EP0227706A1 - Procede de transformation de dechets organiques et mineraux en materiaux solides, inertes et insolubles dans l'eau - Google Patents

Procede de transformation de dechets organiques et mineraux en materiaux solides, inertes et insolubles dans l'eau

Info

Publication number
EP0227706A1
EP0227706A1 EP86903191A EP86903191A EP0227706A1 EP 0227706 A1 EP0227706 A1 EP 0227706A1 EP 86903191 A EP86903191 A EP 86903191A EP 86903191 A EP86903191 A EP 86903191A EP 0227706 A1 EP0227706 A1 EP 0227706A1
Authority
EP
European Patent Office
Prior art keywords
mass
waste
temperature
bodies
quicklime
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
EP86903191A
Other languages
German (de)
English (en)
French (fr)
Inventor
Georges Biez
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.)
LOMA FINANCE Inc
Original Assignee
LOMA FINANCE Inc
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 LOMA FINANCE Inc filed Critical LOMA FINANCE Inc
Publication of EP0227706A1 publication Critical patent/EP0227706A1/fr
Ceased legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/02Agglomerated materials, e.g. artificial aggregates
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/04Waste materials; Refuse
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/04Waste materials; Refuse
    • C04B18/0427Dry materials
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B40/00Processes, in general, for influencing or modifying the properties of mortars, concrete or artificial stone compositions, e.g. their setting or hardening ability
    • C04B40/02Selection of the hardening environment
    • 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
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Definitions

