EP0262291A1 - Device for refuse pyrolysis - Google Patents

Device for refuse pyrolysis Download PDF

Info

Publication number
EP0262291A1
EP0262291A1 EP87106352A EP87106352A EP0262291A1 EP 0262291 A1 EP0262291 A1 EP 0262291A1 EP 87106352 A EP87106352 A EP 87106352A EP 87106352 A EP87106352 A EP 87106352A EP 0262291 A1 EP0262291 A1 EP 0262291A1
Authority
EP
European Patent Office
Prior art keywords
pyrolysis
flue gas
waste incineration
combustion chamber
gases
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
EP87106352A
Other languages
German (de)
French (fr)
Inventor
Arvid Christmann
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.)
Deutsche Babcock Anlagen AG
Original Assignee
Deutsche Babcock Anlagen AG
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 Deutsche Babcock Anlagen AG filed Critical Deutsche Babcock Anlagen AG
Publication of EP0262291A1 publication Critical patent/EP0262291A1/en
Ceased legal-status Critical Current

Links

Images

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/027Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
    • F23G5/0273Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage using indirect heating
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • F23G5/46Recuperation of heat

Definitions

  • the invention relates to a device for pyrolysis of waste materials, in particular contaminated sites, with an indirectly heated pyrolysis reactor, from which a pyrolysis gas line is led to a combustion chamber.
  • a device of the type specified at the outset is described, for example, in AT-PS 3 46 997. From this document, however, it does not appear that the use of the pyrolysis gases in a conventional gas burner or in an internal combustion engine because of the composition of the pyrolysis gases and various admixtures contained in them are problematic in practice.
  • a self-sufficient pyrolysis system ie a system that is equipped with the necessary units for cleaning and using the pyrolysis gases, therefore requires a high investment.
  • Such an effort is not always economically justifiable, especially if the amount of the materials to be disposed of - as is often the case with contaminated sites - is limited so that the system can only be used for a limited period of time.
  • the invention has for its object to reduce the investment in a device of the type mentioned in the beginning and in particular to save the effort for cleaning the pyrolysis gases.
  • the solution according to claim 1 is particularly simple and cheap.
  • the solution according to claim 2 is intended for special cases in which the pyrolysis gas has more thermally stable substances, e.g. Dioxin, can contain, especially for the pyrolysis of PCB-containing residues from transformer oils.
  • Dioxin e.g. Dioxin
  • the feature of claim 3 also allows the use of the residual heat contained in the exhaust gases from the heating of the pyrolysis reactor.
  • the feature of claim 4 enables economically viable pyrolysis treatment of special wastes even if they can only be eliminated in a limited amount.
  • the feature of claim 5 enables the saving of additional fuel for the pyrolysis treatment. This is particularly important if the material to be pyrolytically treated has only a low energy potential.
  • FIGS. 1 and 2 each show a process diagram to illustrate the invention.
  • FIG. 1 - separated by a dashed line 1 - a conventional waste incineration system is shown, consisting essentially of a furnace 2, a steam boiler 3, a flue gas cleaning system 4, a suction 5 and a chimney 6.
  • the arrows drawn between the individual units represent symbolic represents the flue gas duct.
  • the invention is not tied to a specific system. It can be designed, for example, as roller grate or moving grate firing for the combustion of domestic and commercial waste or as a rotary kiln with or without an afterburner chamber for the combustion of industrial or special waste.
  • a pyrolysis reactor 7 is set up, preferably an indirectly heated rotary kiln, with feed lines 8 for fuel and combustion air.
  • the rotary kiln 7 is fed with waste material via a feed device 9, e.g. with oil-soaked soil. Solid residues are discharged via a discharge device 10.
  • the pyrolysis gas is passed through a pipeline 11, which is well insulated to avoid condensation and is as short as possible, into the furnace 2 and burned there in a burner, not shown, which serves as a support burner for waste incineration.
  • the flue gas from the burner mixes with the flue gas from the refuse furnace and contributes to heating the steam boiler 3.
  • the exhaust gas from the heating of the pyrolysis reactor 7 is introduced into the steam boiler 3 via an exhaust gas line 12 in the corresponding temperature zone, where it largely emits its heat content and mixes with the rest of the exhaust gas stream.
  • the entire flue gas is freed from solid and gaseous admixtures in the flue gas cleaning system 4 and is released into the open via the suction 5 through the chimney 6.
  • the plant illustrated in FIG. 2 is intended in particular for the disposal of waste materials which may contain harmful, thermally more stable substances, such as chlorinated biphenyls. It differs from the system according to FIG. 1 in that the pyrolysis gas is fed via a line 13 to a combustion chamber 14 which is separate from the furnace 2 and there at one temperature is burned separately above 1200 ° C. The high combustion temperature ensures that the harmful substances are safely decomposed. In the furnace 2, the usual flue gas temperature level of 800 to 900 ° C can be maintained. The flue gas produced in the combustion chamber 14 is introduced via a line 15 into the flue gas duct of the furnace 2 before entering the steam boiler 3.
  • the pyrolysis gas is fed via a line 13 to a combustion chamber 14 which is separate from the furnace 2 and there at one temperature is burned separately above 1200 ° C.
  • the high combustion temperature ensures that the harmful substances are safely decomposed.
  • the usual flue gas temperature level of 800 to 900 ° C can be maintained.
  • the pyrolysis reactor 7 is heated in the system according to FIG. 2 by means of a partial flow of hot flue gases, which branches off from the flue gas duct via a line 16 before entering the steam boiler 3 and is led to the pyrolysis reactor 7 via a hot gas filter 17.
  • the system shown schematically in FIG. 2 corresponds to the system described first. It is of course also possible to heat the pyrolysis reactor with hot flue gas from the waste incineration plant if, as in the embodiment shown in FIG. 1, the pyrolysis gases are burned in the waste incineration plant.

