickness of the object 103 to be determined. You may make it select as selection reference data in the recycled resin of the thickness corresponding to the measured thickness of the to-be-determined object 103. FIG. This will be described later.

 次に、検出ユニット106から入力された被判定物103の吸収スペクトルと、選択基準データとを判定部107bで比較して、被判定物103の吸収スペクトルの判定を判定部107bで行う(ステップS2)。このとき、入力された吸収スペクトルは、ゲインを判定部107bで調整された後に、スペクトルの平準化が判定部107bで行われる。 Next, the determination unit 107b compares the absorption spectrum of the determination target 103 input from the detection unit 106 with the selection reference data, and the determination unit 107b determines the absorption spectrum of the determination target 103 (step S2). ). At this time, after the gain of the input absorption spectrum is adjusted by the determination unit 107b, spectrum leveling is performed by the determination unit 107b.

 最後に、ステップS2の比較に基づいて、被判定物103がリサイクル樹脂か否かを判定部107bで判定する(ステップS3)。ステップS3における判定の方法の一例として、吸収スペクトルの特徴量から必要な情報を抽出するケモメトリックス手法を判定部107bで用いる。ケモメトリックス手法とは、算出した多数及び多変量のデータから数学的手法又は統計的手法を用いて、最適な処理方法で有効な結果を推定する手法である。なお、他の手法として、線形重回帰分析法、又は主成分分析法、PLS(Partial Least Squires)回帰分析法等を判定部107bで用いても良い。また、クラスター分析を用いても良く、その中でマハラノビス距離又は非対称マハラノビス距離を判定部107bで用いても良い。 Finally, based on the comparison in step S2, the determination unit 107b determines whether the determination object 103 is a recycled resin (step S3). As an example of the determination method in step S3, the determination unit 107b uses a chemometric technique that extracts necessary information from the feature amount of the absorption spectrum. The chemometrics method is a method for estimating an effective result by an optimal processing method using a mathematical method or a statistical method from calculated multivariate data and multivariate data. As another method, a linear multiple regression analysis method, a principal component analysis method, a PLS (Partial Last Squires) regression analysis method, or the like may be used in the determination unit 107b. Further, cluster analysis may be used, and among them, the Mahalanobis distance or the asymmetric Mahalanobis distance may be used in the determination unit 107b.

 以上のように、リサイクル樹脂の判定装置100によって、被判定物103が、リサイクル樹脂であるか否かが判定される。 As described above, it is determined by the recycled resin determination device 100 whether or not the determination target object 103 is recycled resin.

 ところで、ステップS1では、測定厚みと等しい厚みのリサイクル樹脂における基準データを、記憶部107aに記憶されている複数の基準データの中から選択基準データとして選択する場合を説明している。ミックスプラスチックを構成する被判定物103には、様々な厚みの被判定物103が含まれる。つまり、測定厚みと等しい厚みの基準データを選択するためには、膨大な量の基準データを予め記憶部107aに記憶させねばならない。扱う基準データの量が膨大になれば、この中から、特定の基準データを選択する判定部107bにも負担を強いることになる。そのため、判定部107bの処理速度の低下を招く場合が生じる。 Incidentally, in step S1, a case is described in which the reference data for the recycled resin having the same thickness as the measured thickness is selected as the selection reference data from among a plurality of reference data stored in the storage unit 107a. The determination object 103 constituting the mixed plastic includes the determination objects 103 having various thicknesses. That is, in order to select reference data having a thickness equal to the measured thickness, a huge amount of reference data must be stored in the storage unit 107a in advance. If the amount of reference data to be handled becomes enormous, a burden is imposed on the determination unit 107b that selects specific reference data from among them. For this reason, the processing speed of the determination unit 107b may be reduced.

 そこで、発明者らは、選択基準データが対応する厚みと、被判定物103の測定厚みとの差が、0.5mm以下となるように、選択基準データを判定部107bで選択すればよいことを実験の結果から見出した。こうすることで、測定厚みと一致する厚みのリサイクル樹脂における選択基準データを判定部107bで用いなくとも、判定精度の低下を招くことなく、リサイクル樹脂の判定が判定部107bで可能であることを発明者らは見出した。これについて実験データに基づいて説明する。 Therefore, the inventors may select the selection criterion data by the determination unit 107b so that the difference between the thickness corresponding to the selection criterion data and the measured thickness of the determination target object 103 is 0.5 mm or less. Was found from the experimental results. By doing so, it is possible to determine the recycled resin in the determination unit 107b without causing a decrease in determination accuracy without using the selection reference data in the recycled resin having a thickness matching the measured thickness in the determination unit 107b. The inventors have found. This will be described based on experimental data.

 図3から、透明なPSの吸収スペクトルには、各厚みに応じたノイズが、基準吸収スペクトルに乗った状態である。つまり、基準データは、基準吸収スペクトルと、厚みに対応したノイズとを含むデータである。ここでのノイズとは、搬送路(コンベアベルト101)からの反射光(赤外反射光105)に起因する吸収スペクトルを言う。 From FIG. 3, in the absorption spectrum of transparent PS, noise corresponding to each thickness is on the reference absorption spectrum. That is, the reference data is data including a reference absorption spectrum and noise corresponding to the thickness. Here, the noise refers to an absorption spectrum caused by reflected light (infrared reflected light 105) from the conveyance path (conveyor belt 101).

 基準吸収スペクトルは、樹脂の厚みによらず一定であるから、ノイズは厚みに起因して変化する。つまり、厚みを算出した樹脂の吸収スペクトルから、樹脂の厚みに対応するノイズを減算すれば、厚みに依存しない基準吸収スペクトルのみに基づく判定が可能となる。 Since the standard absorption spectrum is constant regardless of the thickness of the resin, the noise changes due to the thickness. That is, if noise corresponding to the thickness of the resin is subtracted from the absorption spectrum of the resin whose thickness has been calculated, determination based only on the reference absorption spectrum that does not depend on the thickness becomes possible.

