CA2045406A1 - Process for the valorization of solid wastes, in particular household refuse, and device for its implementation - Google Patents
Process for the valorization of solid wastes, in particular household refuse, and device for its implementationInfo
- Publication number
- CA2045406A1 CA2045406A1 CA 2045406 CA2045406A CA2045406A1 CA 2045406 A1 CA2045406 A1 CA 2045406A1 CA 2045406 CA2045406 CA 2045406 CA 2045406 A CA2045406 A CA 2045406A CA 2045406 A1 CA2045406 A1 CA 2045406A1
- Authority
- CA
- Canada
- Prior art keywords
- reactor
- wastes
- mixture
- mass
- process according
- 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.)
- Abandoned
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B18/00—Use 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
- C04B18/04—Waste materials; Refuse
- C04B18/06—Combustion residues, e.g. purification products of smoke, fumes or exhaust gases
- C04B18/10—Burned or pyrolised refuse
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/20—Agglomeration, binding or encapsulation of solid waste
- B09B3/25—Agglomeration, binding or encapsulation of solid waste using mineral binders or matrix
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/20—Agglomeration, binding or encapsulation of solid waste
- B09B3/25—Agglomeration, binding or encapsulation of solid waste using mineral binders or matrix
- B09B3/27—Binding by sodium silicate, e.g. cement or water glass
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/006—General arrangement of incineration plant, e.g. flow sheets
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/60—Separating
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/70—Blending
- F23G2201/701—Blending with additives
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/80—Shredding
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2202/00—Combustion
- F23G2202/10—Combustion in two or more stages
- F23G2202/102—Combustion in two or more stages with supplementary heating
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2203/00—Furnace arrangements
- F23G2203/80—Furnaces with other means for moving the waste through the combustion zone
- F23G2203/801—Furnaces with other means for moving the waste through the combustion zone using conveyors
- F23G2203/8013—Screw conveyors
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Ceramic Engineering (AREA)
- Materials Engineering (AREA)
- Civil Engineering (AREA)
- Combustion & Propulsion (AREA)
- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Processing Of Solid Wastes (AREA)
- Paper (AREA)
Abstract
ABSTRACT The present invention relates to a process for the valorization of solid wastes, comprising at least 30% by weight of cellulosic materials, in particular household refuse; the said process including the preliminary steps of grinding and sorting the said wastes in order to remove metallic elements from them. The said process consists of thermally treating - in a tubular reactor (13) equipped with an Archimedean screw (24) and heated by the injection of hot combustion gases at its entrance, the said reactor being maintained under a slight partial vacuum - a mixture of a homogeneous mass containing the said shredded wastes and mineral products, the said mixture containing in particular quick lime, calcium carbonate, and caustic soda; the said thermal treatment and the introduction of the said minerals ensuring a rise in temperature of the said mixture in the first part of the reactor sufficient to produce an intense luminous radiation. The invention also relates to a device for the implementation of the said process. Fig. 2
Description
2 ~
Process for the valorization of solid wastes, in particular household reuse, and devlce for its implementation.
me present mvention relates to a process for the valorization of solid waste3, comprising at least 30% by weight of cellulosic materials.
The invention also rela~es to a device for the implemeneatlon of the sald process.
At present, two main sy~tems are known for the treatment of such wastes. They may be stored in so-called controlled dumps, even deposited unofficially at rural s~tes. They may also be incinerated.
Neither of these systems permits an actual valorization of these wastes and both cause pollution. The pyrolysis of these wastes, which contain chlorinated or fluorinsted p}astic materials, 8enerate toxlc gases, such as chlorine and dioxine... Their ~ccumulation, without treatment, also leads, in time, to the generation of biogases (especially methsn~) which are dangerous as result of the~r odour and/or their fire hazard.
Furthermore, the minerali~ation of these wastes in the soll leads to the appearance of dsngerous c~verns.
It is an ob~ect of the present invention to obviate or mitigate at least one disadvantage of prior processes for treating solid wastes.
According to the invention, a process i9 proposed for the disposal of the said wastes without creating p~llution, the said process leadlng to the development of a useful material.
The said process is advsntageously implemented for the valorization of household refuse. Generally speaking, it may be implemented for ~ny type of waqte, household, industrial, agricultural.. , containing 8 minimal amount of cellulose.
This process enable the harmul effects and pollution csused by the said wastes to be ellmiDated by 8enerating an inert material.
This material - a fine or medium type of sand - may be u~ed in p~rticular in construction, f~r sanding roads, as a filler... It is safe and bacterial development is not observed within it even after a lapse of time.
The proces~ of ~he invention is implemented, as indlcated above, with solid wastes, comprising at least 3~% by weight o cellulosic materials. It l~cludes the preliminary steps of grinding 2 ~ ~ 3 ~
the said wastes and then of sorting the latter in order to remove metallic elements from them. It consists of thermally tr~ating - in a tubular reactor fitted with a Archimedean screw and heated by injection of hot combustion gases at its inle~, the said reactor being maintained under a slight partial vacuum - a mixture of a homogeneous mass cont~ining the said shredded wastes and mineral products, the said mixture containing in particular quick lime, calcium carbonate, and caustic soda; the said thermal ~reatment and the introduction o the said minerals ensuring a rise in temperature of the said mixture in the first part of the reactor sufficient to produce an intense luminous radiation.