  • the present invention relates to a process for transforming solid waste, comprising at least 30%, by weight, of cellulose materials, into solid materials, inert and insoluble in water.
  • This process can in particular be applied to transform household refuse or industrial waste, consisting of mixtures, of various compositions, of organic and mineral materials, into materials usable in the building industry and civil engineering.
  • the present invention aims to overcome these drawbacks by providing a process for transforming organic and mineral waste into inert materials, usable for example in the building industry and civil engineering, this process comprising operations during which the treated waste undergoes a significant reduction in volume and is transformed into an inert solid product without any risk of release of toxic gas, or other harmful materials, during or after the implementation of the process.
  • the method according to the invention is characterized in that the metallic bodies possibly contained in the waste are eliminated, then the waste is ground and homogenized, so as to form a homogeneous pulverulent mass, the mass in the form of a plurality of solid bodies and, finally, these bodies are subjected, in the presence of quicklime, to a heat treatment comprising an initial heating phase causing sudden heat to the core of the bodies, from a temperature initial temperature less than 100 ° C, up to a temperature at least equal to 250 ° C but lower than the pyrolysis temperature of plastics possibly present in the initial mass of waste.
  • the moisture content of the solid bodies is adjusted to a value of 27 to .30% by weight, before the heat treatment.
  • the moisture content of the solid bodies is adjusted to a value of 27 to .30% by weight, before the heat treatment.
  • the pressure under which the mass is compressed to form the solid bodies is between 150 and 900 bars.
  • the mass is compressed in the form of granules constituted by cylindrical bodies having a diameter between 4 and 20 millimeters and a length between 6 and 30 millimeters.
  • At least one additive is incorporated into the pulverulent mass of waste, at the latest before proceeding to the compression operation of this mass.
  • quicklime powder corresponding, for example, to a proportion of between 0.3 and 10% of the pulverulent mass of waste, in this mass, before carrying out the compression operation. of the latter.
  • the purpose of this incorporation of quicklime is to bring about a rise in the temperature of the mass of waste to an optimal value for the compression process, that is to say, for example, to a temperature of the order of t 80 ° C, as a result of the reaction of quicklime with the water present in the mass of waste.
  • Quicklime can be incorporated into the waste mass alone or as a mixture with a certain quantity of at least one calcium salt, such as carbonate, for example in CaO / CO-Ca weight proportions of between 2: 1 and 1 : 5.
  • the blocks of mass of waste are heated to the core to a temperature between 250 and 300 ° C. and then maintained a certain time at this temperature, this initial heating phase being followed by an intermediate cooling phase during which the temperature gradually decreases, to a value between 60 and 80 ° C, and a final phase of maintenance at a temperature between 60 and 80 ° C.
  • the total duration of the heat treatment is between 20 and 45 minutes.
  • the total duration of the initial heating phase corresponds to approximately one third of the total duration of the heat treatment.
  • the heat treatment is carried out by moving, with a constant speed, the granules, from a first heating zone at temperature between 250 and 300 ° C, to an end heating zone at temperature between 60 and 800 ° C, passing through an intermediate zone in which a temperature gradient prevails corresponding to a gradual variation of the temperature, in the direction of movement of the granules, between the temperature of the first heating zone and that of the end of heating zone, the granules being introduced, at the start of the first zone of heating, simultaneously with quicklime powder or a powder mixture of quicklime and at least one calcium salt, in the divided solid state.
  • the calcium salt is calcium carbonate.
  • the proportion of quicklime, or mixture of quicklime and at least one calcium salt, added to the granules just before subjecting these granules to heat treatment corresponds to 0.3 to 0.5 percent by weight of CaO and 0.3 to 0.5 percent by weight of calcium salt.
  • the heat treatment is carried out by passing the granules through a rotary tunnel oven, the axis of rotation of which is placed in a practically horizontal position, this oven being provided with a internal helical ramp allowing the transport of the blocks at constant speed from one end to the other of the oven.
  • the materials which are liable to be subjected to the process according to the invention can be of very varied origin and composition.
  • it can be household waste as well as industrial waste or residues.
  • the average composition of the treated material is within the following limits (expressed in percentage by weight): cellulosic materials: 5060% starchy materials (such as starch): 6 to 7% plastics (synthetic polymer resins): 6 to
  • the garbage and waste arising from the removal from the collection places are subjected to the usual sorting and sieving operations in order to separate the possibly recoverable and / or recyclable objects as such, in particular the large metal masses.
  • the preparation of the mass of waste in the form of a homogeneous pulverulent mixture practically free of metallic materials, and in particular of iron can be carried out by grinding and mixing, these two operations being able to be carried out simultaneously or separately and combined with one or more operations of sorting intended for the separation of metal pieces and more particularly pieces of iron-based materials.
  • this mass can be subjected to a first, coarse grinding, up to an average size of pieces of about 50 millimeters, this grinding being carried out before or after a magnetic sorting intended for the removal of particles of iron and the like.
  • an additional mineral filler in order to modify the overall composition of the mass, in particular with a view to influencing the composition and the. characteristics of the final product, for example to give it a desired density.
  • the addition of this additional charge can be carried out either before the incorporation of the binder in the mass of crushed waste, ie at the same time as this operation.
  • the mineral additional filler As a constituent of the mineral additional filler, it is possible, for example, to use one or more materials chosen from the following: clacium carbonate, gypsum, plaster, blast furnace fly ash, magnesia, barium sulfate , lithopone, dolomite, clayey materials, powdered coal.
  • the total proportion of materials constituting this additional charge is such that it constitutes from 20 to 40% by weight of the overall amount of the mixture of the mass of waste with this charge.
