EP0722777B1 - Method for processing slag from waste incineration plants - Google Patents

Method for processing slag from waste incineration plants Download PDF

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Publication number
EP0722777B1
EP0722777B1 EP95810783A EP95810783A EP0722777B1 EP 0722777 B1 EP0722777 B1 EP 0722777B1 EP 95810783 A EP95810783 A EP 95810783A EP 95810783 A EP95810783 A EP 95810783A EP 0722777 B1 EP0722777 B1 EP 0722777B1
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EP
European Patent Office
Prior art keywords
screening stage
screen
fraction
stage
slag
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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.)
Expired - Lifetime
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EP95810783A
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German (de)
French (fr)
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EP0722777A1 (en
Inventor
Markus Bürgin
Bruno Carcer
Alfred Edlinger
Jean-Marc Martelli
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Martin GmbH fuer Umwelt und Energietechnik
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ABB Asea Brown Boveri Ltd
Asea Brown Boveri AB
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Priority claimed from DE19501830A external-priority patent/DE19501830A1/en
Priority claimed from DE1995108293 external-priority patent/DE19508293A1/en
Application filed by ABB Asea Brown Boveri Ltd, Asea Brown Boveri AB filed Critical ABB Asea Brown Boveri Ltd
Publication of EP0722777A1 publication Critical patent/EP0722777A1/en
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03BSEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
    • B03B9/00General arrangement of separating plant, e.g. flow sheets
    • B03B9/04General arrangement of separating plant, e.g. flow sheets specially adapted for furnace residues, smeltings, or foundry slags

Definitions

  • the invention relates to a method for processing of slag from waste incineration plants, in which the raw slag after passing the grate directly and without prior quenching in a water bath in at least two Fractions being separated, and these two fractions separated be treated further, the coarse fraction using a wet detoxifier is fed.
  • Such a processing method is, for example, from known from EP-0 437 679 B1.
  • the slag is released immediately after the furnace quenched in a wet purifier. Without additional Washing the slag can be lowered of the heavy metal content in the slag and not achieve it considerable amounts of toxins remain in the Slag.
  • EP-0 437 679 describes a method for treating residues a waste incineration plant known, in which the raw slag after passing through the grate in two Fractions is separated. The rust slag, boiler ash and rust diarrhea separated into two fractions. The fraction with components whose diameter is less than 100 to 300 mm, is melted in a separate melting furnace, the larger components of the grate and boiler ash are introduced into a wet slag remover.
  • the invention as characterized in the claims is, the task is based on a method of the beginning Specify the type mentioned, the simple separation of the Fine fraction enables air to be sealed off from the combustion chamber and cooling the second fraction with simple Means can be achieved.
  • Waste is burned in an incinerator 1.
  • the one there smoke gases and entrained particles are in a known manner a separation and filter stage 2 prepared, for example described and shown in EP-0 437 679 B1 is.
  • the grate ash gets directly from the grate into a first sieve stage 3. This is preferably a sieve conveyor grate educated.
  • Such devices are known and are in addition to other areas of application also in waste incineration plants used to screen the fine fraction (see brochure "Jost sieve conveyor grates" from Jost AG Maschinenfabrik, CH-3627 Heimberg, FOT 1.92 - 3000, undated).
  • this first Sieve stage is the separation of the raw slag into one Fine fraction with particle diameters smaller than 25 ... 35 mm and a corresponding coarse fraction.
  • the coarse fraction arrives as Sieve overflow in a wet slag 4 known design. This also provides the air seal on the coarse fraction side safe from the inside of the oven.
  • the fine fraction smaller than 25 ... 35 mm becomes a second sieving stage, e.g. a strainer screen or preferably one Vibrating sieve also of known design, supplied.
  • the second sieve stage 5 also the rust diarrhea from the Incinerator 1 are supplied, which in the figure by a dashed line is symbolized.
  • 2 mm is specially treated, e.g. melted in a melting furnace 7.
  • the sieve overflow of the second sieve stage 5 is in a grinding stage 6 mechanically crushed, e.g. in a ball mill.
  • the ground is then Good in a third (optional) screening stage 8, e.g. one Bar sieve, again separated into two fractions, namely one Fine fraction with particle size 0 ... 2 mm and a coarse fraction greater than 2 mm.
  • the fine fraction - it contains compared to Fine fraction 0 ... 2 mm of the second sieving stage 5 fewer pollutants - Is also fed to the melting furnace 7, the Coarse fraction - it essentially only consists of Inert substances - can be deposited.
  • a sorting stage between the grinding stage 6 and the third sieving stage 8 9 be interposed in order to already have metal parts, preferably separated according to ferrous and non-ferrous metals, and to discard other inert substances.
  • a discharge device preferably a screw conveyor 10 to provide the cooling and Air sealing functions combined.
  • This screw conveyor 10 also serves as an air seal the fine fraction side of the first sieve stage 3 opposite the incinerator 1 and also acts as a cooling device for the Ash cooling because of the design of a screw conveyor the goods to be conveyed over a large area with the screw conveyors in Comes into contact and the latter can simply be cooled. Should the screw conveyor 10 function as Airlock can prove to be inefficient, this can a double pendulum flap 11, also in the literature double-leaf butterfly valve, can be connected.
  • Burnt out slag 12 falls at the end of the grate 13 in a slag shaft 14, the walls of which so far are drawn down that they dip into the wet slag 4.
  • Deflection flap 15 is pivotally arranged. As a rule, this is Deflection flap 15 swung out of its vertical position and closes the direct access to the wet slag remover 4.
  • Burnt-out slag then becomes the first screening stage 3 supplied, which is preferably designed as a sieve conveyor grate is.
  • the sieve overflow of the first sieve stage 3 goes directly into the wet slag remover 4 below the sieve stage 3.
  • the arrangement is taken so that the sieve overflow into one Shaft 16 falls, the walls 17, 18 of which are pulled down so far are that they end below water level 19. On in this way the air is sealed off from the slag shaft 14 and thus reached the inside of the oven.
  • the sieve diarrhea is in one or more funnels 20, 21 caught under the first sieving stage 3 and over suitable Discharge devices 10, e.g. Screw conveyors or trough chain conveyors, carried out separately and dry and is as in Further described in connection with Fig.1.
  • suitable Discharge devices e.g. Screw conveyors or trough chain conveyors, carried out separately and dry and is as in Further described in connection with Fig.1.
  • the deflection flap 15 can be vertical be placed (shown in broken lines in Fig. 3), so that the entire slag is discharged conventionally (wet) can.