According to the invention, the wastes are thus subjected to a specific thermal treatment which generates a radiant reaction.
The said wastes were first ground and freed of the metallic elements which they contained. They are used shredded in the form of a homogeneous mass in a mixture with mineral products. They are shreddded in order to bè available in the form of Eine particles from whlch a homogeneous mass is easily produced.
The said wastes contain at least 30% by weight of ce}lulosic materials. As indicated above, they are advantageously household refuse which usually contains about 60% by weight of cellulosic materials, 3% of plastic materials, 7% of metallic products, 4% of glass and 20%
of various materials...
The wastes are thermally treated according to the invention in a mixture wlth minerals, and in particular quick lime, calcium carbonate and caustic soda. These minerals are intended to react exothermically during the process. Advantageously, they are selected SO a9 to develop a maximal activity within the mass while being used in reasonable quantities. Hence, a very reactive quick lime is advantageously selected. As for the calcium carbonate, natural calcium carbonates are advantageously used, for economic reasons, said calcium carbonates bein~, if necessarv, enriched with calcium by addition of calcium chloride,...
The mixture - homogeneous mass containing the shredded wastes and minerals - is heated directly at the entrance of the reactor by the injection into it of hot combustion gases. Such hot gases may result, for example, from the combustion o~ gas or fuel oil.
The reactor used is a reactor equipped with an Archimedean screw or endless screw. Such a screw enables the mass of the reactants to be conveyed to the interior of the reactor and ensures that they undergo a certain de~ree of mixing.
The reactor is maintained under a slight partial vacuum for the evacuation of the gases. In fact, steam is principally drawn off.
In the type of reactor described above, it has been shown according to the lnvention that it is possible to fossllize wastes containing at least 30% of cellulosic materials without generating pollutants. This accelerated fossilization probably takes place at the moment when the intense luminous emission appears in the reactor.
It i9 the result of the sction of heat ~ in fact, a thermal shock, since hot 8ases are in~ected directly at the entrance of the reactor - on a mixture containing certain reactant~.
The process of the invention only leads to the expected result - elimination of pollutants and production of an inert product (in the form of brittle fragments) - if the said luminous emission or "aura"
is observed in the reactor.
The composition of the mixture to be introduced into the said reactor and the temperature to which it is appropriate to heat the said mixture on its entry into the said reactor are parameters to be specified for the purpose of producing the said "aura".
Their determination and optimization are operations wlthin the capacity of the person skilled in the art.
The homogeneous mass containing the shredded wastes is advantageously produced by mixing the said wastes upstream from the reactor with calcium carbonate and, preferably, natural calcium carbonates in which calcium chloride has optlonally been incorporated.
The mixing only occurs satisfactorily if the wastes have a certain degree of humidity and this is usually the case. The degree of humidity must not, however9 adversely effect the subsequent resction. It is advantageously comprised between 20 and 40%. In order to exhibit such a de8ree of humidity, the wastes may be dried ~par~ially) beforehand - if necessary - or, on the other hand moistened. 30 - 40~ by weight of natural calclum carbonates are incorporated into ~he said wastes exhibiting such 8 degree of humidity. As indicated abo~e, this mass of calcium carbonates may be first enrlched in calcium by the addition of calcium chloride to it.
To the said homogeneous mass - shredded wastes + calcium carbonates - other minerals and,in particular, as specified above, quick lime and caustic soda are added according to the invention in order to produce the desired result under the effect of heat.
It is also advantageous to add carbonated silicates (Na2Ca2Mg4H4SiO~(C03)3 type).
The introduction of these minerals - quick lime, calcium carbonate (in particular natural calcium carbonates optionally enriched in calcium chloride), caustic soda, and advantageously carbonated silicates - enable the deslred result to be obtained : the appearance of an "aura" by direct heatin~ of the mixture and the production of an inert mas3 in the form of brittle fragments.
The said minerals, other than calciwn carbonate (optionally containing calcium chloride) are introduced for the purposes of the invention (for the generation of the "aura'~in a proportion o about 5 to 35% by weight of the said homogeneous mass. The minimal quantity used obviously depends on the constitution of the said homogeneous mass and in particular on the conten~ of cellulosic matter present Z5 in the wastes to be treated. They are advantageously used in approximately equivalent amounts (l/39 1/3, 1/3):
- quick lime between 10 and 45%
- caustic soda between 5 and 35%
- silicate carbonates between 10 and 45% by weight of the ternary mixture (quick lime ~ caustic soda + silicate carbonates~.
The reactive mass thus constituted - homogeneous mass +
minerals - is subiected to a thermal shock on entering the reactor by the injection into it of hot gases.
The "aura" necessary for fossilization is observed according to the inYention when the said reactive mass is at a temperature of 250 to 300C. This temperature may be obtained within the mass according to the invention by the injection of gases combusted at 500-600C.
It has previously been pointed out that on being discharged from the reactor the mass exists in the form of brittle fragments.
