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GB2164331A - Waste disposal apparatus - Google Patents

Waste disposal apparatus Download PDF

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Publication number
GB2164331A
GB2164331A GB8419555A GB8419555A GB2164331A GB 2164331 A GB2164331 A GB 2164331A GB 8419555 A GB8419555 A GB 8419555A GB 8419555 A GB8419555 A GB 8419555A GB 2164331 A GB2164331 A GB 2164331A
Authority
GB
United Kingdom
Prior art keywords
tower
pelletiser
fraction
compost
light fraction
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
GB8419555A
Other versions
GB2164331B (en
GB8419555D0 (en
Inventor
Thomas Richard Wotton
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to GB8419555A priority Critical patent/GB2164331B/en
Publication of GB8419555D0 publication Critical patent/GB8419555D0/en
Priority to JP21155384A priority patent/JPS6140888A/en
Publication of GB2164331A publication Critical patent/GB2164331A/en
Application granted granted Critical
Publication of GB2164331B publication Critical patent/GB2164331B/en
Expired legal-status Critical Current

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Classifications

    • 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
    • C10L5/46Solid fuels essentially based on materials of non-mineral origin on sewage, house, or town refuse
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03BSEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
    • B03B9/00General arrangement of separating plant, e.g. flow sheets
    • B03B9/06General arrangement of separating plant, e.g. flow sheets specially adapted for refuse
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00Fertilisers from household or town refuse
    • C05F9/02Apparatus for the manufacture
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • 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
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/52Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Engineering & Computer Science (AREA)
  • Manufacturing & Machinery (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)

Abstract

A waste disposal apparatus includes a shredder 4 to shred waste material to a required product size. The shredded material is passed through a magnetic separator 8 to a pneumatic separator 16 which separates the light fraction from the heavy fraction. An aerobic process is carried out on the heavy fraction in a digestor tower 18 to convert the heavy fraction into compost. The light fraction is fed to a pelletiser 36 which converts the light fraction into pellets of refuse derived fuel. <IMAGE>

