EP0347519B1 - Process for eliminating waste products resulting from the recycling of waste paper in the paper and cardboard industry - Google Patents
Process for eliminating waste products resulting from the recycling of waste paper in the paper and cardboard industry Download PDFInfo
- Publication number
- EP0347519B1 EP0347519B1 EP89102100A EP89102100A EP0347519B1 EP 0347519 B1 EP0347519 B1 EP 0347519B1 EP 89102100 A EP89102100 A EP 89102100A EP 89102100 A EP89102100 A EP 89102100A EP 0347519 B1 EP0347519 B1 EP 0347519B1
- Authority
- EP
- European Patent Office
- Prior art keywords
- trash
- substance
- waste
- paper
- dried
- 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
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Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/002—Incineration of waste; Incinerator constructions; Details, accessories or control therefor characterised by their grates
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/008—Incineration of waste; Incinerator constructions; Details, accessories or control therefor adapted for burning two or more kinds, e.g. liquid and solid, of waste being fed through separate inlets
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/04—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment drying
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2203/00—Furnace arrangements
- F23G2203/107—Furnace arrangements with vibrating grate
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2206/00—Waste heat recuperation
- F23G2206/10—Waste heat recuperation reintroducing the heat in the same process, e.g. for predrying
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2209/00—Specific waste
- F23G2209/22—Waste papers
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2209/00—Specific waste
- F23G2209/28—Plastics or rubber like materials
Definitions
- the invention relates to a method for removing trapping and residual materials occurring in the paper and cardboard industry during the recycling of waste paper, the trapping materials being dewatered (see e.g. DE-B-2 339 591).
- the raw material i.e. the paper fiber damaged.
- a paper fiber can be reused four to six times before it breaks.
- the resulting pieces of fiber accumulate in the production water and are collected via flotation plants.
- the concentrate mainly consists of wood and cellulose fibers, which are called capture materials.
- the residues consist of more than 95% by weight of plastic in the form of adhesive tapes, foils, etc., which are separated directly from the recycling process and are usually taken to the capture materials independently.
- residual substances are also understood to mean what is known as a “reject”.
- the trapping materials have only been dewatered mechanically to a dry content of about 35% and then sent to a landfill.
- the residues were also deposited independently of this. Taking into account that about 10% of the waste paper used is in the form of catch and residues, whereby the weight ratio of catch materials to residues is about 9: 1, and for ecological reasons an increased use of waste paper is required and on the other hand the available landfill capacities become scarcer, it becomes immediately clear that other ways of eliminating the catch and residues must be found.
- the invention has for its object to find measures for eliminating the catch and residues that are no longer burdened by disposal or landfill problems.
- the invention teaches in procedural terms that the pre-dewatered capture materials are dried to a residual water content of at least 25% by weight, based on the amount of capture material, and then continuously stratified, covered with the residues and burned with underwind to form slag will.
- the invention is based on the knowledge that the pre-dewatered capture materials after further drying without any problems, i.e. can be burned with the residual materials without primary energy if the combustion takes place in the form of a stratification, the lower layer being formed by the catching materials and the upper layer being formed by the residual materials.
- the resulting slag can be used for other purposes, in any case it does not represent a landfill problem anymore.
- the combustion gases formed during the combustion of the trapping and residual materials are subjected to heat recovery, in particular used for generating steam; here the resulting heat of combustion is used. It is advisable to dry the pre-dewatered capture materials to a residual water content of at least 20% by weight, based on the amount of capture material; then the process is not as sensitive to the combustion of the residues.
- the water vapor generated can be used in papermaking, but it is also possible, as in the preferred embodiment, to pre-dry the pre-dewatered capture materials by heating with at least some of the water vapor generated. Alone or in combination, however, the pre-dewatered capture materials can also be dried with at least some of the combustion gases generated during the combustion of the capture and residual materials. In this context, one can get rid of possible exhaust air problems in a particularly simple manner by subjecting the exhaust air generated during the drying of the trapping materials to a post-combustion together with the combustion gases generated during the combustion of the trapping and residual materials.