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  • Curing Cements, Concrete, And Artificial Stone (AREA)
  • Processing Of Solid Wastes (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
  • Combined Means For Separation Of Solids (AREA)
  • Fertilizers (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

The method involves raw slag being separated into at least two fractions and the first fraction has a particle size of up to 80 mm, pref. 32 mm in a first phase. The screen overflow from the first phase is supplied to the wet slag separator (4). The through-fall through the screen and through the fire rack is sent to a second screen phase (5) to separate the fine material. The screen overflow from the second phase is mechanically pulverised after sorting out the metal and inert materials and the through-fall from the second phase is sent to a melting furnace (7) for separate processing. A third screen phase (8) can be included.

Description

TECHNISCHES GEBIETTECHNICAL AREA

Die Erfindung bezieht sich auf ein Verfahren zum Aufbereiten von Schlacke aus Müllverbrennungsanlagen, bei welchem die Rohschlacke nach Passieren des Feuerungsrostes direkt und ohne vorheriges Abschrecken in einem Wasserbad in mindestens zwei Fraktionen getrennt wird, und diese beiden Fraktionen getrennt weiterbehandelt werden, wobei die Grobfraktion einem Nassentschlacker zugeführt wird.The invention relates to a method for processing of slag from waste incineration plants, in which the raw slag after passing the grate directly and without prior quenching in a water bath in at least two Fractions being separated, and these two fractions separated be treated further, the coarse fraction using a wet detoxifier is fed.

Ein derartiges Aufbereitungsverfahren ist beispielsweise aus der EP-0 437 679 B1 bekannt.Such a processing method is, for example, from known from EP-0 437 679 B1.

TECHNOLOGISCHER HINTERGRUND UND STAND DER TECHNIKTECHNOLOGICAL BACKGROUND AND PRIOR ART

Bei der Verbrennung von Siedlungsabfällen fallen etwa 250 kg Schlacke pro Tonne Müll als Reststoff an. Die anfallende Schlacke weist direkt nach dem Ofen Gehalte an Schadstoffen auf, welche ihre weitere Verwendung, z.B. als Baustoff, verhindern. Die Ablagerung der Schlacke in Deponien führt zu einer Gefährdung der Umwelt, wenn nicht besondere Vorkehrungen getroffen werden, z.B. das Auffangen des Sickerwassers.When municipal waste is incinerated, about 250 kg fall Slag per ton of waste as a waste. The accruing Slag contains pollutants immediately after the furnace on their further use, e.g. as a building material, prevent. The deposition of the slag in landfills leads to a Danger to the environment, if not special precautions be hit, e.g. collecting the leachate.