Description

SPECIFICATION Waste disposal process Technical field The present invention relates to a waste disposable process, and is particularly concerned with but not restricted to a process for disposing of household and commercial waste.
Two conventional methods of disposing of household waste are: (a) By the tipping of raw rubbish, and (b) By incineration.
Tipping is the more commonly used method of disposal but this method has unattractive features particularly where it is not properly controlled. It can provide a source of water pollution, and it can become an attraction for disease carrying insects and vermin.
The incineration of waste is expensive.
It has also been proposed to provide a waste disposal process which can produce compost. With this previously proposed process a significant amount of the waste material has to be rejected as being of no further use.
Object of the invention It is the aim of the invention to provide a waste disposal process in which the aforementioned difficulties are alleviated.
Statements of invention The present invention relates to a waste disposal process comprising shredding the waste material to a required product size, separating the ferrous material from the waste material, separating the light fraction from the heavy fraction, feeding the heavy fraction through the top of a digestor tower, carrying out an aerobic process in the tower under controlled conditions to convert the heavy fraction into compost, and feeding the light fraction to a pelletizer to form pellets of refuse derived fuel.
The pelletiser may comprise a feed shredder and a pre-dryer to reduce the moisture content of the material.
The pellets may be cooled and screened, the pellets above a preselected size being bagged or stored in bulk.The pellets below a preselected size are recirculated into the pelletiser for pettelisation.
Figure in the drawing An embodiment of the invention will now be described by way of example with reference to the accompanying illustrative block schematic drawing of a composting plant.
Detailed description of the drawing Referring to the drawing, waste material to be processed is brought to a plant reception area (2) where it is weighed. Two weighbridges mounted on either side of a weighbridge office are located at this reception area (2), one weighbridge or Quin' traffic and the other weighbridge for QOut' traffic.
Each weighbridge is of the load cell type and is sunk into a shallow pit so that the weighbridge platform is flush with the ground level. Each weighbridge has anti-skid deck plates of self draining pattern which are mounted on a heavy duty steel superstructure of welded construction. This superstructure is mounted on high grade load cells and each weighbridge will include restrainers, kerbing and bearing plates. Each weighbridge is graduated up to 50,000 k.g. in 10 k.g. divisions on a digital weight indicator having numerals which are 30 mm high.
The weighbridges are arranged automatically to print out four copies of a suitable size ticket together with a tallyroll. Both the tickets and the tallyroll will record the required data, such as for example date and time, Quin' and QOut' weights, the material code and the automatic calculation of the nett weight.
The weighed material is tipped onto a concrete apron and passed onto two slow moving horizontal plate feeders which are each two meters wide and ten meters long. These plate feeders are driven by units which can provide variable speeds and torque control. These feeders are mounted in a shallow reception hopper so as to be approximately at ground level thereby enabling items such as oxygen bottles which will cause damage to the plant to be removed by hand.
These slow moving feeders onto two inclined plate feeders designed to operate at approximately three times that of the slower moving feeders.
These inclined plate feeders carry the waste material into the primary shredders (4), and they have continuous side skirt plates terminating at the shredder hood.
Each primary shredder (4) is a hammer mill having a throat size of 120 cm x 150 cm, and is driven at 850 rpm by a 350 HP motor capable of reducing approximately 55 tonnes of waste per hour to the required shredded size.
Each hammer mill possess a feed hood complete with anti flyback curtain, a vee belt drive complete with motor pulley, pulveriser pulley and vee belts, a 350 HP slipring motor complete with slide rails, suitable for a 50 Hz supply, a vee belt drive guard and a fabricated base frame.
Two belt conveyors (6) which are 1.20 m wide convey the shredded material from the shredders (4) to magnetic separators (8). There are two magnetic separators (8), one at the head of each belt conveyor (6). These magnetic separators (8) remove magnetizeable material from the shredded waste material. The remainder of this shredded waste material is then conveyed to two rotary trommel screens (10) which are approximately 2 m diameter by 7 m long and are driven by variable speed drive units incorporating torque control.Each trommel screen (10) is mounted in a 3 mm thick mild steel dust enclosure, and is located on a platform provided with a ground level walkway and all necessary chutes and supports.
The smaller sized material - Qthe fines' - is collected from the trommel screens (10) by a fines conveyor (12) and fed onto main feed conveyor (14).