  • the incorporation of the additive into the mass of crushed waste possibly containing the additional charge is advantageously carried out in a mixing device (for example a vertical mixer) and followed by a stay in another mixing device (for example a horizontal mixer) in which the impregnation of the ground material with the additive is continued, for example for a period of the order of 15 to 20 minutes, so as to obtain a homogeneous mixture of the ground material and the additive in which the latter permeates this material perfectly.
  • a mixing device for example a vertical mixer
  • another mixing device for example a horizontal mixer
  • any material in the pulverulent, liquid or pasty state can be used, which can be incorporated intimately and homogeneously into the ground material by giving it properties, in particular with regard to plasticity and rheological characteristics, allowing the subsequent placing of the mixture in the form of solid bodies capable of keeping their cohesion during the final operation of thermochemical treatment.
  • pulverulent product consisting of a mixture, in weight proportions of between 1: 2 and 2: 1, of a first powder containing
  • a second powder obtained by drying cassava flour swollen by heating, until boiling, in an aqueous medium containing formaldehyde and ammonia for example, using 0.5 to 2 parts of formaldehyde and 0, 5 to 2 parts of ammonia at 40 ° Balm for 10 to 40 parts by weight of cassava flour.
  • the amount of additive can be, for example, between 0.5 and 5%, by weight, relative to the weight of the homogeneous mass of waste.
  • the operation of compressing the mass mixture of waste (possibly containing an additional charge) and additive as well as, if necessary, quicklime or mixture of quicklime and at least one calcium salt can be carried out , in a manner known per se, according to the form which it is desired to give to the material constituting the final product of desired transformation.
  • a granulated material for example in the form of small cylinders having a length of 6 to 30 millimeters and a diameter of 4 to 20 millimeters, an industrial type granulating apparatus is used, allowing '' granulate under a pressure of 150 to 900 bar.
  • the proportion of quicklime or mixture of quicklime and calcium carbonate relative to the solid bodies subjected to the heat treatment is preferably from 0.3 to 0.5%, by weight, of CaO and from 0.3 to 0 , 5%, by weight, of calcium carbonate.
  • the total heating time is between 20 and 45 minutes, the duration of the first heating phase preferably corresponding to one third of the total heating time.
  • the solid bodies to be treated performs the heat treatment by moving, with a constant speed, the solid bodies to be treated from a first heating zone, at a temperature between 250 and 300 ° C, to an end of heating zone at a temperature between 60 and 80 ° C, passing through an intermediate heating zone • in which there is a temperature gradient corresponding to a progressive variation of the temperature, in the direction of movement of the solid bodies between the temperature of the first heating zone and that from the end of heating zone, the solid bodies subjected to the heat treatment being introduced at the same time as quicklime or the mixture of quicklime and calcium salt at the start of the first heating zone, for example by sprinkling the bodies solids by quicklime powder or the powdery mixture of quicklime and calcium salt just before the bodies are introduced into the first heating zone.
  • a tubular rotary oven having an axis placed in a practically horizontal position is used to carry out the heat treatment, the material subjected to the heat treatment being introduced at the end of this oven corresponding to the first heating zone, and the material having undergone the heat treatment leaving the oven in the vicinity of its opposite end.
  • the final product is in the form of inert and insoluble blocks, for example cylindrical granules, composed almost exclusively of mineral matter and having a structure similar to that of limestone rocks. This product is capable of numerous uses, in particular as building elements, coating or filling in the building and civil engineering industries.
  • the garbage passes through a sieve trommel which makes it possible to select the pieces having a maximum size of 6 centimeters, the refusal being directed again towards the primary receiving pit.
  • the garbage thus selected is directed on a conveyor belt associated with a magnetic deferiser and a magnetic pulley placed at the head of this conveyor in order to allow to remove all the particles of ferro-magnetic materials which may have remained in the garbage originating from the primary grinding.
  • the refuse thus treated then falls into a secondary shredder, making it possible to reduce it to particles having an average size of 2 to 30 millimeters.
  • the mass of ground garbage is then directed into a ribbon mixer where a binder prepared by mixing 1Q parts by weight of flour is incorporated.
  • a homogeneous pulverulent mixture is thus obtained which is introduced into a rotary granulator in which cylindrical granules are formed, having a diameter of 5 millimeters and a length of 15 millimeters, by compression of the mixture under a pressure of 600 bars.
  • the granules thus obtained contain approximately 30% by weight of moisture.
  • These granules are introduced continuously, as well as a mixture of quicklime and calcium carbonate in an amount corresponding to 0.35% of finely pulverized quicklime (average particle size: 60 to 100 microns) and 0.35% of powdered technical calcium carbonate (average size 80 to 150 microns), containing at least 20% by weight of calcium, at the entrance of a tubular rotary kiln with a diameter of 1 meter and a length of 9 meters and a rotational speed adjusted so that the passage time of the material treated in the oven is of the order of 40 minutes.
  • the tube furnace is heated by means of a gas burner arranged at its end through which the granules and the mixture of quicklime and calcium carbonate are introduced.
  • the granules are gradually entrained in the furnace, by means of a helical screw placed inside thereof, and exit at the end opposite to that by which they are introduced, the total duration of residence of the granules in the oven being 40 minutes.
  • the granules pass successively in a first heating zone in which they stay for 15 minutes at a temperature between 280 ° C and 260 ° C, then for 15 minutes in an area where .
  • . fundamental temperature decreases approximately linearly between 260 and 80 ° C and finally for 10 minutes in a final heating zone where they are maintained between 80 ° C and 60 ° C.
  • Example 2 The procedure is as in Example 1, but incorporating into the ground rubbish mass, at the same time as the binder, an amount of construction plaster waste such as the ratio of the amount of plaster to the total amount of 'garbage and additional charge constituted by this plaster is equal to 30% by weight.

