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WO2001038259A2 - Method for recycling the organic fraction of municipal solid waste and the like - Google Patents

Method for recycling the organic fraction of municipal solid waste and the like Download PDF

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Publication number
WO2001038259A2
WO2001038259A2 PCT/EP2000/011594 EP0011594W WO0138259A2 WO 2001038259 A2 WO2001038259 A2 WO 2001038259A2 EP 0011594 W EP0011594 W EP 0011594W WO 0138259 A2 WO0138259 A2 WO 0138259A2
Authority
WO
WIPO (PCT)
Prior art keywords
organic fraction
organic
liquid part
order
liquid
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
Application number
PCT/EP2000/011594
Other languages
French (fr)
Other versions
WO2001038259A3 (en
Inventor
Luciano Zoia
Fabio Piasentin
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.)
BIOENERGY Srl
Original Assignee
BIOENERGY Srl
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 BIOENERGY Srl filed Critical BIOENERGY Srl
Priority to AU31547/01A priority Critical patent/AU3154701A/en
Publication of WO2001038259A2 publication Critical patent/WO2001038259A2/en
Publication of WO2001038259A3 publication Critical patent/WO2001038259A3/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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Classifications

    • 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
    • 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
    • Y02E50/30Fuel 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
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Definitions

  • the present invention relates to a method for recycling the organic fraction of municipal solid waste and the like.
  • the source of the organic fraction is municipal solid waste derived from separate collection or sorted collection.
  • the produced amount of liquid fraction owing to its intrinsic characteristics, is the source of unpleasant odors, considerable processing and/or disposal costs, etcetera.
  • the aim of the present invention is to provide a dense organic liquid which is of excellent quality and is separate from the remaining fibrous part.
  • a consequent object is to provide such an organic liquid through simple and safe operations.
  • Another object is to provide sterilization of the residual products.
  • a further object is to provide a low-cost apparatus for sorting the resulting product.
  • a still further object is to increase disposal volumes for an equal fermentation plant.
  • Another object is to use insufficiently sorted fractions with good process results.
  • Another object is to expand the categories of waste that can be processed by means of a fermentation-based recovery process.
  • Another object is to obtain a higher quality and a larger amount of biogas.
  • Another object is a possible increase in the supply load, with a consequent increase in the specific potential of fermentation plants.
  • a method for recycling a pre-screened organic fraction of municipal solid waste and the like derived from separate or sorted collections characterized in that it comprises the steps of: shredding the pre-screened organic fraction, breaking up the cell membrane of the organic fraction; crushing the shredded organic fraction in order to separate a liquid part from a first solid part; subjecting to an anaerobic process said liquid part in order to obtain a second solid part and biogas.
  • Figure 1 is a block diagram of the layout of a method according to the invention.
  • FIG. 2 is another more detailed block diagram of an operating step of the method of Figure 1. Way of carrying out the Invention
  • the method comprises a first step 10 for opening bags, since the material arrives loose and contained in bags which must be opened in order to allow the discharge of the organic material.
  • the material is then subjected to a screening process 11, which consists in cleaning by separating out plastics, various containers, metals, etcetera.
  • the organic material is then shredded, step 12, undergoing comminution and breaking the plant cell walls so as to facilitate the release of the cell sap, and is then crushed, step 13.
  • step 13 separation occurs between a liquid-dense part 14 on one side and a woody-fibrous solid part 15, with the remaining impurities, on the other.
  • steps 12 and 13 are provided by means of various types of apparatus, such as variable-pitch screw feeders, press heads, pressing systems using shock waves produced by explosion or air or gas pressure, accompanied by a series of perforated grids or membranes which allow drainage of the dense liquid 14 and retain the solid fraction or fiber 15 and/or the impurities inside the pressure region.
  • the resulting liquid part 14 has a light brown color, a density approximately equal to that of oil, a pungent acrid odor, a percentage of total solids on the dry substance of 7-15%, a percentage of volatile solids on the dry substance of 70-75%, a C/N (carbon/nitrogen) ratio of 1/12 ⁇ 2%, a percentage of impurity of less than 0.5% and a pH of 4-5.
  • the steps 10, 11, 12 and 13 sort the organic fraction of municipal solid waste and the like, achieving a degree of cleaning of the material with particle size and uniformity adapted for feeding anaerobic reactors 20, opening a new frontier in the use of this biological process in the field of recovery and reuse.
  • the material to be fermented In order to achieve good fermentation and thus maximize the yield in biogas production, the material to be fermented must in fact be as much as possible dispersed and solubilized in a liquid, so as to increase the efficiency of the breakdown of carbon compounds on the part of methane- generating bacteria.
  • the steps 10, 11, 12 and 13 provide an extremely fine dispersion of the liquid.
  • the organic liquid 14 is used for a subsequent step which is constituted by an anaerobic process 16 for producing biogas 21, while the fibrous part 15 is sent to the aerobic process 28.
  • the liquid part 14 is thus destined for the anaerobic fermentation process 16, collecting into a discharge region 17 and, by means of a pump 18, into a homogenization tank 19, from which it then enters an anaerobic reactor 20.
  • Biogas 21 exits from the reactor 20 and can be advantageously utilized to obtain heat 22 and/or electric power 23.
  • a spent substance second solid part
  • sludge 25 and a supernatant liquid part 26, destined for biological conditioning 27, are obtained by means of a belt press 24 which is per se known.
  • the extraction of the liquids allows to accelerate and optimize the fermentation process and to select only the part that is useful for anaerobic fermentation, at the same time releasing a residue which is sanitized and is to be used, in the composting process, as organic material with a high nitrogen content (5-6%) in a mixture with the woody-fibrous part in order to obtain a biological organic fertilizer.
  • the system is provided as an alternative to current waste disposal systems, demonstrating that it integrates perfectly in the recovery of biomasses as a renewable and alternative energy source.
  • the materials and the dimensions may be any according to requirements.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)
  • Transition And Organic Metals Composition Catalysts For Addition Polymerization (AREA)
  • Treatment Of Sludge (AREA)