Landscapes

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Incineration Of Waste (AREA)

Abstract

Ein Pyrolysereaktor (7) ist mit einer Müllverbrennungsanlage (1) gekoppelt. Die Pyrolysegase gelangen bei einer Variante direkt in die Feuerung (2) der Müllverbrennungsanlage (1) Bei einer anderen Variante werden sie in einer separaten Verbrennungskammer (14) verbrannt, und die entstehenden Rauchgase werden in den Rauchgaskanal der Müllverbrennungsanlage (1) eingespeist. Dadurch werden die bei autarken Pyrolyseanlagen erforderlichen Aggregate für die Reinigung und Nutzung der Pyrolysegase und für die Rauchgasreinigung eingespartA pyrolysis reactor (7) is coupled to a waste incineration plant (1). In one variant, the pyrolysis gases go directly into the furnace (2) of the waste incineration plant (1). In another variant, they are burned in a separate combustion chamber (14), and the resulting flue gases are fed into the flue gas duct of the waste incineration plant (1). This saves the units required for self-sufficient pyrolysis plants for cleaning and using the pyrolysis gases and for flue gas cleaning

Description

Die Erfindung betrifft eine Vorrichtung zur Pyrolyse von Abfallstoffen, insbesondere von Altlasten mit einem indirekt beheizten Pyrolysereaktor, von dem eine Pyrolysegasleitung zu einer Verbrennungskammer geführt ist.The invention relates to a device for pyrolysis of waste materials, in particular contaminated sites, with an indirectly heated pyrolysis reactor, from which a pyrolysis gas line is led to a combustion chamber.

Mit Hilfe der Pyrolyse ist es möglich, in umweltfreundlicher Weise gewisse problematische Abfallstoffe zu beseitigen. Hierzu gehören insbesondere die sogenannten Altlasten, wie z.B. mit Ölen oder Lösungsmitteln verseuchtes Erdreich, Teerrückstände, Säureharze und dergleichen, aber auch andere spezielle Abfälle, wie Altreifen oder Reste von kunststoffisolierten Kabeln. Als Rückstand fällt ein festes Produkt an, das verwertbare und/oder deponiefähige Bestandteile enthält. Außerdem wird ein brennbares Pyrolysegas gewonnen.With the help of pyrolysis, it is possible to remove certain problematic waste materials in an environmentally friendly manner. This includes in particular the so-called contaminated sites, such as Soil contaminated with oils or solvents, tar residues, acid resins and the like, but also other special waste, such as used tires or the remains of plastic-insulated cables. A solid product is obtained as a residue, which contains usable and / or landfillable components. A flammable pyrolysis gas is also obtained.