- the dried and layered capture materials can be covered with up to 100% by weight of residual materials, based on the amount of solids, and fed to the combustion; optimal conditions are, however, provided that the dried and layered capture materials are covered with a maximum of 15 wt.
- the combustion gases are expediently subjected to dedusting. In any case, it is advisable to incorporate fly ash from the combustion gases into the slag. In any case, this slag can easily be used as a building material, so that there are no more landfill problems at all.
- the only drawing figure shows schematically a device for removing trapping materials on the one hand and residual materials on the other hand, as they occur in the paper and cardboard industry in the recycling of waste paper.
- the capture materials are pre-dewatered in the usual form.
- a combustion furnace 1 with an inclined vibrating grate 2 and underwind feed 3 can be seen in the main.
- a further feed metering device 7 is provided for the residue materials behind the feed metering device 4, which are fed in without further processing.
- a slag collector 8 can be seen under the vibrating grate 2.
- a heat recovery unit in the form of a steam generator 9 is connected downstream of the combustion furnace 1 in the flow direction of the combustion gases. This is connected to the dryer 6 via a schematically indicated line 10.
- the combustion furnace 1, seen in the flow direction of the combustion gases is provided behind the vibrating grate 2 with a combustion gas branch line 11 led to the dryer 6 and the dryer 6 is connected with its exhaust air outlet to a post-combustion chamber 12 of the combustion furnace.
- This post-combustion chamber 12 can be provided with secondary air supplies (not shown) to reduce the CO content of the combustion gases and to support post-combustion.
- the steam generator 9 is followed by a conventional dry dedusting unit 13 and a chimney 14.
- the dry dedusting unit 13 and the steam generator 9 each have a fly ash outlet 15 and 16, respectively, which are connected to the combustion furnace 1 via a line 17.
- Line 17 opens in Slag area of the vibrating grate 2 in the incinerator 1. The fly ash returned to this extent is thus fed with secondary air in the area of the slag zone and integrated into the slag.
- the mode of operation of the device described can easily be seen in the figure.
- the pre-dewatered capture materials are dried in the dryer 6 to a residual water content of at least 25% by weight, in particular 20% by weight, based on the amount of capture material.
- This drying can be dried by heating with at least a part of the water vapor generated and / or with at least a part of the combustion gases generated during the combustion of the capture and residual materials.
- the exhaust air produced in the latter case is then subjected to post-combustion together with the combustion gases in the post-combustion chamber 12.
- the dried capture materials are continuously layered and placed on the vibrating grate 2.
- the residues are covered with a layer and the whole is then incinerated with the formation of slag.
- the fly ash from the dry dedusting is added to this slag.
- the wet slag is used in the construction industry.
Landscapes
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Processing Of Solid Wastes (AREA)
- Paper (AREA)
Abstract
Description
Die Erfindung betrifft ein Verfahren zum Beseitigen von in der Papier- und Kartonindustrie beim Altpapierrecycling anfallenden Fang- und Reststoffen, wobei die Fangstoffe vorentwässert werden (s.z.B. DE-B-2 339 591).The invention relates to a method for removing trapping and residual materials occurring in the paper and cardboard industry during the recycling of waste paper, the trapping materials being dewatered (see e.g. DE-B-2 339 591).