Abstract

A method for recycling an organic fraction of municipal solid waste which derives from separate or sorted collections, comprising the steps of: shredding (12) the organic fraction, breaking up the cell membrane of the organic fraction; crushing (13) the shredded organic fraction in order to separate a liquid part (14) from the first solid part (15); subjecting to an anaerobic process the liquid part (14) in order to obtain a second solid part (25) and biogas (21).

Description

METHOD FOR RECYCLING THE ORGANIC FRACTION OF MUNICIPAL SOLID WASTE AND THE LIKE Technical Field
The present invention relates to a method for recycling the organic fraction of municipal solid waste and the like. Background Art
The source of the organic fraction is municipal solid waste derived from separate collection or sorted collection.
Italian legislative Decree no. 22 of February 5, 1997, in defining a new waste management strategy, introduces its priority in terms of reuse, recovery and disposal under safe conditions.
The application of the biological fermentation process, which converts municipal solid waste or biomasses into mixtures of microorganisms which derive from the increase in the number and quality thereof, using the waste as a nutrient mix, raises some severe practical problems in terms of reuse and transformation determined by the lack of qualitative uniformity of the waste and of the biomasses.
The facilities that process the organic material arriving from the moisture-containing fraction of separate collection encounter considerable problems arising from naturally occurring release and percolation, which is particularly conspicuous in the summer months, of the liquid drainage fraction that originates from the organic matter.
The produced amount of liquid fraction, owing to its intrinsic characteristics, is the source of unpleasant odors, considerable processing and/or disposal costs, etcetera.
The impurities that notoriously accompany the material make it hardly usable for transfer to the anaerobic process also due to the poor quality of the feed, which does not allow to assign the final solid product of fermentation for all kinds of recovery. Moreover, the presence of metallic and stone-like objects in the mass to be sorted and processed causes severe drawbacks and damage to the grinding and sorting equipment. Disclosure of the Invention
The aim of the present invention is to provide a dense organic liquid which is of excellent quality and is separate from the remaining fibrous part.
A consequent object is to provide such an organic liquid through simple and safe operations.
Another object is to provide sterilization of the residual products.
A further object is to provide a low-cost apparatus for sorting the resulting product.
A still further object is to increase disposal volumes for an equal fermentation plant.
Another object is to use insufficiently sorted fractions with good process results. Another object is to expand the categories of waste that can be processed by means of a fermentation-based recovery process.
Another object is to obtain a higher quality and a larger amount of biogas.
Another object is a possible increase in the supply load, with a consequent increase in the specific potential of fermentation plants.
These and other objects which will become better apparent hereinafter are achieved by a method for recycling a pre-screened organic fraction of municipal solid waste and the like derived from separate or sorted collections, characterized in that it comprises the steps of: shredding the pre-screened organic fraction, breaking up the cell membrane of the organic fraction; crushing the shredded organic fraction in order to separate a liquid part from a first solid part; subjecting to an anaerobic process said liquid part in order to obtain a second solid part and biogas. Brief Description of the Drawings Further characteristics and advantages of the invention will become better apparent from the detailed description of the method and of the apparatus for providing it, illustrated only by way of non-limitative example in the accompanying drawings, wherein:
Figure 1 is a block diagram of the layout of a method according to the invention;
Figure 2 is another more detailed block diagram of an operating step of the method of Figure 1. Way of carrying out the Invention
As shown in Figures 1 and 2, the method comprises a first step 10 for opening bags, since the material arrives loose and contained in bags which must be opened in order to allow the discharge of the organic material.
The material is then subjected to a screening process 11, which consists in cleaning by separating out plastics, various containers, metals, etcetera. The organic material is then shredded, step 12, undergoing comminution and breaking the plant cell walls so as to facilitate the release of the cell sap, and is then crushed, step 13.