These recovered fragments are advantageously pulverized. A sand ls thus obtained with a density of the order of 0.3 ~o 0.5. Such a sand cannot easily be used and fillers are advantageously introduced into the process of the invention in order to increase its density. These fillers may be introduced at at leas~ two stages of the process of the invention. They may be incorporated in~o the sand resulting from passage of the solids discharged from the reactor into a disintegrator and/or incorporated during the manufacture of the homogeneous mass - shredded wastes ~ calcium carbonate - before its introduction into the reactor.
Downstream from the reactor any type of filler may be used.
Upstream from it, only neutral fillers may be used. By neutral fillers are meant, in the present context, fillers compatible with the thermal reaction (heating ~ "aura"). Such neutral fillers may be selected Erom calcium carbonate, carbonate of lime,'powered bary~a, the carbonat~d sllicates, powdered clay, powdered sugary-grained gypsum, powdered bauxite,.., or their mixtures. Hence it should be noted that calcium carbonate and the carbonated silicates may be used in the process of the invention in greater amounts than those already mentioned above.
By way of illustration, it should be made clear that the calcium carbonate, carbonate of lime mixture may thus represent up to 50% by weight of the said homogeneous mass (calcium carbonate is thus employed both as reactant and a9 neutral filler).
The baryta (with its sediment) may be used in a proportion of 0 to 30% by weight; cla~ in a proportion of 0 to 15%, gypsum in a proportion of 0 to 20% and bauxite in a proportion of 0 to 20%. The carbonated silicates taken as a whole may be employed up to a maximum of 30% by weight of the total mass at the entrance of the reactor.
The said fillers make it possible to produce a sand of deflned density.
If it is desired to adjust its granulometry - more precisely to increase it - a further step is added to the process of the invention.
The mass issuing from the reactor, after being pulverized and optionally having neutral fillers incorporat:ed within it, is available in ~he form of a Yery fine, even impalpable, powder.
Such a powder ls advantageously condit:ioned with pelletizing binders in order to increase its granulometry for the production, in particular, of a medium sand, which can be used in construction.
The binder is advantageously mixed with the powder in a vertical pelletizer of the Flexomix type; the mixture is then dried, which leads to the crystallization of the said binder.
The said binder must be selected 90 as to comply w-lth the inert, stable character of the product obtsined by the process of the invention. It must not introduce bacteria. It is possible to use in particular sodiu~ silicate which will react with the calcium present ln the grains of the product.
It i8 also possible to use a binder based on quick lime, cement slurrles, blast-furnace slags and carboxymethyl cellulose (or equivalent). Another binder whlch can be used i9 a binder based on water-soluble pitch.
This step involving the treatment of a powdery material in order to increase its granulometry i9 perfectly well-known to the person skilled in the art.
In this way, waste products are valorized according to the invention without causlng pollution in as much as it did not appear necessary to heat the reactive mass in the reactor to a temperature hi8her than 300C (pyrolysis of plastic materials). The combustion gases, introduced at the entrance of the reactor to heat the said reactive masq directly, seem either to be trapped in the said mass or to decompose in particular at the time when the said "aura" iq produced.
Another object of the inventlon is a device for the implementation of the procedure as explained above.
The said device comprises es~entially:
- a tubular reactor equipped with an Archimedean screw, ,:
2 ~ o ~
- a combustion chamber with its outlet a~ the entrance to the said reactor for the direot supply of calories, - means for feeding the said reactor, - mea~s for main~aining a slight partial vacuum in the said reactor.
The reactor i8 fed at one end with the reac~ive mass -homogeneous mass containing the shredded waste products and, optionally, neutral fillers + various minerals - by virtue of at least one pressure lock. There may be one pressure lock for the said homogeneous mass and another for the mineral mixture. This (or these) preRsure lock(s) will be airtight, fed by a low pressure screw lock, so that under no circumstances is the partial vacuum at ~he interior of the reactor - necessary for the evacuation of the gases - impaired by an inflow of external air.
The displacement o~ the said mass to the interior of the reactor is carried out by means of the Archimedean screw (or endless screw). It also ensures the contlnuous homogenizatloll of the said mass.
The combustion chamber is located upstream from the reactor.
It may be an oil burner or a ga5 burner.
The hot gases which are gener~ted there, are conveyed to the entrance of the reactor. It has already been pointed out that the expected result is obtained in particular with a temperature at the entrance of the resctor of the order of 500 ~o 600C.
The reactants are themselves introduced at room temperature and undergo a thermal shock.
Advantageously, the homogeneous mass containing the shredded waste product~, calcium carbonate and possibly other minerals, is produced upstream from the reactor in a ~ibbon mixer.
At the exit from the said reactor, the mass has already been subjected to a certain degree of cooling. The discharge of the said mass is advantageously carried out in a decompre~sion lock which allows the separation of the gases, on the one hand, and the solids, on the other.
The said solids are discharged by gravity~
:, - ' :' , ' . . :
2 ~
Advantageously, the fines are recovered by passing the vapours through at least one cyclone separator. The said vapours - mainly constituted of water vapour - are evacuated, for example, by means of a natural stack.
; 5 As indicated above, the solids exist in the form of brittle fragments. These fragments can be pulverized in a disintegrator, connected to the device of the invention (downstream from the reactor).