Beim Altpapierrecycling wird der Rohstoff, d.h. die Papierfaser geschädigt. Eine Papierfaser kann vier- bis sechsmal wiederverwendet werden, bevor sie bricht. Die hier entstehenden Faserstücke reichern sich im Produktionswasser an und werden über Flotationsanlagen aufgefangen. Das Konzentrat besteht zum überwiegenden Teil aus Holz- und Zellstoffasern, die man Fangstoffe nennt. Die Reststoffe bestehen zu mehr als 95 Gew.-% aus Kunststoffanteilen in Form von Klebebändern, Folien usw., die direkt aus dem Recyclingprozeß abgetrennt und üblicherweise unabhängig zu den Fangstoffen geführt werden. Unter Reststoffen wird im Rahmen der vorliegenden Erfindung auch sogenanntes "reject" verstanden.In waste paper recycling, the raw material, i.e. the paper fiber damaged. A paper fiber can be reused four to six times before it breaks. The resulting pieces of fiber accumulate in the production water and are collected via flotation plants. The concentrate mainly consists of wood and cellulose fibers, which are called capture materials. The residues consist of more than 95% by weight of plastic in the form of adhesive tapes, foils, etc., which are separated directly from the recycling process and are usually taken to the capture materials independently. In the context of the present invention, residual substances are also understood to mean what is known as a “reject”.
Im Rahmen der bekannten Maßnahmen der eingangs genannten Art hat man die Fangstoffe lediglich mechanisch bis auf einen Trockengehalt von etwa 35 % entwässert und danach einer Deponie zugeführt. Auch die Reststoffe wurden unabhängig davon deponiert. Berücksichtigt man, daß etwa 10 % des Altpapiereinsatzes in Form von Fang- und Reststoffen anfallen, wobei das Gewichtsverhältnis von Fangstoffen zu Reststoffen etwa 9 : 1 beträgt, und aus ökologischen Gründen ein erhöhter Altpapiereinsatz gefordert wird und auf der anderen Seite die zur Verfügung stehenden Deponiekapazitäten knapper werden, wird unmittelbar deutlich, daß andere Wege zur Beseitigung der Fang- und Reststoffe gefunden werden müssen.As part of the known measures of the type mentioned at the outset, the trapping materials have only been dewatered mechanically to a dry content of about 35% and then sent to a landfill. The residues were also deposited independently of this. Taking into account that about 10% of the waste paper used is in the form of catch and residues, whereby the weight ratio of catch materials to residues is about 9: 1, and for ecological reasons an increased use of waste paper is required and on the other hand the available landfill capacities become scarcer, it becomes immediately clear that other ways of eliminating the catch and residues must be found.
Der Erfindung liegt die Aufgabe zugrunde, Maßnahmen zur Beseitigung der Fang- und Reststoffe zu finden, die nicht mehr von Entsorgungs- bzw. Deponieproblemen belastet sind.The invention has for its object to find measures for eliminating the catch and residues that are no longer burdened by disposal or landfill problems.
Zur Lösung dieser Aufgabe lehrt die Erfindung in verfahrensmäßiger Hinsicht, daß die vorentwässerten Fangstoffe bis auf einen Restwassergehalt von, bezogen auf die Fangstoffmenge, mindestens 25 Gew.-% getrocknet und anschließend fortlaufend geschichtet, mit den Reststoffen überschichtet und mit Unterwind unter Bildung von Schlacke verbrannt werden.In order to achieve this object, the invention teaches in procedural terms that the pre-dewatered capture materials are dried to a residual water content of at least 25% by weight, based on the amount of capture material, and then continuously stratified, covered with the residues and burned with underwind to form slag will.
Die Erfindung geht hierbei von der Erkenntnis aus, daß die vorentwässerten Fangstoffe nach weiterer Trocknung ohne weiteres, d.h. ohne Primärenergie mit den Reststoffen verbrannt werden können, wenn die Verbrennung in Form einer Schichtung erfolgt, wobei die untere Schicht von den Fangstoffen und die obere Schicht von den Reststoffen gebildet wird. Die entstehende Schlacke kann anderweitig verwendet werden, stellt jedenfalls mengenmäßig kein Deponieproblem mehr dar.The invention is based on the knowledge that the pre-dewatered capture materials after further drying without any problems, i.e. can be burned with the residual materials without primary energy if the combustion takes place in the form of a stratification, the lower layer being formed by the catching materials and the upper layer being formed by the residual materials. The resulting slag can be used for other purposes, in any case it does not represent a landfill problem anymore.