During step 13, separation occurs between a liquid-dense part 14 on one side and a woody-fibrous solid part 15, with the remaining impurities, on the other. Advantageously, the steps 12 and 13 are provided by means of various types of apparatus, such as variable-pitch screw feeders, press heads, pressing systems using shock waves produced by explosion or air or gas pressure, accompanied by a series of perforated grids or membranes which allow drainage of the dense liquid 14 and retain the solid fraction or fiber 15 and/or the impurities inside the pressure region.
The resulting liquid part 14 has a light brown color, a density approximately equal to that of oil, a pungent acrid odor, a percentage of total solids on the dry substance of 7-15%, a percentage of volatile solids on the dry substance of 70-75%, a C/N (carbon/nitrogen) ratio of 1/12 ± 2%, a percentage of impurity of less than 0.5% and a pH of 4-5. The steps 10, 11, 12 and 13 sort the organic fraction of municipal solid waste and the like, achieving a degree of cleaning of the material with particle size and uniformity adapted for feeding anaerobic reactors 20, opening a new frontier in the use of this biological process in the field of recovery and reuse.
In order to achieve good fermentation and thus maximize the yield in biogas production, the material to be fermented must in fact be as much as possible dispersed and solubilized in a liquid, so as to increase the efficiency of the breakdown of carbon compounds on the part of methane- generating bacteria.
The steps 10, 11, 12 and 13 provide an extremely fine dispersion of the liquid.
In this manner, foreign matters, such as plastics of any kind, paper, wood, inert materials, metals and other various materials are eliminated. Moreover, the fibrous organic fraction that is scarcely putrescible and therefore useless in the subsequent anaerobic fermentation process is also eliminated from the useful nutrient component, such as carbohydrates (starch, sugars, etcetera), proteins, fats, alcohols, organic acids, etcetera.
The end result is a dense organic liquid 14 which is separate from the remaining fibrous part 15.
The organic liquid 14 is used for a subsequent step which is constituted by an anaerobic process 16 for producing biogas 21, while the fibrous part 15 is sent to the aerobic process 28.
Practical tests have shown that this liquid 14 is excellent for the fermentation yield of the process 16.
The liquid part 14 is thus destined for the anaerobic fermentation process 16, collecting into a discharge region 17 and, by means of a pump 18, into a homogenization tank 19, from which it then enters an anaerobic reactor 20.
Biogas 21 exits from the reactor 20 and can be advantageously utilized to obtain heat 22 and/or electric power 23. In addition to the biogas 21, a spent substance (second solid part), i.e., a substance which can no longer be subjected to a fermentation process, also leaves the reactor 20; sludge 25 and a supernatant liquid part 26, destined for biological conditioning 27, are obtained by means of a belt press 24 which is per se known.
The sludge 25, together with the solid part 15 obtained from the crushing 13 and the shredding 12 of the organic fraction of the waste, is subjected to an aerobic process 28 in order to obtain a compost 29.
In practice, it is a matter of utilizing the fermentation potential of the drainage material of the organic fraction currently obtained from conventional composting methods and which, despite being currently produced in limited quantities, is the cause of considerable problems and of high treatment and/or disposal costs.
In addition to solving the problem of the management of the drainage material, which is currently produced in an incidental and unwanted step in a very small percentage, in practice it is possible to obtain a material which has excellent yields both in quantitative terms and in qualitative terms.
The extraction of the liquids, achieved by breaking up the cell membrane, allows to accelerate and optimize the fermentation process and to select only the part that is useful for anaerobic fermentation, at the same time releasing a residue which is sanitized and is to be used, in the composting process, as organic material with a high nitrogen content (5-6%) in a mixture with the woody-fibrous part in order to obtain a biological organic fertilizer. The system is provided as an alternative to current waste disposal systems, demonstrating that it integrates perfectly in the recovery of biomasses as a renewable and alternative energy source.
The present invention is susceptible of modifications and variations, all of which are within the scope of the inventive concept. The constructive details may be replaced with other technically equivalent means.
The materials and the dimensions may be any according to requirements.
The disclosures in Italian Patent Application No. PD99A000266 from which this application claims priority are incorporated herein by reference.