The oversized material from the trommel screens (10) is passed to a vibrational pneumatic separator (16) which separates the light material, such as papers and plastics, from the heavier material. This heavier material is passed to the main feed conveyor (14) where it combines with the fines from the trommel screens (10). The main feed conveyor (14) comprises a single inclined belt 1.40 m wide which is completely enclosed where it runs outside a building. This conveyor (14) transports rejected fine material from the trommel screen (10) and heavier material from the separator (16) to digestor towers (18). A chute is located at the heading of the main feed conveyor (14) to feed into the number 1 or the number 2 digestor tower. The main feed conveyor (14) is supported on a series of trestles manufactured in braced frames.A trestle is located at the head of the conveyor (14) adjacent to the digestor towers (18) so as to take the main reaction from the head of the conveyor (14) in order to minimize the load on the towers (18). These frames also support a three drum type gravity take-up device.
The two glass coated, steel, open-topped towers (18) are provided with an internal diameter of 9 m and a height of 24 m. These towers (18) are made of glass which is fused to steel sheets which are bolted together with plastics-headed high tensile steel bolts, nuts and washers. The lap joints between the steel sheets are sealed with a specialised mastic sealant.
The tower structure includes a vertical ladder with five intermediate access platforms. A top cage located on the ladder and a walkway is provided to connect the main walkway with a horizontal catwalk. An opening 23 cm square is provided in each tower (18) with a cover plate and circular screw flanges. A door is mounted in the base sheet of each tower (18) to allow access under the steel floor.
A mild steel plate floor is located 980 mm above the base of each tower (18), and this floor is perforated to allow the passage of air therethrough.
Five thermocouples are provided at equally spaced vertical points along the height of each tower (18), and these thermocouples are connected to a six point recording thermometer in a control room. The six temperatures recorded are the ambient temperature, together with the internal temperature of the material in the tower at the five points. This information is critical to the maintainance of the maximum aerobic efficiency of the plant. The recordings enable operators to effect required temperatures for pathogen kill and sterilisation and these recordings identify any low temperature areas within the tower (18) which require additional treatment by the insertion of localised air pokers. In addition, gas analysis equipment is available to analyse samples of the gases emitted from the top of a tower (18).
Each tower (18) operates on a continuous basis with 100 tonnes of shredded material being fed into the top of the tower (18) daily from the conveyor (14), and the equivalent amount (approximately 60 tonnes) of compost being removed from the base of the tower (18). Air is provided by air compressors, in response to the aforementioned temperature readings, and passed into a plenum chamber in the base of a tower (18). This air then passes through the perforated floor of the tower (18) and is allowed to percolate through the material and along the full height of the tower (18) hereby effecting complete aerobic decomposition.
The material resides in a tower (18) for a period of 14 days, but primary decomposition takes place over a period of approximately 10 days. The last four days spent in the tower (18) complete the total degeneration of the material and replace the curing period required by other systems.
The composted material is removed from the base of a tower (18) by a rotary extractor having a capacity of 15-20 tonnes per hour, and this composted material is passed along a feed conveyor (20) to two product crushers (22). The feed conveyor (20) is 1 m wide and is provided with full length skirts. The product crushers (22) are designed to reduce the compost material to a size less than 15 mm, and these crushers are driven by 25 HP motors.
The material is then passed from the product crusher (22) to a vibrating compost screen (24) 1.8 m wide x 4.5 m long included in a 3 mm mild steel dust enclosure. This screen (24) is provided complete with a supporting structure, sheeted housing, access platforms and the necessary chutes. This compost screen (24) has a 15 mm mesh and the material passing though this screen is the final composted product which is passed along a fine compost conveyor (26) to bagging plant (28). This conveyor (26) is 1.2 m wide and the bagging plant (28) is complete will full length skirts.
Oversize material is returned from the screen (24) along a return conveyor (30) to the reception area (2) for recirculation and reprocessing. The conveyor (30) is 1 m and is provided with full length skirts and a walkway on one side.
The bagging plant (28) is capable of filling 3x50 k.g. bags per minute and this bagging plant (28) includes a belt feed automatic weigher with a discharge chute and a foot valve operated pneumatic bag holder. The plant (28) also includes a continuous band heat sealer with a sealing conveyor, and an inclined conveyor to elevate sealed bags to should height for easy handling. The light fraction of the material from the separator (16) is passed to twin pelletising plants Each pelletising plant comprises a feed shredder (32) and a pre-dryer (34) to reduce the moisture content of the material to approximately 15-. The material is then pelletised in a pelletiser (36) and cooled in an after-cooler (38).
The pellets are then screened in a screen (40), and the pellets above a preselected size are emitted from the screen (40) and either bagged or stored in bulk for sale. The fine material passing through the screen (40) is recirculated into the pelletiser (36) for re-pelletisation.
The pellets from the screen (40) which have been produced by the pelletiser plants constitute refuse derived fuel, and on a tonnage basis approximately 30- of the input tonnage to the plant is produced as compost, and 30- as refuse derived fuel. The re maining tonnage is lost in the process as water vapour, emitted gases (mainly Co2) and extracted ferrous metals.