Eine Vorrichtung der eingangs angegebenen Gattung ist z.B. in der AT-PS 3 46 997 beschrieben. Aus dieser Schrift geht aber nicht hervor, daß die Nutzung der Pyrolysegase in einem üblichen Gasbrenner oder auch in einer Brennkraftmaschine wegen der Zusammensetzung der Pyrolysegase und der in ihnen enthaltenen verschiedenen Beimengungen in der Praxis mit Problemen verbunden ist. Die DE-OS 27 32 418, die DE-OS 24 32 504 und die US-PS 42 06 186, die sich eingehend mit diesen Problemen befassen, lassen erkennen, daß zur Behandlung der Pyrolysegase ein erheblicher Aufwand an peripheren Aggregaten erforderlich ist. In der EP-A1 0 111 081 und der bereits erwähnten AT-PS 3 46 997 wird zwar vorgeschlagen, die Entstehung gewisser gasförmiger Verunreinigungen, wie Halogenwasserstoffe oder Schwefeldioxid, dadurch zu vermeiden, daß vor oder beim Schwelprozeß feinkörniges basisches Material zugesetzt wird. Hierdurch wird zwar der Aufwand für die nachträgliche Beseitigung dieser Schadgase eingespart; andererseits verursacht aber ein stark erhöhter Staubgehalt der Pyrolysegase einen erhöhten Aufwand für die Entstaubung.A device of the type specified at the outset is described, for example, in AT-PS 3 46 997. From this document, however, it does not appear that the use of the pyrolysis gases in a conventional gas burner or in an internal combustion engine because of the composition of the pyrolysis gases and various admixtures contained in them are problematic in practice. DE-OS 27 32 418, DE-OS 24 32 504 and US-PS 42 06 186, which deal in detail with these problems, show that a considerable amount of peripheral equipment is required to treat the pyrolysis gases. In EP-A1 0 111 081 and the already mentioned AT-PS 3 46 997 it is proposed to avoid the formation of certain gaseous impurities, such as hydrogen halide or sulfur dioxide, by adding fine-grained basic material before or during the smoldering process. This saves the effort for the subsequent removal of these harmful gases; on the other hand, however, a greatly increased dust content of the pyrolysis gases causes an increased effort for dedusting.

Ein Problem liegt auch darin, daß geeignete Abnehmer für das in schwankender Menge und schwankender Qualität anfallende Pyrolysegas nicht immer vorhanden sind. Die Nutzung in der Pyrolyseanlage selbst setzt entsprechende Einrichtungen voraus.Another problem lies in the fact that suitable customers for the pyrolysis gas produced in fluctuating quantities and quality are not always available. Appropriate facilities are required for use in the pyrolysis plant itself.

Eine autarke Pyrolyseanlage, d.h. eine Anlage, die mit den notwendigen Aggregaten für die Reinigung und Nutzung der Pyrolysegase ausgestattet ist, bedingt daher einen hohen Investitionsaufwand. Ein solcher Aufwand ist wirtschaftlich nicht immer vertretbar, vor allem wenn die Menge der zu beseitigenden Stoffe - wie z.B. vielfach bei Altlasten-begrenzt ist, so daß die Anlage nur für einen begrenzten Zeitraum nutzbar ist.A self-sufficient pyrolysis system, ie a system that is equipped with the necessary units for cleaning and using the pyrolysis gases, therefore requires a high investment. Such an effort is not always economically justifiable, especially if the amount of the materials to be disposed of - as is often the case with contaminated sites - is limited so that the system can only be used for a limited period of time.

Der Erfindung liegt die Aufgabe zugrunde, bei einer Vorrichtung der eingangs angegebenen Gattung den Investitionsaufwand zu verkleinern und insbesondere den Aufwand für die Reinigung der Pyrolysegase einzusparen.The invention has for its object to reduce the investment in a device of the type mentioned in the beginning and in particular to save the effort for cleaning the pyrolysis gases.

Diese Aufgabe wird durch die kennzeichnenden Merkmale des Anspruchs 1 oder alternativ durch die kennzeichnenden Merkmale des Anspruchs 2 gelöst.This object is achieved by the characterizing features of claim 1 or alternatively by the characterizing features of claim 2.

Die Lösung gemäß Anspruch 1 ist besonders einfach und billig.The solution according to claim 1 is particularly simple and cheap.

Die Lösung gemäß Anspruch 2 ist für spezielle Fälle vorgesehen, bei denen das Pyrolysegas thermisch stabilere Substanzen, wie z.B. Dioxin, enthalten kann, insbesondere für die Pyrolyse von PCB-haltigen Rückständen aus Transformatorenölen.The solution according to claim 2 is intended for special cases in which the pyrolysis gas has more thermally stable substances, e.g. Dioxin, can contain, especially for the pyrolysis of PCB-containing residues from transformer oils.