Claims

1. A method for recycling a organic pre-screened fraction of municipal solid waste and the like derived from separate or sorted collections, characterized in that it comprises the steps of: shredding the pre-screened organic fraction, breaking up the cell membrane of the organic fraction; crushing the shredded organic fraction in order to separate a liquid part from a first solid part; subjecting to an anaerobic process said liquid part in order to obtain a second solid part and biogas.
2. The method according to claim 1, further comprising the step of: separating said second solid part into sludge and a supernatant liquid part by means of a belt press.
3. The method according to claim 2, characterized in that said supernatant is subjected to biological conditioning.
4. The method according to claim 2, comprising the step of: subjecting to an aerobic process said first solid part and/or said sludge in order to obtain a compost.
5. The method according to claim 1, characterized in that said liquid part, before undergoing the anaerobic process, is collected in a homogenization tank.
6. The method according to claim 5, characterized in that said liquid part is collected into a discharge region and, by means of a pump, into said homogenization tank.
7. Use of a liquid part obtained from a process for shredding and crushing a pre-screened organic fraction of municipal solid waste and the like deriving from separate or sorted collections in order to perform an anaerobic process.
PCT/EP2000/011594 1999-11-26 2000-11-21 Method for recycling the organic fraction of municipal solid waste and the like Ceased WO2001038259A2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
AU31547/01A AU3154701A (en) 1999-11-26 2000-11-21 Method for recycling the organic fraction of municipal solid waste and the like

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
IT1999PD000266 IT1306696B1 (en) 1999-11-26 1999-11-26 PROCEDURE FOR THE RECYCLING OF THE ORGANIC FRACTION OF URBAN AND SIMILAR WASTE.
ITPD99A000266 1999-11-26

Publications (2)