The powder obtained may then be treated in a mixer/crystallizer assembly in order to control its granulometry. In the said mixer, it is mixed with at least one pelletizing binder~ The devlce of the invention may thus advantageously be connected to its essential elements - reactor and the means for heating, feeding,and keepin~
the partial vacuum - upstream from the ssid reactor a ribbon mixer and in successlon downstream from the said reactor a disintegrator and a mixer/drier-crystallizer aqsembly.
The appended figures 1 snd 2 lllustrate the implementation of the process of the invention.
More precisely, figure 1 shows schematically a waste treatment plant~ in which the said process is implemented and figure 2 shows the elements (of the device of the invention) essential to the implementation of the said procedure.
The numbers in these figures represent :
- 1, a hopper with sliding bottom and a sliding door, - 2, a screw-thread grinder, - 3, an overband scrap metal remover, - 4, an escalating conveyer with magnetic drum, - 5, shredder feed conveyer, - 6, a magnetic cage, At this stage of the device, the wastes have been ground and the metallic elements which they contain have been removed.
Process for the valorization of solid wastes, in particular household reuse, and devlce for its implementation.
me present mvention relates to a process for the valorization of solid waste3, comprising at least 30% by weight of cellulosic materials.
The invention also rela~es to a device for the implemeneatlon of the sald process.
At present, two main sy~tems are known for the treatment of such wastes. They may be stored in so-called controlled dumps, even deposited unofficially at rural s~tes. They may also be incinerated.
Neither of these systems permits an actual valorization of these wastes and both cause pollution. The pyrolysis of these wastes, which contain chlorinated or fluorinsted p}astic materials, 8enerate toxlc gases, such as chlorine and dioxine... Their ~ccumulation, without treatment, also leads, in time, to the generation of biogases (especially methsn~) which are dangerous as result of the~r odour and/or their fire hazard.
Furthermore, the minerali~ation of these wastes in the soll leads to the appearance of dsngerous c~verns.
It is an ob~ect of the present invention to obviate or mitigate at least one disadvantage of prior processes for treating solid wastes.
According to the invention, a process i9 proposed for the disposal of the said wastes without creating p~llution, the said process leadlng to the development of a useful material.
The said process is advsntageously implemented for the valorization of household refuse. Generally speaking, it may be implemented for ~ny type of waqte, household, industrial, agricultural.. , containing 8 minimal amount of cellulose.
This process enable the harmul effects and pollution csused by the said wastes to be ellmiDated by 8enerating an inert material.
This material - a fine or medium type of sand - may be u~ed in p~rticular in construction, f~r sanding roads, as a filler... It is safe and bacterial development is not observed within it even after a lapse of time.
The proces~ of ~he invention is implemented, as indlcated above, with solid wastes, comprising at least 3~% by weight o cellulosic materials. It l~cludes the preliminary steps of grinding 2 ~ ~ 3 ~
the said wastes and then of sorting the latter in order to remove metallic elements from them. It consists of thermally tr~ating - in a tubular reactor fitted with a Archimedean screw and heated by injection of hot combustion gases at its inle~, the said reactor being maintained under a slight partial vacuum - a mixture of a homogeneous mass cont~ining the said shredded wastes and mineral products, the said mixture containing in particular quick lime, calcium carbonate, and caustic soda; the said thermal ~reatment and the introduction o the said minerals ensuring a rise in temperature of the said mixture in the first part of the reactor sufficient to produce an intense luminous radiation.
According to the invention, the wastes are thus subjected to a specific thermal treatment which generates a radiant reaction.
The said wastes were first ground and freed of the metallic elements which they contained. They are used shredded in the form of a homogeneous mass in a mixture with mineral products. They are shreddded in order to bè available in the form of Eine particles from whlch a homogeneous mass is easily produced.
The said wastes contain at least 30% by weight of ce}lulosic materials. As indicated above, they are advantageously household refuse which usually contains about 60% by weight of cellulosic materials, 3% of plastic materials, 7% of metallic products, 4% of glass and 20%
of various materials...
The wastes are thermally treated according to the invention in a mixture wlth minerals, and in particular quick lime, calcium carbonate and caustic soda. These minerals are intended to react exothermically during the process. Advantageously, they are selected SO a9 to develop a maximal activity within the mass while being used in reasonable quantities. Hence, a very reactive quick lime is advantageously selected. As for the calcium carbonate, natural calcium carbonates are advantageously used, for economic reasons, said calcium carbonates bein~, if necessarv, enriched with calcium by addition of calcium chloride,...
The mixture - homogeneous mass containing the shredded wastes and minerals - is heated directly at the entrance of the reactor by the injection into it of hot combustion gases. Such hot gases may result, for example, from the combustion o~ gas or fuel oil.
The reactor used is a reactor equipped with an Archimedean screw or endless screw. Such a screw enables the mass of the reactants to be conveyed to the interior of the reactor and ensures that they undergo a certain de~ree of mixing.
The reactor is maintained under a slight partial vacuum for the evacuation of the gases. In fact, steam is principally drawn off.
In the type of reactor described above, it has been shown according to the lnvention that it is possible to fossllize wastes containing at least 30% of cellulosic materials without generating pollutants. This accelerated fossilization probably takes place at the moment when the intense luminous emission appears in the reactor.
