WO2019049266A1 - Pretreatment method for frond of oil palm and manufacturing process for biomass fuel - Google Patents

Pretreatment method for frond of oil palm and manufacturing process for biomass fuel Download PDF

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Publication number
WO2019049266A1
WO2019049266A1 PCT/JP2017/032290 JP2017032290W WO2019049266A1 WO 2019049266 A1 WO2019049266 A1 WO 2019049266A1 JP 2017032290 W JP2017032290 W JP 2017032290W WO 2019049266 A1 WO2019049266 A1 WO 2019049266A1
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WIPO (PCT)
Prior art keywords
leaves
oil palm
water
mass
oil
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PCT/JP2017/032290
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French (fr)
Japanese (ja)
Inventor
裕太 田原
鈴木 崇幸
靖訓 田中
裕司 福田
Original Assignee
太平洋セメント株式会社
リマテックホールディングス株式会社
株式会社関西再資源ネットワーク
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Application filed by 太平洋セメント株式会社, リマテックホールディングス株式会社, 株式会社関西再資源ネットワーク filed Critical 太平洋セメント株式会社
Priority to PCT/JP2017/032290 priority Critical patent/WO2019049266A1/en
Priority to JP2017561992A priority patent/JP6289789B1/en
Priority to MYPI2018000460A priority patent/MY194802A/en
Publication of WO2019049266A1 publication Critical patent/WO2019049266A1/en

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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/44Solid fuels essentially based on materials of non-mineral origin on vegetable substances
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Definitions

  • the present invention relates to a method for pretreating oil palm leaves and leaves and a method for producing biomass fuel, in effective use of oil leaves and leaves as biomass fuel.
  • Oil palm trunks (Oil Palm Trunk, hereinafter sometimes referred to as “palm trunks” or “OPT”) may be harvested and renewed every 25 to 30 years, and 2-3 oil palm harvests may be cut off.
  • a large number of oil palm stems and leaves (sometimes referred to as “palm stems and leaves” or “OPF” hereinafter), which are 30 to 50 palm trees per tree, are excreted. .
  • EFB is under development for the effective utilization technology for pulp for papermaking and biomass fuel
  • OPT is under development for the effective utilization technology for converting squeezed liquid into ethanol.
  • Patent Document 1 discloses a technique for effectively using EFB as a biomass fuel.
  • OPF oil palm stems and leaves
  • biomass power generation is expected to have the effect of suppressing the progress of global warming. For this reason, if it is understood that oil palm stems and leaves (OPF) that are not effectively used at present can be effectively used as a fuel for biomass power generation, momentum for actively using OPF is increased, and the transportation as described above There is a good possibility that the problem of can be solved by policy reasons.
  • OPF oil palm stems and leaves
  • OPF has a heat quantity equivalent to that of EFB and is sufficiently usable as a biomass fuel.
  • the alkali metal causes a chemical reaction in the heating device (power generation boiler) to generate a low melting point substance, and the low melting point substance produced is, for example, There is a risk of causing problems such as obstructing the flow of the fluidized bed in the fluidized bed heating device.
  • biomass fuel containing a large amount of chlorine is used as a fuel for power generation, there is a possibility that a low melting point substance may be generated in the power generation boiler or the power generation boiler may be corroded as the alkali metal.
  • the present inventors considered that pretreatment for removing alkali metals and chlorine from OPF is necessary.
  • the alkali metal content in the fuel is preferably 0.2% by mass or less
  • the chlorine content in the fuel is preferably 0.1% by mass or less.
  • the method for pre-treating the stems and leaves of oil palm is Heating the stems and leaves of oil palm (a), Squeezing the stems and leaves of the oil palm heated in the step (a) (b) Washing the leaves and leaves of the oil palm squeezed in the step (b) while applying physical impact (c); It comprises a step (d) of draining and then washing the leaves and leaves of the oil palm washed in the step (c) with water.
  • the plant cells in the stems and leaves of the oil palm become soft.
  • the subsequent pressing step (b) and washing step (c) the plant cells of the leaves and leaves of the oil palm are easily destroyed, and alkali metals and chlorine can be efficiently removed from the leaves and leaves of oil palm .
  • the heating step (a) can be a step of heating using steam.
  • saturated steam can be used.
  • the stems and leaves of oil palm are squeezed to destroy plant cells in the stems and leaves, and a certain amount of water contained in the stems and leaves of oil palm is removed.
  • the water is preferably removed so that the water content in the stems and leaves of oil palm is 60% by mass or less.
  • alkali metals and chlorine contained in the stems and leaves of the oil palm are removed from the stems and leaves of the oil palm together with the squeezed compressed water.
  • the plant cells constituting the stems and leaves of the oil palm are destroyed, whereby alkali metals and chlorine are easily removed from the stems and leaves of the oil palm efficiently in the next water washing step (c).
  • the leaves and leaves of the oil palm are subjected to washing while being physically shocked. That is, in this step (c), the plant cells in the stems and leaves of oil palm are washed with water while being destroyed. Thereby, the alkali metal and chlorine in the stems and leaves of oil palm that were not squeezed out in the pressing step (b) can be eluted into the washing water.
  • the physical impact in the washing step (c) may be by continuous (continuous) pressurization, but may be by intermittent application of instantaneous impact. By employing the latter, the time required for the water washing step (c) can be minimized.
  • the stems and leaves of the oil palm after the water washing step (c) is completed are drained and then water washing is performed.
  • this step (d) alkali metals and chlorine dissolved in water adhering to the surface of the leaves and leaves of oil palm can be removed.
  • this water sprinkling washing step (d) the water (water after washing) after being sprinkled on the oil palm leaves is dissolved as compared with the water after water rinsing the oil palm leaves in the water washing step (c).
  • the amount of alkali metal and chlorine is low. For this reason, after recovering the water used at the sprinkling water washing process (d), it does not matter as what is used for the flush water of a water washing process (c). As a result, the total amount of water used in the method of the present invention is reduced, and drainage treatment of water after being used in the water washing step can be omitted or simplified.
  • the squeezing step (b) is carried out, for example, by putting the oil palm stems and leaves into a squeezer and operating it. For this reason, when the stems and leaves of a large oil palm are put into the press as it is, the stems and leaves themselves of the oil palm itself are too large to be able to sufficiently squeeze in the press, or it may occur in the first place. For this reason, in the above method, it is possible to include the step (e) of crushing the palm leaves of oil palm so as to have a long fiber length of 300 mm or less before performing the pressing step (b). The crushing step (e) may be performed before the heating step (a), or may be performed after the heating step (a) and before the pressing step (b). .
  • the leaves and leaves of the oil palm are washed with water in an amount of 3 parts by mass or more and 22 parts by mass or less with respect to 1 part by mass (dry mass) of the leaves and leaves It does not matter as a thing to do.
  • the stem and leaves of the oil palm are sprayed in an amount of 3 parts by mass or more and 20 parts by mass or less with respect to 1 part by mass (dry mass) of the oil palm to be watered. It does not matter as what is sprayed and washed.
  • a step (f) of further squeezing the stems and leaves of the oil palm may be included.
  • the squeezing step (f) is performed again to extract the water contained in the plant cells of the leaves and leaves of oil palm, so it is dissolved in the water. Alkali metals and chlorine are removed. As a result, alkali metals and chlorine can be further removed from the stems and leaves of oil palm.
  • a step (g) of further washing the leaves and leaves of the oil palm with water After the step (g), a step (h) of squeezing the stems and leaves of the oil palm may be further included.
  • alkali metals and chlorine adhering to the surface of the leaves and leaves of oil palms can be further removed, and they can be contained in the disrupted plant cells etc. It is also possible to further remove trace amounts of alkali metals and chlorine remaining inside the leaves and leaves of oil palm.
  • the method for producing biomass fuel according to the present invention is After completion of the above-described method for pre-treatment of oil palm stem and leaf, drying the oil palm stem and leaf until the water content in the oil palm stem and leaf is 20% by mass or less; After the step (i), the method comprises the steps of: (j) shaping the dried leaves and leaves of the oil palm into a pellet.
  • the leaves of oil palm can be suitably used as a biomass fuel in a state where alkali metals and chlorine are sufficiently removed.
  • the size of the pellets may be a bulk density of 0.50 kg / L or more. The size of the pellet can be appropriately set in consideration of transport efficiency and handling.
  • the step (k) may be performed between the step (i) and the step (j) to crush the stems and leaves of the oil palm until the long fiber length becomes 20 mm or less.
  • the foliage of the oil palm is miniaturized and the execution of the forming step (j) is facilitated.
  • the oil and fat derived from the leaves and leaves of the oil palm obtained after completion of the method for pre-treating the leaves and leaves of oil palm described above may be used as a molding aid.
  • this fat and oil it is possible to increase the heat quantity of the pellet while enhancing the utilization efficiency of the oil and palm leaves.
  • oil palm leaves and leaves oil leaves and leaves that have not been effectively used at present can be used for utilization of biomass fuel.
  • FIG. 4 is a block diagram schematically illustrating an example of an apparatus that implements the method illustrated in the flow chart of FIG. 3;
  • FIG. 1 is a flow chart schematically showing one embodiment of a method for pre-processing a foliage of an oil palm according to the present invention and a method for producing a biomass fuel.
  • FIG. 2 is a block diagram which shows typically an example of the apparatus (It calls a "biomass fuel-ized apparatus”.) Which implements the pre-processing method of the foliage of oil palm which concerns on this invention, and the manufacturing method of biomass fuel. is there.
  • the flow of biomass material is indicated by a solid line with an arrow
  • the flow of liquid (water and oil) is indicated by a dotted line with an arrow.
  • the method for producing a biomass fuel according to the present invention includes step S10 corresponding to the pre-treatment step and step S20 corresponding to the post-treatment step.
  • the pretreatment step S10 includes a heating step S11, a pressing step S12, a water washing step S13, a water spray washing step S14, and a pressing step S15.
  • the post-processing step S20 includes a drying step S21, a crushing step S22, and a molding step S23.
  • the biomass fueling device 1 of the present embodiment is configured to include a pretreatment device 2 and a post-treatment device 3.
  • the pretreatment device 2 includes a heater 11, a hopper 12, a squeezing machine 13, a water washing device 14, a vibrating sieve (sieve) 15, a vibrating sieve 16, a washing water supply device 17, a flush water tank 18, a water pump 19, and flush water. It comprises the supply apparatus 21, the oil-water separator 22, the waste water treatment apparatus 24, and the press 25.
  • the post-processing device 3 includes a dryer 32, a crusher 33, a molding machine 34, and an oil feed pump 35.
  • the stem and leaf e1 of oil palm collected from a plantation or the like is introduced into the heater 11 and heated by the heater 11.
  • the palm leaf e1 of the oil palm is particularly rich in potassium among alkali metals, and the content thereof is 0.2 to 0.5% by mass of the leaf part and 0.8 to 1.3% by mass of the stem part .
  • the chlorine content is 0.2 to 0.4% by mass in the leaf part and 0.1 to 0.6% by mass in the stem part.
  • the stem and leaf e1 of this oil palm contains 60 to 70% by mass of water.
  • the stem and leaf e2 of the oil palm becomes a state in which the plant cells are softened. It is preferable that the degree of softness of the stem and leaf e2 of the oil palm after heating be made flexible as a whole so as not to affect the handling in the subsequent steps. More specifically, in the heating step S1, it is preferable to heat for 15 to 60 minutes using saturated steam at 100 to 200 ° C.
  • the heating device 11 is not limited to the device mode or heating principle as long as the stem and leaf e2 of the heated oil palm becomes soft and easy to handle, but heating is performed using steam or saturated steam. Is preferred.
  • the heater 11 may be a general device for softening plants, such as a steamer, a steamer, a hot air device (dryer), a hot water reservoir (pan), and the like. Among these, it is preferable to use a steamer or a steamer because it can sufficiently soften the palm leaf e1 of oil palm in a short time.
  • the pretreatment device 2 may not necessarily include the heater 11.
  • the heating step S11 corresponds to the step (a).
  • the press 13 destroys the plant cells of the oil palm stem and leaf e2 which has already been softened by pressurizing the oil palm stem and leaf e2, which has been input, and removes the alkali metal and chlorine contained in the plant cells. Squeeze out with. At this time, it is preferable to squeeze the water content of the stem and leaf e3 of the oil palm after squeezing to 60% by mass or less, and the squeezing machine 13 is not limited to that type as long as it can squeeze within this range.
  • the press 13 can use general-purpose apparatuses, such as a hydraulic press (vertical type and horizontal type), a uniaxial press (screw type), and a biaxial press (extruder). Among these, it is preferable to use a twin-screw press (extruder) because the time required is short and continuous processing is possible.
  • the alkali metal and chlorine contained in the stem and leaf e3 of the oil palm after the pressing step S12 is completed are mostly dissolved in the water contained in the stem and leaf e3 of the oil palm. Therefore, it can be said that the content of alkali metal and chlorine in the stem and leaf e3 of the oil palm is proportional to the residual water content of the stem and leaf e3 of the oil palm.
  • the residual water content of the oil and pepper e3 can be used as an indicator of the content of alkali metal and chlorine contained in the oil and fat e3.
  • the residual water content of the oil palm stem and leaf e3 is also an indicator of the degree of destruction of the plant cells of the oil palm stem and leaf e2 by the press 13. The smaller the residual water content, the greater the amount of the destroyed plant cells.
  • the residual water content of the stem and leaf e3 of this oil palm is preferably 60% by mass or less, more preferably 55% by mass or less, and 50% by mass from the viewpoint of reducing the alkali metal and chlorine contents and from the viewpoint of destroying many plant cells.
  • the following are particularly preferred. If the residual water content of the stem and leaf e3 of the oil palm is 60% by mass or less, the alkali metal content is 0.2% by mass or less by passing through the water washing step S13 and the water sprinkling cleaning step S14 performed later. It is possible to obtain an oil palm stem and leaf having a chlorine content of 0.1% by mass or less.
  • the alkali metal content of the stem and leaf e3 of the oil palm having a residual water content of 60% by mass is 0.2 to 0.8% by mass, and the chlorine content is 0.1 to 0.5% by mass.
  • the discharged water (hereinafter referred to as “pressed water”) SW1 obtained by execution of the pressing step S12 is sent to the oil / water separator 22.
  • the oil-water separator 22 separates the supplied compressed water SW1 into the water content W3 and the fat and oil content O1.