Normalerweise wird die Schlacke unmittelbar nach dem Ofenaustritt in einem Nassentschlacker abgeschreckt. Ohne zusätzliches Waschen der Schlacke lässt sich dabei eine Absenkung des Schwermetallgehalts in der Schlacke nicht erzielen, und es es verbleiben erhebliche Anteile von Giftstoffen in der Schlacke.Usually, the slag is released immediately after the furnace quenched in a wet purifier. Without additional Washing the slag can be lowered of the heavy metal content in the slag and not achieve it considerable amounts of toxins remain in the Slag.

Aus der EP-0 437 679 ist ein Verfahren zum Behandeln von Rückständen einer Abfallverbrennungsanlage bekannt, bei welchem die Rohschlacke nach Passieren des Feuerungsrostes in zwei Fraktionen getrennt wird. Dabei wird die Rostschlacke, Kesselasche und der Rostdurchfall in zwei Fraktionen getrennt. Die Fraktion mit Bestandteilen, deren Durchmesser kleiner als 100 bis 300 mm ist, wird in einem separaten Schmelzofen geschmolzen, die grösseren Bestandteile der Rost- und Kesselasche werden in einen Nassentschlacker eingeleitet.EP-0 437 679 describes a method for treating residues a waste incineration plant known, in which the raw slag after passing through the grate in two Fractions is separated. The rust slag, boiler ash and rust diarrhea separated into two fractions. The fraction with components whose diameter is less than 100 to 300 mm, is melted in a separate melting furnace, the larger components of the grate and boiler ash are introduced into a wet slag remover.

Diese vergleichsweise grobe Klassierung führt letzten Endes dazu, dass dem Schmelzofen Bestandteile zugeführt werden, die eigentlich eine derartige Sonderbehandlung nicht benötigen.This comparatively rough classification ultimately leads to the fact that components are supplied to the melting furnace that actually do not need such special treatment.

In der EP-Patentschrift 0 372 039 wird nun erstmals ein Weg zur Aufbereitung von Schlacke aus Kehricht- und Abfallverbrennungsöfen aufgezeigt, wobei die Schlacke nach dem Ofen direkt und ohne vorherige Abschreckung in einem Wasserbad der Grobreinigung (Entfernen unverbrannten Grobgutes und magnetischer Teile) zugeführt wird. Danach wird die grob gereinigte Schlacke in mindestens zwei Fraktionen getrennt und einer Fraktion alle Partikel, welche kleiner als 2 mm sind, zugewiesen.In EP patent 0 372 039 a way is now for the first time for processing slag from waste and incinerators shown, the slag directly after the furnace and without prior deterrence in a water bath Coarse cleaning (removing unburned coarse material and magnetic Parts) is supplied. Then the roughly cleaned Slag separated into at least two fractions and one Fraction assigned to all particles that are smaller than 2 mm.

Diesem bekannten Verfahren liegt die Erkenntnis zugrunde, dass die Feinfraktion den grössten Teil der ursprünglich in der Schlacke beim Schlackenaustritt enthaltenen Schadstoffe enthält. Sie wird einer Sonderbehandlung zugeführt. Die Grobfraktion hingegen ist für die direkte Verwendung als Baustoff oder zur Ablagerung in Deponien geeignet. This known method is based on the knowledge that the fine fraction most of the originally in the Contains slag at the pollutants contained in the slag outlet. It will be given special treatment. The coarse fraction however, is for direct use as a building material or suitable for disposal in landfills.

Bei der technischen Realisierung des Verfahrens nach der EP-Patentschrift 0 372 039 bereitet es nun gewisse technische Schwierigkeiten, einerseits den Feinanteil 0...2 mm abzutrennen - herkömmliche Siebförderer oder andere Klassiereinrichtungen neigen zur Verstopfung, andererseits muss der Luftabschluss gegen den Verbrennungsraum hin gewährleistet sein, und auch die Kühlung der Grobfraktion ist problematisch.In the technical implementation of the method according to the EP patent 0 372 039 it now prepares certain technical Difficulties, on the one hand, to separate the fine fraction 0 ... 2 mm - conventional screen conveyors or other classifying devices tend to clog, on the other hand, the air seal be guaranteed against the combustion chamber, and cooling the coarse fraction is also problematic.