 そこで、厚みが1mmのPSについて算出した吸収スペクトルから、厚みが2mm、3mmのPSにそれぞれ対応するノイズを減算した吸収スペクトル、および、PSの基準吸収スペクトルを図6にそれぞれ示す。図6では、縦軸に吸光度、横軸に波長(μm)を示す。PSの吸収スペクトルの特徴量として、波長帯域1.763μmにピークを示すことが知られている。図6のP1領域が、PSの吸収スペクトルのピークが現れる場所である。P1領域において、厚みが2mm、3mmのPSに対応するノイズを減算した吸収スペクトルは、基準吸収スペクトルからのばらつきを有するため、リサイクル樹脂を精度良く判定できない。このことから、被判定物103の測定厚みと、選択基準データに含まれるノイズが対応する厚みとの間に、1mm以上の差がある場合、精度良く判定を行うことができないことが理解できる。 Therefore, FIG. 6 shows an absorption spectrum obtained by subtracting noise corresponding to PS having a thickness of 2 mm and 3 mm from an absorption spectrum calculated for PS having a thickness of 1 mm, and a reference absorption spectrum of PS, respectively. In FIG. 6, the vertical axis represents absorbance and the horizontal axis represents wavelength (μm). As a feature quantity of an absorption spectrum of PS, it is known that a peak is shown in a wavelength band of 1.763 μm. The P1 region in FIG. 6 is where the peak of the PS absorption spectrum appears. In the P1 region, the absorption spectrum obtained by subtracting noise corresponding to PS having a thickness of 2 mm or 3 mm has a variation from the reference absorption spectrum, and therefore, the recycled resin cannot be accurately determined. From this, it can be understood that when there is a difference of 1 mm or more between the measured thickness of the determination target object 103 and the thickness corresponding to the noise included in the selection reference data, the determination cannot be performed with high accuracy.

 次に、厚みが1.5mmのPSについて算出した吸収スペクトルから、厚み1mmのPSに対応するノイズを減算した吸収スペクトル、及び、PSの基準吸収スペクトルを図7にそれぞれ示す。図7では、縦軸に吸光度、横軸に波長(μm)を示す。図7のP2領域が、PSの吸収スペクトルのピークが現れる場所である。このように、被判定物103の測定厚みに対して0.5mm差のあるノイズ(厚み1mmのPSに対応するノイズ)を用いて補正を行った場合は、特徴量を示すピークを確認することができ、精度良く判定することが可能である。 Next, FIG. 7 shows an absorption spectrum obtained by subtracting noise corresponding to PS having a thickness of 1 mm from the absorption spectrum calculated for PS having a thickness of 1.5 mm, and a reference absorption spectrum of PS, respectively. In FIG. 7, the vertical axis represents absorbance and the horizontal axis represents wavelength (μm). The P2 region in FIG. 7 is where the peak of the PS absorption spectrum appears. As described above, when correction is performed using noise having a difference of 0.5 mm with respect to the measured thickness of the determination target object 103 (noise corresponding to PS having a thickness of 1 mm), a peak indicating a feature amount should be confirmed. Can be determined with high accuracy.

 前記に一例を示したような実験を行った結果、発明者らは、被判定物103の測定厚みとの差が0.5mm以内の厚みのリサイクル樹脂における基準データを選択基準データに用いれば、被判定物103がリサイクル樹脂か否かを判定可能であると発明者らは見出した。 As a result of conducting an experiment as shown in the example above, the inventors used the reference data in the recycled resin having a thickness within 0.5 mm as a difference from the measured thickness of the determination target object 103 as the selection reference data. The inventors have found that it is possible to determine whether the object 103 is a recycled resin.

 すなわち、図4Aの記憶部107aには、1mm間隔の厚みのリサイクル樹脂における基準データを記憶させれば良いことが理解できる。選択基準データの厚みと測定厚みとの差の最大値が0.5mmとなるからである。これにより、記憶部107aに予め記憶すべき基準データの量を低減させることが可能である。また、このように、選択基準データの厚みと測定厚みとの差に0.5mmの許容範囲を設けることで、判定部107bも、選択対象となる基準データの量が少なくなるため、高速に処理を行うことが可能である。 That is, it can be understood that the storage unit 107a in FIG. 4A may store reference data for recycled resin having a thickness of 1 mm. This is because the maximum difference between the thickness of the selection reference data and the measured thickness is 0.5 mm. Thereby, it is possible to reduce the amount of reference data to be stored in advance in the storage unit 107a. In addition, by providing an allowable range of 0.5 mm for the difference between the thickness of the selection reference data and the measured thickness in this way, the determination unit 107b also reduces the amount of reference data to be selected, so that it can process at high speed. Can be done.

 さらに、本発明者らは、被判定物103の厚みを測定するオーダーについても、1mm間隔で良いことを見出した。被判定物103の厚み(測定厚み)を1mm間隔で測定すれば、測定厚みと、実際の被判定物103の厚みとの差が、0.5mm以下となるからである。この場合、測定する間隔に対応させた厚みのリサイクル樹脂における基準データを記憶部107aに記憶させればよい。 Furthermore, the present inventors have found that the order of measuring the thickness of the object 103 to be determined may be 1 mm intervals. This is because if the thickness (measurement thickness) of the object to be determined 103 is measured at intervals of 1 mm, the difference between the measured thickness and the actual thickness of the object to be determined 103 is 0.5 mm or less. In this case, the reference data for the recycled resin having a thickness corresponding to the measurement interval may be stored in the storage unit 107a.