  • the oil-water separator 22 is not limited to this type as long as it can realize the function of separating water and fat from the liquid in which water and fat are mixed.
  • an oil / water separator or a centrifugal deoiling machine can be used, but from the viewpoint of cleaning the water W3 discharged out of the system after waste water treatment, the centrifugal deoiling machine by high speed centrifugal separation It is preferred to use
  • This squeezing step S12 corresponds to the step (b).
  • the stem and leaf e3 of the oil palm after the pressing step S12 is completed is delivered to the water washing device 14, where the water washing step S13 is performed.
  • the water washing step S13 is a step of washing the oil palm stem and leaf e3 while washing the oil palm stem and leaf e3 with physical impact to destroy plant cells of the oil palm stem and leaf e3.
  • the flush device 14 is supplied with flush water W1 from the flush water supply device 21, and flushes the stems and leaves e3 of the oil palm using the flush water W1.
  • the flush water supply device 21 includes a tank for storing flush water W1 and a water injection port for delivering the stored flush water W1 to the flush device 14 at a predetermined flow rate.
  • the water washing apparatus 14 is preferably configured to be able to perform water washing while intermittently applying an instantaneous physical impact to the stem and leaf e3 of the oil palm.
  • the water washing device 14 is a cylindrical device to which the flush water W1 is supplied from the flush water supply device 21, and it is physically applicable to the rotation mechanism which rotates in the axial direction and the stems and leaves e3 of the oil palm housed in this device. It is possible to adopt a configuration including an impact medium for giving a dynamic impact.
  • the washing device 14 is a cylindrical device to which the washing water W1 is supplied from the washing water supply device 21, and has a shaft provided with a plurality of paddles inside the device, and The shaft is configured to be rotatable.
  • Such devices are sometimes referred to as paddle mixers.
  • the leaves and leaves e3 of the oil palm are supplied into the apparatus from the vicinity of one end of the apparatus, and flow to the vicinity of the other end of the apparatus according to the flow of the flush water W1. In this way, while the palm leaf e3 of the oil palm moves in the water washing device 14, it is crushed by the paddle at the time when it passes through the installation site of the paddle.
  • the paddles correspond to the impact media.
  • the water washing apparatus 14 is not limited to the paddle mixer as described above as long as it can wash water while applying physical impact to the stems and leaves e3 of the oil palm.
  • a desalt separator in which the flush water W1 is supplied from the flush water supply device 21.
  • the desolate separator is a drum-shaped container having a lifter attached to its inner surface, which rotates about an axis extending in the horizontal direction or an axis slightly inclined from the horizontal direction, and is housed movably in this container This device is equipped with multiple iron rods and combines the functions of both the drum washer and the rod mill.
  • the iron rod as an impact medium has a length substantially the same as the length of the sample room of the water washing apparatus 14 with respect to the volume Am 3 of the sample room of the water washing apparatus 14
  • the impact medium may be a spherical member, and in this case, it is preferable to use a member having a diameter of 25 mm or more at a filling rate of 7 to 15%.
  • the washing device 14 a wet trommel can be employed.
  • the water washing device 14 does not necessarily have to be provided with an impact medium, and is provided with only the rotating device, and by stirring the stem and leaf e3 of the oil palm in the rotating device, It is also possible to adopt a configuration in which physical impact is given to the stem and leaf e3 of the oil palm by dropping it several times.
  • the amount of flush water W1 used in the flush step S13 is an oil palm to be cleaned from the viewpoint of efficiently removing the alkali metal and chlorine from the stems and leaves e3 of oil palm and from the viewpoint of suppressing the amount of flush water W1 used.
  • dry base dry mass basis
  • this wash water W1 is used to dissolve and remove the alkali metal and chlorine contained in the stem and leaf e3 of oil palm, it is most preferable that the water does not contain alkali metal and chlorine. .
  • the concentration of alkali metal and chlorine in the water contained in the stem and leaf e3 of oil palm is as high as 0.2 to 0.8% by mass and 0.1 to 0.5% by mass, respectively.
  • the alkali metal and chlorine content of the flush water W1 may be 0.1% by mass or less. Therefore, from the viewpoint of suppressing the amount of waste water treated by the waste water treatment apparatus 24 described later, in the present embodiment, the waste washing water W5 after being used in the water washing step S14 of the next step is used as the washing water W1. be able to.
  • the alkali metal and chlorine content of the waste cleaning water W5 is 0.02 mass% or less, and is within the range which can be used as the washing water W1.
  • the water washing step S13 corresponds to the step (c).
  • the stem and leaf e4 of the oil palm after the completion of the water washing step S13 is supplied to the vibrating sieve 15 together with the water (drain water wash water W2) used in the water washing step S13.
  • the stem and leaf e4 of the oil palm are not allowed to pass through, and a plurality of holes with a size that allows passage of water (drainage flush water W2) are provided. For this reason, the mixture of oil palm stem and leaf e4 and drained flush water W2 supplied to the vibrating screen 15 is drained and washed out of the oil palm stem and leaf e4 remaining on the upper surface of the vibrating screen 15 and drained drained on the lower surface of the vibrating screen 15. It is separated into water W2.
  • the washing water supply device 17 includes a tank for storing the washing water W4, and a water spouting water inlet for sprinkling the stored washing water W4 toward the vibrating screen 16.
  • washing water W4 used at this water spray washing process S14.
  • the amount of the water W4 sprayed is preferably 2 to 12 parts by mass (3 to 20 parts by mass on a dry basis), and more preferably 3 to 5 parts by mass, with respect to 1 part by mass of the stems and leaves e4 of oil palm Part (5 to 8 parts by mass on a dry basis).
  • the alkali metal and / or the chlorine dissolved water adhering to the surface of the stem and leaf e4 of the oil palm after the completion of the water cleaning step S13 is washed away.
  • the stem and leaf e5 of the oil palm supplied from the vibrating screen 16 has an alkali metal content of 0.2 mass% or less and a chlorine content of 0.1 mass% or less descend.
  • the vibrating sieve 16 does not allow the stem and leaf e5 of the oil palm to pass through, and a plurality of holes with a size that allows passage of water (waste water W5) is provided. Thereby, a certain amount or more of the washing water W4 (waste water W5) attached to the surface of the stem and leaf e5 of the oil palm is shaken off by the vibrating sieve 16, and the stem and leaf e5 of the oil palm is drained.
  • the vibrating sieve 16 applies vibration to the oil palm stem and leaf e5 placed on the sieve and the water attached to the oil palm stem and leaf e5 to such an extent that large water droplets do not remain on the oil palm stem and leaf e5. You can remove it.
  • the sieves of the vibrating sieve 15 and the vibrating sieve 16 separate and collect water and stems and leaves of oil palm. More specifically, the drainage wash water W2 and the oil palm stem and leaves e4, the drainage washing water W5 and the oil palm In order to separate and collect the stems and leaves e5, the nominal opening is preferably 4 mm or less, more preferably 2.8 mm or less.
  • the vibrating screen 15 and the vibrating screen 16 are provided so as to be connected to each other.
  • the oil palm stem and leaf e4 and rinse the oil palm stem and leaf e4 after draining with water if it is possible to drain the oil palm stem and leaf e5 after water spray cleaning processing is completed, it is realized with one vibrating sieve. It does not matter. That is, it does not matter if the foliage e4 of the oil palm is drained on the upstream side of one vibrating sieve and the irrigation and drainage on the foliage e4 of the palm is performed on the downstream side.
  • the drainage wash water W2 distributed by the vibrating screen 15 is delivered to the oil / water separator 22 described above.
  • the oil / water separator 22 separates the mixed fluid of the press water SW1 discharged from the press 13 and the drained flush water W2 into the water W3 and the fat and oil portion O1.
  • the mechanism for separating the squeezed water SW1 from the oil water and the mechanism for separating the drainage water W2 from the oil water may be separately provided.
  • the waste cleaning water W5 distributed by the vibrating screen 16 is collected and stored in the waste cleaning water tank 18.
  • a part of the waste washing water W5 stored in the waste washing water tank 18 is supplied to the washing water supply device 21 by the water feeding pump 19 and circulated and used as the washing water W1.
  • the other part of the waste cleaning water W5 is supplied to the waste water treatment device 24.
  • the water pump 19 is not particularly limited as long as it is a liquid pump, and a general-purpose device such as a spiral pump or a piston pump can be used.
  • the water spray cleaning step S14 corresponds to the step (d).
  • the stem and leaf e5 of the oil palm after the water spray cleaning step S14 is completed is supplied to the press 25 and the pressing step is executed again.
  • the press 25 is provided to pressurize the stem and leaf e5 of the oil palm to squeeze out the washing water W4 or the drainage washing water W5 contained in the stem and leaf e5 of the oil palm.
  • the press 25 is not particularly limited as long as it can press the water content of the stem and leaf e6 of the oil palm after pressing to 70% by mass or less, and the hydraulic press (vertical type, horizontal type) General-purpose devices such as uniaxial press (screw type), twin-screw press (extruder) and the like can be used.
  • the stem and leaf e6 of the oil palm whose water content has been reduced to 70% by mass or less by the press 25 has an alkali metal content of 0.1% by mass or less and a chlorine content of 0.05% by mass or less.
  • the compressed water SW2 discharged from the squeezer 25 is supplied to the waste water treatment device 24.
  • the water W3 separated by the oil-water separator 22 and the drainage cleaning water W5 stored in the drainage tank 18 are also supplied to the drainage processing device 24.
  • the water W3 supplied to the waste water treatment device 24, the waste wash water W5 and the squeezed water SW2 are discharged to the outside of the system as waste water W6 after being subjected to appropriate waste water treatment. Thereby, drainage treatment can be performed collectively in one place in the drainage treatment device 24.
  • waste cleaning water W5 and compressed water SW2 have high BOD (biological oxygen demand), COD (chemical oxygen demand) and SS (suspension substance), so waste water treatment equipment 24 It is preferable to use a settling tank or an activated sludge tank (aeration tank).
  • This squeezing step S15 corresponds to the step (f).
  • the pretreatment step S10 of the present invention it is possible to obtain an oil palm stem and leaf e5 having an alkali metal content of at most 0.2 mass% and a chlorine content of at most 0.1 mass%. Furthermore, as in the present embodiment, by performing the squeezing step S15 after the water spray cleaning step S14, the oil palm having an alkali metal content of 0.1 mass% or less and a chlorine content of 0.05 mass% or less A stem and leaf e6 can be obtained.
  • the leaves and leaves e6 of the oil palm after the pretreatment step S10 is carried out is introduced into the drier 32 so that its water content in the drier 32 is preferably 20% by mass or less, more preferably 17% by mass or less Be dried.
  • the dryer 32 is not particularly limited in its type and the like, as long as it can dry the palm leaves e6 of the oil palm to a water content of 20% by mass or less, but a rotary dryer capable of continuous operation can be suitably used.
  • the contained water is reduced, so that the working efficiency of the crushing step S22 and the forming step S23 in the latter stage can be improved. Thereby, the quality of the obtained biomass fuel is equalized, and the quality change due to the moisture of the obtained biomass fuel is suppressed.
  • the drying step S21 corresponds to the step (i).
  • the stem and leaf e7 of the oil palm is supplied to the crusher 33 and transformed into the stem and leaf e8 of oil palm having a long fiber length of 20 mm or less.
  • the crusher 33 general equipment such as a uniaxial crusher or a twin-screw crusher can be used.
  • the crushing step S22 is a step for crushing the stem and leaf e7 of the oil palm after the completion of the drying step S21 to improve the working efficiency of the subsequent forming step S23. Since the stem and leaf e7 of the oil palm after completion of the drying step S21 may include those having a long fiber length reaching about 300 mm, the stem and leaf e7 of oil palm is crushed in this crushing step S22, preferably 20 mm Hereinafter, it is more preferably deformed into stem and leaf e8 of oil palm of 10 mm or less. However, in the below-mentioned forming process S23, when forming is possible with the stem and leaf e7 of the oil palm after completion of the drying process S21, the crushing process S22 may be omitted.
  • the crushing step S22 corresponds to the step (k).
  • the palm leaves e8 of the oil palm are supplied to the molding machine 34 and transformed into pellets (biomass fuel) e9.
  • a pellet-like biomass fuel e9 having a bulk density of 0.50 kg / L or more, a compressive strength of 1.5 N / mm 2 or more, and a heat amount of 3500 kcal / kg or more is produced.
  • the bulk density is the test method specified in JIS Z 7302-9 "Waste solidified fuel-Part 9: Bulk density test method”
  • the crushing strength is JIS Z 8841 "granulate-strength test method”.
  • the heat quantity is a measured value obtained by the test based on the test method specified in JIS Z 7302-2 “Waste solidified fuel-Part 2: calorific value test method”.
  • a sludge-like fat and oil component O1 obtained by being separated by the oil-water separator 22 is supplied to the stem and leaf e8 of the oil palm in the molding machine 34 by the oil feeding pump 35.
  • the oil component O1 is used as a molding aid in the molding machine 34. Since the oil component O1 has a heat quantity, it can be increased by supplying it to the stems and leaves e8 of oil palm to mold the biomass fuel e9 after molding. However, when the content of the alkali metal and / or chlorine contained in the oil and fat portion O1 is large, the oil and fat portion O1 can not be used as a molding aid.
  • the size of the pellet can be appropriately determined in consideration of transport efficiency and handling.
  • the biomass fuel e9 after molding can be used as a solid fuel in a CFB (circulating fluidized bed) boiler apparatus or the like for power generation, or can be used as a coal alternative fuel in a cement burning apparatus or the like.
  • the molding step S23 corresponds to the step (j).
  • Example 1 An embodiment of the pretreatment method using the pretreatment device 2 will be described with reference to Table 1.
  • the potassium content shown in Table 1 is the result of measuring the solution obtained by completely dissolving the sample with an acid by ICP emission spectrometry.
  • the chlorine content is the test result obtained in accordance with the test method of JIS Z 7302-6 "Waste solidified fuel-Part 6: Total chlorine content test method".
  • the values without brackets in the column of removal rates of potassium and chlorine in Table 1 indicate the total removal rates (mass%) up to each step, and the values in the parentheses are removal rates from the previous step (mass%) Is shown.
  • the alkali content of the leaves and leaves of the oil palm is 0.16% by mass, and the chlorine content is 0.075% by mass. Furthermore, when pressing process S15 is performed after that, the alkali content of the foliage of an oil palm is 0.08 mass%, and the chlorine content is 0.025 mass%.