Claims (15)

1. A waste disposal process comprising shredding the waste material to a required product size, separating the ferrous material from the waste material, separating the light fraction from the heavy fraction, feeding the heavy fraction through the top of a digestor tower, carrying out an aerobic process in the tower under controlled conditions to convert the heavy fraction into compost, and feeding the light fraction to a pelletiser to form pellets of refuse derived fuel.
2. A process as claimed in Claim 1 including shredding the light fraction in the pelletiser.
3. A process as claimed in Claim 2 including pre-drying the shredded light fraction.
4. A process as claimed in any preceding Claim including cooling and screening the pellets.
5. A process as claimed in any preceding Claim including recirculating the pellets below a preselected size into the pelletiser for re-pelletisation.
6. A process as claimed in any preceding Claim in which the ferrous material is separated magnetically.
7. A process as claimed in any preceding Claim in which the compost is crushed and screened.
8. Apparatus for carrying out a waste disposal process including a shredder to shred the waste material to a required product size, a first separator to separate the ferrous material from the waste material, a second separator to separate the light fraction from the heavy fraction, a digestor tower in which an aerobic process can be carried out under controlled conditions to convert the heavy fraction into compost, and a pelletiser to form pellets of refuse derived fuel from the light fraction.
9. An apparatus as claimed in Claim 8 in which the pelletiser comprises a feed shredder.
10. An apparatus as claimed in Claim 9 in which the pelletiser comprises a pre-dryer.
11. An apparatus as claimed in any one of Claims 8 to 10 including an after-cooler and a screen to cool and screen the pellets.
12. An apparatus as claimed in any one of Claims 8 to 11 in which the first separator is a magnetic separator.
13. An apparatus as claimed in any one of Claims 8 to 12 including a crusher and a screen to crush and screen the compost from the digestor tower.
14. A waste disposal process substantially as herein described with reference to the accompanying drawing.
15. A waste disposal apparatus substantially as herein described and shown in the accompanying drawing.
GB8419555A 1984-08-01 1984-08-01 Waste disposal apparatus Expired GB2164331B (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
GB8419555A GB2164331B (en) 1984-08-01 1984-08-01 Waste disposal apparatus
JP21155384A JPS6140888A (en) 1984-08-01 1984-10-11 Waste treatment and equipment therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
GB8419555A GB2164331B (en) 1984-08-01 1984-08-01 Waste disposal apparatus

Publications (3)

Publication Number Publication Date
GB8419555D0 GB8419555D0 (en) 1984-09-05
GB2164331A true GB2164331A (en) 1986-03-19
GB2164331B GB2164331B (en) 1988-01-20

Family

ID=10564752

Family Applications (1)

Application Number Title Priority Date Filing Date
GB8419555A Expired GB2164331B (en) 1984-08-01 1984-08-01 Waste disposal apparatus

Country Status (2)

Country Link
JP (1) JPS6140888A (en)
GB (1) GB2164331B (en)

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0281699A1 (en) * 1987-03-13 1988-09-14 Denys Herbert George Tollemache Turned and aerated silo composting plant
DE4031417A1 (en) * 1990-10-04 1992-04-09 Peter Prof Dr Kraus METHOD FOR SEPARATING METAL-CONTAINING WASTE COMPONENTS
EP0636679A1 (en) 1993-07-28 1995-02-01 GALLOOMETAL, naamloze vennootschap Solid fuel from shredder waste
AT403554B (en) * 1996-05-08 1998-03-25 Adl Gmbh METHOD FOR THE STORAGE OF SHREDDER WASTE IN WASTE PLANTS
WO2000039255A1 (en) * 1998-12-23 2000-07-06 Arcadis Heidemij Realisatie B.V. Method for producing fuel from the biomass component of organic wet fraction (owf)
US6136590A (en) * 1998-02-24 2000-10-24 Kruse; Robert A. Waste materials recycling method and apparatus
AT407131B (en) * 1999-04-12 2000-12-27 Walter Stoiber Process for obtaining wood chips or pellets from green cuttings
EP1310307A2 (en) * 2001-11-07 2003-05-14 Vapo Oy Method and arrangement for utilizing dry solid waste from households
GB2419889A (en) * 2004-11-06 2006-05-10 Aea Technology Plc Energy from waste
GB2480318A (en) * 2010-05-14 2011-11-16 Advanced Recycling Tech A method of processing waste to produce a fuel product
CN102776048A (en) * 2012-07-02 2012-11-14 刘柱良 Preparation process for granular fuels
WO2016051214A1 (en) * 2014-09-30 2016-04-07 Konstantinos Soukos Method and system for the recycling and treatment of municipal solid waste

