EP1401789A2 - Verfahren zur behandlung von abfällen, vorrichtungen und zusammensetzung zur durchführung des verfahrens - Google Patents

Verfahren zur behandlung von abfällen, vorrichtungen und zusammensetzung zur durchführung des verfahrens

Info

Publication number
EP1401789A2
EP1401789A2 EP02762532A EP02762532A EP1401789A2 EP 1401789 A2 EP1401789 A2 EP 1401789A2 EP 02762532 A EP02762532 A EP 02762532A EP 02762532 A EP02762532 A EP 02762532A EP 1401789 A2 EP1401789 A2 EP 1401789A2
Authority
EP
European Patent Office
Prior art keywords
waste
container
products
mass
fermentable
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.)
Withdrawn
Application number
EP02762532A
Other languages
English (en)
French (fr)
Inventor
Philippe Brisset
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.)
NEMEAU
Original Assignee
Naturem Environnement SAS
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
Priority claimed from FR0108851A external-priority patent/FR2826885B1/fr
Priority claimed from FR0108850A external-priority patent/FR2826884B1/fr
Application filed by Naturem Environnement SAS filed Critical Naturem Environnement SAS
Publication of EP1401789A2 publication Critical patent/EP1401789A2/de
Withdrawn legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/90Apparatus therefor
    • C05F17/964Constructional parts, e.g. floors, covers or doors
    • C05F17/971Constructional parts, e.g. floors, covers or doors for feeding or discharging materials to be treated; for feeding or discharging other material
    • C05F17/979Constructional parts, e.g. floors, covers or doors for feeding or discharging materials to be treated; for feeding or discharging other material the other material being gaseous
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/20Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/50Treatments combining two or more different biological or biochemical treatments, e.g. anaerobic and aerobic treatment or vermicomposting and aerobic treatment
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/145Feedstock the feedstock being materials of biological origin
    • 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

  • incineration is the simplest and best known solution. Given the heterogeneity of the products treated, it causes significant pollution risks for the environment, which motivates the realization of increasingly complex and consequently more and more expensive installations. Composting is another aerobic solution which treats fermentable organic matter, but which comes up against the reality of excessively long residence times, incompatible with the treatment of large tonnages.
  • An object of the invention is to provide a waste treatment process, an apparatus and compositions for implementing the process, making it possible to obtain a stable product in a very short time, and at a reasonable cost.
  • the use of a closed container to contain the waste during the biological degradation step makes it possible to accelerate the heating of the waste and the release of water vapor, and makes it possible to collect both the gaseous emanations emitted by the waste, as well as the pore water produced by the degradation of the fermentable organic matter from the water structurally included in the fermentable organic matter; the partial nature of the degradation makes it possible to keep chains of relatively large organic materials which are useful in particular for enriching cultivated land.
  • FIG. 1 is a functional diagram of an installation allowing the implementation of the method.
  • This phase continues with a step of introducing the waste by a conveyor 1 into a tank 2.
  • the tank 2 is closed to thermally isolate the waste from the ambient environment.
  • the height of storage of the waste in the tank is preferably at least two meters to promote heating of the products.
  • the first additive, additive A is composed of iron Fe chips, magnetite Fe 2 O 3 and Fe 3 O 4 , potassium phosphate K 3 PO 4 , potassium iodide Kl, sodium iodide Nal, citronellol, citronellal or lemon essence C10H10O and cobalamin, retinol, ascorbic acid, and tocopherol. Each component can be incorporated in variable proportions from 0% to 100% of the additive.
  • This first additive is a nutrient. It plays a fundamental role in boosting aerobic degradation reactions at much faster speeds than in the natural cycle, actively participating in the absorption of odorous molecules, thus regulating the olfactory nuisances that may be encountered on waste treatment and transformation sites. .
  • the nutrients used are phosphorus, potassium, cobalamin, retinol, ascorbic acid and tocopherol.
  • the nutrients cause the optimum biological conditions for a rapid natural rise in temperature.
  • Catalysts help living cells, microorganisms, to carry out their biological metabolism by consuming thanks to the oxygen supply from aeration forced, fermentable organic matter from waste; iodine can be added to promote heating of the waste due to its radioactivity.
  • additive B occurs after the forced ventilation catalyzed by additive A, it
  • This waste included 6 T of organic matter (comprising 40% of dry matter and 60% of water), 1 T of plastics (surrounded by 0.15 T of water included in the weight), 1.5 T of metals, leather and textiles (surrounded by 0.25 T of water included in the weight), 0.5 T of rubble (surrounded by 0.1 T of water included in the weight); organic matter included various biodegradable elements, including peelings, paper, cardboard and wood.
  • the gases emitted were carbon dioxide, oxygen and nitrogen.
  • the product obtained after 10 hours of biological treatment consisted of:
  • the total therefore weighed 5.3 T with 0.4 T of water or 7% humidity.
  • the process gases have been recovered. They consisted of ammonia and water vapor. Recovered, this condensation water represents 4.1 m3.
  • the method according to the invention makes it possible to obtain a stable product (in contact with air), after a very short treatment time (a few hours in particular as regards biological treatment).
  • This process only performs partial degradation of organic matter; this degradation occurs at the periphery of the pieces of organic material (peels, paper, cardboard), but also that which is between the pieces of products. It is this part of organic matter which is acidified.
  • the COOH radical loses its H +.
  • the long chains of organic matter are cut at the C-C bonds producing smaller molecules. These reactions take place at the level of the cytoplasm of microorganisms and outside the cell.
  • the rise in temperature beyond 65 ° C makes it possible to destroy or at least block the functioning of mesophilic and thermophilic microorganisms.
  • the first treatment phase produces pore water from structural water. This water improves the yield of the chemical reaction of the second phase.
  • the mineralization of the surface part of the organic matter also makes it possible to physically separate the water from the solid matter, so that the separation of the water by blower is facilitated: the ventilation makes it possible to dry the waste considerably, which is then easier to sort.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Molecular Biology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Biotechnology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Microbiology (AREA)
  • Biochemistry (AREA)
  • Organic Chemistry (AREA)
  • Tropical Medicine & Parasitology (AREA)
  • Processing Of Solid Wastes (AREA)
EP02762532A 2001-07-04 2002-07-04 Verfahren zur behandlung von abfällen, vorrichtungen und zusammensetzung zur durchführung des verfahrens Withdrawn EP1401789A2 (de)