KURZE DARSTELLUNG DER ERFINDUNGSUMMARY OF THE INVENTION

Der Erfindung, wie sie in den Patentansprüchen gekennzeichnet ist, liegt die Aufgabe zugrunde, ein Verfahren der eingangs genannten Gattung anzugeben, das die einfache Abtrennung des Feinanteils ermöglicht, ein Luftabschluss gegenüber dem Verbrennungsraum und die Abkühlung der zweiten Fraktion mit einfachen Mitteln erzielt werden kann.The invention as characterized in the claims is, the task is based on a method of the beginning Specify the type mentioned, the simple separation of the Fine fraction enables air to be sealed off from the combustion chamber and cooling the second fraction with simple Means can be achieved.

Der Erfindung liegt dabei die Idee zugrunde, den mit Schadstoffen belasteten Feinanteil auf "trockenem" Wege abzutrennen, und den schadstoffarmen Grobanteil "nass" weiterzubearbeiten. Diese Vorgehensweise - man könnte sie stichwortartig mit "Halbtrocken-Entschlackung" bezeichnen - bietet in Kombination mit der zweistufigen Gewinnung des Feinanteils 0...2 mm zahlreiche Vorteile:

  • einfache Abtrennung des Feinanteils mit herkömmlichen Klassiereinrichtungen
  • einfach durchzuführender Luftabschluss gegenüber dem Verbrennungsraum, und zwar für beide Partikelströme, wobei insbesondere die Nassentschlackung der Grobfraktion um 30 mm mit bewährter Technologie durchgeführt werden kann
Die Erfindung und weitere mit ihr erzielbare Vorteile werden nachstehend anhand eines Ausführungsbeispiels näher erläutert. The invention is based on the idea of separating the fine fraction contaminated with pollutants in a "dry" way and further processing the coarse fraction low in pollutants "wet". This procedure - you could call it "semi-dry detoxification" - offers in combination with the two-stage extraction of the fine fraction 0 ... 2 mm numerous advantages:
  • easy separation of the fine fraction with conventional classifying devices
  • air can be easily sealed off from the combustion chamber for both particle streams, whereby in particular the wet detoxification of the coarse fraction by 30 mm can be carried out with proven technology
The invention and further advantages which can be achieved with it are explained in more detail below on the basis of an exemplary embodiment.

KURZE BESCHREIBUNG DER ZEICHNUNGBRIEF DESCRIPTION OF THE DRAWING

In der Zeichnung ist ein Ausführungsbeispiel der Erfindung schematisch dargestellt; dabei zeigt

Fig. 1
eine aus einzelnen Baugruppen zusammengestellten Anlage zum Aufbereiten von Schlacke aus Müllverbrennungsanlagen;
Fig.2
einen vereinfachten Längsschnitt durch einen Teil einer Müllverbrennungsanlage;
Fig.3
einen mehr ins Detail gegehenden Schnitt durch die erste Siebstufe der Anlage gemäss Fig.2.
In the drawing, an embodiment of the invention is shown schematically; shows
Fig. 1
a system composed of individual assemblies for processing slag from waste incineration plants;
Fig. 2
a simplified longitudinal section through part of a waste incineration plant;
Fig. 3
a more detailed section through the first screening stage of the system according to Fig. 2.