Beide Lösungen beruhen auf dem gemeinsamen Konzept, das Pyrolysegas ungereinigt zu verbrennen und für die Reinigung des Rauchgases die bei einer Müllverbrennungsanlage ohnehin vorhandenen Aggregate zu nutzen. Dies ist in den meisten praktisch vorkommenden Fällen problemlos möglich, da die Menge der organischen Anteile der durch Pyrolyse zu beseitigenden Sonderabfälle relativ gering ist im Vergleich zur Menge des kommunalen und gewerblichen Mülls, der in einer Müllverbrennungsanlage durchgesetzt wird.Both solutions are based on the common concept of incinerating the pyrolysis gas unpurified and using the units that are already present in a waste incineration plant to purify the flue gas. This is easily possible in most practical cases, since the amount of organic parts of the special waste to be removed by pyrolysis is relatively small compared to the amount of municipal and commercial waste that is put through in a waste incineration plant.

Das Merkmal des Anspruchs 3 erlaubt auch die Nutzung der in den Abgasen d er Heizung des Pyrolysereaktors enthaltenen Restwärme.The feature of claim 3 also allows the use of the residual heat contained in the exhaust gases from the heating of the pyrolysis reactor.

Durch das Merkmal des Anspruchs 4 wird eine wirtschaftlich tragbare Pyrolysebehandlung von Sonderabfällen auch dann ermöglicht, wenn diese nur in begrenzter Menge zu beseitigen sind.The feature of claim 4 enables economically viable pyrolysis treatment of special wastes even if they can only be eliminated in a limited amount.

Das Merkmal des Anspruchs 5 ermöglicht die Einsparung von Zusatzbrennstoff für die Pyrolysebehandlung. Dies ist insbesondere von Bedeutung, wenn das pyrolytisch zu behandelnde Material nur ein geringes Energiepotential hat.The feature of claim 5 enables the saving of additional fuel for the pyrolysis treatment. This is particularly important if the material to be pyrolytically treated has only a low energy potential.

Die Figuren 1 und 2 zeigen zur Veranschaulichung der Erfindung je ein Verfahrensschema.FIGS. 1 and 2 each show a process diagram to illustrate the invention.

In Figur 1 ist - durch eine gestrichelte Linie 1 abgetrennt - eine herkömmliche Müllverbrennungsanlage dargestellt, bestehend im wesentlichen aus einer Feuerung 2, einem Dampfkessel 3, einer Rauchgasreinigungsanlage 4, einem Saugzug 5 und einem Schornstein 6. Die zwischen den einzelnen Aggregaten gezeichneten Pfeile stellen symbolisch den Rauchgaskanal dar.In Figure 1 - separated by a dashed line 1 - a conventional waste incineration system is shown, consisting essentially of a furnace 2, a steam boiler 3, a flue gas cleaning system 4, a suction 5 and a chimney 6. The arrows drawn between the individual units represent symbolic represents the flue gas duct.

Bezüglich der Feuerung ist die Erfindung nicht an ein bestimmtes System gebunden. Sie kann z.B. als Walzenrost- oder Vorschubrostfeuerung zur Verbrennung von Hausmüll und Gewerbemüll oder als Drehrohrofen mit oder ohne Nachbrennkammer zur Verbrennung von Industrie- oder Sondermüll ausgebildet sein.With regard to the firing, the invention is not tied to a specific system. It can be designed, for example, as roller grate or moving grate firing for the combustion of domestic and commercial waste or as a rotary kiln with or without an afterburner chamber for the combustion of industrial or special waste.

In unmittelbarer Nähe der Müllverbrennungsanlage 1 ist ein Pyrolysereaktor 7 aufgestellt, vorzugsweise ein indirekt beheizter Drehrohrofen, mit Zuleitungen 8 für Brennstoff und Verbrennungsluft. Der Drehrohrofen 7 wird über eine Aufgabevorrichtung 9 mit Abfallstoff beschickt, z.B. mit öldurchtränktem Erdreich. Über eine Austragvorrichtung 10 werden feste Rückstände ausgetragen. Das Pyrolysegas wird über eine Rohrleitung 11, die zur Vermeidung von Kondensation gut wärmeisoliert und möglichst kurz ist, in die Feuerung 2 geleitet und dort in einem nicht dargestellten Brenner, der als Stützbrenner für die Müllverbrennung dient, verbrannt. Das Rauchgas des Brenners mischt sich mit dem Rauchgas der Müllfeuerung und trägt zur Beheizung des Dampfkessels 3 bei. Das Abgas der Heizung des Pyrolysereaktors 7 wird über eine Abgasleitung 12 in der entsprechenden Temperaturzone in den Dampfkessel 3 eingeleitet, wo es seinen Wärmeinhalt weitgehend abgibt und sich mit dem übrigen Abgasstrom mischt. Das gesamte Rauchgas wird in der Rauchgasreinigungsanlage 4 von festen und gasförmigen Beimischungen befreit und gelangt über den Saugzug 5 durch den Schornstein 6 ins Freie.In the immediate vicinity of the waste incineration plant 1, a pyrolysis reactor 7 is set up, preferably an indirectly heated rotary kiln, with feed lines 8 for fuel and combustion air. The rotary kiln 7 is fed with waste material via a feed device 9, e.g. with oil-soaked soil. Solid residues are discharged via a discharge device 10. The pyrolysis gas is passed through a pipeline 11, which is well insulated to avoid condensation and is as short as possible, into the furnace 2 and burned there in a burner, not shown, which serves as a support burner for waste incineration. The flue gas from the burner mixes with the flue gas from the refuse furnace and contributes to heating the steam boiler 3. The exhaust gas from the heating of the pyrolysis reactor 7 is introduced into the steam boiler 3 via an exhaust gas line 12 in the corresponding temperature zone, where it largely emits its heat content and mixes with the rest of the exhaust gas stream. The entire flue gas is freed from solid and gaseous admixtures in the flue gas cleaning system 4 and is released into the open via the suction 5 through the chimney 6.