 1mm間隔で被判定物103の測定厚みを測定するための手段として、図2に示す参照ユニット112を説明する。 A reference unit 112 shown in FIG. 2 will be described as means for measuring the measured thickness of the determination target object 103 at intervals of 1 mm.

 参照ユニット112は、ファイバ型光分波器120と、反射ミラー群121とを備えて構成される。ファイバ型光分波器120は、入射した参照光L2を波長毎に分波する。反射ミラー群121は、ファイバ型光分波器120で分波された参照光L2をそれぞれ異なる光路長となるように反射する複数のミラー121a~121eで構成される。参照光L2に含まれる光の波長を780~860nmに設定しているため、ここでは、ファイバ型光分波器120で、参照光L2を波長780nm、800nm、820nm、840nm、860nmの光にそれぞれ分光する。この場合、反射ミラー群121を構成する各ミラー121a~121eは、1mm間隔で、波長毎に異なる光路長差を付与するように配置されている。具体的には、参照光L2に含まれる波長780nmの光の光路長が、コンベアベルト101で反射する物体光L1の光路長よりも1mm短くなるように、波長780nmの光を反射するミラー121aが配置されている。また、参照光L2に含まれる波長800nmの光の光路長が、コンベアベルト101から反射する物体光L1の光路長よりも2mm短くなるように、波長800nmの光を反射するミラー121bが配置されている。同様に、波長820nmの光を反射するミラー121cと、波長840nmの光を反射するミラー121dと、波長860nmの光を反射するミラー121eとは、物体光L1と参照光L2との光路長差が、それぞれ、3mmと、4mmと、5mmとなるように配置されている。これにより、参照光L2と物体光L1とを干渉させた際に、強め合った波長を検出することで、物体光L1の光路長を測定できる。 The reference unit 112 includes a fiber type optical demultiplexer 120 and a reflection mirror group 121. The fiber type optical demultiplexer 120 demultiplexes the incident reference light L2 for each wavelength. The reflection mirror group 121 includes a plurality of mirrors 121a to 121e that reflect the reference light L2 demultiplexed by the fiber-type optical demultiplexer 120 so as to have different optical path lengths. Since the wavelength of the light included in the reference light L2 is set to 780 to 860 nm, here, the reference light L2 is converted into light having wavelengths of 780 nm, 800 nm, 820 nm, 840 nm, and 860 nm, respectively. Spectroscopy. In this case, the mirrors 121a to 121e constituting the reflecting mirror group 121 are arranged so as to give different optical path length differences for each wavelength at intervals of 1 mm. Specifically, the mirror 121a that reflects light having a wavelength of 780 nm is arranged so that the optical path length of light having a wavelength of 780 nm included in the reference light L2 is 1 mm shorter than the optical path length of object light L1 reflected by the conveyor belt 101. Has been placed. In addition, a mirror 121b that reflects light having a wavelength of 800 nm is disposed so that the optical path length of light having a wavelength of 800 nm included in the reference light L2 is 2 mm shorter than the optical path length of object light L1 reflected from the conveyor belt 101. Yes. Similarly, the mirror 121c that reflects light with a wavelength of 820 nm, the mirror 121d that reflects light with a wavelength of 840 nm, and the mirror 121e that reflects light with a wavelength of 860 nm have an optical path length difference between the object light L1 and the reference light L2. Are arranged to be 3 mm, 4 mm, and 5 mm, respectively. Thereby, when the reference light L2 and the object light L1 are caused to interfere, the optical path length of the object light L1 can be measured by detecting the strengthened wavelength.

 物体光L1は、コンベアベルト101上の被判定物103の表面で反射されるため、例えば、波長780nmの光が干渉により強まった場合、被判定物103の表面は、コンベアベルト101から1mmの位置(高さ)にあるとわかる。被判定物103は、ミックスプラスチックとして小片に粉砕されているため、コンベアベルト101からの被判定物103の表面の位置(高さ)を、被判定物103の厚みとみなすことが可能である。従って、物体光L1の光路長を測定することで、被判定物103の厚みを測定可能である。 Since the object light L1 is reflected by the surface of the determination object 103 on the conveyor belt 101, for example, when light with a wavelength of 780 nm is strengthened by interference, the surface of the determination object 103 is positioned 1 mm from the conveyor belt 101. You can see that it is at (height). Since the determination object 103 is crushed into small pieces as a mixed plastic, the position (height) of the surface of the determination object 103 from the conveyor belt 101 can be regarded as the thickness of the determination object 103. Therefore, the thickness of the determination target object 103 can be measured by measuring the optical path length of the object light L1.

 なお、被判定物103の厚みが1.2mmの場合、厚み1mmに対応する波長(780nm)の参照光L2と厚み2mmに対応する波長(800nm)の参照光L2とが物体光L1と干渉を生じる。この場合、厚み1mmに対応する波長(780nm)の参照光L2による干渉が、厚み2mmに対応する波長(800nm)の参照光L2による干渉よりも強く生じるため、被判定物103の厚み(測定厚み)を1mmとして測定する。このとき、測定厚みを1.0mmとした、実際の厚みが1.2mmの被判定物103について、厚み1mmのリサイクル樹脂における基準データ(選択基準データ)を用いて、判定を行う。 When the thickness of the object 103 to be determined is 1.2 mm, the reference light L2 having a wavelength corresponding to the thickness of 1 mm (780 nm) and the reference light L2 having a wavelength corresponding to the thickness of 2 mm (800 nm) interfere with the object light L1. Arise. In this case, interference by the reference light L2 having a wavelength (780 nm) corresponding to the thickness of 1 mm is stronger than interference by the reference light L2 having a wavelength (800 nm) corresponding to the thickness of 2 mm. ) Is measured as 1 mm. At this time, determination is performed using the reference data (selection reference data) for the recycled resin having a thickness of 1 mm with respect to the determination target object 103 having a measured thickness of 1.0 mm and an actual thickness of 1.2 mm.