WEGE ZUR AUSFÜHRUNG DER ERFINDUNGWAYS OF CARRYING OUT THE INVENTION

In einem Verbrennungsofen 1 wird Müll verbrannt. Die dabei entstehenden Rauchgase und mitgerissene Partikel (Flugasche als Kesselasche und Filterasche) werden in bekannter Weise in einer Abscheide- und Filterstufe 2 aufbereitet, wie es beispielsweise in der EP-0 437 679 B1 beschrieben und dargestellt ist. Die Rostasche gelangt unmittelbar vom Ofenrost in eine erste Siebstufe 3. Diese ist vorzugsweise als Siebförderrost ausgebildet. Derartige Einrichtungen sind bekannt und werden neben anderen Einsatzgebieten auch in Kehrrichtverbrennungsanlagen zum Aussieben des Feinanteils eingesetzt (vgl. Prospekt "Jost Siebförderroste" der Firma Jost AG Maschinenfabrik, CH-3627 Heimberg, FOT 1.92 - 3000, undatiert). In dieser ersten Siebstufe erfolgt die Auftrennung der Rohschlacke in eine Feinfraktion mit Partikeldurchmessern kleiner 25...35 mm und eine entsprechende Grobfraktion. Die Grobfraktion gelangt als Siebüberlauf in einen Nassentschlacker 4 bekannter Bauart. Dieser stellt gleichzeitig den Luftabschluss auf der Grobfraktionseite gegenüber dem Ofeninneren sicher. Die Feinfraktion kleiner 25...35 mm wird einer zweiten Siebstufe, z.B einem Spannwellensieb oder vorzugsweise einem Schwingsieb ebenfalls bekannter Bauart, zugeführt. Optional kann der zweiten Siebstufe 5 auch der Rostdurchfall aus dem Verbrennungsofen 1 zugeführt werden, was in der Figur durch eine strichliert gezeichnete Linie symbolisiert ist. Der Siebdurchfall der zweiten Siebstufe 5 mit Partikeln von 0...2 mm wird sonderbehandelt, z.B. in einem Schmelzofen 7 eingeschmolzen. Der Siebüberlauf der zweiten Siebstufe 5 wird in einer Mahlstufe 6 mechanisch zerkleinert, z.B. in einer Kugelmühle. Im Beispielsfall wird anschliessend das gemahlene Gut in einer dritten (optionalen) Siebstufe 8, z.B. einem Stabsieb, wiederum in zwei Fraktionen getrennt, nämlich eine Feinfraktion mit Partikelgrösse 0...2 mm und eine Grobfraktion grösser 2 mm. Die Feinfraktion - sie enthält im Vergleich zur Feinfraktion 0... 2 mm der zweiten Siebstufe 5 weniger Schadstoffe - wird ebenfalls dem Schmelzofen 7 zugeführt, die Grobfraktion - sie besteht im wesentlichen nur noch aus Inertstoffen - kann deponiert werden. Unter Umständen kann zwischen der Mahlstufe 6 und der dritten Siebstufe 8 eine Sortierstufe 9 zwischengeschaltet sein, um hier schon Metallteile, vorzugsweise getrennt nach Eisen- und Nichteisenmetallen, und andere Inertstoffe auszusondern.Waste is burned in an incinerator 1. The one there smoke gases and entrained particles (fly ash as kettle ash and filter ash) are in a known manner a separation and filter stage 2 prepared, for example described and shown in EP-0 437 679 B1 is. The grate ash gets directly from the grate into a first sieve stage 3. This is preferably a sieve conveyor grate educated. Such devices are known and are in addition to other areas of application also in waste incineration plants used to screen the fine fraction (see brochure "Jost sieve conveyor grates" from Jost AG Maschinenfabrik, CH-3627 Heimberg, FOT 1.92 - 3000, undated). In this first one Sieve stage is the separation of the raw slag into one Fine fraction with particle diameters smaller than 25 ... 35 mm and a corresponding coarse fraction. The coarse fraction arrives as Sieve overflow in a wet slag 4 known design. This also provides the air seal on the coarse fraction side safe from the inside of the oven. The fine fraction smaller than 25 ... 35 mm becomes a second sieving stage, e.g. a strainer screen or preferably one Vibrating sieve also of known design, supplied. Optional can the second sieve stage 5 also the rust diarrhea from the Incinerator 1 are supplied, which in the figure by a dashed line is symbolized. The Sieving diarrhea of the second sieving stage 5 with particles from 0 ... 2 mm is specially treated, e.g. melted in a melting furnace 7. The sieve overflow of the second sieve stage 5 is in a grinding stage 6 mechanically crushed, e.g. in a ball mill. In the example, the ground is then Good in a third (optional) screening stage 8, e.g. one Bar sieve, again separated into two fractions, namely one Fine fraction with particle size 0 ... 2 mm and a coarse fraction greater than 2 mm. The fine fraction - it contains compared to Fine fraction 0 ... 2 mm of the second sieving stage 5 fewer pollutants - Is also fed to the melting furnace 7, the Coarse fraction - it essentially only consists of Inert substances - can be deposited. Under certain circumstances a sorting stage between the grinding stage 6 and the third sieving stage 8 9 be interposed in order to already have metal parts, preferably separated according to ferrous and non-ferrous metals, and to discard other inert substances.