Die in Figur 2 veranschaulichte Anlage ist insbesondere für die Beseitigung von Abfallstoffen vorgesehen, die schädliche, thermisch stabilere Stoffe, wie z.B. chlorierte Biphenyle, enthalten können. Sie unterscheidet sich von der Anlage gemäß Figur 1 dadurch, daß über eine Leitung 13 das Pyrolysegas einer von der Feuerung 2 getrennten Verbrennungskammer 14 zugeführt wird und dort bei einer Temperatur über 1200 °C separat verbrannt wird. Durch die hohe Verbrennungstemperatur wird eine sichere Zersetzung der schädlichen Stoffe erreicht. In der Feuerung 2 kann das bei der Müllverbrennung übliche Rauchgasstemperaturniveau von 800 bis 900 °C beibehalten werden. Das in der Brennkammer 14 entstehende Rauchgas wird über eine Leitung 15 vor dem Eintritt in den Dampfkessel 3 in den Rauchgaskanal der Feuerung 2 eingeleitet.The plant illustrated in FIG. 2 is intended in particular for the disposal of waste materials which may contain harmful, thermally more stable substances, such as chlorinated biphenyls. It differs from the system according to FIG. 1 in that the pyrolysis gas is fed via a line 13 to a combustion chamber 14 which is separate from the furnace 2 and there at one temperature is burned separately above 1200 ° C. The high combustion temperature ensures that the harmful substances are safely decomposed. In the furnace 2, the usual flue gas temperature level of 800 to 900 ° C can be maintained. The flue gas produced in the combustion chamber 14 is introduced via a line 15 into the flue gas duct of the furnace 2 before entering the steam boiler 3.

Die Beheizung des Pyrolysereaktors 7 erfolgt bei der Anlage gemäß Fig. 2 mittels eines Teilstroms heißer Rauchgase, der vor dem Eintritt in den Dampfkessel 3 über eine Leitung 16 vom Rauchgaskanal abgezweigt und über ein Heißgasfilter 17 zum Pyrolysereaktor 7 geführt ist.The pyrolysis reactor 7 is heated in the system according to FIG. 2 by means of a partial flow of hot flue gases, which branches off from the flue gas duct via a line 16 before entering the steam boiler 3 and is led to the pyrolysis reactor 7 via a hot gas filter 17.

Ansonsten stimmt die in Figur 2 schematisch dargestellte Anlage mit der zuerst beschriebenen Anlage überein. Die Beheizung des Pyrolysereaktors mit heißem Rauchgas der Müllverbrennungsanlage ist natürlich auch möglich, wenn-wie bei dem in Fig. 1 dargestellten Ausführungsbeispiel-die Pyrolysegase in der Müllfeuerung verbrannt werden. Otherwise, the system shown schematically in FIG. 2 corresponds to the system described first. It is of course also possible to heat the pyrolysis reactor with hot flue gas from the waste incineration plant if, as in the embodiment shown in FIG. 1, the pyrolysis gases are burned in the waste incineration plant.