It i9 the result of the sction of heat ~ in fact, a thermal shock, since hot 8ases are in~ected directly at the entrance of the reactor - on a mixture containing certain reactant~.
The process of the invention only leads to the expected result - elimination of pollutants and production of an inert product (in the form of brittle fragments) - if the said luminous emission or "aura"
is observed in the reactor.
The composition of the mixture to be introduced into the said reactor and the temperature to which it is appropriate to heat the said mixture on its entry into the said reactor are parameters to be specified for the purpose of producing the said "aura".
Their determination and optimization are operations wlthin the capacity of the person skilled in the art.
The homogeneous mass containing the shredded wastes is advantageously produced by mixing the said wastes upstream from the reactor with calcium carbonate and, preferably, natural calcium carbonates in which calcium chloride has optlonally been incorporated.
The mixing only occurs satisfactorily if the wastes have a certain degree of humidity and this is usually the case. The degree of humidity must not, however9 adversely effect the subsequent resction. It is advantageously comprised between 20 and 40%. In order to exhibit such a de8ree of humidity, the wastes may be dried ~par~ially) beforehand - if necessary - or, on the other hand moistened. 30 - 40~ by weight of natural calclum carbonates are incorporated into ~he said wastes exhibiting such 8 degree of humidity. As indicated abo~e, this mass of calcium carbonates may be first enrlched in calcium by the addition of calcium chloride to it.
To the said homogeneous mass - shredded wastes + calcium carbonates - other minerals and,in particular, as specified above, quick lime and caustic soda are added according to the invention in order to produce the desired result under the effect of heat.
It is also advantageous to add carbonated silicates (Na2Ca2Mg4H4SiO~(C03)3 type).
The introduction of these minerals - quick lime, calcium carbonate (in particular natural calcium carbonates optionally enriched in calcium chloride), caustic soda, and advantageously carbonated silicates - enable the deslred result to be obtained : the appearance of an "aura" by direct heatin~ of the mixture and the production of an inert mas3 in the form of brittle fragments.
The said minerals, other than calciwn carbonate (optionally containing calcium chloride) are introduced for the purposes of the invention (for the generation of the "aura'~in a proportion o about 5 to 35% by weight of the said homogeneous mass. The minimal quantity used obviously depends on the constitution of the said homogeneous mass and in particular on the conten~ of cellulosic matter present Z5 in the wastes to be treated. They are advantageously used in approximately equivalent amounts (l/39 1/3, 1/3):
- quick lime between 10 and 45%
- caustic soda between 5 and 35%
- silicate carbonates between 10 and 45% by weight of the ternary mixture (quick lime ~ caustic soda + silicate carbonates~.
The reactive mass thus constituted - homogeneous mass +
minerals - is subiected to a thermal shock on entering the reactor by the injection into it of hot gases.
The "aura" necessary for fossilization is observed according to the inYention when the said reactive mass is at a temperature of 250 to 300C. This temperature may be obtained within the mass according to the invention by the injection of gases combusted at 500-600C.
It has previously been pointed out that on being discharged from the reactor the mass exists in the form of brittle fragments.
These recovered fragments are advantageously pulverized. A sand ls thus obtained with a density of the order of 0.3 ~o 0.5. Such a sand cannot easily be used and fillers are advantageously introduced into the process of the invention in order to increase its density. These fillers may be introduced at at leas~ two stages of the process of the invention. They may be incorporated in~o the sand resulting from passage of the solids discharged from the reactor into a disintegrator and/or incorporated during the manufacture of the homogeneous mass - shredded wastes ~ calcium carbonate - before its introduction into the reactor.
Downstream from the reactor any type of filler may be used.
Upstream from it, only neutral fillers may be used. By neutral fillers are meant, in the present context, fillers compatible with the thermal reaction (heating ~ "aura"). Such neutral fillers may be selected Erom calcium carbonate, carbonate of lime,'powered bary~a, the carbonat~d sllicates, powdered clay, powdered sugary-grained gypsum, powdered bauxite,.., or their mixtures. Hence it should be noted that calcium carbonate and the carbonated silicates may be used in the process of the invention in greater amounts than those already mentioned above.
By way of illustration, it should be made clear that the calcium carbonate, carbonate of lime mixture may thus represent up to 50% by weight of the said homogeneous mass (calcium carbonate is thus employed both as reactant and a9 neutral filler).
The baryta (with its sediment) may be used in a proportion of 0 to 30% by weight; cla~ in a proportion of 0 to 15%, gypsum in a proportion of 0 to 20% and bauxite in a proportion of 0 to 20%. The carbonated silicates taken as a whole may be employed up to a maximum of 30% by weight of the total mass at the entrance of the reactor.
The said fillers make it possible to produce a sand of deflned density.
If it is desired to adjust its granulometry - more precisely to increase it - a further step is added to the process of the invention.
The mass issuing from the reactor, after being pulverized and optionally having neutral fillers incorporat:ed within it, is available in ~he form of a Yery fine, even impalpable, powder.
Such a powder ls advantageously condit:ioned with pelletizing binders in order to increase its granulometry for the production, in particular, of a medium sand, which can be used in construction.
The binder is advantageously mixed with the powder in a vertical pelletizer of the Flexomix type; the mixture is then dried, which leads to the crystallization of the said binder.