 このように、1mm間隔で測定厚みを測定すれば、実際の厚みとの差が0.5mm以下となるため、1mm間隔で準備した基準データを用いることが可能である。これにより、予め準備すべき基準データの数を減らすことが可能である。さらに、厚みの測定を1mm間隔で行うため、演算処理部107の負荷を低減できる。この場合、測定する厚みの間隔と、対応する厚みとを一致させた基準データを準備する必要がある。 Thus, if the measured thickness is measured at intervals of 1 mm, the difference from the actual thickness is 0.5 mm or less, so it is possible to use reference data prepared at intervals of 1 mm. Thereby, the number of reference data to be prepared in advance can be reduced. Furthermore, since the thickness is measured at intervals of 1 mm, the load on the arithmetic processing unit 107 can be reduced. In this case, it is necessary to prepare reference data in which the thickness interval to be measured is matched with the corresponding thickness.

 本第1実施形態では、一例として、厚みが0.3~5.5mm程度の被判定物103を想定しているため、参照ユニット112における反射ミラー群121のミラーの数を5枚とし、準備する基準データも、1mmから、1mm間隔で、5mmまでの厚みに対応する5種類としている。なお、被判定物103の厚みばらつきが変化すれば、それに対応させて、ミラーの数を6枚以上または4枚以下とし、基準データの種類又は数を変化させればよい。さらに、光源111から出射される測定光の波長も780以上1360nm未満の範囲で変化させればよい。 In the first embodiment, as an example, the determination target 103 having a thickness of about 0.3 to 5.5 mm is assumed. Therefore, the number of mirrors in the reflection mirror group 121 in the reference unit 112 is five, and preparation is performed. The reference data to be used are also five types corresponding to thicknesses from 1 mm to 1 mm at intervals of 1 mm. If the thickness variation of the determination target 103 changes, the number of mirrors may be set to 6 or more and 4 or less, and the type or number of reference data may be changed. Furthermore, the wavelength of the measurement light emitted from the light source 111 may be changed in a range of 780 or more and less than 1360 nm.

 また、1mm間隔の光路長を有する参照光L2に干渉を生じさせるために、光源111の可干渉距離を、1mm以上とする。さらに、3種類以上の波長の参照光L2が同時に干渉しないためにも、可干渉距離を2mm未満とすることが望ましい。 Further, in order to cause interference in the reference light L2 having an optical path length of 1 mm intervals, the coherence distance of the light source 111 is set to 1 mm or more. Furthermore, it is desirable that the coherence distance is less than 2 mm so that the reference light L2 having three or more types of wavelengths does not interfere simultaneously.

 なお、各波長の干渉光の強度の比率から、0.1mm以下の精度で被判定物103の厚みを測定することが可能である。例えば、厚みが1.2mmの被判定物103と厚みが1.3mmの被判定物103とでは、1mmに対応する波長(780nm)の参照光L2の干渉強度と、2mmに対応する波長(800nm)の参照光L2の干渉強度との差が異なる。よって、この干渉強度の差を事前に測定しておく事で、0.1mm以下の精度で測定厚みの測定が可能である。 It should be noted that the thickness of the determination object 103 can be measured with an accuracy of 0.1 mm or less from the ratio of the intensity of the interference light of each wavelength. For example, in the object 103 having a thickness of 1.2 mm and the object 103 having a thickness of 1.3 mm, the interference intensity of the reference light L2 having a wavelength corresponding to 1 mm (780 nm) and a wavelength corresponding to 2 mm (800 nm) ) Is different from the interference intensity of the reference light L2. Therefore, by measuring the difference in interference intensity in advance, the measurement thickness can be measured with an accuracy of 0.1 mm or less.

 ここでは、被判定物103が、PSの場合について説明したが、被判定物103がPP又はABSなどの他の樹脂でも、同様の結果が得られる。樹脂の種類によらずに、厚みに対応する補正データ(厚みに対応したノイズ)を、算出した吸収スペクトルから減算することで、被判定物103の判定を精度良く行うことができる。ただし、樹脂の種類毎にそれぞれ対応した補正データを用いれば、より高精度に、樹脂の判定を行うことが可能である。樹脂の厚みが大きくなると、樹脂自身による吸収の影響を受け、これに起因して樹脂の種類毎に厚みに対応する補正データが異なる場合があるからである。なお、厚みが0.5mmより小さい場合は、搬送路(コンベアベルト101)の吸収スペクトル(搬送路吸収スペクトル)を補正データとして用いればよい。 Here, although the case where the determination target 103 is PS has been described, the same result can be obtained even when the determination target 103 is other resin such as PP or ABS. Regardless of the type of resin, the determination object 103 can be accurately determined by subtracting the correction data corresponding to the thickness (noise corresponding to the thickness) from the calculated absorption spectrum. However, if correction data corresponding to each type of resin is used, it is possible to determine the resin with higher accuracy. This is because if the thickness of the resin is increased, the resin is affected by absorption by the resin itself, and the correction data corresponding to the thickness may be different for each type of resin due to this. When the thickness is smaller than 0.5 mm, the absorption spectrum (conveyance path absorption spectrum) of the conveyance path (conveyor belt 101) may be used as the correction data.

 但し、基準吸収スペクトルは、樹脂の種類毎に異なるため、樹脂の種類毎に異なる基準吸収スペクトルを記憶部107aに準備又は取得する必要がある。従って、樹脂の種類毎に異なる基準データを記憶部107aに記憶するのが好ましい。基準データは、基準吸収スペクトルと、厚みに対応したノイズ(補正データ)とを含むからである。 However, since the reference absorption spectrum is different for each type of resin, it is necessary to prepare or acquire a different reference absorption spectrum for each type of resin in the storage unit 107a. Therefore, it is preferable to store different reference data for each type of resin in the storage unit 107a. This is because the reference data includes a reference absorption spectrum and noise (correction data) corresponding to the thickness.