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Ceramic Engineering (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Structural Engineering (AREA)
  • Civil Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Processing Of Solid Wastes (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Curing Cements, Concrete, And Artificial Stone (AREA)
EP86903191A 1985-06-19 1986-06-11 Procede de transformation de dechets organiques et mineraux en materiaux solides, inertes et insolubles dans l'eau Ceased EP0227706A1 (fr)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CH2601/85A CH665785A5 (fr) 1985-06-19 1985-06-19 Procede de transformation de dechets organiques et mineraux en materiaux solides, inertes et insolubles dans l'eau.
CH2601/85 1985-06-19

Publications (1)

Publication Number Publication Date
EP0227706A1 true EP0227706A1 (fr) 1987-07-08

Family

ID=4237429

Family Applications (1)

Application Number Title Priority Date Filing Date
EP86903191A Ceased EP0227706A1 (fr) 1985-06-19 1986-06-11 Procede de transformation de dechets organiques et mineraux en materiaux solides, inertes et insolubles dans l'eau

Country Status (29)

Country Link
EP (1) EP0227706A1 (da)
JP (1) JPS63500237A (da)
KR (1) KR870700581A (da)
CN (1) CN1004336B (da)
AR (1) AR244115A1 (da)
AU (1) AU583635B2 (da)
BE (1) BE904902A (da)
BR (1) BR8606734A (da)
CH (1) CH665785A5 (da)
DE (1) DE3690328T1 (da)
DK (1) DK81487A (da)
ES (2) ES8700644A1 (da)
FI (1) FI870637A (da)
FR (1) FR2583742A1 (da)
GB (1) GB2187183B (da)
GR (1) GR861553B (da)
HU (1) HUT47875A (da)
IL (1) IL79102A0 (da)
IT (1) IT1190587B (da)
JO (1) JO1488B1 (da)
NL (1) NL8620210A (da)
NZ (1) NZ216586A (da)
OA (1) OA08676A (da)
PT (1) PT82773B (da)
SE (1) SE459236B (da)
TN (1) TNSN86092A1 (da)
WO (1) WO1986007589A1 (da)
YU (1) YU100686A (da)
ZA (1) ZA864479B (da)

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE1166601B (de) * 1958-06-10 1964-03-26 Oil Seed Products Inc Verfahren zur Herstellung eines Futtermittels durch Entgiften der Extraktionsrueckstaende von Senf- oder Rapssaat
CH672309A5 (da) * 1987-03-19 1989-11-15 Catrel Sa
AT388315B (de) * 1987-06-05 1989-06-12 Simmering Entsorgungsbetriebe Verfahren und einrichtung zur herstellung wasserunloeslicher granulate, formkoerper od.dgl.
CH673454A5 (da) * 1987-11-02 1990-03-15 Catrel Sa
EP0427899A1 (fr) * 1989-11-16 1991-05-22 Société GOMACRIS S.A. Procédé de valorisation de déchets solides notamment d'ordures ménagères et dispositif pour sa mise en oeuvre
GB9208479D0 (en) * 1992-04-16 1992-06-03 Cpis Limited Method of making refuse-derived fuel and fuel made by the method
EP0602293B1 (fr) * 1992-12-07 1997-07-02 de Blangy, Gérard Procédé et dispositif de traitement et de valorisation de déchets transformant ceux-ci en matériaux non polluants et réutilisables
AU667659B3 (en) * 1995-06-19 1996-03-28 Petemic Technology Pty Ltd A waste recycling process and apparatus
KR100940345B1 (ko) * 2007-12-20 2010-02-04 최용규 섬유 분말을 이용한 섬유 겔의 제조방법, 이의 활용방법 및제조된 종이

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2286116A1 (fr) * 1974-09-26 1976-04-23 Ponnier Andre Procede pour fabrication, a partir d'ordures menageres, d'agregats destines a substituer les graviers naturels
FR2409242A1 (fr) * 1977-11-22 1979-06-15 Ponnier Andre Procede de fabrication destine a la fabrication de panneaux, de cloisons ou de granulats
FR2472421A1 (fr) * 1979-03-13 1981-07-03 Geronimo Hilaire Procede de transformation des ordures menageres en graviers artificiels
US4333909A (en) * 1980-05-09 1982-06-08 Foster Wheeler Energy Corporation Fluidized bed boiler utilizing precalcination of acceptors
DE3226798C2 (de) * 1982-07-17 1994-02-03 Willibald Juergens Verfahren zum Beseitigen und Verwerten von Abfallstoffen
DE3226851A1 (de) * 1982-07-17 1984-01-19 Skw Trostberg Ag, 8223 Trostberg Verfahren zur herstellung von reinem branntkalk

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See references of WO8607589A1 *