  • the alkali content of the foliage of oil palm can be reduced to 0.2 mass% or less, and chlorine content to 0.1 mass% or less.
  • FIG. 3 is a flow chart corresponding to this alternative embodiment and is shown following FIG. 1, and FIG. 4 is an example of the configuration of an apparatus for carrying out the method of this alternative embodiment according to FIG. It is illustrated. As shown in FIG. 4, in this configuration, the stem and leaf e5 of the oil palm after the water has been distributed by the vibrating sieve 16 is supplied to the dryer 32, and the drying step S21 is performed.
  • the efoliated palm oil e5 obtained after completion of the water sprinkling washing step S14 has an alkali content of 0.2% by mass or less and a chlorine content of 0.1 It can be less than mass%.
  • the pressing machine 25 shown in FIG. 2 since the pressing machine 25 shown in FIG. 2 is not provided, the water W3 and the waste cleaning water W5 are supplied to the waste water treatment apparatus 24.
  • the step of crushing the stems and leaves of oil palm may be further included before the execution of the pressing step S12.
  • the pretreatment device 2 is provided with a crusher similar to the crusher 33, and before the crusher is inserted into the stems and leaves e1 of oil palm before being introduced into the heater 11 or into the press 13.
  • the stem and leaf e2 of the oil palm may be crushed so as to have a long fiber length of 300 mm or less. Thereby, the pressing process in the pressing machine 13 can be performed efficiently.
  • This crushing step corresponds to step (e).
  • the waste washing water W5 is described as being used as the washing water W1 by circulating and supplying it to the washing water supply device 21, but this aspect is optional. In other words, all the drainage cleaning water W5 may be discharged to the drainage processing device 24.
  • the configuration is such that the pressed water SW2 discharged from the pressing machine 25 is supplied to the drainage treatment device 24, the water W3 passes through the oil / water separator 22 similarly to the pressed water SW1. May be supplied to the waste water treatment apparatus 24, and the oil and fat content O1 may be supplied to the molding machine 34.

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Abstract

The present invention provides an oil palm frond pretreatment method with which it is possible to efficiently remove alkali metals and chlorine from fronds of an oil palm (OPF). The oil palm frond pretreatment method according to the present invention comprises: step (a) for heating fronds of an oil palm; step (b) for squeezing the oil palm fronds heated in step (a); step (c) for washing the fronds squeezed in step (b) with water while a physical impact is being applied to the fronds; and step (d) for straining the oil palm fronds washed with water in step (c) and then subjecting the fronds to water spray cleaning.

Description

アブラヤシの茎葉の前処理方法、バイオマス燃料の製造方法Pretreatment method of oil palm stem and leaf, production method of biomass fuel
 本発明は、アブラヤシの茎葉をバイオマス燃料として有効利用するにあたって、アブラヤシの茎葉を前処理する方法、及びバイオマス燃料を製造する方法に関する。 TECHNICAL FIELD The present invention relates to a method for pretreating oil palm leaves and leaves and a method for producing biomass fuel, in effective use of oil leaves and leaves as biomass fuel.
 世界のパーム油生産量は5500万トンを超え、日本においても年間約70万トンのパーム油が、インスタント麺等の食品向けや、洗剤や石鹸等の非食品向けに使用されている。 The world palm oil production amount exceeds 55 million tons, and in Japan, about 700,000 tons of palm oil is used for foods such as instant noodles and non-foods such as detergents and soaps.
 ところで、パーム油の生産工程及びパーム油を産するアブラヤシのプランテーションからは、アブラヤシ果房から果実を脱果した後に残る空果房(Empty Fruit Bunches、以後「EFB」と称する場合がある。)、25~30年毎に伐採更新されるアブラヤシの樹幹(Oil Palm Trunk、以後「パーム樹幹」又は「OPT」と称する場合がある。)、及びアブラヤシ果房1個の採取につき2~3本が切り落とされ、更にパーム樹幹伐採時にはパーム樹幹1本あたり30~50本生えているアブラヤシの茎葉(Oil Palm Frond、以後「パーム茎葉」又は「OPF」と称する場合がある。)が、大量に排出される。 By the way, from the production process of palm oil and the plantation of oil palm producing palm oil, empty fruit bunch (Empty Fruit Bunches, hereinafter referred to as "EFB") which remains after defruiting fruit from oil palm fruit bunch, Oil palm trunks (Oil Palm Trunk, hereinafter sometimes referred to as "palm trunks" or "OPT") may be harvested and renewed every 25 to 30 years, and 2-3 oil palm harvests may be cut off. In addition, at the time of palm trunk harvesting, a large number of oil palm stems and leaves (sometimes referred to as “palm stems and leaves” or “OPF” hereinafter), which are 30 to 50 palm trees per tree, are excreted. .
 EFBは、製紙用パルプ原料やバイオマス燃料への有効利用技術の開発が進められており、OPTは、搾汁液のエタノール変換等の有効利用技術の開発が進められている。例えば、下記特許文献1には、EFBをバイオマス燃料として有効利用するための技術が開示されている。 EFB is under development for the effective utilization technology for pulp for papermaking and biomass fuel, and OPT is under development for the effective utilization technology for converting squeezed liquid into ethanol. For example, Patent Document 1 below discloses a technique for effectively using EFB as a biomass fuel.
 しかしながら、アブラヤシの茎葉(OPF)は、量的にはEFBやOPTを上回り、例えばマレーシア1国でも乾燥重量で年間4000万トン以上が排出されるにもかかわらず、プランテーションに放置されたままで、現時点では堆肥的活用以外には利用されていない。この理由としては、OPFは、量が多いのみならず、個々の長さが5mを超える大きさのものが存在するため、人力による運搬が困難であり、車両による運搬が必要である一方で、アブラヤシが生息しているヤシ畑には現時点では大型の車両が走行できるようなスペースが十分には確保されていないという、運搬上の課題によるところが大きい。 However, oil palm stems and leaves (OPF) exceed EFB and OPT quantitatively, for example, despite being discharged to plantations in spite of more than 40 million tons of dry weight per year in dry weight in Malaysia. In addition to composting, it is not used. The reason for this is that OPF is not only large in quantity, but because individual lengths exceed 5 m, it is difficult to carry it manually and while it needs to be carried by a vehicle, This is largely due to the transportation problem that there is not enough space in the palm fields in which oil palms live to allow large vehicles to travel.
特開2010-270320号公報JP, 2010-270320, A
 ところで、バイオマス発電は、カーボンニュートラルの観点から、温暖化の進展を抑制する効果が期待されている。このため、現時点では有効利用されていないアブラヤシの茎葉(OPF)についても、仮にバイオマス発電用燃料として有効活用できることが分かれば、積極的にOPFを有効活用する機運が高まり、前述したような運搬上の課題は、政策的な理由によって解決する可能性が十分に考えられる。 By the way, from the viewpoint of carbon neutrality, biomass power generation is expected to have the effect of suppressing the progress of global warming. For this reason, if it is understood that oil palm stems and leaves (OPF) that are not effectively used at present can be effectively used as a fuel for biomass power generation, momentum for actively using OPF is increased, and the transportation as described above There is a good possibility that the problem of can be solved by policy reasons.
 このような背景の下、本発明者らは、OPFをバイオマス燃料に利用することが可能かどうかにつき、鋭意研究を行った。その結果、OPFは、EFB同等の熱量を有しており、バイオマス燃料として十分に利用可能であることを確認した。一方で、本発明者らは、OPFが、燃料とした場合に忌避成分となるアルカリ金属や塩素を多量に含んでいることを確認した。 Under such circumstances, the present inventors conducted intensive studies as to whether it is possible to use OPF as a biomass fuel. As a result, it was confirmed that OPF has a heat quantity equivalent to that of EFB and is sufficiently usable as a biomass fuel. On the other hand, the present inventors confirmed that OPF contains a large amount of alkali metal and chlorine, which are repellent components when used as fuel.
 アルカリ金属が多く含まれているバイオマス燃料を発電用燃料に利用すると、アルカリ金属が加熱装置(発電ボイラ)内で化学反応を起こして低融点物質を生成させ、生成した低融点物質が、例えば、流動層式加熱装置内の流動層の流れを妨げる等のトラブルを生じさせるおそれがある。また、塩素が多く含まれているバイオマス燃料を発電用燃料に利用すると、アルカリ金属と同様に発電ボイラ内で低融点物質を生成させたり、発電ボイラを腐食させるおそれがある。 When a biomass fuel containing a large amount of alkali metal is used as a fuel for power generation, the alkali metal causes a chemical reaction in the heating device (power generation boiler) to generate a low melting point substance, and the low melting point substance produced is, for example, There is a risk of causing problems such as obstructing the flow of the fluidized bed in the fluidized bed heating device. In addition, when biomass fuel containing a large amount of chlorine is used as a fuel for power generation, there is a possibility that a low melting point substance may be generated in the power generation boiler or the power generation boiler may be corroded as the alkali metal.
 従って、本発明者らは、OPFをバイオマス燃料として有効活用するためには、OPFに対してアルカリ金属や塩素を除去するための前処理が必要であると考えた。具体的には、燃料中のアルカリ金属含有量は0.2質量%以下であることが好ましく、燃料中の塩素含有量は0.1質量%以下であることが好ましい。しかしながら、現時点において、OPFをバイオマス燃料として積極的に活用することについては検討されていないところ、このOPFに含まれるアルカリ金属や塩素を効率的に除去する方法についても、現時点では存在していない。 Therefore, in order to effectively utilize OPF as a biomass fuel, the present inventors considered that pretreatment for removing alkali metals and chlorine from OPF is necessary. Specifically, the alkali metal content in the fuel is preferably 0.2% by mass or less, and the chlorine content in the fuel is preferably 0.1% by mass or less. However, at present, there is no discussion about actively using OPF as a biomass fuel, but at present there is no method for efficiently removing alkali metals and chlorine contained in this OPF.
 本発明は、上記の課題に鑑み、アブラヤシの茎葉(OPF)から効率よくアルカリ金属及び塩素を除去することのできる、アブラヤシの茎葉の前処理方法を提供することを目的とする。また、本発明は、この前処理方法を経て得られたアブラヤシの茎葉を用いた、バイオマス燃料の製造方法を提供することを目的とする。 An object of the present invention is to provide a method for pretreatment of oil palm stem and leaves, which can efficiently remove alkali metals and chlorine from oil palm stem and leaves (OPF). Another object of the present invention is to provide a method for producing a biomass fuel using the oil palm leaves obtained by the pretreatment method.
 本発明に係るアブラヤシの茎葉の前処理方法は、
 アブラヤシの茎葉を加熱する工程(a)と、
 前記工程(a)によって加熱された前記アブラヤシの茎葉を圧搾する工程(b)と、
 前記工程(b)によって圧搾された前記アブラヤシの茎葉に、物理的衝撃を与えながら水洗する工程(c)と、
 前記工程(c)によって水洗された前記アブラヤシの茎葉を、水切りした後に散水洗浄する工程(d)とを有することを特徴とする。
The method for pre-treating the stems and leaves of oil palm according to the present invention is
Heating the stems and leaves of oil palm (a),
Squeezing the stems and leaves of the oil palm heated in the step (a) (b)
Washing the leaves and leaves of the oil palm squeezed in the step (b) while applying physical impact (c);
It comprises a step (d) of draining and then washing the leaves and leaves of the oil palm washed in the step (c) with water.
 上記工程(a)でアブラヤシの茎葉を加熱されることで、アブラヤシの茎葉中の植物細胞が柔らかくなる。この結果、その後に行われる圧搾工程(b)や水洗工程(c)で、アブラヤシの茎葉の植物細胞が破壊され易くなり、アルカリ金属及び塩素を効率よくアブラヤシの茎葉から除去することが可能になる。 By heating the stems and leaves of the oil palm in the step (a), the plant cells in the stems and leaves of the oil palm become soft. As a result, in the subsequent pressing step (b) and washing step (c), the plant cells of the leaves and leaves of the oil palm are easily destroyed, and alkali metals and chlorine can be efficiently removed from the leaves and leaves of oil palm .
 この加熱工程(a)は、蒸気を使用して加熱する工程とすることができる。一例としては、飽和蒸気を使用することができる。 The heating step (a) can be a step of heating using steam. As an example, saturated steam can be used.
 本発明の方法では、圧搾工程(b)において、アブラヤシの茎葉が圧搾されて茎葉中の植物細胞が破壊されると共に、アブラヤシの茎葉に含まれる水分が一定量除去される。この工程(b)の終了後に、アブラヤシの茎葉に含まれる水分が60質量%以下になるように、水分が除去されるのが好ましい。この圧搾工程(b)により、アブラヤシの茎葉に含まれていたアルカリ金属及び塩素が、搾り出された圧搾水と共にアブラヤシの茎葉から除去される。更に、この圧搾工程(b)において、アブラヤシの茎葉を構成する植物細胞が破壊されることによって、次の水洗工程(c)においてアルカリ金属及び塩素が効率よくアブラヤシの茎葉から除去されやすくなる。 In the method of the present invention, in the pressing step (b), the stems and leaves of oil palm are squeezed to destroy plant cells in the stems and leaves, and a certain amount of water contained in the stems and leaves of oil palm is removed. After the completion of this step (b), the water is preferably removed so that the water content in the stems and leaves of oil palm is 60% by mass or less. In the squeezing step (b), alkali metals and chlorine contained in the stems and leaves of the oil palm are removed from the stems and leaves of the oil palm together with the squeezed compressed water. Furthermore, in the squeezing step (b), the plant cells constituting the stems and leaves of the oil palm are destroyed, whereby alkali metals and chlorine are easily removed from the stems and leaves of the oil palm efficiently in the next water washing step (c).
 本発明の方法では、水洗工程(c)において、アブラヤシの茎葉に物理的衝撃を与えながら水洗される。すなわち、この工程(c)では、アブラヤシの茎葉中の植物細胞が破壊されながら水洗される。これにより、圧搾工程(b)では搾り出されなかったアブラヤシの茎葉中のアルカリ金属及び塩素を水洗水中に溶出させることができる。 In the method of the present invention, in the washing step (c), the leaves and leaves of the oil palm are subjected to washing while being physically shocked. That is, in this step (c), the plant cells in the stems and leaves of oil palm are washed with water while being destroyed. Thereby, the alkali metal and chlorine in the stems and leaves of oil palm that were not squeezed out in the pressing step (b) can be eluted into the washing water.