Claims (5)

1. Vorrichtung zur Pyrolyse von Abfallstoffen, i nsbesondere von Altlasten, mit einem indirekt beheizten Pyrolysereaktor, von dem eine Pyrolysegasleitung zu einer Verbrennungskammer geführt ist, dadurch gekennzeichnet, daß die Verbrennungskammer die Feuerung (2) einer Müllverbrennungsanlage (1) ist.1. Apparatus for pyrolysis of waste materials, in particular contaminated sites, with an indirectly heated pyrolysis reactor, from which a pyrolysis gas line is led to a combustion chamber, characterized in that the combustion chamber is the furnace (2) of a waste incineration plant (1). 2. Vorrichtung zur Pyrolyse von Abfallstoffen, insbesondere von Altlasten, mit einem indirekt beheizten Pyrolysereaktor, von dem eine Pyrolysegasleitung zu einer Verbrennungskammer geführt ist, dadurch gekennzeichnet, daß eine von einer separaten Verbrennungskammer (14) für die Pyrolysegase ausgehende Abgasleitung (15) in den Rauchgaskanal der Feuerung (2) einer Müllverbrennungsanlage (1) mündet.2. Apparatus for pyrolysis of waste materials, in particular contaminated sites, with an indirectly heated pyrolysis reactor, from which a pyrolysis gas line is led to a combustion chamber, characterized in that an exhaust gas line (15) emanating from a separate combustion chamber (14) for the pyrolysis gases Flue gas duct of the furnace (2) of a waste incineration plant (1) opens. 3. Vorrichtung nach Anspruch 1 oder 2, gekennzeichnet durch eine von der Heizung des Pyrolysereaktors (7) ausgehende, innerhalb eines nachgeschalteten Dampfkessels (3) in den Rauchgaskanal mündende Abgasleitung (12).3. Apparatus according to claim 1 or 2, characterized by an from the heating of the pyrolysis reactor (7), within a downstream steam boiler (3) opening into the flue gas duct (12). 4. Vorrichtung nach einem der Ansprüche 1 bis 3, dadurch gekennzeichnet, daß der Pyrolysereaktor (7) fahrbar ist.4. Device according to one of claims 1 to 3, characterized in that the pyrolysis reactor (7) is mobile. 5. Vorrichtung nach einem der Ansprüche 1 bis 4, dadurch gekennzeichnet, daß eine vom Rauchgaskanal abgezweigte Leitung (16) zum Pyrolysereaktor (7) geführt ist.5. Device according to one of claims 1 to 4, characterized in that a branched from the flue gas duct (16) is guided to the pyrolysis reactor (7).
EP87106352A 1986-08-01 1987-05-02 Device for refuse pyrolysis Ceased EP0262291A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DE19863626106 DE3626106A1 (en) 1986-08-01 1986-08-01 DEVICE FOR PYROLYSIS OF WASTE
DE3626106 1986-08-01

Publications (1)

Publication Number Publication Date
EP0262291A1 true EP0262291A1 (en) 1988-04-06

Family

ID=6306506

Family Applications (1)

Application Number Title Priority Date Filing Date
EP87106352A Ceased EP0262291A1 (en) 1986-08-01 1987-05-02 Device for refuse pyrolysis

Country Status (3)

Country Link
US (1) US4774895A (en)
EP (1) EP0262291A1 (en)
DE (1) DE3626106A1 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1990000700A1 (en) * 1988-07-15 1990-01-25 Asea Brown Boveri Aktiengesellschaft Process for depolluting an appliance
EP0401460A1 (en) * 1989-06-05 1990-12-12 Masamoto Kaneko A method and apparatus for disposing waste
US5707592A (en) * 1991-07-18 1998-01-13 Someus; Edward Method and apparatus for treatment of waste materials including nuclear contaminated materials