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE3614325A1 (en) * 1986-04-28 1987-10-29 Organ Faser Technology Co METHOD AND DEVICE FOR PROCESSING HOUSEHOLD, COMMERCIAL AND OTHER SIMILAR DISEASE
JP3967552B2 (en) 2001-02-19 2007-08-29 本田技研工業株式会社 Gas-liquid separator for engines
CN105032891B (en) * 2015-07-09 2017-03-15 大连惠川环保科技有限公司 A kind of complete resource domestic garbage pyrolysis energy conversion method

Cited By (17)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0281699A1 (en) * 1987-03-13 1988-09-14 Denys Herbert George Tollemache Turned and aerated silo composting plant
DE4031417A1 (en) * 1990-10-04 1992-04-09 Peter Prof Dr Kraus METHOD FOR SEPARATING METAL-CONTAINING WASTE COMPONENTS
EP0636679A1 (en) 1993-07-28 1995-02-01 GALLOOMETAL, naamloze vennootschap Solid fuel from shredder waste
AT403554B (en) * 1996-05-08 1998-03-25 Adl Gmbh METHOD FOR THE STORAGE OF SHREDDER WASTE IN WASTE PLANTS
US6136590A (en) * 1998-02-24 2000-10-24 Kruse; Robert A. Waste materials recycling method and apparatus
CN1094803C (en) * 1998-02-24 2002-11-27 罗伯特·A·克鲁斯 Method and device for recycling waste materials
WO2000039255A1 (en) * 1998-12-23 2000-07-06 Arcadis Heidemij Realisatie B.V. Method for producing fuel from the biomass component of organic wet fraction (owf)
AT407131B (en) * 1999-04-12 2000-12-27 Walter Stoiber Process for obtaining wood chips or pellets from green cuttings
EP1310307A2 (en) * 2001-11-07 2003-05-14 Vapo Oy Method and arrangement for utilizing dry solid waste from households
EP1310307A3 (en) * 2001-11-07 2004-04-21 Vapo Oy Method and arrangement for utilizing dry solid waste from households
GB2419889A (en) * 2004-11-06 2006-05-10 Aea Technology Plc Energy from waste
GB2480318A (en) * 2010-05-14 2011-11-16 Advanced Recycling Tech A method of processing waste to produce a fuel product
GB2540888A (en) * 2010-05-14 2017-02-01 Biocentre Tech Ltd Waste processing
GB2480318B (en) * 2010-05-14 2017-04-05 Biocentre Tech Ltd Waste processing
GB2540888B (en) * 2010-05-14 2017-05-31 Biocentre Tech Ltd Waste processing
CN102776048A (en) * 2012-07-02 2012-11-14 刘柱良 Preparation process for granular fuels
WO2016051214A1 (en) * 2014-09-30 2016-04-07 Konstantinos Soukos Method and system for the recycling and treatment of municipal solid waste

Also Published As

Publication number Publication date
JPS6140888A (en) 1986-02-27
GB2164331B (en) 1988-01-20
GB8419555D0 (en) 1984-09-05

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PCNP Patent ceased through non-payment of renewal fee
728C Application made for restoration (sect. 28/1977)
728A Order made restoring the patent (sect. 28/1977)
PCNP Patent ceased through non-payment of renewal fee

Effective date: 19920801