EP0722777B1 - Method for processing slag from waste incineration plants - Google Patents
Method for processing slag from waste incineration plants Download PDFInfo
- 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
- Authority
- EP
- European Patent Office
- Prior art keywords
- screening stage
- screen
- fraction
- stage
- slag
- 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.)
- Expired - Lifetime
Links
- 239000002893 slag Substances 0.000 title claims abstract description 39
- 238000000034 method Methods 0.000 title claims abstract description 17
- 238000012545 processing Methods 0.000 title claims abstract description 7
- 238000004056 waste incineration Methods 0.000 title claims description 8
- 239000002245 particle Substances 0.000 claims abstract description 9
- 229910052751 metal Inorganic materials 0.000 claims abstract description 6
- 239000002184 metal Substances 0.000 claims abstract description 6
- 239000000463 material Substances 0.000 claims abstract description 5
- 238000012216 screening Methods 0.000 claims description 23
- 238000001816 cooling Methods 0.000 claims description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 5
- -1 ferrous metals Chemical class 0.000 claims description 3
- 239000000126 substance Substances 0.000 claims description 3
- 238000010791 quenching Methods 0.000 claims description 2
- 230000000171 quenching effect Effects 0.000 claims description 2
- 238000010304 firing Methods 0.000 claims 3
- 230000007717 exclusion Effects 0.000 claims 2
- 238000003723 Smelting Methods 0.000 claims 1
- 150000002739 metals Chemical class 0.000 claims 1
- 238000002844 melting Methods 0.000 abstract description 6
- 230000008018 melting Effects 0.000 abstract description 6
- 239000005425 throughfall Substances 0.000 abstract 2
- 238000007873 sieving Methods 0.000 description 8
- 239000002956 ash Substances 0.000 description 6
- 206010012735 Diarrhoea Diseases 0.000 description 5
- 239000003344 environmental pollutant Substances 0.000 description 5
- 231100000719 pollutant Toxicity 0.000 description 5
- 238000000926 separation method Methods 0.000 description 5
- 239000002699 waste material Substances 0.000 description 5
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 4
- 238000002485 combustion reaction Methods 0.000 description 3
- 238000013461 design Methods 0.000 description 3
- 238000000227 grinding Methods 0.000 description 3
- 239000004566 building material Substances 0.000 description 2
- 238000001784 detoxification Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 1
- 230000000712 assembly Effects 0.000 description 1
- 238000000429 assembly Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000010881 fly ash Substances 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 239000003053 toxin Substances 0.000 description 1
- 231100000765 toxin Toxicity 0.000 description 1
- 108700012359 toxins Proteins 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03B—SEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
- B03B9/00—General arrangement of separating plant, e.g. flow sheets
- B03B9/04—General 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.
Landscapes
- 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
Description
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.
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
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
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
- 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
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.
- 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.
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
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
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
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
- 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)
- 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).
- 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).
- 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.
- 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).
- 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).
- 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.
- 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) .
- 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) .
- 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.
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
ID=26011768
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)
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)
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 |
-
1995
- 1995-10-30 TW TW084111469A patent/TW277101B/en not_active IP Right Cessation
- 1995-11-24 KR KR1019950043641A patent/KR100404642B1/en not_active IP Right Cessation
- 1995-12-07 US US08/568,837 patent/US5671688A/en not_active Expired - Lifetime
- 1995-12-11 DE DE59508422T patent/DE59508422D1/en not_active Expired - Lifetime
- 1995-12-11 PT PT95810783T patent/PT722777E/en unknown
- 1995-12-11 EP EP95810783A patent/EP0722777B1/en not_active Expired - Lifetime
- 1995-12-11 DK DK95810783T patent/DK0722777T3/en active
- 1995-12-11 AT AT95810783T patent/ATE193466T1/en active
- 1995-12-11 ES ES95810783T patent/ES2148466T3/en not_active Expired - Lifetime
-
1996
- 1996-01-18 JP JP00657696A patent/JP4149529B2/en not_active Expired - Lifetime
- 1996-01-19 NO NO960233A patent/NO309365B1/en unknown
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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