The said binder must be selected 90 as to comply w-lth the inert, stable character of the product obtsined by the process of the invention. It must not introduce bacteria. It is possible to use in particular sodiu~ silicate which will react with the calcium present ln the grains of the product.
It i8 also possible to use a binder based on quick lime, cement slurrles, blast-furnace slags and carboxymethyl cellulose (or equivalent). Another binder whlch can be used i9 a binder based on water-soluble pitch.
This step involving the treatment of a powdery material in order to increase its granulometry i9 perfectly well-known to the person skilled in the art.
In this way, waste products are valorized according to the invention without causlng pollution in as much as it did not appear necessary to heat the reactive mass in the reactor to a temperature hi8her than 300C (pyrolysis of plastic materials). The combustion gases, introduced at the entrance of the reactor to heat the said reactive masq directly, seem either to be trapped in the said mass or to decompose in particular at the time when the said "aura" iq produced.
Another object of the inventlon is a device for the implementation of the procedure as explained above.
The said device comprises es~entially:
- a tubular reactor equipped with an Archimedean screw, ,:
2 ~ o ~
- a combustion chamber with its outlet a~ the entrance to the said reactor for the direot supply of calories, - means for feeding the said reactor, - mea~s for main~aining a slight partial vacuum in the said reactor.
The reactor i8 fed at one end with the reac~ive mass -homogeneous mass containing the shredded waste products and, optionally, neutral fillers + various minerals - by virtue of at least one pressure lock. There may be one pressure lock for the said homogeneous mass and another for the mineral mixture. This (or these) preRsure lock(s) will be airtight, fed by a low pressure screw lock, so that under no circumstances is the partial vacuum at ~he interior of the reactor - necessary for the evacuation of the gases - impaired by an inflow of external air.
The displacement o~ the said mass to the interior of the reactor is carried out by means of the Archimedean screw (or endless screw). It also ensures the contlnuous homogenizatloll of the said mass.
The combustion chamber is located upstream from the reactor.
It may be an oil burner or a ga5 burner.
The hot gases which are gener~ted there, are conveyed to the entrance of the reactor. It has already been pointed out that the expected result is obtained in particular with a temperature at the entrance of the resctor of the order of 500 ~o 600C.
The reactants are themselves introduced at room temperature and undergo a thermal shock.
Advantageously, the homogeneous mass containing the shredded waste product~, calcium carbonate and possibly other minerals, is produced upstream from the reactor in a ~ibbon mixer.
At the exit from the said reactor, the mass has already been subjected to a certain degree of cooling. The discharge of the said mass is advantageously carried out in a decompre~sion lock which allows the separation of the gases, on the one hand, and the solids, on the other.
The said solids are discharged by gravity~
:, - ' :' , ' . . :
2 ~
Advantageously, the fines are recovered by passing the vapours through at least one cyclone separator. The said vapours - mainly constituted of water vapour - are evacuated, for example, by means of a natural stack.
; 5 As indicated above, the solids exist in the form of brittle fragments. These fragments can be pulverized in a disintegrator, connected to the device of the invention (downstream from the reactor).
The powder obtained may then be treated in a mixer/crystallizer assembly in order to control its granulometry. In the said mixer, it is mixed with at least one pelletizing binder~ The devlce of the invention may thus advantageously be connected to its essential elements - reactor and the means for heating, feeding,and keepin~
the partial vacuum - upstream from the ssid reactor a ribbon mixer and in successlon downstream from the said reactor a disintegrator and a mixer/drier-crystallizer aqsembly.
The appended figures 1 snd 2 lllustrate the implementation of the process of the invention.
More precisely, figure 1 shows schematically a waste treatment plant~ in which the said process is implemented and figure 2 shows the elements (of the device of the invention) essential to the implementation of the said procedure.
The numbers in these figures represent :
- 1, a hopper with sliding bottom and a sliding door, - 2, a screw-thread grinder, - 3, an overband scrap metal remover, - 4, an escalating conveyer with magnetic drum, - 5, shredder feed conveyer, - 6, a magnetic cage, At this stage of the device, the wastes have been ground and the metallic elements which they contain have been removed.
- 7, a screw-thread shredder, - 8, a mixer feed conveyer, - 9, a powder silo with lock screw, containing in particular natural calclum carbonates, - 10, a band mixer, :
- 11, feed conveyer for ~he reactor, - 12, a powder silo wi~h lock screw, - 13, the reactor for accelerated fossilization, The elements (11) and (12) sre the mealns by which the reactor 5 i5 fed.
- 14 and lS, two cyclon~s (for the recovery of the ~ine~), - 16, the feed conveyer for the disintegrator, - 17, the said disintegrator (vertical), - 18, the feed conveyer for the pelletizer, - 19, the said Flexomix vertical pelletizer, - 20, the feed conYeyer for the drying vat, - 21, the said drying vat, - 22, the stockpile conveyer, - 23, the combustion chamber, - 24, the Archimedean screw in the interior of the reactor, - 25 view ports for observing the interior of the said reactor, - 26, the discharge chute o~ the said reactor.
In such a plant, 11 869.2 tons o~ waste are treated per hour.