Also Published As

Publication number Publication date
TNSN86092A1 (fr) 1990-01-01
NZ216586A (en) 1989-05-29
SE8700625D0 (sv) 1987-02-16
HUT47875A (en) 1989-04-28
IT1190587B (it) 1988-02-16
IT8667480A0 (it) 1986-06-11
GR861553B (en) 1986-09-05
OA08676A (fr) 1989-03-31
FI870637A0 (fi) 1987-02-16
AR244115A1 (es) 1993-10-29
CH665785A5 (fr) 1988-06-15
AU5953786A (en) 1987-01-13
DK81487D0 (da) 1987-02-18
DK81487A (da) 1987-02-18
WO1986007589A1 (fr) 1986-12-31
GB8702398D0 (en) 1987-03-11
FR2583742A1 (fr) 1986-12-26
FI870637A (fi) 1987-02-16
BR8606734A (pt) 1987-08-11
ES555969A0 (es) 1987-02-16
BE904902A (fr) 1986-10-01
NL8620210A (nl) 1987-05-04
SE459236B (sv) 1989-06-19
JPS63500237A (ja) 1988-01-28
ES8703132A1 (es) 1987-02-16
GB2187183A (en) 1987-09-03
ES8700644A1 (es) 1986-11-16
CN86104053A (zh) 1986-12-17
GB2187183B (en) 1989-02-22
KR870700581A (ko) 1987-12-30
DE3690328T1 (da) 1987-08-27
SE8700625L (sv) 1987-02-16
CN1004336B (zh) 1989-05-31
JO1488B1 (en) 1988-03-10
ES551578A0 (es) 1986-11-16
YU100686A (en) 1988-06-30
PT82773A (en) 1986-07-01
PT82773B (en) 1987-10-13
AU583635B2 (en) 1989-05-04
IL79102A0 (en) 1986-09-30
ZA864479B (en) 1988-02-24
IT8667480A1 (it) 1987-12-11

Similar Documents

Publication Publication Date Title
CH672309A5 (da)
BE1003543A4 (fr) Procede de fabrication de ciment.
JPH01254285A (ja) ごみ焼却灰固形物及びその製造方法
US6758893B2 (en) Granular pigments useful to color concrete
US20100116181A1 (en) Method of making cellulose/plastic pellets having a low plastic content
EP0227706A1 (fr) Procede de transformation de dechets organiques et mineraux en materiaux solides, inertes et insolubles dans l'eau
CH673454A5 (da)
EP1571135B1 (fr) Procédé de fabrication d'éléments de construction incorporant des boues d'épuration
CH667603A5 (fr) Procede de transformation de dechets organiques et mineraux en materiaux solides, inertes et insolubles dans l'eau.
JP2003261878A (ja) 炭化物の製造方法
CN112795415A (zh) 配制物和方法
JP2008126185A (ja) 焼成物およびその製造方法
Borowski An overview of particle agglomeration techniques to waste utilization
CN112795416A (zh) 用于形成燃料粒料的方法
CH685557A5 (fr) Procédé de fabrication de ciment.
JPS5837269B2 (ja) 無機物の成形方法
EP1462507A1 (fr) Procédé pour la fabrication d'agglomérés et agglomérés combustibles
WO2023242731A1 (en) Agglomerated product for use in the steelmaking process
RU1786151C (ru) Способ получени брикетов из промышленных дисперсных материалов
NO870628L (no) Fremgangsmaate for aa omvandle organisk og mineralsk avfall til faste, inerte og vannopploeselige materialer.
JPH01122944A (ja) 人工軽量骨材製造における焼成用成形物
Graytee et al. Pilot study on the development of synthetic lightweight aggregates
FR2752387A1 (fr) Procede de stabilisation-solidification des residus d'incineration des dechets urbains ou industriels et installation pour sa mise en oeuvre
DD247891A5 (de) Verfahren zur Umwandlung feste Abfälle

Legal Events

Date Code Title Description
PUAI Public reference made under article 153(3) epc to a published international application that has entered the european phase

Free format text: ORIGINAL CODE: 0009012

17P Request for examination filed

Effective date: 19870309

AK Designated contracting states

Kind code of ref document: A1

Designated state(s): AT BE DE NL SE

TCAT At: translation of patent claims filed
DET De: translation of patent claims
TCNL Nl: translation of patent claims filed
17Q First examination report despatched

Effective date: 19881012

STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: THE APPLICATION HAS BEEN REFUSED

18R Application refused

Effective date: 19900209

RIN1 Information on inventor provided before grant (corrected)

Inventor name: BIEZ, GEORGES