Families Citing this family (22)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE3811820A1 (en) * 1987-08-03 1989-02-16 Siemens Ag METHOD AND SYSTEM FOR THERMAL WASTE DISPOSAL
DE3939745A1 (en) * 1989-08-04 1991-02-07 Ruhrkohle Umwelttechnik Gmbh Pyrolysis gas treatment - by indirectly heating contaminated soil and transferring to coking plant, etc.
US5129995A (en) * 1990-02-01 1992-07-14 General Motors Corporation Pyrolysis process and apparatus
US5198018A (en) * 1991-02-14 1993-03-30 General Motors Corporation Pyrolysis process and apparatus
DE4107200A1 (en) * 1991-03-06 1992-09-10 Siemens Ag Thermal redn. of industrial waste - by removing organic and inorganic material using low temp. distn. reactor, and treating waste material of low heat value
DE4420420A1 (en) * 1994-06-10 1995-12-14 Siemens Ag Process and plant for waste processing
DE4440984C2 (en) * 1994-11-17 1997-08-21 Siemens Ag Power plant with a gas turbine
DE4442136C2 (en) * 1994-11-26 1997-10-02 Hoelter Heinz Process for the combustion of fossil fuel and waste
DE19617034C1 (en) * 1994-11-26 1997-11-13 Hoelter Heinz Combustion process for fossil fuel and refuse
DE19619402C1 (en) * 1994-11-26 1998-01-22 Hoelter Heinz Fossil fuel and waste material burning method
US6966874B2 (en) * 1997-10-14 2005-11-22 Erth Technologies, Inc. Concentric tubular centrifuge
AU4873397A (en) * 1996-10-22 1998-05-15 Traidec S.A. Plant for thermolysis and energetic upgrading of waste products
FR2754883B1 (en) * 1996-10-22 1998-12-24 Traidec Sa PLANT FOR THE THERMOLYSIS DESTRUCTION OF MEAT FLOURS AND THE ENERGY RECOVERY OF THESE FLOURS
DE19646099C1 (en) * 1996-11-08 1997-12-11 Steinmueller Gmbh L & C Incineration of waste and fossil fuels
WO2002068569A2 (en) * 2001-02-28 2002-09-06 The Penn State Research Foundation Reducing nitrogen oxides and carbon loss from emissions
US20030127310A1 (en) * 2002-01-07 2003-07-10 Lemmons Donald W. Method and system for extracting hydrocarbon fuel products from waste material
US20070289507A1 (en) * 2006-06-16 2007-12-20 Alternative Power Solutions Inc. System, method and apparatus for pyrolizing waste material
US20090007484A1 (en) * 2007-02-23 2009-01-08 Smith David G Apparatus and process for converting biomass feed materials into reusable carbonaceous and hydrocarbon products
US7893307B2 (en) * 2007-02-23 2011-02-22 Smith David G Apparatus and process for converting feed material into reusable hydrocarbons
US20110036280A1 (en) * 2009-08-12 2011-02-17 Bruce Toase Waste processing system
AT520225B1 (en) * 2017-07-25 2021-08-15 Seccon Gmbh Process for the recovery of valuable materials from waste products
CN110606637B (en) * 2019-10-18 2024-06-11 南京永禾环保工程有限公司 Organic sludge pyrolysis furnace

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2432504A1 (en) 1974-07-04 1976-01-15 Karl Dipl Ing Kiener Gaseous fuel from waste - produced by low temp. carbonisation and gasification of the coke
AT346997B (en) 1976-06-11 1978-12-11 Potuzak Karl PROCESS FOR PROCESSING OF ACID TEER
DE2732418A1 (en) 1977-07-18 1979-02-01 Linde Ag Thermal treatment of refuse - by low temp. carbonisation and passing gases through fixed ceramic bed
US4206186A (en) 1975-02-06 1980-06-03 Holter Gesellschaft Fur Patentverwertungsverfahren Mbh Refuse pyrolysis
EP0111081A1 (en) 1979-06-25 1984-06-20 BKMI Industrieanlagen GmbH Process for the pyrolysis of waste materials
DE3310534A1 (en) * 1983-03-23 1984-10-04 C. Deilmann AG, 4444 Bad Bentheim DEVICE FOR RECOVERING ENERGY FROM PYROLIZABLE, CARBONATED WASTE MATERIALS, ALTERNATING COMPOSITION
US4485745A (en) * 1981-01-22 1984-12-04 Mannesmann Veba Umwelttechnik Gmbh Method for thermal processing of solid waste and the apparatus for carrying out the method
DE3400976A1 (en) * 1984-01-13 1985-08-01 Saarberg-Hölter-Umwelttechnik GmbH, 6600 Saarbrücken Energy system for environmentally friendly refuse degassing or coal-refuse degassing with following fluidised bed furnace and integrated low temperature carbonisation gas combustion chamber and heat exchanger

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2242012C3 (en) * 1972-08-23 1975-10-16 Mannesmann Ag, 4000 Duesseldorf Process for the joint disposal of industrial and household waste as well as sewage sludge
US3818869A (en) * 1973-01-02 1974-06-25 Combustion Eng Method of operating a combined gasification-steam generating plant
FR2331752A1 (en) * 1975-11-13 1977-06-10 Picard Du Chambon Michel Domestic waste treatment unit - has primary air heater with pre:drying and double walled heat converter interconnected by lift
US4432290A (en) * 1979-10-30 1984-02-21 The Agency Of Industrial Science And Technology Method of pyrolyzing organic material using a two-bed pyrolysis system
DE3447079A1 (en) * 1984-08-28 1986-03-06 Carl Still Gmbh & Co Kg, 4350 Recklinghausen Process for thermally treating contaminated soil