 水洗工程(c)における物理的衝撃は、継続的(連続的)な加圧によるものでも構わないが、瞬間的な衝撃を断続的に加えることによるものでも構わない。後者を採用することで、水洗工程(c)に要する時間を必要最小限に抑えることができる。 The physical impact in the washing step (c) may be by continuous (continuous) pressurization, but may be by intermittent application of instantaneous impact. By employing the latter, the time required for the water washing step (c) can be minimized.
 本発明の方法では、散水洗浄工程(d)において、水洗工程(c)が完了した後のアブラヤシの茎葉を水切りした後に散水洗浄される。この工程(d)により、アブラヤシの茎葉の表面に付着している水に溶解されているアルカリ金属及び塩素を除去することができる。 In the method of the present invention, in the water sprinkling and washing step (d), the stems and leaves of the oil palm after the water washing step (c) is completed are drained and then water washing is performed. By this step (d), alkali metals and chlorine dissolved in water adhering to the surface of the leaves and leaves of oil palm can be removed.
 なお、この散水洗浄工程(d)において、アブラヤシの茎葉に散水された後の水(洗浄後の水)は、水洗工程(c)でアブラヤシの茎葉を水洗した後の水と比較して、溶解しているアルカリ金属量及び塩素量が少ない。このため、散水洗浄工程(d)で使用された水を回収した後、水洗工程(c)の水洗水に利用するものとしても構わない。これにより、本発明の方法で使用される総水量が低減されると共に、散水洗浄工程で使用された後の水の排水処理を省略又は簡略化することができる。 In addition, in this water sprinkling washing step (d), the water (water after washing) after being sprinkled on the oil palm leaves is dissolved as compared with the water after water rinsing the oil palm leaves in the water washing step (c). The amount of alkali metal and chlorine is low. For this reason, after recovering the water used at the sprinkling water washing process (d), it does not matter as what is used for the flush water of a water washing process (c). As a result, the total amount of water used in the method of the present invention is reduced, and drainage treatment of water after being used in the water washing step can be omitted or simplified.
 ところで、アブラヤシの茎葉の中には、5mを超えるような大型のものが存在する。圧搾工程(b)は、例えば圧搾機にアブラヤシの茎葉を投入して稼働させることにより実行される。このため、大型のアブラヤシの茎葉をそのまま圧搾機に投入した場合、アブラヤシの茎葉自体が大きすぎて圧搾機内で十分に圧搾できなかったり、そもそも圧搾機内に投入できない場合も起こり得る。このため、上記方法において、圧搾工程(b)の実行前に、アブラヤシの茎葉を長繊維長が300mm以下となるように破砕する工程(e)を有するものとしても構わない。この破砕工程(e)は、加熱工程(a)の前に行われるものとしても構わないし、加熱工程(a)の後であって、圧搾工程(b)の前に行われるものとしても構わない。 By the way, among the stems and leaves of oil palm, there are large ones exceeding 5 m. The squeezing step (b) is carried out, for example, by putting the oil palm stems and leaves into a squeezer and operating it. For this reason, when the stems and leaves of a large oil palm are put into the press as it is, the stems and leaves themselves of the oil palm itself are too large to be able to sufficiently squeeze in the press, or it may occur in the first place. For this reason, in the above method, it is possible to include the step (e) of crushing the palm leaves of oil palm so as to have a long fiber length of 300 mm or less before performing the pressing step (b). The crushing step (e) may be performed before the heating step (a), or may be performed after the heating step (a) and before the pressing step (b). .
 上記方法において、水洗工程(c)では、水洗される対象となる前記アブラヤシの茎葉1質量部(乾燥質量)に対して、3質量部以上22質量部以下の水量で、前記アブラヤシの茎葉を水洗するものとしても構わない。同様に、散水洗浄工程(d)では、散水される対象となる前記アブラヤシの茎葉1質量部(乾燥質量)に対して、3質量部以上20質量部以下の散水量で、前記アブラヤシの茎葉を散水洗浄するものとしても構わない。この範囲内の水量で水洗/散水洗浄が行われることで、水の使用量を一定の範囲内に抑制しながらも、アルカリ金属や塩素を除去する効果が発揮される。 In the above method, in the washing step (c), the leaves and leaves of the oil palm are washed with water in an amount of 3 parts by mass or more and 22 parts by mass or less with respect to 1 part by mass (dry mass) of the leaves and leaves It does not matter as a thing to do. Similarly, in the water sprinkling and washing step (d), the stem and leaves of the oil palm are sprayed in an amount of 3 parts by mass or more and 20 parts by mass or less with respect to 1 part by mass (dry mass) of the oil palm to be watered. It does not matter as what is sprayed and washed. By performing water washing / sprinkling washing with the amount of water within this range, the effect of removing alkali metals and chlorine is exhibited while suppressing the amount of water used within a certain range.
 上記方法において、前記工程(d)の後に、前記アブラヤシの茎葉を更に圧搾する工程(f)を有するものとしても構わない。 In the above method, after the step (d), a step (f) of further squeezing the stems and leaves of the oil palm may be included.
 上述したように、圧搾工程(b)及び水洗工程(c)を経て、アブラヤシの茎葉の植物細胞は、少なくとも一部が破壊される。このため、水洗工程(c)及び散水洗浄工程(d)によってアブラヤシの茎葉に供給される水(水洗水/洗浄水)の一部が、アブラヤシの茎葉の植物細胞内に取り込まれる可能性がある。上記のように、散水洗浄工程(d)の終了後に、改めて圧搾工程(f)が実行されることで、アブラヤシの茎葉の植物細胞に内包されている水が取り出されるため、当該水に溶解しているアルカリ金属や塩素が除去される。この結果、アブラヤシの茎葉からアルカリ金属や塩素を更に除去することができる。 As described above, at least a part of the plant cells of the leaves and leaves of oil palm is destroyed through the squeezing step (b) and the water washing step (c). For this reason, a part of the water (wash water / wash water) supplied to the leaves and leaves of oil palm by the water washing step (c) and the water washing step (d) may be taken into plant cells of the leaves and leaves of oil palm . As described above, after the completion of the water spray washing step (d), the squeezing step (f) is performed again to extract the water contained in the plant cells of the leaves and leaves of oil palm, so it is dissolved in the water. Alkali metals and chlorine are removed. As a result, alkali metals and chlorine can be further removed from the stems and leaves of oil palm.
 上記方法において、前記工程(f)の後に、前記アブラヤシの茎葉を更に散水洗浄する工程(g)と、
 前記工程(g)の後に、前記アブラヤシの茎葉を更に圧搾する工程(h)とを有するものとしても構わない。
In the above method, after the step (f), a step (g) of further washing the leaves and leaves of the oil palm with water;
After the step (g), a step (h) of squeezing the stems and leaves of the oil palm may be further included.
 この工程(g)及び(h)が実行されることで、アブラヤシの茎葉の表面に付着しているアルカリ金属や塩素を更に除去することができると共に、破壊された植物細胞内等に含有している、アブラヤシの茎葉の内部に残留する微量のアルカリ金属や塩素についても更に除去することができる。 By performing the steps (g) and (h), alkali metals and chlorine adhering to the surface of the leaves and leaves of oil palms can be further removed, and they can be contained in the disrupted plant cells etc. It is also possible to further remove trace amounts of alkali metals and chlorine remaining inside the leaves and leaves of oil palm.
 また、本発明に係るバイオマス燃料の製造方法は、
 上述したアブラヤシの茎葉の前処理方法の完了後に、前記アブラヤシの茎葉を、当該アブラヤシの茎葉に含まれる水分が20質量%以下になるまで乾燥させる工程(i)と、
 前記工程(i)の後に、乾燥した前記アブラヤシの茎葉をペレットに成型する工程(j)とを有することを特徴とする。
Moreover, the method for producing biomass fuel according to the present invention is
After completion of the above-described method for pre-treatment of oil palm stem and leaf, drying the oil palm stem and leaf until the water content in the oil palm stem and leaf is 20% by mass or less;
After the step (i), the method comprises the steps of: (j) shaping the dried leaves and leaves of the oil palm into a pellet.
 上記方法によれば、アブラヤシの茎葉を、アルカリ金属や塩素が充分に除去された状態でバイオマス燃料として好適に用いることができる。なお、工程(j)において、ペレットの大きさを、かさ密度0.50kg/L以上とするものとしても構わない。このペレットの大きさは輸送効率やハンドリング性を考慮して適宜設定することができる。 According to the above method, the leaves of oil palm can be suitably used as a biomass fuel in a state where alkali metals and chlorine are sufficiently removed. In the step (j), the size of the pellets may be a bulk density of 0.50 kg / L or more. The size of the pellet can be appropriately set in consideration of transport efficiency and handling.
 上記方法において、前記工程(i)と前記工程(j)との間に、前記アブラヤシの茎葉を長繊維長が20mm以下となるまで破砕する工程(k)を有するものとしても構わない。この工程(k)を実行することで、アブラヤシの茎葉が小型化され、成型工程(j)の実行が容易化される。 In the above method, the step (k) may be performed between the step (i) and the step (j) to crush the stems and leaves of the oil palm until the long fiber length becomes 20 mm or less. By performing this step (k), the foliage of the oil palm is miniaturized and the execution of the forming step (j) is facilitated.
 なお、前記工程(j)において、上述したアブラヤシの茎葉の前処理方法の完了後に得られた、前記アブラヤシの茎葉由来の油脂を、成型助剤として使用するものとしても構わない。この油脂を用いることで、アブラヤシの茎葉の利用効率を高めながら、ペレットの熱量を増加させることができる。 In the step (j), the oil and fat derived from the leaves and leaves of the oil palm obtained after completion of the method for pre-treating the leaves and leaves of oil palm described above may be used as a molding aid. By using this fat and oil, it is possible to increase the heat quantity of the pellet while enhancing the utilization efficiency of the oil and palm leaves.
 本発明の方法によれば、アブラヤシの茎葉(OPF)からアルカリ金属及び塩素を効率よく除去できるため、現時点で有効利用されていなかったアブラヤシの茎葉を、バイオマス燃料の利用に供することができる。 According to the method of the present invention, since alkali metals and chlorine can be efficiently removed from oil palm leaves and leaves (OPF), oil leaves and leaves that have not been effectively used at present can be used for utilization of biomass fuel.
本発明に係るアブラヤシの茎葉の前処理方法及びバイオマス燃料の製造方法を模式的に示すフローチャートである。It is a flow chart which shows typically the pretreatment method of the foliage of oil palm concerning the present invention, and the manufacturing method of biomass fuel. 図1のフローチャートに示される方法を実施する装置の一例を模式的に示すブロック図である。It is a block diagram which shows typically an example of the apparatus which implements the method shown by the flowchart of FIG. 本発明に係るアブラヤシの茎葉の前処理方法及びバイオマス燃料の製造方法の別実施形態の態様を模式的に示すフローチャートである。It is a flowchart which shows typically the aspect of another embodiment of the pre-processing method of the foliage of an oil palm which concerns on this invention, and the manufacturing method of a biomass fuel. 図3のフローチャートに示される方法を実施する装置の一例を模式的に示すブロック図である。FIG. 4 is a block diagram schematically illustrating an example of an apparatus that implements the method illustrated in the flow chart of FIG. 3;
 以下、本発明に係るアブラヤシの茎葉の前処理方法及びバイオマス燃料の製造方法の実施形態につき、適宜図面を参照して説明する。 Hereinafter, an embodiment of a method for pre-treating foliage leaves and a method for producing biomass fuel according to the present invention will be described with reference to the drawings as appropriate.
 図1は、本発明に係るアブラヤシの茎葉の前処理方法及びバイオマス燃料の製造方法の一実施形態を模式的に示すフローチャートである。また、図2は、本発明に係るアブラヤシの茎葉の前処理方法及びバイオマス燃料の製造方法を実施する装置(以下、「バイオマス燃料化装置」と呼ぶ。)の一例を模式的に示すブロック図である。図2において、バイオマス材料の流れを矢印付きの実線で示し、液体(水分や油分)の流れを矢印付き破線で示す。 FIG. 1 is a flow chart schematically showing one embodiment of a method for pre-processing a foliage of an oil palm according to the present invention and a method for producing a biomass fuel. Moreover, FIG. 2 is a block diagram which shows typically an example of the apparatus (It calls a "biomass fuel-ized apparatus".) Which implements the pre-processing method of the foliage of oil palm which concerns on this invention, and the manufacturing method of biomass fuel. is there. In FIG. 2, the flow of biomass material is indicated by a solid line with an arrow, and the flow of liquid (water and oil) is indicated by a dotted line with an arrow.
 図1に示されるように、本発明に係るバイオマス燃料の製造方法は、前処理工程に対応するステップS10と、後処理工程に対応するステップS20とを含んで構成される。 As shown in FIG. 1, the method for producing a biomass fuel according to the present invention includes step S10 corresponding to the pre-treatment step and step S20 corresponding to the post-treatment step.
 図1に示される例では、前処理工程S10は、加熱工程S11、圧搾工程S12、水洗工程S13、散水洗浄工程S14、及び圧搾工程S15を備える。また、後処理工程S20は、乾燥工程S21、破砕工程S22、及び成型工程S23を備える。 In the example shown in FIG. 1, the pretreatment step S10 includes a heating step S11, a pressing step S12, a water washing step S13, a water spray washing step S14, and a pressing step S15. The post-processing step S20 includes a drying step S21, a crushing step S22, and a molding step S23.
 また、図2に示されるように、本実施形態のバイオマス燃料化装置1は、前処理装置2と、後処理装置3とを有して構成される。前処理装置2は、加熱機11、ホッパ12、圧搾機13、水洗装置14、振動篩(ふるい)15、振動篩16、洗浄水供給装置17、排洗浄水タンク18、送水ポンプ19、水洗水供給装置21、油水分離機22、排水処理装置24、及び圧搾機25を含んで構成される。後処理装置3は、乾燥機32、破砕機33、成型機34、及び送油ポンプ35を含んで構成される。 Further, as shown in FIG. 2, the biomass fueling device 1 of the present embodiment is configured to include a pretreatment device 2 and a post-treatment device 3. The pretreatment device 2 includes a heater 11, a hopper 12, a squeezing machine 13, a water washing device 14, a vibrating sieve (sieve) 15, a vibrating sieve 16, a washing water supply device 17, a flush water tank 18, a water pump 19, and flush water. It comprises the supply apparatus 21, the oil-water separator 22, the waste water treatment apparatus 24, and the press 25. The post-processing device 3 includes a dryer 32, a crusher 33, a molding machine 34, and an oil feed pump 35.