Für die weitere Ausgestaltung bestehen im Rahmen der Erfindung mehrere Möglichkeiten. So werden nach einer bevorzugten Ausführungsform die bei der Verbrennung der Fang- und Reststoffe entstehenden Verbrennungsgase einer Wärmerückgewinnung unterworfen, insbesondere zur Wasserdampferzeugung eingesetzt; hier erfolgt also eine Ausnutzung der entstehenden Verbrennungswärme. Empfehlenswert ist es, die vorentwässerten Fangstoffe bis auf einen Restwassergehalt von, bezogen auf die Fangstoffmenge, mindestens 20 Gew.-% zu trocknen; dann ist das Verfahren bezüglich der Verbrennung der Reststoffe nicht so empfindlich.There are several possibilities for the further configuration within the scope of the invention. Thus, according to a preferred embodiment, the combustion gases formed during the combustion of the trapping and residual materials are subjected to heat recovery, in particular used for generating steam; here the resulting heat of combustion is used. It is advisable to dry the pre-dewatered capture materials to a residual water content of at least 20% by weight, based on the amount of capture material; then the process is not as sensitive to the combustion of the residues.
Der erzeugte Wasserdampf kann bei der Papierherstellung verwendet werden, man kann aber auch wie nach bevorzugter Ausführungsform die vorentwässerten Fangstoffe durch Beheizung mit zumindest einem Teil des erzeugten Wasserdampfes vortrocknen. Allein oder in Kombination dazu können aber die vorentwässerten Fangstoffe auch mit zumindest einem Teil bei der Verbrennung der Fang- und Reststoffe entstehenden Verbrennungsgase getrocknet werden. In diesem Zusammenhang entledigt man sich auf besonders einfache Weise möglichen Abluftproblemen, indem die bei der Trocknung der Fangstoffe entstehende Abluft zusammen mit den bei der Verbrennung der Fang- und Reststoffe entstehenden Verbrennungsgasen einer Nachverbrennung unterworfen wird. Die getrockneten und geschichteten Fangstoffe können mit, bezogen auf die Feststoffmenge, bis zu 100 Gew.-% Reststoffen überschichtet und der Verbrennung zugeführt werden; optimale Verhältnisse sind jedoch gegeben, wenn die getrockneten und geschichteten Fangstoffe mit, bezogen auf die Feststoffmenge, höchstens 15 Gew.-% Reststoffen überschichtet und der Verbrennung zugeführt werden. Zweckmäßigerweise wird man die Verbrennungsgase einer Entstaubung unterwerfen. Jedenfalls empfiehlt es sich, Flugasche aus den Verbrennungsgasen in die Schlacke einzubinden. Diese Schlacke kann jedenfalls ohne weiteres als Baustoff eingesetzt werden, so daß insgesamt dann überhaupt keine Deponieprobleme mehr anfallen.The water vapor generated can be used in papermaking, but it is also possible, as in the preferred embodiment, to pre-dry the pre-dewatered capture materials by heating with at least some of the water vapor generated. Alone or in combination, however, the pre-dewatered capture materials can also be dried with at least some of the combustion gases generated during the combustion of the capture and residual materials. In this context, one can get rid of possible exhaust air problems in a particularly simple manner by subjecting the exhaust air generated during the drying of the trapping materials to a post-combustion together with the combustion gases generated during the combustion of the trapping and residual materials. The dried and layered capture materials can be covered with up to 100% by weight of residual materials, based on the amount of solids, and fed to the combustion; optimal conditions are, however, provided that the dried and layered capture materials are covered with a maximum of 15 wt. The combustion gases are expediently subjected to dedusting. In any case, it is advisable to incorporate fly ash from the combustion gases into the slag. In any case, this slag can easily be used as a building material, so that there are no more landfill problems at all.