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2432504A1 (en) 1974-07-04 1976-01-15 Karl Dipl Ing Kiener Gaseous fuel from waste - produced by low temp. carbonisation and gasification of the coke
US4206186A (en) 1975-02-06 1980-06-03 Holter Gesellschaft Fur Patentverwertungsverfahren Mbh Refuse pyrolysis
AT346997B (en) 1976-06-11 1978-12-11 Potuzak Karl PROCESS FOR PROCESSING OF ACID TEER
DE2732418A1 (en) 1977-07-18 1979-02-01 Linde Ag Thermal treatment of refuse - by low temp. carbonisation and passing gases through fixed ceramic bed
EP0111081A1 (en) 1979-06-25 1984-06-20 BKMI Industrieanlagen GmbH Process for the pyrolysis of waste materials
US4485745A (en) * 1981-01-22 1984-12-04 Mannesmann Veba Umwelttechnik Gmbh Method for thermal processing of solid waste and the apparatus for carrying out the method
DE3310534A1 (en) * 1983-03-23 1984-10-04 C. Deilmann AG, 4444 Bad Bentheim DEVICE FOR RECOVERING ENERGY FROM PYROLIZABLE, CARBONATED WASTE MATERIALS, ALTERNATING COMPOSITION
DE3400976A1 (en) * 1984-01-13 1985-08-01 Saarberg-Hölter-Umwelttechnik GmbH, 6600 Saarbrücken Energy system for environmentally friendly refuse degassing or coal-refuse degassing with following fluidised bed furnace and integrated low temperature carbonisation gas combustion chamber and heat exchanger

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1990000700A1 (en) * 1988-07-15 1990-01-25 Asea Brown Boveri Aktiengesellschaft Process for depolluting an appliance
EP0401460A1 (en) * 1989-06-05 1990-12-12 Masamoto Kaneko A method and apparatus for disposing waste
US5707592A (en) * 1991-07-18 1998-01-13 Someus; Edward Method and apparatus for treatment of waste materials including nuclear contaminated materials

Also Published As

Publication number Publication date
US4774895A (en) 1988-10-04
DE3626106A1 (en) 1988-02-11

Similar Documents

Publication Publication Date Title
EP0262291A1 (en) Device for refuse pyrolysis
EP0509134B1 (en) Process and installation for the thermal processing of waste materials contaminated with organic components particularly scrap metal
DE4313102A1 (en) Method of reducing the amount of exhaust gas to eliminate NO¶x¶ emissions from combustion, preferably from waste incineration
EP0581918B1 (en) Process for melting down combustion residues in slag
DE2722767C2 (en) Process for the high temperature treatment of the gaseous and vaporous products resulting from the pyrolysis of household and industrial waste
WO1990003856A1 (en) Process and device for processing slag and other combustion residues from waste incineration plants
DE3635068C2 (en)
EP0442902B1 (en) A process and device for treating contaminated soil
EP0241657B1 (en) Apparatus for the disposal of toxic substances
EP0069752B1 (en) Thermal exploitation of refuse and plant for implementing such method
EP0862019B1 (en) Method and device for thermal treatment of fly ash from grate incinerators
DE19522457A1 (en) Method and device for treating household waste
WO2007069038A2 (en) Device for energetically utilizing solid waste
DE3716444C2 (en)
DE3728487C2 (en) Process for the pyrolytic treatment of waste or pollutants
EP0940166B1 (en) Processing of residual material and fumes
EP0815393B1 (en) Process for processing domestic waste
EP1203060A1 (en) Method of evaluating gas from a sedimentation basin
DE102010049379A1 (en) Device useful for continuous energetic recycling of solid waste, comprises material supply device with sealing device, drying zone, smoldering zone, coke discharge device, incinerating screw and thermal post-combustion device
DE4337421C1 (en) Multi-stage high-temperature incineration of waste materials having inert constituents and apparatus for carrying out this process
AT392961B (en) Process and device for heat recovery in the dewatering of sludges
DE19938034A1 (en) Cleaning of contaminated e.g. soils, slurries, production wastes, involves gasification of contaminants together with fuel, followed by oxidation of the gas
DE2928222A1 (en) METHOD FOR PURIFYING PROCESS GAS OF WASTE PYROLYSIS
DE19510390A1 (en) Carbonising waste to form e.g. pyrolysis prod.
EP0610521A1 (en) Process for the disposal of hazardous waste in a cement kiln

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

AK Designated contracting states

Kind code of ref document: A1

Designated state(s): DE FR IT NL

17P Request for examination filed

Effective date: 19880419

17Q First examination report despatched

Effective date: 19880722

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: 19890526

APAF Appeal reference modified

Free format text: ORIGINAL CODE: EPIDOSCREFNE

RIN1 Information on inventor provided before grant (corrected)

Inventor name: CHRISTMANN, ARVID