 なお、被判定物103の吸収スペクトルと、選択基準データとを用いて判定部107bで被判定物103の判定を行う際に、ノイズを減算した被判定物103の吸収スペクトルと、基準吸収スペクトルとに基づいて被判定物103の判定を行ってもよい。また、ノイズを加算した基準吸収スペクトルと、被判定物103の吸収スペクトルとに基づいて、被判定物103の判定を行ってもよい。また、ノイズを加算した基準吸収スペクトルを基準データとして厚み毎に複数種類予め準備し、この基準データの中で選択した選択基準データと被判定物103の吸収スペクトルとに基づいて、被判定物103の判定を行ってもよい。 When the determination unit 107b determines the determination target 103 using the absorption spectrum of the determination target 103 and the selection reference data, the absorption spectrum of the determination target 103 obtained by subtracting noise, the reference absorption spectrum, and the like. The determination object 103 may be determined based on the above. Further, the determination of the determination target object 103 may be performed based on the reference absorption spectrum added with noise and the absorption spectrum of the determination target object 103. Further, a plurality of types of reference absorption spectra to which noise has been added are prepared in advance as reference data for each thickness, and based on the selection reference data selected from the reference data and the absorption spectrum of the determination target 103, the determination target 103 The determination may be made.

 次に、図1に示すリサイクル樹脂の判定装置100による樹脂判別手法のフローを、図8を用いて説明する。 Next, the flow of the resin discrimination method by the recycled resin determination device 100 shown in FIG. 1 will be described with reference to FIG.

 まず、ホッパー102の動作により、その上部に配置されている被判定物103が、コンベアベルト101上の投入領域93Aの任意の場所に投下される(ステップS21)。 First, by the operation of the hopper 102, the determination object 103 arranged on the upper part is dropped to an arbitrary place in the input area 93A on the conveyor belt 101 (step S21).

 次に、コンベアベルト101は常に稼動しているので、その流れによって、被判定物103が検出ユニット106の下方の検出領域93Bに運ばれる。検出領域93Bに運ばれた被判定物103に対して、検出ユニット106の厚み測定部106aと吸収スペクトル算出部106bとによって測定厚みの測定、及び、吸収スペクトルの算出が実施される(ステップS22)。 Next, since the conveyor belt 101 is always in operation, the object 103 is conveyed to the detection area 93B below the detection unit 106 by the flow. The measured thickness and the absorption spectrum are measured by the thickness measuring unit 106a and the absorption spectrum calculating unit 106b of the detection unit 106 for the determination target 103 carried to the detection region 93B (step S22). .

 次に、被判定物103の測定厚み、及び、吸収スペクトルに基づいて、被判定物103がリサイクル樹脂か否かを判定部107bで判定する。判定の手段は、図5に示すフローの通りである(ステップS23)。 Next, the determination unit 107b determines whether the determination target 103 is a recycled resin based on the measured thickness of the determination target 103 and the absorption spectrum. The determination means is as shown in the flow of FIG. 5 (step S23).

 次に、リサイクル樹脂と判定された被判定物103(リサイクル樹脂103a)は、制御部97の制御の下に、パルスエアノズル108による吹き飛ばしが実施され、リサイクルボックス109に収納される(ステップS24)。 Next, to-be-determined object 103 (recycled resin 103a) determined to be recycled resin is blown out by pulse air nozzle 108 under the control of control unit 97 and stored in recycling box 109 (step S24).

 リサイクル樹脂でないと判定された被判定物103(非リサイクル樹脂103b)は、制御部97の制御の下に、パルスエアノズル108による吹き飛ばしが実施されず、コンベアベルト101からの自由落下により非リサイクルボックス110に収納される(ステップS25)。 The to-be-determined object 103 (non-recycled resin 103 b) determined not to be recycled resin is not blown out by the pulse air nozzle 108 under the control of the control unit 97, and the non-recycled box 110 is caused by free fall from the conveyor belt 101. (Step S25).

 以上のように、被判定物103の中から、リサイクル樹脂103aを判定部107bで判定し、判定したリサイクル樹脂103aのみをパルスエアノズル108で選別することが可能である。 As described above, it is possible to determine the recycled resin 103a from the determination object 103 by the determination unit 107b and to select only the determined recycled resin 103a by the pulse air nozzle 108.

 なお、選別部又は選別機構であるパルスエアノズル108を複数ラインならべて、それぞれに対応したリサイクルボックス109を準備しておけば、たとえばPPとPSとそれ以外といった分別も可能となる。 In addition, if a plurality of lines of pulse air nozzles 108 as a sorting unit or a sorting mechanism are arranged and a recycle box 109 corresponding to each is prepared, sorting such as PP and PS can be performed.

 なお、外部クロックによって、検出ユニット106に備わる厚み測定部106aと吸収スペクトル算出部106bとを同期して動作させるが、基本的には、同じ測定点で、測定厚みのデータと吸収スペクトルのデータとが一度に算出される。 Although the thickness measurement unit 106a and the absorption spectrum calculation unit 106b provided in the detection unit 106 are operated in synchronization with an external clock, basically, the measurement thickness data and the absorption spectrum data are measured at the same measurement point. Are calculated at once.

 なお、ここでは、全光透過率が70%以上の樹脂を、透明な樹脂として説明している。 Here, a resin having a total light transmittance of 70% or more is described as a transparent resin.