Der Transport des noch sehr heissen Siebdurchfalls der ersten Siebstufe 3 zur zweiten Siebstufe 5 erfolgt normalerweise durch an sich bekannte Fördereinrichtungen. Vorzugsweise sieht hier eine Weiterbildung der Erfindung vor, ein Austragsorgan, vorzugsweise einen Schneckenförderer 10, vorzusehen, das Kühlund Lufabschlussfunktionen auf sich vereinigt. Dieser Schneckenförderer 10 dient gleichzeitig als Luftabschlussorgan auf der Feinanteilseite der ersten Siebstufe 3 gegenüber dem Verbrennungsofen 1 und wirkt aber auch als Kühlapparat für die Aschenkühlung, weil bei einem Schneckenförderer bauartbeding das zu fürdernde Gut grossflächig mit den Förderschnecken in Berührung kommt und letztere einfach gekühlt werden können. Sollte sich der Schneckenförderer 10 in seiner Funktion als Luftabschlussorgan als zu wenig effizient erweisen, kann diesem eine Doppelpendelklappe 11, in der Literatur auch mit zweiflügeliger Absperrklappe bezeichnet, nachgeschaltet werden.The transport of the still very hot sieve diarrhea of the first Screening stage 3 to second screening stage 5 is normally carried out through known funding facilities. Preferably sees here is a further development of the invention, a discharge device, preferably a screw conveyor 10 to provide the cooling and Air sealing functions combined. This screw conveyor 10 also serves as an air seal the fine fraction side of the first sieve stage 3 opposite the incinerator 1 and also acts as a cooling device for the Ash cooling because of the design of a screw conveyor the goods to be conveyed over a large area with the screw conveyors in Comes into contact and the latter can simply be cooled. Should the screw conveyor 10 function as Airlock can prove to be inefficient, this can a double pendulum flap 11, also in the literature double-leaf butterfly valve, can be connected.

Wie aus Fig.2 und 3 hervorgeht, lässt sich das beschriebene "Halbtrockenverfahren" ohne grossen Aufwand in eine Müllverbrennungsanlage integrieren. In diesen beiden Figuren sind dabei nur die Komponenten dargestellt, welche den Kern der Erfindung betreffen, nämlich Abtrennen der ersten Fraktion mit einer Partikelgrösse um 30 mm in der ersten Siebstufe und Nassentschlackung des Siebüberlaufs dieser Siebstufe.As can be seen from FIGS. 2 and 3, this can be described "Semi-dry process" without much effort in a waste incineration plant integrate. In these two figures are only the components that represent the core of the Invention relate to, namely separating the first fraction with a particle size around 30 mm in the first sieving stage and Wet purification of the sieve overflow of this sieving stage.

Ausgebrannte Schlacke 12 (grob/fein) fällt am Ende des Rostes 13 in einen Schlackenschacht 14, dessen Wände so weit nach unten gezogen sind, dass sie in den Nassentschlacker 4 hineintauchen. In der Seitenwand des Schlackenschachtes ist eine Umlenkklappe 15 schwenkbar angeordnet. Im Regelfall ist diese Umlenkklappe 15 aus ihrer senkrechten Position ausgeschwenkt und verschliesst den direkten Zugang zum Nassentschlacker 4. Ausgebrannte Schlacke wird dann direkt der ersten Siebstufe 3 zugeführt, die vorzugsweise als Siebförderrost ausgebildet ist. Der Siebüberlauf der ersten Siebstufe 3 gelangt direkt in den Nassentschlacker 4 unterhalb der Siebstufe 3. Die Anordnung ist dabei so getroffen, dass der Siebüberlauf in einen Schacht 16 fällt, dessen Wände 17, 18 so weit nach unten gezogen sind, dass sie unterhalb des Wasserniveaus 19 enden. Auf diese Weise wird der Luftabschluss gegenüber dem Schlackenschacht 14 und damit dem Ofeninneren erreicht.Burnt out slag 12 (coarse / fine) falls at the end of the grate 13 in a slag shaft 14, the walls of which so far are drawn down that they dip into the wet slag 4. There is one in the side wall of the slag shaft Deflection flap 15 is pivotally arranged. As a rule, this is Deflection flap 15 swung out of its vertical position and closes the direct access to the wet slag remover 4. Burnt-out slag then becomes the first screening stage 3 supplied, which is preferably designed as a sieve conveyor grate is. The sieve overflow of the first sieve stage 3 goes directly into the wet slag remover 4 below the sieve stage 3. The arrangement is taken so that the sieve overflow into one Shaft 16 falls, the walls 17, 18 of which are pulled down so far are that they end below water level 19. On in this way the air is sealed off from the slag shaft 14 and thus reached the inside of the oven.