 以下、それぞれの工程について、適宜図2を参照しながら詳述する。 Each step will be described in detail below with reference to FIG. 2 as appropriate.
 [前処理工程]
 まず、前処理工程S10について説明する。
[Pretreatment process]
First, the pretreatment step S10 will be described.
  (加熱工程S11)
 まず、プランテーション等から採取されたアブラヤシの茎葉e1が、加熱機11に投入され、同加熱機11において加熱される。アブラヤシの茎葉e1は、アルカリ金属の中でも特にカリウムを多く含み、その含有量は、葉の部分が0.2~0.5質量%、茎の部分が0.8~1.3質量%である。また、塩素の含有量は、葉の部分が0.2~0.4質量%、茎の部分が0.1~0.6質量%である。そして、このアブラヤシの茎葉e1は、60~70質量%の水分を含んでいる。
(Heating process S11)
First, the stem and leaf e1 of oil palm collected from a plantation or the like is introduced into the heater 11 and heated by the heater 11. The palm leaf e1 of the oil palm is particularly rich in potassium among alkali metals, and the content thereof is 0.2 to 0.5% by mass of the leaf part and 0.8 to 1.3% by mass of the stem part . The chlorine content is 0.2 to 0.4% by mass in the leaf part and 0.1 to 0.6% by mass in the stem part. And, the stem and leaf e1 of this oil palm contains 60 to 70% by mass of water.
 加熱後のアブラヤシの茎葉e2は、その植物細胞が柔らかくされた状態となる。加熱後のアブラヤシの茎葉e2の柔らかさの程度は、次工程以降でのハンドリングに支障が生じない程度に、全体に柔軟性を持たせるのが好ましい。より具体的には、この加熱工程S1では、100~200℃の飽和蒸気を用いて15~60分加熱するのが好ましい。 After heating, the stem and leaf e2 of the oil palm becomes a state in which the plant cells are softened. It is preferable that the degree of softness of the stem and leaf e2 of the oil palm after heating be made flexible as a whole so as not to affect the handling in the subsequent steps. More specifically, in the heating step S1, it is preferable to heat for 15 to 60 minutes using saturated steam at 100 to 200 ° C.
 加熱機11は、加熱後のアブラヤシの茎葉e2が柔らかくなって、ハンドリングしやすい状態を実現できる範囲内であれば、装置態様や加熱原理には限定されないが、蒸気又は飽和蒸気を使用して加熱するのが好適である。一例として、加熱機11は、蒸し器、スチーマー、温風装置(ドライヤー)、温水溜め(鍋)等の、植物を柔らかくするための一般的な装置が使用され得る。これらの中では、短い所要時間でアブラヤシの茎葉e1を十分に柔らかくすることができるという理由により、蒸し器やスチーマーを使用するのが好ましい。 The heating device 11 is not limited to the device mode or heating principle as long as the stem and leaf e2 of the heated oil palm becomes soft and easy to handle, but heating is performed using steam or saturated steam. Is preferred. As an example, the heater 11 may be a general device for softening plants, such as a steamer, a steamer, a hot air device (dryer), a hot water reservoir (pan), and the like. Among these, it is preferable to use a steamer or a steamer because it can sufficiently soften the palm leaf e1 of oil palm in a short time.
 ところで、アブラヤシは、マレーシアやインドネシアといった熱帯雨林気候地帯に多く生息している。これらの地域においては、2週間程度の期間、アブラヤシの茎葉e1を野外に野積みするだけで、植物細胞を十分に柔らかくすることができる場合がある。このような場合、アブラヤシの茎葉e1を一定期間にわたって野積みする工程が加熱工程S11に対応し、前処理装置2は必ずしも加熱機11を備えなくても構わない。 By the way, oil palms inhabit in tropical rain forest climate areas such as Malaysia and Indonesia. In these areas, plant cells may be able to be sufficiently softened by simply piling palm leaves e1 in the field for a period of about two weeks. In such a case, the step of laying the stems and leaves e1 of the oil palm over a fixed period corresponds to the heating step S11, and the pretreatment device 2 may not necessarily include the heater 11.
 この加熱工程S11が、前記工程(a)に対応する。 The heating step S11 corresponds to the step (a).
  (圧搾工程S12)
 加熱工程S11を経て柔らかくされたアブラヤシの茎葉e2は、ホッパ12に投入されて蓄えられる。そして、このアブラヤシの茎葉e2は、ホッパ12から所定の流量(速度)で、適宜圧搾機13へと供給される。
(Squeeze process S12)
The stems and leaves e2 of the oil palm softened through the heating step S11 are charged into the hopper 12 and stored. And the stem and leaf e2 of this oil palm is suitably supplied to the expression machine 13 from the hopper 12 by predetermined flow volume (speed).
 圧搾機13は、投入されたアブラヤシの茎葉e2に加圧することで、既に柔らかくされていたアブラヤシの茎葉e2の植物細胞を破壊すると共に、同植物細胞に含まれていたアルカリ金属及び塩素を、水分と共に絞り出す。このとき、圧搾機13は、圧搾後のアブラヤシの茎葉e3の水分量を60質量%以下に圧搾するのが好ましく、この範囲内で圧搾できるものであれば、その形式には限定されない。一例として、圧搾機13は、油圧プレス機(垂直型、水平型)、一軸圧搾機(スクリュー型)、二軸圧搾機(エクストルーダー)等の汎用の装置を使用できる。これらの中では、所要時間が短く、且つ連続式の処理が可能であるという理由により、二軸圧搾機(エクストルーダー)を使用するのが好ましい。 The press 13 destroys the plant cells of the oil palm stem and leaf e2 which has already been softened by pressurizing the oil palm stem and leaf e2, which has been input, and removes the alkali metal and chlorine contained in the plant cells. Squeeze out with. At this time, it is preferable to squeeze the water content of the stem and leaf e3 of the oil palm after squeezing to 60% by mass or less, and the squeezing machine 13 is not limited to that type as long as it can squeeze within this range. As an example, the press 13 can use general-purpose apparatuses, such as a hydraulic press (vertical type and horizontal type), a uniaxial press (screw type), and a biaxial press (extruder). Among these, it is preferable to use a twin-screw press (extruder) because the time required is short and continuous processing is possible.
 この圧搾工程S12により、アブラヤシの茎葉e2の植物細胞に含まれていたアルカリ金属及び塩素の一部が溶け込んだ水が、アブラヤシの茎葉e2から絞り出されて排出される。この結果、圧搾工程S12が完了した後のアブラヤシの茎葉e3は、圧搾工程S12実行前のアブラヤシの茎葉e2と比較して、アルカリ金属及び塩素の含有量が低下する。 In the squeezing step S12, water in which a part of the alkali metal and chlorine contained in the plant cells of the stem and leaf e2 of the oil palm is dissolved is extracted from the stem and leaf e2 of the oil palm and discharged. As a result, as for the stem and leaf e3 of an oil palm after completion of pressing process S12, content of an alkali metal and chlorine falls compared with the stem and leaf e2 of oil palm before execution of pressing process S12.
 ところで、圧搾工程S12が完了した後のアブラヤシの茎葉e3に含まれるアルカリ金属及び塩素は、そのほとんどがアブラヤシの茎葉e3内に含まれる水分に溶解して存在する。従って、アブラヤシの茎葉e3のアルカリ金属及び塩素含有量は、アブラヤシの茎葉e3の残存水分量に比例するといえる。つまり、アブラヤシの茎葉e3の残存水分量を、アブラヤシの茎葉e3に含まれるアルカリ金属及び塩素の含有量の指標とすることができる。更に、アブラヤシの茎葉e3の残存水分量は、圧搾機13によるアブラヤシの茎葉e2の植物細胞の破壊の程度の指標ともなり、この残存水分量が少ないほど、破壊された植物細胞の量が多いことを意味する。 By the way, the alkali metal and chlorine contained in the stem and leaf e3 of the oil palm after the pressing step S12 is completed are mostly dissolved in the water contained in the stem and leaf e3 of the oil palm. Therefore, it can be said that the content of alkali metal and chlorine in the stem and leaf e3 of the oil palm is proportional to the residual water content of the stem and leaf e3 of the oil palm. In other words, the residual water content of the oil and pepper e3 can be used as an indicator of the content of alkali metal and chlorine contained in the oil and fat e3. Furthermore, the residual water content of the oil palm stem and leaf e3 is also an indicator of the degree of destruction of the plant cells of the oil palm stem and leaf e2 by the press 13. The smaller the residual water content, the greater the amount of the destroyed plant cells. Means
 このアブラヤシの茎葉e3の残存水分量は、アルカリ金属及び塩素含有量を低下させる観点、及び植物細胞を多く破壊する観点から、60質量%以下が好ましく、55質量%以下がより好ましく、50質量%以下が特に好ましい。アブラヤシの茎葉e3の残存水分量が60質量%以下であれば、この後に行われる水洗工程S13、及び散水洗浄工程S14を経ることで、アルカリ金属含有量が0.2質量%以下であり、且つ、塩素含有量が0.1質量%以下のアブラヤシの茎葉を得ることができる。なお、残存水分量が60質量%のアブラヤシの茎葉e3のアルカリ金属含有量は0.2~0.8質量%であり、また塩素含有量は0.1~0.5質量%である。 The residual water content of the stem and leaf e3 of this oil palm is preferably 60% by mass or less, more preferably 55% by mass or less, and 50% by mass from the viewpoint of reducing the alkali metal and chlorine contents and from the viewpoint of destroying many plant cells. The following are particularly preferred. If the residual water content of the stem and leaf e3 of the oil palm is 60% by mass or less, the alkali metal content is 0.2% by mass or less by passing through the water washing step S13 and the water sprinkling cleaning step S14 performed later. It is possible to obtain an oil palm stem and leaf having a chlorine content of 0.1% by mass or less. The alkali metal content of the stem and leaf e3 of the oil palm having a residual water content of 60% by mass is 0.2 to 0.8% by mass, and the chlorine content is 0.1 to 0.5% by mass.
 なお、本実施形態では、圧搾工程S12が実行されることで得られる排出水(以下、「圧搾水」という。)SW1が、油水分離機22に送られる。油水分離機22は、供給された圧搾水SW1を、水分W3と油脂分O1とに分離する。油水分離機22は、水分と油脂分とが混在する液体から、水分と油脂分とを分離する機能を実現することができる構成であれば、その形式には限定されない。例えば、油水分離機22としては、油水分離桝や遠心脱油機を使用可能であるが、排水処理後に系外排出される水分W3を清浄にする観点からは、高速遠心分離による遠心脱油機を使用するのが好ましい。 In the present embodiment, the discharged water (hereinafter referred to as “pressed water”) SW1 obtained by execution of the pressing step S12 is sent to the oil / water separator 22. The oil-water separator 22 separates the supplied compressed water SW1 into the water content W3 and the fat and oil content O1. The oil-water separator 22 is not limited to this type as long as it can realize the function of separating water and fat from the liquid in which water and fat are mixed. For example, as the oil / water separator 22, an oil / water separator or a centrifugal deoiling machine can be used, but from the viewpoint of cleaning the water W3 discharged out of the system after waste water treatment, the centrifugal deoiling machine by high speed centrifugal separation It is preferred to use
 この圧搾工程S12が、前記工程(b)に対応する。 This squeezing step S12 corresponds to the step (b).
  (水洗工程S13)
 圧搾工程S12が完了した後のアブラヤシの茎葉e3は、水洗装置14に送出され、この水洗装置14において水洗工程S13が実行される。水洗工程S13は、アブラヤシの茎葉e3に物理的衝撃を与えてアブラヤシの茎葉e3の植物細胞を破壊しながら、アブラヤシの茎葉e3を水洗する工程である。水洗装置14は、水洗水供給装置21から水洗水W1が供給され、この水洗水W1を用いてアブラヤシの茎葉e3を水洗する。水洗水供給装置21は、水洗水W1を貯水するためのタンクと、貯水された水洗水W1を所定の流量で水洗装置14に送出するための注水口とを備える。
(Washing process S13)
The stem and leaf e3 of the oil palm after the pressing step S12 is completed is delivered to the water washing device 14, where the water washing step S13 is performed. The water washing step S13 is a step of washing the oil palm stem and leaf e3 while washing the oil palm stem and leaf e3 with physical impact to destroy plant cells of the oil palm stem and leaf e3. The flush device 14 is supplied with flush water W1 from the flush water supply device 21, and flushes the stems and leaves e3 of the oil palm using the flush water W1. The flush water supply device 21 includes a tank for storing flush water W1 and a water injection port for delivering the stored flush water W1 to the flush device 14 at a predetermined flow rate.
 水洗装置14は、より好ましくは、アブラヤシの茎葉e3に対して、瞬間的な物理的な衝撃を、断続的に加えながら水洗を行うことができる構成が好ましい。例えば、水洗装置14は、水洗水供給装置21から水洗水W1が供給される円筒形状の装置であって、軸方向に回転する回転機構と、この装置内に収容されたアブラヤシの茎葉e3に物理的衝撃を与える衝撃媒体とを備える構成を採用することができる。 More preferably, the water washing apparatus 14 is preferably configured to be able to perform water washing while intermittently applying an instantaneous physical impact to the stem and leaf e3 of the oil palm. For example, the water washing device 14 is a cylindrical device to which the flush water W1 is supplied from the flush water supply device 21, and it is physically applicable to the rotation mechanism which rotates in the axial direction and the stems and leaves e3 of the oil palm housed in this device. It is possible to adopt a configuration including an impact medium for giving a dynamic impact.