 なお、図4Bに示すように、基準データ取得部の別の例として、記憶部107aとは別に設けた基準データ取得部107cから基準データを必要に応じて取得してもよい。また、通信回線107dを経由して、外部のデータベース107eから基準データを必要に応じて基準データ取得部107cで取得してもよい。 As shown in FIG. 4B, as another example of the reference data acquisition unit, reference data may be acquired as necessary from a reference data acquisition unit 107c provided separately from the storage unit 107a. Further, the reference data may be acquired by the reference data acquisition unit 107c as needed from the external database 107e via the communication line 107d.

 また、パルスエアノズル108は、コンベアベルト101の幅方向に複数あれば、コンベアベルト101の幅方向に複数個の被判定物103がコンベアベルト101に載置されていても、複数の被判定物103を個々に判別可能である。
<第1変形例>
 図9に、第1実施形態の参照ユニット112の変形例である参照ユニット133を示す。
In addition, if there are a plurality of pulse air nozzles 108 in the width direction of the conveyor belt 101, a plurality of determination objects 103 are provided even if a plurality of determination objects 103 are placed on the conveyor belt 101 in the width direction of the conveyor belt 101. Can be individually determined.
<First Modification>
FIG. 9 shows a reference unit 133 that is a modification of the reference unit 112 of the first embodiment.

 図2に示す参照ユニット112では、ファイバ型光分波器120の大きさが課題となって、小型化が困難である。そこで、図9の第1変形例の参照ユニット133では、ファイバ型光分波器120の代わりに、回折格子134を用いて小型化を図る。この参照ユニット133は、回折格子134と、複数(図9では5個)の集光レンズで構成される集光レンズ群135と、複数(図9では5個)の反射ミラーで構成される反射ミラー群136とで構成される。 In the reference unit 112 shown in FIG. 2, the size of the fiber-type optical demultiplexer 120 is a problem, and it is difficult to reduce the size. Therefore, in the reference unit 133 of the first modified example in FIG. 9, the diffraction grating 134 is used instead of the fiber type optical demultiplexer 120 to reduce the size. The reference unit 133 includes a diffraction grating 134, a condensing lens group 135 composed of a plurality (five in FIG. 9) of condensing lenses, and a reflection composed of a plurality of (five in FIG. 9) reflecting mirrors. And a mirror group 136.

 参照ユニット133に入射した参照光L2は、回折格子134にて、波長780nmと、800nmと、820nmと、840nmと、860nmとに分光される。分光された参照光L2は、集光レンズ群135のそれぞれの集光レンズを介して、反射ミラー群136のそれぞれの反射ミラーにて反射される。反射ミラー群136のそれぞれの反射ミラーにて反射した参照光L2は、その光路を逆進するようにして、集光レンズ群135のそれぞれの集光レンズを介して、参照ユニット133から出射する。この場合、各波長の参照光L2には1mm間隔で異なる光路長が付与されるように、回折格子134と、集光レンズ群135と、反射ミラー群136とが配置されている。 The reference light L2 incident on the reference unit 133 is split by the diffraction grating 134 into wavelengths of 780 nm, 800 nm, 820 nm, 840 nm, and 860 nm. The split reference light L2 is reflected by the respective reflecting mirrors of the reflecting mirror group 136 through the respective condensing lenses of the condensing lens group 135. The reference light L2 reflected by the respective reflecting mirrors of the reflecting mirror group 136 is emitted from the reference unit 133 via the respective condensing lenses of the condensing lens group 135 so as to travel backward in the optical path. In this case, the diffraction grating 134, the condenser lens group 135, and the reflection mirror group 136 are arranged so that different optical path lengths are given to the reference light L2 of each wavelength at intervals of 1 mm.

 これにより、第1変形例の参照ユニット133では、装置の小型化を図りつつ、参照ユニット112と同様の効果を奏することができる。 Thereby, the reference unit 133 of the first modification can achieve the same effect as the reference unit 112 while reducing the size of the apparatus.

 ここまで、図2の厚み測定部106aは、赤外光105と異なる測定光を用いる光干渉計(光干渉法)によって測定厚みを測定するものとして説明している。一方、厚み測定部106aは、三角測量器(三角測量法)によって測定厚みを測定するものであってもよい。ただし、光干渉計を用いる方が、上述の様に、取得する測定厚みのオーダーを容易に制御できるため、厚み測定部106aは光干渉計によって測定厚みを測定するものが望ましい。 Heretofore, the thickness measuring unit 106a in FIG. 2 has been described as measuring the measured thickness using an optical interferometer (optical interferometry) that uses measurement light different from the infrared light 105. On the other hand, the thickness measuring unit 106a may measure the measured thickness using a triangulation instrument (triangulation method). However, since the order of the measured thickness to be obtained can be easily controlled as described above when the optical interferometer is used, it is desirable that the thickness measuring unit 106a measures the measured thickness with the optical interferometer.