Der Siebdurchfall wird in einem oder mehreren Trichtern 20, 21 unter der ersten Siebstufe 3 aufgefangen und über geeignete Austragvorrichtungen 10, z.B. Schneckenförderern oder Trogkettenförderern, separat und trocken ausgetragen und wird wie im Zusammenhang mit Fig.1 beschrieben weiterbehandelt. Im Störder ersten Siebstufe 3 kann die Umlenkklappe 15 vertikal gestellt werden (strichliert in Fig.3 eingezeichnet), so dass die gesamte Schlacke konventionell (nass) ausgetragen werden kann.The sieve diarrhea is in one or more funnels 20, 21 caught under the first sieving stage 3 and over suitable Discharge devices 10, e.g. Screw conveyors or trough chain conveyors, carried out separately and dry and is as in Further described in connection with Fig.1. In the conveyor first screening stage 3, the deflection flap 15 can be vertical be placed (shown in broken lines in Fig. 3), so that the entire slag is discharged conventionally (wet) can.

BEZEICHNUNGSLISTELIST OF DESIGNATIONS

11
VerbrennungsofenIncinerator
22nd
Abscheide- und FilterstufeSeparation and filter stage
33rd
erste Siebstufefirst sieve stage
44th
NassentschlackerWet purifier
55
zweite Siebstufesecond sieve stage
66
MahlstufeGrinding stage
77
SchmelzofenMelting furnace
88th
dritte Siebstufethird sieve stage
99
optionale Sortierstufeoptional sorting level
1010th
SchenckenfördererSchencken conveyor
1111
DoppelpendelklappeDouble swing flap
1212th
ausgebrannte Schlackeburnt out slag
1313
Rostrust
1414
SchlackenschachtSlag shaft
1515
UmlenkklappeDeflection flap
1616
SchachtShaft
17,1817.18
Wände von 16Walls of 16
1919th
Wasserniveau in 4Water level in 4
20,2120.21
AuffangtrichterCollecting funnel

Claims (9)

  1. Method for processing slag from waste incineration plants, in which the raw slag, after passing over the firing grate, is separated into at least two fractions in a water bath, directly and without previous quenching, and these two fractions are further treated separately, the coarse fraction being fed to a wet-slag remover (4), characterized in that the first fraction, with a particle size up to 80 mm, preferably up to about 32 mm, is separated in a first screening stage (3), and the screen overflow from the first screening stage (3) is fed to the wet-slag removal means, in that the screen through fraction and, if appropriate, the grate through fraction from the firing grate are fed to a second screening stage (5) for the purpose of separating the fine component 0...2 mm, in that the screen overflow from the second screening stage, if appropriate following the screening out of metallic and inert substances, is comminuted mechanically and the screen through fraction from the second screening stage (5) is fed to a special treatment means, for example a smelting furnace (7).
  2. Method according to Claim 1, characterized in that the screen overflow from the second screening stage, after mechanical comminution, is fed to a third screening stage (8), and the fine component 0...2 mm from this third screening stage is likewise fed to a special treatment means, preferably being specially treated together with the screen through fraction obtained in the second screening stage (5).
  3. Method according to Claim 1 or 2, characterized in that the first screening stage (3) is integrated into the firing grate of the incineration furnace (1) or directly follows it.
  4. Method according to Claim 3, characterized in that a mesh screen conveyor is used as the first screening stage (3) and/or a vibrating screen is used as the second screening stage (5).
  5. Method according to Claim 3 or 4, characterized in that the screen overflow from the first screening stage (3) is fed directly to the wet-slag remover (4).
  6. Method according to one of Claims 1 to 5, characterized in that the screen through fraction from the first screening stage (3) is transported to the second screening stage (5) by means of a discharge unit (10), which at the same time acts as an air exclusion unit.
  7. Method according to Claim 6, characterized in that cooling of the material to be discharged is carried out at the same time in the discharge unit (10) .
  8. Method according to Claim 6 or 7, characterized in that the air exclusion is additionally brought about by means of a double swinging flap arrangement (12), which is connected downstream of the discharge unit (10) .
  9. Method according to one of Claims 2 to 8, characterized in that a sorting stage (9) is connected in between the second (5) and third (8) screening stages, in order to remove metals, preferably separated into ferrous metals and non-ferrous metals, and other inert materials.
EP95810783A 1995-01-21 1995-12-11 Method for processing slag from waste incineration plants Expired - Lifetime EP0722777B1 (en)

Applications Claiming Priority (4)