 具体的な例として、水洗装置14は、水洗水供給装置21から水洗水W1が供給される円筒形状の装置であって、同装置の内部に、複数のパドルを備え付けた軸を有し、この軸が回転可能に構成されている。このような装置は、パドルミキサと称されることがある。アブラヤシの茎葉e3は、装置の一方の端部付近から同装置内に供給され、水洗水W1の流れに従って装置の他方の端部付近へと流れる。このようにアブラヤシの茎葉e3が水洗装置14内を移動中に、パドルの設置箇所を通過する時点で、パドルによって押しつぶされる。この結果、パドルが設けられている箇所を通過するたびに、瞬間的な衝撃を受けながら、アブラヤシの茎葉e3は水洗装置14内で水洗処理が行われる。この態様では、パドルが衝撃媒体に対応する。 As a specific example, the washing device 14 is a cylindrical device to which the washing water W1 is supplied from the washing water supply device 21, and has a shaft provided with a plurality of paddles inside the device, and The shaft is configured to be rotatable. Such devices are sometimes referred to as paddle mixers. The leaves and leaves e3 of the oil palm are supplied into the apparatus from the vicinity of one end of the apparatus, and flow to the vicinity of the other end of the apparatus according to the flow of the flush water W1. In this way, while the palm leaf e3 of the oil palm moves in the water washing device 14, it is crushed by the paddle at the time when it passes through the installation site of the paddle. As a result, each time the paddle passes through the portion where the paddles are provided, the stems and leaves e3 of the oil palm are washed in the water washing device 14 while receiving an instantaneous impact. In this aspect, the paddles correspond to the impact media.
 水洗装置14は、アブラヤシの茎葉e3に対して物理的衝撃を加えながら水洗を行うことのできる構成であれば、上記のようなパドルミキサに限定されない。他の例としては、水洗水供給装置21から水洗水W1が供給される、デソルトセパレータを利用することもできる。デソルトセパレータとは、水平方向に延設された軸線又は水平方向から若干傾斜した軸線回りに回転する、内面にリフターが付設されたドラム状の容器と、この容器内に移動可能に収容された複数本の鉄棒とを備え、ドラムウォッシャとロッドミルの両方の機能を併せ持つ装置である。リフターによって持ち上げられた後に落下する鉄棒の衝撃によってアブラヤシの茎葉e3の植物細胞を破壊すると共に、かかる鉄棒の自重と容器の回転による撹拌効果により、アブラヤシの茎葉e3を効率よく押しつぶすことができる。 The water washing apparatus 14 is not limited to the paddle mixer as described above as long as it can wash water while applying physical impact to the stems and leaves e3 of the oil palm. As another example, it is possible to use a desalt separator in which the flush water W1 is supplied from the flush water supply device 21. The desolate separator is a drum-shaped container having a lifter attached to its inner surface, which rotates about an axis extending in the horizontal direction or an axis slightly inclined from the horizontal direction, and is housed movably in this container This device is equipped with multiple iron rods and combines the functions of both the drum washer and the rod mill. The impact of the iron rod falling after being lifted by the lifter destroys the plant cells of the oil palm stem and leaf e3 and, due to the weight of the iron rod and the stirring effect by the rotation of the container, the oil palm stem and leaf e3 can be crushed efficiently.
 水洗装置14をデソルトセパレータで構成する場合、衝撃媒体としての鉄棒は、水洗装置14の試料室の容積Am3に対して、長さが水洗装置14の試料室の長さとほぼ同じであって、体積が0.015A~0.04Am3の棒状部材を4~10本使用するのが好ましく、5~8本使用するのがより好ましい。また、衝撃媒体を球状部材とすることも可能であり、この場合、φ25mm以上の部材を充填率7~15%で使用するのが好ましい。 When the water washing apparatus 14 is constituted by a desolate separator, the iron rod as an impact medium has a length substantially the same as the length of the sample room of the water washing apparatus 14 with respect to the volume Am 3 of the sample room of the water washing apparatus 14 Preferably, 4 to 10 rod-like members having a volume of 0.015 A to 0.04 Am 3 are used, and more preferably 5 to 8 are used. Further, the impact medium may be a spherical member, and in this case, it is preferable to use a member having a diameter of 25 mm or more at a filling rate of 7 to 15%.
 水洗装置14のその他の例としては、湿式トロンメルを採用することができる。また、水洗装置14は、必ずしも衝撃媒体を備える必要はなく、回転装置のみを備え、アブラヤシの茎葉e3を回転装置内で撹拌することで、アブラヤシの茎葉e3の自重によって回転装置の内側面に向かって複数回落下させることでアブラヤシの茎葉e3に対して物理的衝撃を与える構成を採用することもできる。 As another example of the washing device 14, a wet trommel can be employed. In addition, the water washing device 14 does not necessarily have to be provided with an impact medium, and is provided with only the rotating device, and by stirring the stem and leaf e3 of the oil palm in the rotating device, It is also possible to adopt a configuration in which physical impact is given to the stem and leaf e3 of the oil palm by dropping it several times.
 この水洗工程S13で使用される水洗水W1の量は、アブラヤシの茎葉e3からアルカリ金属及び塩素を効率的に除去する観点、及び水洗水W1の使用量を抑制する観点から、洗浄対象であるアブラヤシの茎葉e3の1質量部に対して、好ましくは2~13質量部(乾燥質量基準でのアブラヤシの茎葉e3の1質量部に対して(以下、「ドライベース」という。)3~22質量部)であり、より好ましくは3~5質量部(ドライベースで5~8質量部)である。 The amount of flush water W1 used in the flush step S13 is an oil palm to be cleaned from the viewpoint of efficiently removing the alkali metal and chlorine from the stems and leaves e3 of oil palm and from the viewpoint of suppressing the amount of flush water W1 used. Preferably 2 to 13 parts by mass with respect to 1 part by mass of the stems and leaves e3 (hereinafter referred to as "dry base" with respect to 1 part by mass of the palm leaves e3 on a dry mass basis (hereinafter referred to as "dry base") And more preferably 3 to 5 parts by mass (5 to 8 parts by mass on a dry basis).
 また、この水洗水W1は、アブラヤシの茎葉e3が含有するアルカリ金属及び塩素を溶解して、除去するために用いられるものであることから、アルカリ金属及び塩素を含まない水であることが最も好ましい。ただし、上述したように、アブラヤシの茎葉e3内に含まれる水分中のアルカリ金属及び塩素濃度は、それぞれ0.2~0.8質量%、0.1~0.5質量%と高いことから、水洗水W1のアルカリ金属及び塩素含有量は0.1質量%以下であればよい。そこで、後述される排水処理装置24での排水処理量を抑制する観点から、本実施形態では、次工程の散水洗浄工程S14で使用された後の排洗浄水W5を、水洗水W1として使用することができる。なお、後述されるように、排洗浄水W5のアルカリ金属及び塩素含有量は0.02質量%以下であり、水洗水W1として利用できる範囲内である。 Moreover, since this wash water W1 is used to dissolve and remove the alkali metal and chlorine contained in the stem and leaf e3 of oil palm, it is most preferable that the water does not contain alkali metal and chlorine. . However, as described above, the concentration of alkali metal and chlorine in the water contained in the stem and leaf e3 of oil palm is as high as 0.2 to 0.8% by mass and 0.1 to 0.5% by mass, respectively. The alkali metal and chlorine content of the flush water W1 may be 0.1% by mass or less. Therefore, from the viewpoint of suppressing the amount of waste water treated by the waste water treatment apparatus 24 described later, in the present embodiment, the waste washing water W5 after being used in the water washing step S14 of the next step is used as the washing water W1. be able to. In addition, as described later, the alkali metal and chlorine content of the waste cleaning water W5 is 0.02 mass% or less, and is within the range which can be used as the washing water W1.
 この水洗工程S13が、前記工程(c)に対応する。 The water washing step S13 corresponds to the step (c).
  (散水洗浄工程S14)
 水洗工程S13が完了した後のアブラヤシの茎葉e4は、水切りがされた後に、散水洗浄が施される。より具体的には、以下の通りである。
(Sprinkler cleaning step S14)
The stem and leaf e4 of the oil palm after the completion of the water washing step S13 is subjected to water washing after being drained. More specifically, it is as follows.
 水洗工程S13が完了した後のアブラヤシの茎葉e4は、水洗工程S13で使用された後の水(排水洗水W2)と共に、振動篩15に供給される。振動篩15は、アブラヤシの茎葉e4は通過させず、水(排水洗水W2)は通過可能な範囲の大きさの孔部が複数設けられている。このため、振動篩15に供給された、アブラヤシの茎葉e4と排水洗水W2の混合物は、振動篩15の篩上面に残存するアブラヤシの茎葉e4と、振動篩15の篩下面に流出する排水洗水W2とに分離される。 The stem and leaf e4 of the oil palm after the completion of the water washing step S13 is supplied to the vibrating sieve 15 together with the water (drain water wash water W2) used in the water washing step S13. In the vibrating screen 15, the stem and leaf e4 of the oil palm are not allowed to pass through, and a plurality of holes with a size that allows passage of water (drainage flush water W2) are provided. For this reason, the mixture of oil palm stem and leaf e4 and drained flush water W2 supplied to the vibrating screen 15 is drained and washed out of the oil palm stem and leaf e4 remaining on the upper surface of the vibrating screen 15 and drained drained on the lower surface of the vibrating screen 15. It is separated into water W2.
 その後、振動篩15の篩上面に残存したアブラヤシの茎葉e4は、この振動篩15に連接して設けられた振動篩16に移動される。振動篩16では、アブラヤシの茎葉e4に対して、洗浄水供給装置17から供給される洗浄水W4が散水される。洗浄水供給装置17は、洗浄水W4を貯水するためのタンクと、貯水された洗浄水W4を振動篩16に向けて散水するための散水用注水口とを備える。 Thereafter, the stem and leaf e4 of the oil palm remaining on the upper surface of the vibrating screen 15 is moved to the vibrating screen 16 provided so as to be connected to the vibrating screen 15. In the vibrating screen 16, the washing water W4 supplied from the washing water supply device 17 is sprayed to the stem and leaf e4 of the oil palm. The washing water supply device 17 includes a tank for storing the washing water W4, and a water spouting water inlet for sprinkling the stored washing water W4 toward the vibrating screen 16.
 この散水洗浄工程S14で使用される洗浄水W4には、アルカリ金属及び塩素含有量が0.01質量%以下のものを用いるのが好ましい。また、この洗浄水W4の散水量は、アブラヤシの茎葉e4の1質量部に対して、好ましくは2~12質量部(ドライベースで3~20質量部)であり、より好ましくは3~5質量部(ドライベースで5~8質量部)である。 It is preferable to use that whose alkali metal and chlorine content are 0.01 mass% or less as washing water W4 used at this water spray washing process S14. In addition, the amount of the water W4 sprayed is preferably 2 to 12 parts by mass (3 to 20 parts by mass on a dry basis), and more preferably 3 to 5 parts by mass, with respect to 1 part by mass of the stems and leaves e4 of oil palm Part (5 to 8 parts by mass on a dry basis).
 この散水洗浄工程S14によって、水洗工程S13の完了後にアブラヤシの茎葉e4の表面に付着した、アルカリ金属及び/又は塩素が溶解した水が洗い流される。この結果、散水洗浄工程S14の完了後、すなわち振動篩16から供給されるアブラヤシの茎葉e5は、アルカリ金属含有量が0.2質量%以下であり、塩素含有量が0.1質量%以下に低下する。 In the water spray cleaning step S14, the alkali metal and / or the chlorine dissolved water adhering to the surface of the stem and leaf e4 of the oil palm after the completion of the water cleaning step S13 is washed away. As a result, after completion of the water spray cleaning step S14, that is, the stem and leaf e5 of the oil palm supplied from the vibrating screen 16 has an alkali metal content of 0.2 mass% or less and a chlorine content of 0.1 mass% or less descend.
 振動篩16は、振動篩15と同様に、アブラヤシの茎葉e5は通過させず、水(排洗浄水W5)は通過可能な範囲の大きさの孔部が複数設けられている。これにより、アブラヤシの茎葉e5の表面に付着した、一定量以上の洗浄水W4(排洗浄水W5)が、振動篩16によって振り落とされ、アブラヤシの茎葉e5が水切りされる。振動篩16は、篩に載せたアブラヤシの茎葉e5に振動を加えるなどして、アブラヤシの茎葉e5に大きな水滴が残存しないことを目視で確認できる程度に、アブラヤシの茎葉e5に付着された水分を取り除けばよい。 Like the vibrating sieve 15, the vibrating sieve 16 does not allow the stem and leaf e5 of the oil palm to pass through, and a plurality of holes with a size that allows passage of water (waste water W5) is provided. Thereby, a certain amount or more of the washing water W4 (waste water W5) attached to the surface of the stem and leaf e5 of the oil palm is shaken off by the vibrating sieve 16, and the stem and leaf e5 of the oil palm is drained. The vibrating sieve 16 applies vibration to the oil palm stem and leaf e5 placed on the sieve and the water attached to the oil palm stem and leaf e5 to such an extent that large water droplets do not remain on the oil palm stem and leaf e5. You can remove it.
 なお、振動篩15及び振動篩16の篩目は、水とアブラヤシの茎葉とを分離して回収するため、より詳細には、排水洗水W2とアブラヤシの茎葉e4、及び排洗浄水W5とアブラヤシの茎葉e5をそれぞれ分離して回収するため、公称目開き4mm以下が好ましく、2.8mm以下が更に好ましい。 The sieves of the vibrating sieve 15 and the vibrating sieve 16 separate and collect water and stems and leaves of oil palm. More specifically, the drainage wash water W2 and the oil palm stem and leaves e4, the drainage washing water W5 and the oil palm In order to separate and collect the stems and leaves e5, the nominal opening is preferably 4 mm or less, more preferably 2.8 mm or less.
 また、本実施形態では、振動篩15及び振動篩16が相互に連接して設けられているものとして説明した。しかしながら、アブラヤシの茎葉e4の水切りと、水切り後のアブラヤシの茎葉e4を散水洗浄した後、散水洗浄処理完了後のアブラヤシの茎葉e5の水切りとを行うことができれば、1機の振動篩で実現しても構わない。すなわち、1機の振動篩の上流側でアブラヤシの茎葉e4の水切りが行われ、下流側でアブラヤシの茎葉e4に対する散水洗浄及び水切りが行われるものとしても構わない。 Further, in the present embodiment, it has been described that the vibrating screen 15 and the vibrating screen 16 are provided so as to be connected to each other. However, if it is possible to drain the oil palm stem and leaf e4 and rinse the oil palm stem and leaf e4 after draining with water, if it is possible to drain the oil palm stem and leaf e5 after water spray cleaning processing is completed, it is realized with one vibrating sieve. It does not matter. That is, it does not matter if the foliage e4 of the oil palm is drained on the upstream side of one vibrating sieve and the irrigation and drainage on the foliage e4 of the palm is performed on the downstream side.