The time taken or the mass to p8SS to the interior of the reactor is about 3Q min.
The luminous emission or "aura" was observed in the vicini~y of the first third of the reactor whereas the temperature at the interior of the mass conveyed into the said reactor is 250~C; the temperature at the entrance to the reactor varyin~ between 500 and 600C.
In such a plant, 11 869.2 tons o~ waste are treated per hour.
The time taken or the mass to p8SS to the interior of the reactor is about 3Q min.
The luminous emission or "aura" was observed in the vicini~y of the first third of the reactor whereas the temperature at the interior of the mass conveyed into the said reactor is 250~C; the temperature at the entrance to the reactor varyin~ between 500 and 600C.
Claims (10)
1. Process for the valorization of solid wastes, comprising at least 30% by weight of cellulosic materials, in particular household refuse; the said process including the preliminary steps of grinding and sorting of the said wastes in order to remove from them metallic elements, characterized in that it consists of thermally treating -in a tubular reactor (13) equipped with a Archimedean screw (24) and heated by injection of hot combustion gases at its entrance, the said reactor being maintained under a slight partial vacuum - a mixture of a homogeneous mass containing the said shredded wastes and mineral products, the said mixture containing in particular quick lime, calcium carbonate and caustic soda; the said thermal treatment and the introduction of the said minerals ensuring a rise in temperature of the said mixture in the first part of the reactor such as to produce an intense luminous radiation.
2. Process according to Claim 1, characterized in that the said homogeneous mass includes the said shredded wastes, exhibiting a degree of humidity between 20 and 40%, and 30 to 40% by weight of natural calcium carbonates.
3. Process according to one of the Claims 1 or 2, characterized in that the said mixture also contains carbonated silicates.
4. Process according to any one of the Claims 1 to 3, characterized in that the mineral products employed - other than the calcium carbonate intimately mixed beforehand with the shredded wastes -represent from 5 to 35% by weight of the said homogeneous mass.
5. Process according to any one of the Claims 1 to 4, characterized in that the mixture introduced into the reactor also contains neutral fillers - selected from calcium carbonate, carbonate of lime, powdered baryta, carbonated silicates, powdered clay, powdered sugary-grained gypsum, powdered bauxite or their mixtures - in order to regulate the density of the products discharged from the said reactor.
6. Process according to any one of the Claims 1 to 5, characterized in that the mass discharged from the said reactor is treated, after pulverization and the optional intimate mixing with it of neutral fillers, with at least one pelletizing binder in order to produce a product - of the sand type - of defined granulometry.
7. Device for the implementation of the process according to any one of the preceding claims, characterized in that it comprises:
- a tubular reactor (13) equipped with an Archimedean screw (24);
- a combustion chamber (23) with its outlet at the entrance of the said reactor for the direct supply of calories;
- means (11, 12) for feeding the said reactor;
- means for maintaining a slight partial vacuum in the said reactor.
- a tubular reactor (13) equipped with an Archimedean screw (24);
- a combustion chamber (23) with its outlet at the entrance of the said reactor for the direct supply of calories;
- means (11, 12) for feeding the said reactor;
- means for maintaining a slight partial vacuum in the said reactor.
8. Device according to Claim 7, characterized in that it comprises, upstream from the said reactor a ribbon mixer (10) for the production of the said homogeneous mass from the shredded wastes.
9. Device according to one of the Claims 7 or 8, characterized in that it comprises downstream from the reactor a pulverizer (17) which converts the mass discharged from the said reactor into a very fine powder.
10. Device according to Claim 9, characterized in that it comprises downstream from the said pulverizer (17) a mixer (19) for the pelletization of the said powder into particles and means (21) for drying/crystallization of the said particles obtained.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
EP19890403148 EP0427899A1 (en) | 1989-11-16 | 1989-11-16 | Process for the valorisation of solid waste in particular garbage and apparatus for carrying out this method |
EP89403148.3 | 1989-11-16 |
Publications (1)
Publication Number | Publication Date |
---|---|
CA2045406A1 true CA2045406A1 (en) | 1991-05-17 |
Family
ID=8203005