Application Number Priority Date Filing Date Title
DE19501830 1995-01-21
DE19501830A DE19501830A1 (en) 1995-01-21 1995-01-21 Method for preparing slag from rubbish incinerators
DE1995108293 DE19508293A1 (en) 1995-03-09 1995-03-09 Method for preparing slag from rubbish incinerators
DE19508293 1995-03-09

Publications (2)

Publication Number Publication Date
EP0722777A1 EP0722777A1 (en) 1996-07-24
EP0722777B1 true EP0722777B1 (en) 2000-05-31

Family

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Family Applications (1)

Application Number Title Priority Date Filing Date
EP95810783A Expired - Lifetime EP0722777B1 (en) 1995-01-21 1995-12-11 Method for processing slag from waste incineration plants

Country Status (11)

Country Link
US (1) US5671688A (en)
EP (1) EP0722777B1 (en)
JP (1) JP4149529B2 (en)
KR (1) KR100404642B1 (en)
AT (1) ATE193466T1 (en)
DE (1) DE59508422D1 (en)
DK (1) DK0722777T3 (en)
ES (1) ES2148466T3 (en)
NO (1) NO309365B1 (en)
PT (1) PT722777E (en)
TW (1) TW277101B (en)

Families Citing this family (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0908674A1 (en) * 1997-10-13 1999-04-14 Asea Brown Boveri AG Process for the combustion of refuse in an incinerator and for processing the residues from the incineration
DE59707290D1 (en) 1997-10-13 2002-06-20 Alstom Process for treating slag and / or ash from the thermal treatment of waste
DE10213790B4 (en) * 2002-03-27 2006-05-24 Martin GmbH für Umwelt- und Energietechnik Waste incineration method in a waste incineration plant
DE10213788B4 (en) * 2002-03-27 2007-04-26 Martin GmbH für Umwelt- und Energietechnik Method for influencing the properties of combustion residues from an incinerator
DE10213789B4 (en) * 2002-03-27 2006-04-20 Martin GmbH für Umwelt- und Energietechnik Process for the treatment of combustion residues of a combustion plant
DE10306132A1 (en) * 2003-02-14 2004-08-26 Gerhard Scherer Treatment of slag from waste incineration plants
RU2359930C2 (en) * 2007-07-04 2009-06-27 Техком Гмбх Treatment method of slag after its outlet from metallurgycal tank and device for its implementation
US9566587B2 (en) 2012-10-12 2017-02-14 Blue Sky Mines Ltd. Methods of and systems for treating incinerated waste
WO2015007314A1 (en) 2013-07-17 2015-01-22 Georg Schons Method for processing slag in waste incineration plants, and waste incineration plant
CA2961423C (en) * 2014-09-16 2019-02-26 Hitachi Zosen Inova Ag Method and device for processing slag occurring in a combustion chamber of a refuse incineration plant
DE102014115854A1 (en) 2014-10-30 2016-05-04 Georg Schons Method for handling slag and rust diarrhea of a waste incineration plant and waste incineration plant

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0368962B1 (en) * 1988-05-31 1993-03-10 Leo Schwyter Ag Process and device for cleaning slag from refuse incinerators
JP2857437B2 (en) * 1988-06-16 1999-02-17 アセア・ブラウン・ボベリ・アクチエンゲゼルシヤフト Method and apparatus for preparing slag from waste combustion furnace
DE3939344C2 (en) * 1989-11-29 1993-11-04 Babcock Anlagen Gmbh METHOD FOR TREATING RESIDUES OF A WASTE COMBUSTION PLANT AND WASTE COMBUSTION PLANT FOR CARRYING OUT THE METHOD
DE4117444C2 (en) * 1991-05-28 1993-11-11 Babcock Anlagen Gmbh Process for treating residues from a waste incineration plant and waste incineration plant for carrying out the process
US5356082A (en) * 1991-06-21 1994-10-18 Resource Recycling, Inc. Incinerated waste material treatment

Also Published As

Publication number Publication date
TW277101B (en) 1996-06-01
DE59508422D1 (en) 2000-07-06
PT722777E (en) 2000-11-30
JPH08229430A (en) 1996-09-10
NO309365B1 (en) 2001-01-22
EP0722777A1 (en) 1996-07-24
KR960028976A (en) 1996-08-17
KR100404642B1 (en) 2004-01-28
NO960233D0 (en) 1996-01-19
NO960233L (en) 1996-07-22
ATE193466T1 (en) 2000-06-15
DK0722777T3 (en) 2000-10-09
ES2148466T3 (en) 2000-10-16
US5671688A (en) 1997-09-30
JP4149529B2 (en) 2008-09-10

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