 本実施形態では、振動篩15で振り分けられた、排水洗水W2は、上述した油水分離機22に送出される。油水分離機22では、圧搾機13から排出された圧搾水SW1と、この排水洗水W2との混合流体を、水分W3と油脂分O1とに分離する。なお、圧搾水SW1を油水分離する機構と、排水洗水W2を油水分離する機構とを、別体で設ける構成としても構わない。 In the present embodiment, the drainage wash water W2 distributed by the vibrating screen 15 is delivered to the oil / water separator 22 described above. The oil / water separator 22 separates the mixed fluid of the press water SW1 discharged from the press 13 and the drained flush water W2 into the water W3 and the fat and oil portion O1. The mechanism for separating the squeezed water SW1 from the oil water and the mechanism for separating the drainage water W2 from the oil water may be separately provided.
 また、本実施形態では、振動篩16で振り分けられた排洗浄水W5は、排洗浄水タンク18に回収・貯水される。排洗浄水タンク18に貯水された排洗浄水W5は、一部が、送水ポンプ19によって水洗水供給装置21に供給されて、水洗水W1として循環利用される。また、排洗浄水W5の他の一部は、排水処理装置24に供給される。送水ポンプ19は、液体用ポンプであれば特に制限はなく、渦巻きポンプやピストンポンプなどの汎用の装置を使用できる。 Further, in the present embodiment, the waste cleaning water W5 distributed by the vibrating screen 16 is collected and stored in the waste cleaning water tank 18. A part of the waste washing water W5 stored in the waste washing water tank 18 is supplied to the washing water supply device 21 by the water feeding pump 19 and circulated and used as the washing water W1. Further, the other part of the waste cleaning water W5 is supplied to the waste water treatment device 24. The water pump 19 is not particularly limited as long as it is a liquid pump, and a general-purpose device such as a spiral pump or a piston pump can be used.
 この散水洗浄工程S14が、前記工程(d)に対応する。 The water spray cleaning step S14 corresponds to the step (d).
  (圧搾工程S15)
 本実施形態では、散水洗浄工程S14が完了した後のアブラヤシの茎葉e5が圧搾機25に供給され、再度圧搾工程が実行される。圧搾機25は、アブラヤシの茎葉e5を加圧して、アブラヤシの茎葉e5に含まれている洗浄水W4又は排洗浄水W5を搾り出すために備えられる。圧搾機25は、圧搾後のアブラヤシの茎葉e6の水分量を70質量%以下に圧搾できるものであれば特に限定されず、圧搾機13と同様に、油圧プレス機(垂直型、水平型)、一軸圧搾機(スクリュー型)、二軸圧搾機(エクストルーダー)等の汎用の装置を使用できる。
(Squeeze process S15)
In the present embodiment, the stem and leaf e5 of the oil palm after the water spray cleaning step S14 is completed is supplied to the press 25 and the pressing step is executed again. The press 25 is provided to pressurize the stem and leaf e5 of the oil palm to squeeze out the washing water W4 or the drainage washing water W5 contained in the stem and leaf e5 of the oil palm. The press 25 is not particularly limited as long as it can press the water content of the stem and leaf e6 of the oil palm after pressing to 70% by mass or less, and the hydraulic press (vertical type, horizontal type) General-purpose devices such as uniaxial press (screw type), twin-screw press (extruder) and the like can be used.
 この圧搾機25によって水分量が70質量%以下となったアブラヤシの茎葉e6は、アルカリ金属含有量が0.1質量%以下、塩素含有量が0.05質量%以下に低下する。 The stem and leaf e6 of the oil palm whose water content has been reduced to 70% by mass or less by the press 25 has an alkali metal content of 0.1% by mass or less and a chlorine content of 0.05% by mass or less.
 なお、この圧搾機25から排出される圧搾水SW2は、排水処理装置24に供給される。排水処理装置24には、油水分離機22によって分離された水分W3、及び排水タンク18に貯水されていた排洗浄水W5についても供給される。排水処理装置24に供給された水分W3、排洗浄水W5及び圧搾水SW2は、適切な排水処理を施した後、排水W6として系外に排出される。これにより、排水処理を排水処理装置24において一箇所でまとめて行うことができる。ここで、上記の水分W3、排洗浄水W5及び圧搾水SW2は、BOD(生物的酸素要求量)、COD(化学的酸素要求量)及びSS(懸濁物質)が高いので、排水処理装置24には、沈殿槽や活性汚泥槽(曝気槽)を使用するのが好ましい。 The compressed water SW2 discharged from the squeezer 25 is supplied to the waste water treatment device 24. The water W3 separated by the oil-water separator 22 and the drainage cleaning water W5 stored in the drainage tank 18 are also supplied to the drainage processing device 24. The water W3 supplied to the waste water treatment device 24, the waste wash water W5 and the squeezed water SW2 are discharged to the outside of the system as waste water W6 after being subjected to appropriate waste water treatment. Thereby, drainage treatment can be performed collectively in one place in the drainage treatment device 24. Here, the above-mentioned water W3, waste cleaning water W5 and compressed water SW2 have high BOD (biological oxygen demand), COD (chemical oxygen demand) and SS (suspension substance), so waste water treatment equipment 24 It is preferable to use a settling tank or an activated sludge tank (aeration tank).
 この圧搾工程S15は、工程(f)に対応する。 This squeezing step S15 corresponds to the step (f).
 本発明の前処理工程S10によれば、少なくとも、アルカリ金属含有量が0.2質量%以下で、塩素含有量が0.1質量%以下のアブラヤシの茎葉e5を得ることができる。更に、本実施形態のように、散水洗浄工程S14の後に圧搾工程S15を実行することで、アルカリ金属含有量が0.1質量%以下で、塩素含有量が0.05質量%以下のアブラヤシの茎葉e6を得ることができる。 According to the pretreatment step S10 of the present invention, it is possible to obtain an oil palm stem and leaf e5 having an alkali metal content of at most 0.2 mass% and a chlorine content of at most 0.1 mass%. Furthermore, as in the present embodiment, by performing the squeezing step S15 after the water spray cleaning step S14, the oil palm having an alkali metal content of 0.1 mass% or less and a chlorine content of 0.05 mass% or less A stem and leaf e6 can be obtained.
 [後処理工程]
 次に、後処理工程S20について説明する。
[Post-processing process]
Next, post-processing step S20 will be described.
  (乾燥工程S21)
 前処理工程S10が実行された後のアブラヤシの茎葉e6は、乾燥機32に投入され、乾燥機32において、その水分が、好ましくは20質量%以下、より好ましくは17質量%以下になるように乾燥される。乾燥機32は、アブラヤシの茎葉e6を水分量20質量%以下まで乾燥可能であれば、特にその型式等は限定されないが、連続運転が可能なロータリードライヤーを好適に用いることができる。
(Drying step S21)
The leaves and leaves e6 of the oil palm after the pretreatment step S10 is carried out is introduced into the drier 32 so that its water content in the drier 32 is preferably 20% by mass or less, more preferably 17% by mass or less Be dried. The dryer 32 is not particularly limited in its type and the like, as long as it can dry the palm leaves e6 of the oil palm to a water content of 20% by mass or less, but a rotary dryer capable of continuous operation can be suitably used.
 また、気温、湿度等の環境に依存するが、天日干しによっても水分量20質量%以下までアブラヤシの茎葉e6を乾燥することが可能である。この場合、乾燥工程S21を実行するために乾燥機32を用いる必要はない。 In addition, depending on the environment such as temperature and humidity, it is possible to dry the stem and leaf e6 of oil palm to a water content of 20% by mass or less even by sun drying. In this case, it is not necessary to use the dryer 32 to carry out the drying step S21.
 この乾燥工程S21を経て得られる乾燥後のアブラヤシの茎葉e7によれば、含有する水分が少なくなっていることから、後段の破砕工程S22及び成型工程S23の作業効率を向上させることができる。これにより、得られるバイオマス燃料の品質が均斉化されると共に、得られたバイオマス燃料の湿分による品質変化が抑制される。 According to the dried stems and leaves e7 of the dried oil palm obtained through the drying step S21, the contained water is reduced, so that the working efficiency of the crushing step S22 and the forming step S23 in the latter stage can be improved. Thereby, the quality of the obtained biomass fuel is equalized, and the quality change due to the moisture of the obtained biomass fuel is suppressed.
 この乾燥工程S21が、前記工程(i)に対応する。 The drying step S21 corresponds to the step (i).
  (破砕工程S22)
 乾燥工程S21が完了した後のアブラヤシの茎葉e7は、破砕機33に供給されて長繊維長が20mm以下のアブラヤシの茎葉e8に変形される。破砕機33としては、一軸破砕機、二軸破砕機等の一般的な設備が使用できる。
(Crushing process S22)
After the completion of the drying step S21, the stem and leaf e7 of the oil palm is supplied to the crusher 33 and transformed into the stem and leaf e8 of oil palm having a long fiber length of 20 mm or less. As the crusher 33, general equipment such as a uniaxial crusher or a twin-screw crusher can be used.
 この破砕工程S22は、乾燥工程S21の完了後のアブラヤシの茎葉e7を破砕して、後段の成型工程S23の作業効率を向上させるための工程である。乾燥工程S21の完了後のアブラヤシの茎葉e7は、長繊維長が300mm程度にまで達するものが含まれている場合があるため、この破砕工程S22においてアブラヤシの茎葉e7を破砕して、好ましくは20mm以下、より好ましくは10mm以下のアブラヤシの茎葉e8に変形する。ただし、後述の成型工程S23において、乾燥工程S21の完了後のアブラヤシの茎葉e7のままで成型が可能である場合には、この破砕工程S22を省略しても構わない。 The crushing step S22 is a step for crushing the stem and leaf e7 of the oil palm after the completion of the drying step S21 to improve the working efficiency of the subsequent forming step S23. Since the stem and leaf e7 of the oil palm after completion of the drying step S21 may include those having a long fiber length reaching about 300 mm, the stem and leaf e7 of oil palm is crushed in this crushing step S22, preferably 20 mm Hereinafter, it is more preferably deformed into stem and leaf e8 of oil palm of 10 mm or less. However, in the below-mentioned forming process S23, when forming is possible with the stem and leaf e7 of the oil palm after completion of the drying process S21, the crushing process S22 may be omitted.
 この破砕工程S22が、前記工程(k)に対応する。 The crushing step S22 corresponds to the step (k).
  (成型工程S23)
 破砕工程S22が完了した後のアブラヤシの茎葉e8は、成型機34に供給されて、ペレット(バイオマス燃料)e9に変形される。この成型工程S23により、かさ密度が0.50kg/L以上、圧縮強度が1.5N/mm2以上、熱量が3500kcal/kg以上の、ペレット状のバイオマス燃料e9が生成される。なお、かさ密度は、JISZ 7302-9「廃棄物固形化燃料-第9部:かさ密度試験方法」に規定する試験方法に、圧壊強度は、JIS Z 8841「造粒物-強度試験方法」に規定する試験方法に、熱量は、JIS Z 7302-2「廃棄物固形化燃料-第2部:発熱量試験方法」に規定する試験方法にそれぞれ準拠した試験で得られた測定値である。
(Molding step S23)
After the completion of the crushing step S22, the palm leaves e8 of the oil palm are supplied to the molding machine 34 and transformed into pellets (biomass fuel) e9. By this molding step S23, a pellet-like biomass fuel e9 having a bulk density of 0.50 kg / L or more, a compressive strength of 1.5 N / mm 2 or more, and a heat amount of 3500 kcal / kg or more is produced. The bulk density is the test method specified in JIS Z 7302-9 "Waste solidified fuel-Part 9: Bulk density test method", and the crushing strength is JIS Z 8841 "granulate-strength test method". In the specified test method, the heat quantity is a measured value obtained by the test based on the test method specified in JIS Z 7302-2 “Waste solidified fuel-Part 2: calorific value test method”.
 本実施形態では、成型機34内のアブラヤシの茎葉e8に対して、油水分離機22で分離されることで得られたスラッジ状の油脂分O1が、送油ポンプ35によって供給される。この油脂分O1は、成型機34において、成型助剤として利用される。油脂分O1は、熱量を有しているため、これをアブラヤシの茎葉e8に供給して成型することで、成型後のバイオマス燃料e9の熱量を増加させることができる。ただし、油脂分O1に含有されるアルカリ金属及び/又は塩素の含有量が多い場合には、この油脂分O1を成型助剤として用いないものとすることができる。 In the present embodiment, a sludge-like fat and oil component O1 obtained by being separated by the oil-water separator 22 is supplied to the stem and leaf e8 of the oil palm in the molding machine 34 by the oil feeding pump 35. The oil component O1 is used as a molding aid in the molding machine 34. Since the oil component O1 has a heat quantity, it can be increased by supplying it to the stems and leaves e8 of oil palm to mold the biomass fuel e9 after molding. However, when the content of the alkali metal and / or chlorine contained in the oil and fat portion O1 is large, the oil and fat portion O1 can not be used as a molding aid.
 ペレットの大きさは、輸送効率やハンドリング性を考慮して適宜決定することができる。成型後のバイオマス燃料e9は、発電用のCFB(循環流動層)ボイラ装置等で固形燃料として用いたり、セメント焼成装置等で石炭代替燃料として使用することができる。 The size of the pellet can be appropriately determined in consideration of transport efficiency and handling. The biomass fuel e9 after molding can be used as a solid fuel in a CFB (circulating fluidized bed) boiler apparatus or the like for power generation, or can be used as a coal alternative fuel in a cement burning apparatus or the like.
 この成型工程S23が、前記工程(j)に対応する。 The molding step S23 corresponds to the step (j).
 [実施例]
 前処理装置2を用いた前処理方法の実施例について、表1を参照して説明する。なお、表1に示すカリウム含有量は、試料を酸で全溶解して得られた溶液をICP発光分光分析法で測定した結果である。また、塩素含有量は、JISZ 7302-6「廃棄物固形化燃料-第6部:全塩素分試験方法」の試験方法に準拠して得られた試験結果である。また、表1のカリウム及び塩素の除去率欄の括弧なしの値は各々の工程までの総除去率(質量%)を示しており、括弧内の値は前工程からの除去率(質量%)を示している。
[Example]
An embodiment of the pretreatment method using the pretreatment device 2 will be described with reference to Table 1. In addition, the potassium content shown in Table 1 is the result of measuring the solution obtained by completely dissolving the sample with an acid by ICP emission spectrometry. The chlorine content is the test result obtained in accordance with the test method of JIS Z 7302-6 "Waste solidified fuel-Part 6: Total chlorine content test method". Also, the values without brackets in the column of removal rates of potassium and chlorine in Table 1 indicate the total removal rates (mass%) up to each step, and the values in the parentheses are removal rates from the previous step (mass%) Is shown.