 (第2実施形態)
 第2実施形態に係る、リサイクル樹脂再生品の製造装置141について図10Aを用いて説明する。リサイクル樹脂再生品の製造装置141は、第1実施形態に係るリサイクル樹脂の判定装置100と、リサイクル樹脂成形装置142とを備えて構成される。リサイクル樹脂再生品の製造装置141は、第1実施形態に係るリサイクル樹脂の判定装置100でリサイクル樹脂と判定された被判定物103(リサイクル樹脂103a)を用いてリサイクル樹脂再生品の製造装置141でリサイクル樹脂再生品を製造する。このようなリサイクル樹脂成形装置142としては、特開2001-205632号公報に記載されている工程を実施することができる成形装置を用いることができる。よって、第1実施形態に係るリサイクル樹脂再生品の製造方法としては、第1実施形態に係るリサイクル樹脂の判定装置100で前記被判定物103がリサイクル樹脂か否かを判定する判定ステップと、判定ステップでリサイクル樹脂と判定された被判定物103(リサイクル樹脂103a)を用いてリサイクル樹脂再生品の製造装置141でリサイクル樹脂再生品をリサイクル樹脂再生品の製造装置141で製造する製造ステップとで構成されている。
(Second Embodiment)
A manufacturing apparatus 141 for recycled resin recycled products according to the second embodiment will be described with reference to FIG. 10A. The recycled resin recycled product manufacturing apparatus 141 includes the recycled resin determination apparatus 100 according to the first embodiment and a recycled resin molding apparatus 142. The recycled resin recycled product manufacturing apparatus 141 is the recycled resin recycled product manufacturing apparatus 141 using the determination target article 103 (recycled resin 103a) determined as the recycled resin by the recycled resin determining apparatus 100 according to the first embodiment. Manufactures recycled plastic products. As such a recycled resin molding apparatus 142, a molding apparatus capable of performing the steps described in JP-A-2001-205632 can be used. Therefore, as a method for manufacturing a recycled resin recycled product according to the first embodiment, the determination step of determining whether or not the determination target object 103 is the recycled resin by the recycled resin determination device 100 according to the first embodiment, A manufacturing step of manufacturing a recycled resin recycled product using the recycled resin recycled product manufacturing apparatus 141 using the determination target product 103 (recycled resin 103a) determined to be recycled resin in the step. Has been.

 この成形装置では、まず、リサイクル樹脂として判定された樹脂廃棄物(図1のリサイクル樹脂103a)の粉砕物に金属粉を混合した混合原料82を、図10Bのように、下金型83の凹部83b内に入れる。その後、混合原料82の上に、図10Cのように樹脂廃棄物のみを粉砕した粉砕物81を入れる。その後、図10Dのように、上金型83aを下降させて下金型83との間で加圧成型する。そして、上金型83aと、下金型83とを開いて下金型83から取り出すことにより、図10Eに示すような再生成形品84(リサイクル樹脂再生品)を製造できる。このようにして得た再生成形品84は表面層84aと裏打ち層84bとが一体化した2層構造となる。この表面層84aは、樹脂廃棄物を粉砕した粉砕物と金属粉との混合原料82で成形されるので、メタリック調の表面仕上がりとなる。このため、高級感を高めることができる。このような再生成形品84は、リサイクル樹脂再生品として例えば、建築材として用いられる化粧パネル等、様々な製品に適用することができる。 In this molding apparatus, first, a mixed raw material 82 in which metal powder is mixed with a pulverized product of resin waste (recycled resin 103a in FIG. 1) determined as a recycled resin is formed into a concave portion of a lower mold 83 as shown in FIG. 10B. Put in 83b. Then, the pulverized product 81 obtained by pulverizing only the resin waste as shown in FIG. 10C is put on the mixed raw material 82. Thereafter, as shown in FIG. 10D, the upper mold 83 a is lowered and pressure-molded with the lower mold 83. Then, by opening the upper mold 83a and the lower mold 83 and taking out from the lower mold 83, a recycled molded product 84 (recycled resin recycled product) as shown in FIG. 10E can be manufactured. The regenerated molded product 84 thus obtained has a two-layer structure in which the surface layer 84a and the backing layer 84b are integrated. Since the surface layer 84a is formed of the mixed raw material 82 of the pulverized resin waste and the metal powder, the surface finish is metallic. For this reason, a high-class feeling can be improved. Such a recycled molded product 84 can be applied to various products such as a decorative panel used as a building material as a recycled resin recycled product.

 本第2実施形態に係るリサイクル樹脂再生品の製造装置141により、第1実施形態に係るリサイクル樹脂の判定装置100によってリサイクル樹脂と判定された被判定物103(リサイクル樹脂103a)を用いて、リサイクル樹脂再生品を製造するリサイクル樹脂再生品の製造方法を実施することができる。このため、省資源化を図ることが可能である。 The recycled resin recycled product manufacturing apparatus 141 according to the second embodiment is recycled using the to-be-determined product 103 (recycled resin 103a) determined as the recycled resin by the recycled resin determining apparatus 100 according to the first embodiment. The manufacturing method of the recycled resin recycled product which manufactures a resin recycled product can be implemented. For this reason, it is possible to save resources.

 なお、本発明は、前記実施形態又は変形例に限定されるものではなく、その他種々の態様で実施できる。また、前記様々な実施形態又は変形例のうちの任意の実施形態又は変形例を適宜組み合わせることにより、それぞれの有する効果を奏するようにすることができる。 In addition, this invention is not limited to the said embodiment or modification, It can implement in another various aspect. In addition, by appropriately combining any of the various embodiments or modifications, it is possible to achieve the respective effects.

 本発明にかかるリサイクル樹脂の判定装置によれば、廃棄家電製品等から再資源化のための破砕されたミックスプラスチックから、所望のリサイクル樹脂を判定できる。また、本発明にかかるリサイクル樹脂再生品の製造装置によれば、リサイクル対象の樹脂と判定した被判定物を用いてリサイクル樹脂再生品を製造することが可能である。 According to the apparatus for determining recycled resin according to the present invention, a desired recycled resin can be determined from a crushed mixed plastic for recycling from waste home appliances and the like. Moreover, according to the recycled resin recycled product manufacturing apparatus according to the present invention, it is possible to manufacture a recycled resin recycled product by using a determination target determined as a resin to be recycled.

 本発明は、添付図面を参照しながら実施形態に関連して充分に記載されているが、この技術の熟練した人々にとっては種々の変形又は修正は明白である。そのような変形又は修正は、添付した請求の範囲による本発明の範囲から外れない限りにおいて、その中に含まれると理解されるべきである。 Although the present invention has been fully described in connection with embodiments with reference to the accompanying drawings, various changes or modifications will be apparent to those skilled in the art. Such changes and modifications are to be understood as being included therein unless they depart from the scope of the invention as defined by the appended claims.