Applications Claiming Priority (5)

Application Number Priority Date Filing Date Title
FR0108851 2001-07-04
FR0108850 2001-07-04
FR0108851A FR2826885B1 (fr) 2001-07-04 2001-07-04 Complexe d'additifs pour la transformation de dechets heterogenes solides ou pateux produits par les populations ou par l'industrie
FR0108850A FR2826884B1 (fr) 2001-07-04 2001-07-04 Procede de traitement des dechets menagers ou industriels et installations d'application de ce procede
PCT/FR2002/002351 WO2003004442A2 (fr) 2001-07-04 2002-07-04 Procéde de traitement de déchets, appareils et compositions pour la mise en oeuvre du procédé

Publications (1)

Publication Number Publication Date
EP1401789A2 true EP1401789A2 (de) 2004-03-31

Family

ID=26213081

Family Applications (1)

Application Number Title Priority Date Filing Date
EP02762532A Withdrawn EP1401789A2 (de) 2001-07-04 2002-07-04 Verfahren zur behandlung von abfällen, vorrichtungen und zusammensetzung zur durchführung des verfahrens

Country Status (3)

Country Link
EP (1) EP1401789A2 (de)
AU (1) AU2002328381A1 (de)
WO (1) WO2003004442A2 (de)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2445560B (en) * 2007-01-09 2008-12-31 Inst Of Food Res Method and kit for producing a plant growth medium
ITCZ20080002A1 (it) * 2008-02-14 2009-08-15 Antonio Alfano Processo chimico-fisico per la produzione di fertilizzanti da rifiuti organici e relativo impianto

Family Cites Families (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB495873A (en) * 1937-04-19 1938-11-21 Wellesley Holdings Ltd Improvements relating to the production of organic fertilisers
FR1375668A (fr) * 1962-01-22 1964-10-23 Terres De Chalautre Soc D Procédé pour la fermentation rapide des gadoues et ordures ménagères
AU428978B2 (en) * 1971-08-23 1972-10-06 S. F. R. I. R. (Societe Francaise D'incineration D Residue A process for transforming household garba and like waste by fermentation
JPS5585490A (en) * 1978-12-23 1980-06-27 Kenji Ishihara Compost producing aid compost manufacture using it
FR2546161A1 (fr) * 1983-05-18 1984-11-23 Parpeix Alain Engrais organiques et dispositif de fabrication
DE3637393A1 (de) * 1986-02-19 1987-08-20 Hermann Hofmann Verfahren und vorrichtung zur abfallkompostierung
DE3631170A1 (de) * 1986-07-25 1988-01-28 Mannesmann Ag Verfahren und vorrichtung zur fermentierung von rueckstaenden mit hohem anteil an organischen bestandteilen
ATE178303T1 (de) * 1990-05-09 1999-04-15 Herhof Umwelttechnik Gmbh Verfahren zur kompostierung von abfällen
AT395709B (de) * 1990-11-16 1993-02-25 Voest Alpine Montage Verfahren zum kontrollierten und gesteuerten aeroben biologischen abbau von aminoverbindungen enthaltenden organischen abfaellen
JPH05185062A (ja) * 1992-01-13 1993-07-27 Plando Kenkyusho:Kk 廃棄物による固形物の製造方法
NL9300611A (nl) * 1993-04-07 1994-11-01 Gemac B V Werkwijze voor het bestrijden van hinder van organisch afval.
EP0817763A4 (de) * 1995-03-13 2000-05-31 Jerry W Finney Verminderung der biomasse und verfahren der biologischen entsorgung und produkte
DE19804949A1 (de) * 1998-02-07 1999-08-12 Lurgi Entsorgungstechnik Gmbh Verfahren und Vorrichtung zur Trocknung von organischen Abfällen
AT408985B (de) * 1998-04-07 2002-04-25 Mut Maschinen Umwelttechnik Rotteanlage

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See references of WO03004442A2 *

Also Published As

Publication number Publication date
WO2003004442A2 (fr) 2003-01-16
AU2002328381A1 (en) 2003-01-21
WO2003004442A3 (fr) 2003-11-06

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