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000001
 表1によれば、散水洗浄工程S14が完了した時点で、アブラヤシの茎葉のアルカリ含有量は0.16質量%、塩素含有量は0.075質量%である。更に、その後に圧搾工程S15が実行された場合、アブラヤシの茎葉のアルカリ含有量は0.08質量%、塩素含有量は0.025質量%である。 According to Table 1, when the water spray cleaning step S14 is completed, the alkali content of the leaves and leaves of the oil palm is 0.16% by mass, and the chlorine content is 0.075% by mass. Furthermore, when pressing process S15 is performed after that, the alkali content of the foliage of an oil palm is 0.08 mass%, and the chlorine content is 0.025 mass%.
 以上により、本発明の前処理工程S10によれば、アブラヤシの茎葉のアルカリ含有量を0.2質量%以下、塩素含有量を0.1質量%以下にまで低下させることができる。 As mentioned above, according to pre-processing process S10 of this invention, the alkali content of the foliage of oil palm can be reduced to 0.2 mass% or less, and chlorine content to 0.1 mass% or less.
 [別実施形態]
 以下、別実施形態につき説明する。
[Another embodiment]
Hereinafter, another embodiment will be described.
 〈1〉上述した実施形態では、前処理工程S10において、散水洗浄工程S14の完了後に圧搾工程S15を実行するものとしたが、この圧搾工程S15を省略しても構わない。図3は、この別実施形態に対応したフローチャートを図1にならって図示したものであり、図4は、この別実施形態の方法を実行するための装置の構成例を、図2にならって図示したものである。図4に示すように、この構成では、振動篩16で水分が振り分けられた後のアブラヤシの茎葉e5が、乾燥機32に供給され、乾燥工程S21が実行される。 <1> In the embodiment described above, the squeezing step S15 is performed after the completion of the water spray cleaning step S14 in the pretreatment step S10, but the squeezing step S15 may be omitted. FIG. 3 is a flow chart corresponding to this alternative embodiment and is shown following FIG. 1, and FIG. 4 is an example of the configuration of an apparatus for carrying out the method of this alternative embodiment according to FIG. It is illustrated. As shown in FIG. 4, in this configuration, the stem and leaf e5 of the oil palm after the water has been distributed by the vibrating sieve 16 is supplied to the dryer 32, and the drying step S21 is performed.
 上述したように、圧搾工程S15を実行しない場合であっても、散水洗浄工程S14の完了後に得られるアブラヤシの茎葉e5は、アルカリ含有量を0.2質量%以下、塩素含有量を0.1質量%以下にすることができる。なお、この別実施形態では、図2に示す圧搾機25を備えないため、排水処理装置24には、水分W3及び排洗浄水W5が供給されている。 As described above, even if the squeezing step S15 is not performed, the efoliated palm oil e5 obtained after completion of the water sprinkling washing step S14 has an alkali content of 0.2% by mass or less and a chlorine content of 0.1 It can be less than mass%. In addition, in this another embodiment, since the pressing machine 25 shown in FIG. 2 is not provided, the water W3 and the waste cleaning water W5 are supplied to the waste water treatment apparatus 24.
 〈2〉圧搾工程S12の実行前において、アブラヤシの茎葉を破砕する工程を更に備えるものとしても構わない。具体的には、前処理装置2が、破砕機33と同様の破砕機を備えると共に、この破砕機が、加熱機11に投入する前のアブラヤシの茎葉e1、又は、圧搾機13に投入する前のアブラヤシの茎葉e2を、長繊維長が300mm以下となるように破砕するものとしても構わない。これにより、圧搾機13における圧搾工程を効率的に行うことができる。 <2> The step of crushing the stems and leaves of oil palm may be further included before the execution of the pressing step S12. Specifically, the pretreatment device 2 is provided with a crusher similar to the crusher 33, and before the crusher is inserted into the stems and leaves e1 of oil palm before being introduced into the heater 11 or into the press 13. The stem and leaf e2 of the oil palm may be crushed so as to have a long fiber length of 300 mm or less. Thereby, the pressing process in the pressing machine 13 can be performed efficiently.
 この破砕工程は、工程(e)に対応する。 This crushing step corresponds to step (e).
 〈3〉図1において、圧搾工程S15の実行後、更に散水洗浄工程S14と圧搾工程S15を1回又は複数回繰り返し実行するものとしても構わない。これにより、アブラヤシの茎葉e6の内部に残留する微量のアルカリ金属や塩素を更に除去することができる。圧搾工程S15の実行後に再び実行される散水洗浄工程S14が工程(g)に対応し、その後に実行される圧搾工程S15が工程(h)に対応する。 <3> In FIG. 1, after the execution of the squeezing step S15, the water spray washing step S14 and the squeezing step S15 may be repeated one or more times. As a result, it is possible to further remove a trace amount of alkali metal and chlorine remaining in the stem and leaf e6 of the oil palm. Sprinkling washing process S14 performed again after execution of squeezing process S15 corresponds to a process (g), and squeezing process S15 performed after that corresponds to a process (h).
 〈4〉上記の実施形態では、排洗浄水W5を水洗水供給装置21に循環供給することで、水洗水W1として利用するものとして説明したが、この態様は任意である。すなわち、排洗浄水W5を全て排水処理装置24に排出するものとしても構わない。 <4> In the above embodiment, the waste washing water W5 is described as being used as the washing water W1 by circulating and supplying it to the washing water supply device 21, but this aspect is optional. In other words, all the drainage cleaning water W5 may be discharged to the drainage processing device 24.
 〈5〉上記の実施形態において、圧搾機25から排出される圧搾水SW2を排水処理装置24に供給する構成としたが、圧搾水SW1と同様に、油水分離機22を経由して、水分W3を排水処理装置24に供給し、油脂分O1を成型機34に供給するものとしても構わない。 <5> In the above embodiment, although the configuration is such that the pressed water SW2 discharged from the pressing machine 25 is supplied to the drainage treatment device 24, the water W3 passes through the oil / water separator 22 similarly to the pressed water SW1. May be supplied to the waste water treatment apparatus 24, and the oil and fat content O1 may be supplied to the molding machine 34.
 〈6〉上記の実施形態において、油水分離機22で分離した油脂分O1を成型機34に供給するか否かは任意である。 <6> In the above embodiment, whether or not the oil component O1 separated by the oil / water separator 22 is supplied to the molding machine 34 is optional.
    1   :  バイオマス燃料化装置
    2   :  前処理装置
    3   :  後処理装置
   11   :  加熱機
   12   :  ホッパ
   13   :  圧搾機
   14   :  水洗装置
   15   :  振動篩
   16   :  振動篩
   17   :  洗浄水供給装置
   18   :  排洗浄水タンク
   19   :  送水ポンプ
   21   :  水洗水供給装置
   22   :  油水分離機
   24   :  排水処理装置
   25   :  圧搾機
   32   :  乾燥機
   33   :  破砕機
   34   :  成型機
   35   :  送油ポンプ
DESCRIPTION OF SYMBOLS 1: Biomass fueling apparatus 2: Pre-processing apparatus 3: Post-processing apparatus 11: Heating machine 12: Hopper 13: Press machine 14: Water washing apparatus 15: Vibrating sieve 16: Vibrating sieve 17: Washing water supply apparatus 18: Waste water Tank 19: Water feed pump 21: Flush water supply device 22: Oil / water separator 24: Waste water treatment device 25: Presser 32: Dryer 33: Crusher 34: Molding machine 35: Oil transfer pump

Claims (13)

  1.  アブラヤシの茎葉を加熱する工程(a)と、
     前記工程(a)によって加熱された前記アブラヤシの茎葉を圧搾する工程(b)と、
     前記工程(b)によって圧搾された前記アブラヤシの茎葉に、物理的衝撃を与えながら水洗する工程(c)と、
     前記工程(c)によって水洗された前記アブラヤシの茎葉を、水切りした後に散水洗浄する工程(d)とを有することを特徴とするアブラヤシの茎葉の前処理方法。
    Heating the stems and leaves of oil palm (a),
    Squeezing the stems and leaves of the oil palm heated in the step (a) (b)
    Washing the leaves and leaves of the oil palm squeezed in the step (b) while applying physical impact (c);
    And d) removing the leaves and leaves of the oil palm washed in the step (c) with water and then washing the leaves and leaves in the step (d).
  2.  前記工程(b)よりも前の段階で、前記アブラヤシの茎葉を長繊維長が300mm以下となるように破砕する工程(e)を有することを特徴とする請求項1に記載のアブラヤシの茎葉の前処理方法。 The stem and leaf of oil palm according to claim 1, comprising a step (e) of crushing the stem and leaf of the oil palm so as to have a long fiber length of 300 mm or less at a stage prior to the step (b). Pre-treatment method.
  3.  前記工程(a)は、蒸気を使用した加熱工程であることを特徴とする請求項1又は2に記載のアブラヤシの茎葉の前処理方法。 The method according to claim 1 or 2, wherein the step (a) is a heating step using steam.
  4.  前記工程(b)は、前記アブラヤシの茎葉に含まれる水分が60質量%以下になるように除去する工程であることを特徴とする請求項1~3のいずれか1項に記載のアブラヤシの茎葉の前処理方法。 The stem and leaf of oil palm according to any one of claims 1 to 3, wherein the step (b) is a step of removing water contained in the stem and leaf of the oil palm to be 60% by mass or less. How to preprocess
  5.  前記工程(c)は、瞬間的な前記物理的衝撃を前記アブラヤシの茎葉に繰り返し与えながら水洗する工程であることを特徴とする請求項1~4のいずれか1項に記載のアブラヤシの茎葉の前処理方法。 5. The foliar leaf of oil palm according to any one of claims 1 to 4, wherein the step (c) is a step of washing while repeatedly giving momentary physical impact to the foliage of the oil palm. Pre-treatment method.
  6.  前記工程(c)は、水洗される対象となる前記アブラヤシの茎葉1質量部(乾燥質量)に対して、3質量部以上22質量部以下の水量で、前記アブラヤシの茎葉を水洗する工程であることを特徴とする請求項1~5のいずれか1項に記載のアブラヤシの茎葉の前処理方法。 The step (c) is a step of rinsing the leaves and leaves of the oil palm in a water amount of 3 parts by mass or more and 22 parts by mass or less with respect to 1 part by mass (dry mass) of the leaves and leaves of the oil palm The method for pretreating the leaves and leaves of oil palm according to any one of claims 1 to 5, characterized in that
  7.  前記工程(d)は、散水される対象となる前記アブラヤシの茎葉1質量部(乾燥質量)に対して、3質量部以上20質量部以下の散水量で、前記アブラヤシの茎葉を散水洗浄する工程であることを特徴とする請求項1~6のいずれか1項に記載のアブラヤシの茎葉の前処理方法。 The step (d) is a step of sprinkling the leaves and leaves of the oil palm in an amount of 3 parts by mass or more and 20 parts by mass or less with respect to 1 part by mass (dry mass) of the leaves and leaves of the oil palm The method for pretreating the leaves and leaves of oil palm according to any one of claims 1 to 6, characterized in that
  8.  前記工程(c)において、前記工程(d)で使用された洗浄水が回収された後の水が用いられることを特徴とする請求項1~7のいずれか1項に記載のアブラヤシの茎葉の前処理方法。 The stem and leaf of oil palm according to any one of claims 1 to 7, wherein in the step (c), water after the washing water used in the step (d) is recovered is used. Pre-treatment method.
  9.  前記工程(d)の後に、前記アブラヤシの茎葉を更に圧搾する工程(f)を有することを特徴とする請求項1~8のいずれか1項に記載のアブラヤシの茎葉の前処理方法。 The method for pre-treating stems and leaves of oil palm according to any one of claims 1 to 8, further comprising the step (f) of squeezing stems and leaves of the oil palm after the step (d).
  10.  前記工程(f)の後に、前記アブラヤシの茎葉を更に散水洗浄する工程(g)と、
     前記工程(g)の後に、前記アブラヤシの茎葉を更に圧搾する工程(h)とを有することを特徴とする請求項9に記載のアブラヤシの茎葉の前処理方法。
    After the step (f), the stem and leaves of the oil palm are further washed with water (g);
    The method for pretreatment of oil palm leaves and leaves according to claim 9, further comprising the step (h) of further compressing the leaves and leaves of the oil palm after the step (g).
  11.  請求項1~10のいずれか1項に記載のアブラヤシの茎葉の前処理方法の完了後に、前記アブラヤシの茎葉を、当該アブラヤシの茎葉に含まれる水分が20質量%以下になるまで乾燥させる工程(i)と、
     前記工程(i)の後に、乾燥した前記アブラヤシの茎葉をペレットに成型する工程(j)とを有することを特徴とするバイオマス燃料の製造方法。
    A step of drying stems and leaves of the oil palm after completion of the method of pre-treating stems and leaves of oil palm according to any one of claims 1 to 10 until the water content in the stems and leaves of the oil palm becomes 20% by mass or less i) with
    After the step (i), a step (j) of molding the dried leaves and leaves of the oil palm into a pellet.
  12.  前記工程(i)と前記工程(j)との間に、前記アブラヤシの茎葉を長繊維長が20mm以下となるまで破砕する工程(k)を有することを特徴とする請求項11に記載のバイオマス燃料の製造方法。 The biomass according to claim 11, characterized in that there is a step (k) of crushing the palm leaves of the oil palm until the long fiber length becomes 20 mm or less between the step (i) and the step (j). Fuel production method.
  13.  前記工程(j)は、請求項1~10のいずれか1項に記載のアブラヤシの茎葉の前処理方法の完了後に得られた、前記アブラヤシの茎葉由来の油脂を、成型助剤として使用する工程であることを特徴とする請求項11又は12に記載のバイオマス燃料の製造方法。 The step (j) uses the oil and fat derived from the leaves and leaves of the oil palm obtained after completion of the method for pre-treating the leaves and leaves of oil palm according to any one of claims 1 to 10 as a molding aid The method for producing a biomass fuel according to claim 11 or 12, characterized in that
PCT/JP2017/032290 2017-09-07 2017-09-07 Pretreatment method for frond of oil palm and manufacturing process for biomass fuel WO2019049266A1 (en)

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