Claims (9)

 透明な樹脂である被判定物を搬送する搬送装置と、
 前記被判定物に赤外光を照射する赤外光源と、
 前記赤外光が照射された前記被判定物からの赤外反射光を受光する赤外受光部と、
 前記赤外受光部で受光された前記赤外反射光から前記被判定物の吸収スペクトルを算出する吸収スペクトル算出部と、
 前記被判定物の厚みである測定厚みを測定する厚み測定部と、
 厚み毎に異なるリサイクル樹脂の基準データを予め記憶する記憶部と、
 前記基準データのうち、前記厚み測定部で測定された前記測定厚みに対応する厚みの前記リサイクル樹脂における基準データを選択基準データとして選択し、この選択基準データと、前記吸収スペクトル算出部で算出された前記吸収スペクトルとに基づいて、前記被判定物が前記リサイクル樹脂か否かを判定する判定部と、を備えるリサイクル樹脂の判定装置。
A transport device for transporting an object to be determined, which is a transparent resin;
An infrared light source for irradiating the determination object with infrared light;
An infrared light receiving unit that receives infrared reflected light from the object to be determined irradiated with the infrared light; and
An absorption spectrum calculation unit for calculating an absorption spectrum of the object to be determined from the infrared reflected light received by the infrared light receiving unit;
A thickness measuring unit for measuring a measurement thickness which is a thickness of the object to be determined;
A storage unit that stores in advance reference data for different recycled resins for each thickness;
Among the reference data, the reference data for the recycled resin having a thickness corresponding to the measured thickness measured by the thickness measurement unit is selected as selection reference data, and the selection reference data and the absorption spectrum calculation unit are calculated. And a determination unit that determines whether the determination target is the recycled resin based on the absorption spectrum.
 前記判定部は、前記基準データ取得部で取得された前記基準データのうち、前記厚み測定部で測定された前記測定厚みに基づいて、前記測定厚みとの差が0.5mm以下となる厚みの前記リサイクル樹脂における基準データを前記選択基準データとして選択し、この選択基準データと前記吸収スペクトルとに基づいて前記被判定物が前記リサイクル樹脂か否かを判定する請求項1に記載のリサイクル樹脂の判定装置。 The determination unit has a thickness at which a difference from the measurement thickness is 0.5 mm or less based on the measurement thickness measured by the thickness measurement unit among the reference data acquired by the reference data acquisition unit. The reference data of the recycled resin is selected as the selection reference data, and it is determined whether the determination object is the recycled resin based on the selection reference data and the absorption spectrum. Judgment device.  前記厚み測定部は、前記赤外光と異なる波長の測定光を用いる光干渉計によって、前記測定厚みを測定する請求項1又は2に記載のリサイクル樹脂の判定装置。 3. The recycled resin determination apparatus according to claim 1 or 2, wherein the thickness measurement unit measures the measurement thickness by an optical interferometer using measurement light having a wavelength different from that of the infrared light.  前記赤外光源は、波長1360nm以上2500nm以下の赤外光を照射し、
 前記光干渉計は、波長780nm以上1360nm未満の測定光を用いる
請求項3に記載のリサイクル樹脂の判定装置。
The infrared light source irradiates infrared light having a wavelength of 1360 nm to 2500 nm,
The recycling apparatus according to claim 3, wherein the optical interferometer uses measurement light having a wavelength of 780 nm or more and less than 1360 nm.
 前記基準データは、前記リサイクル樹脂の吸収スペクトルを含む
請求項1又は2に記載のリサイクル樹脂の判定装置。
3. The recycled resin determination apparatus according to claim 1, wherein the reference data includes an absorption spectrum of the recycled resin.
 請求項1又は2に記載のリサイクル樹脂の判定装置によって前記被判定物が前記リサイクル樹脂か否かを判定し、
 前記リサイクル樹脂と判定された被判定物を用いてリサイクル樹脂再生品を製造するリサイクル樹脂再生品の製造方法。
It is determined whether the determination object is the recycled resin by the recycled resin determination device according to claim 1 or 2,
A method for manufacturing a recycled resin recycled product, wherein a recycled resin recycled product is manufactured using the determination target determined as the recycled resin.
 請求項3に記載のリサイクル樹脂の判定装置によって前記被判定物が前記リサイクル樹脂か否かを判定し、
 前記リサイクル樹脂と判定された被判定物を用いてリサイクル樹脂再生品を製造するリサイクル樹脂再生品の製造方法。
It is determined whether or not the determination object is the recycled resin by the determination apparatus for the recycled resin according to claim 3,
A method for manufacturing a recycled resin recycled product, wherein a recycled resin recycled product is manufactured using the determination target determined as the recycled resin.
 請求項4に記載のリサイクル樹脂の判定装置によって前記被判定物が前記リサイクル樹脂か否かを判定し、
 前記リサイクル樹脂と判定された被判定物を用いてリサイクル樹脂再生品を製造するリサイクル樹脂再生品の製造方法。
It is determined whether or not the determination object is the recycled resin by the recycled resin determination device according to claim 4,
A method for manufacturing a recycled resin recycled product, wherein a recycled resin recycled product is manufactured using the determination target determined as the recycled resin.
 請求項5に記載のリサイクル樹脂の判定装置によって前記被判定物が前記リサイクル樹脂か否かを判定し、
 前記リサイクル樹脂と判定された被判定物を用いてリサイクル樹脂再生品を製造するリサイクル樹脂再生品の製造方法。
It is determined whether or not the object to be determined is the recycled resin by the recycled resin determination device according to claim 5,
A method for manufacturing a recycled resin recycled product, wherein a recycled resin recycled product is manufactured using the determination target determined as the recycled resin.
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