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CA 2045406 Abandoned CA2045406A1 (en) | 1989-11-16 | 1990-11-15 | Process for the valorization of solid wastes, in particular household refuse, and device for its implementation |
Country Status (16)
Country | Link |
---|---|
EP (1) | EP0427899A1 (en) |
KR (1) | KR920701065A (en) |
AU (1) | AU6757290A (en) |
BR (1) | BR9007027A (en) |
CA (1) | CA2045406A1 (en) |
CS (1) | CS566290A3 (en) |
DK (1) | DK135191A (en) |
FI (1) | FI913406A0 (en) |
HU (2) | HUT69461A (en) |
IE (1) | IE904129A1 (en) |
MC (1) | MC2177A1 (en) |
MW (1) | MW2591A1 (en) |
PT (1) | PT95907A (en) |
RO (1) | RO106556B1 (en) |
WO (1) | WO1991007361A1 (en) |
YU (1) | YU47234B (en) |
Families Citing this family (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE4130416C1 (en) * | 1991-09-10 | 1992-12-10 | Thermoselect Ag, Vaduz, Li | |
FR2683166A1 (en) * | 1991-11-04 | 1993-05-07 | Services Ste Fse | Method for converting waste, particularly household waste, into essentially mineral material, and installation for implementing the method |
FR2693927B1 (en) * | 1992-07-24 | 1994-10-07 | Philippe Pichat | Process and apparatus for obtaining stabilized molded materials from waste. |
EP0602293B1 (en) * | 1992-12-07 | 1997-07-02 | de Blangy, Gérard | Process and apparatus for treatment and valorisation of waste by transforming in a non-polluable reusable material |
FR2717490B1 (en) * | 1994-03-18 | 1998-12-04 | Osvald Minghi | Method and device for producing fuel by continuous pyrolysis of ground or pasty waste. |
EP0737490A1 (en) * | 1995-04-11 | 1996-10-16 | Hard Ag | Method for immobilization of heavy metals and elements |
EP0689858A1 (en) * | 1995-04-11 | 1996-01-03 | Hard Ag | Process and product of the immobilisation of heavy metals |
CH700824B1 (en) * | 2008-01-30 | 2010-10-29 | Hochschule Rapperswil Inst | Method and apparatus for producing heat-treated products. |
GB201018150D0 (en) | 2010-10-27 | 2010-12-08 | Cathcart Jeremy J | A method of and apparatus for treating waste and a waste product |
CA2984198A1 (en) | 2015-04-30 | 2016-11-03 | Domenico TANFOGLIO | Pyrolysis furnace |
CN106322387B (en) * | 2015-06-18 | 2019-05-10 | 蓝天众成环保工程有限公司 | A method of garbage disposal |
GB201910222D0 (en) * | 2019-07-17 | 2019-08-28 | Rockfuel Innovations Ltd | Limestone processing |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE2701385A1 (en) * | 1977-01-14 | 1978-07-20 | Trasswerk Meurin Betriebs Gmbh | Domestic waste treatment giving lightweight concrete aggregate - by mixing with minerals, pelletising and sintering |
FR2472421A1 (en) * | 1979-03-13 | 1981-07-03 | Geronimo Hilaire | Transforming garbage contg. cellulose into useful products - by reaction with calcium cpd., and agglomerating the reaction product |
DE3346901C2 (en) * | 1983-12-21 | 1986-10-09 | Mannesmann AG, 4000 Düsseldorf | Process for residue-free energetic use of cellulose-rich waste and plant |
CH665785A5 (en) * | 1985-06-19 | 1988-06-15 | Loma Finance Inc | PROCESS FOR THE CONVERSION OF ORGANIC AND MINERAL WASTE INTO SOLID, INERT AND INSOLUBLE MATERIAL IN WATER. |
-
1989
- 1989-11-16 EP EP19890403148 patent/EP0427899A1/en not_active Withdrawn
-
1990
- 1990-11-15 KR KR1019910700746A patent/KR920701065A/en not_active Withdrawn
- 1990-11-15 RO RO147995A patent/RO106556B1/en unknown
- 1990-11-15 WO PCT/FR1990/000817 patent/WO1991007361A1/en active Application Filing
- 1990-11-15 BR BR9007027A patent/BR9007027A/en not_active Application Discontinuation
- 1990-11-15 MC MC90@@D patent/MC2177A1/en unknown
- 1990-11-15 HU HU912373A patent/HUT69461A/en unknown
- 1990-11-15 AU AU67572/90A patent/AU6757290A/en not_active Abandoned
- 1990-11-15 CS CS905662A patent/CS566290A3/en unknown
- 1990-11-15 CA CA 2045406 patent/CA2045406A1/en not_active Abandoned
- 1990-11-15 FI FI913406A patent/FI913406A0/en not_active Application Discontinuation
- 1990-11-15 IE IE412990A patent/IE904129A1/en unknown
- 1990-11-15 HU HU237390A patent/HU912373D0/en unknown
- 1990-11-15 PT PT95907A patent/PT95907A/en not_active Application Discontinuation
- 1990-11-16 YU YU218390A patent/YU47234B/en unknown
-
1991
- 1991-07-15 DK DK135191A patent/DK135191A/en not_active Application Discontinuation
- 1991-07-16 MW MW2591A patent/MW2591A1/en unknown
Also Published As
Publication number | Publication date |
---|---|
FI913406A7 (en) | 1991-07-15 |
HUT69461A (en) | 1995-09-28 |
WO1991007361A1 (en) | 1991-05-30 |
RO106556B1 (en) | 1993-05-31 |
KR920701065A (en) | 1992-08-11 |
MC2177A1 (en) | 1992-05-22 |
DK135191D0 (en) | 1991-07-15 |
DK135191A (en) | 1991-07-15 |
CS566290A3 (en) | 1992-03-18 |
MW2591A1 (en) | 1992-05-13 |
HU912373D0 (en) | 1992-02-28 |
AU6757290A (en) | 1991-06-13 |
BR9007027A (en) | 1991-10-22 |
YU218390A (en) | 1992-07-20 |
FI913406A0 (en) | 1991-07-15 |
YU47234B (en) | 1995-01-31 |
EP0427899A1 (en) | 1991-05-22 |
PT95907A (en) | 1991-09-13 |
IE904129A1 (en) | 1991-05-22 |
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