Publication Number Publication Date
WO2001038259A2 true WO2001038259A2 (en) 2001-05-31
WO2001038259A3 WO2001038259A3 (en) 2001-11-29

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IT (1) IT1306696B1 (en)
WO (1) WO2001038259A2 (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE10144538A1 (en) * 2001-09-11 2003-03-27 Suko Gmbh Production of compost and methane comprises fermenting a mixture of farmyard slurry, a cellulase-enriched liquid and a fermented material containing cellulose-degrading biological agents
EP1508386A1 (en) * 2003-08-13 2005-02-23 Lassila & Tikanoja Oyj Method for waste treatment
DE102007004892A1 (en) * 2007-01-05 2008-07-10 Reinhart von Dr.-Ing. Nordenskjöld Process and device for the treatment of organic residues from biogas plants
EP2311785A1 (en) * 2009-10-16 2011-04-20 KOMPOFERM GmbH Method for treating waste
WO2012062340A1 (en) * 2010-11-09 2012-05-18 Kompoferm Gmbh Method for treating waste
ITAR20120020A1 (en) * 2012-06-28 2013-12-29 Nuova Agri Cultura Srl Societa Agr Icola PROCEDURE FOR THE PRODUCTION OF BIOGAS AND SYNTHESIS GASES.
CN109622572A (en) * 2019-01-11 2019-04-16 贵州甲克虫环境科技有限责任公司 A kind of technique producing building materials collaboration processing house refuse

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2208645A (en) * 1987-08-13 1989-04-12 Future Fuels Limited Processing waste
DE4120808A1 (en) * 1991-06-24 1993-01-14 Recycling Energie Abfall REPROCESSING OF WASTE FOR ANAEROBIC PLANNING OF ORGANIC BIOGENIC COMPONENTS OF WASTE, ESPECIALLY OF BIOMUELL, WET WASTE, RESIDUAL WASTE AND COMMERCIAL WASTE
DE4427644A1 (en) * 1994-08-04 1996-02-08 Hese Gmbh Maschf Ernst Method and device for the treatment of organic bio residues

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE10144538A1 (en) * 2001-09-11 2003-03-27 Suko Gmbh Production of compost and methane comprises fermenting a mixture of farmyard slurry, a cellulase-enriched liquid and a fermented material containing cellulose-degrading biological agents
EP1508386A1 (en) * 2003-08-13 2005-02-23 Lassila & Tikanoja Oyj Method for waste treatment
DE102007004892A1 (en) * 2007-01-05 2008-07-10 Reinhart von Dr.-Ing. Nordenskjöld Process and device for the treatment of organic residues from biogas plants
EP2311785A1 (en) * 2009-10-16 2011-04-20 KOMPOFERM GmbH Method for treating waste
WO2012062340A1 (en) * 2010-11-09 2012-05-18 Kompoferm Gmbh Method for treating waste
CN102612504A (en) * 2010-11-09 2012-07-25 康波费尔姆有限公司 Method for treating waste
AP2950A (en) * 2010-11-09 2014-07-31 Kompoferm Gmbh Method for treating waste
EA020367B1 (en) * 2010-11-09 2014-10-30 Компоферм Гмбх Method for treating waste
CN102612504B (en) * 2010-11-09 2015-12-16 康波费尔姆有限公司 The method used to dispose of garbage
ITAR20120020A1 (en) * 2012-06-28 2013-12-29 Nuova Agri Cultura Srl Societa Agr Icola PROCEDURE FOR THE PRODUCTION OF BIOGAS AND SYNTHESIS GASES.
CN109622572A (en) * 2019-01-11 2019-04-16 贵州甲克虫环境科技有限责任公司 A kind of technique producing building materials collaboration processing house refuse

Also Published As

Publication number Publication date
WO2001038259A3 (en) 2001-11-29
AU3154701A (en) 2001-06-04
IT1306696B1 (en) 2001-10-02
ITPD990266A1 (en) 2001-05-26

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