Im folgenden wird die Erfindung anhand einer Zeichnung näher erläutert.The invention is explained in more detail below with reference to a drawing.
Die einzige Zeichnungsfigur zeigt schematisch eine Vorrichtung zum Beseitigen von Fangstoffen einerseits und Reststoffen andererseits, wie sie in der Papier- und Kartonindustrie beim Altpapierrecycling anfallen. Die Fangstoffe sind dabei in üblicher Form vorentwässert. Man erkennt in der Hauptsache einen Verbrennungsofen 1 mit schräggestelltem Schwingrost 2 und Unterwindzuführung 3. Über dem oberen Rostende ist ein Aufgabedosierer 4 für die Fangstoffe angeordnet, der über eine Transporteinrichtung 5 mit einem Trockner 6 für die vorentwässerten Fangstoffe verbunden ist. Neben und in Richtung der Rostschräge nach unten gesehen ist hinter dem Aufgabedosierer 4 für die Fangstoffe ein weiterer Aufgabedosierer 7 für die Reststoffe vorgesehen, die ohne weitere Aufbereitung zugeführt werden. Unter dem Schwingrost 2 erkennt man einen Schlackensammler 8. Dem Verbrennungsofen 1 ist in Strömungsrichtung der Verbrennungsgase gesehen ein Wärmerückgewinnungsaggregat in Form eines Wasserdampferzeugers 9 nachgeschaltet. Dieser ist über eine schematisch angedeutete Leitung 10 mit dem Trockner 6 verbunden. Außerdem erkennt man, daß der Verbrennungsofen 1 in Strömungsrichtung der Verbrennungsgase gesehen hinter dem Schwingrost 2 mit einer zum Trockner 6 geführten Verbrennungsgaszweigleitung 11 versehen ist und der Trockner 6 mit seinem Abluftauslaß an eine Nachverbrennungskammer 12 des Verbrennungsofens angeschlossen ist. Diese Nachverbrennungskammer 12 kann zur Verringerung des CO-Gehaltes der Verbrennungsgase und zur Unterstützung der Nachverbrennung mit nicht dargestellten Sekundärluftzuführungen versehen sein. Dem Wasserdampferzeuger 9 folgen ein übliches Trockenentstaubungsaggregat 13 und ein Kamin 14. Das Trockenentstaubungsaggregat 13 und der Wasserdampferzeuger 9 weisen jeweils einen Flugascheauslaß 15 bzw. 16 auf, die über eine Leitung 17 mit dem Verbrennungsofen 1 verbunden sind. Die Leitung 17 mündet im Schlackebereich des Schwingrostes 2 in den Verbrennungsofen 1. Die insoweit zurückgeführte Flugasche wird so mit Sekundärluft im Bereich der Schlackezone zugeführt und in die Schlacke eingebunden.The only drawing figure shows schematically a device for removing trapping materials on the one hand and residual materials on the other hand, as they occur in the paper and cardboard industry in the recycling of waste paper. The capture materials are pre-dewatered in the usual form. A combustion furnace 1 with an inclined vibrating grate 2 and
Die Funktionsweise der beschriebenen Vorrichtung ergibt sich unschwer aus der Figur. Die vorentwässerten Fangstoffe werden bis auf einen Restwassergehalt von, bezogen auf die Fangstoffmenge, mindestens 25 Gew.-%, insbesondere 20 Gew.-%, im Trockner 6 getrocknet. Diese Trocknung kann durch Beheizung mit zumindest einem Teil des erzeugten Wasserdampfes und/oder mit zumindest einem Teil der bei der Verbrennung der Fang- und Reststoffe entstehenden Verbrennungsgase getrocknet werden. Die im letzten Fall entstehende Abluft wird dann zusammen mit den Verbrennungsgasen in der Nachverbrennungskammer 12 einer Nachverbrennung unterworfen. Mit Hilfe des Aufgabedosierers 4 werden die getrockneten Fangstoffe fortlaufend geschichtet auf den Schwingrost 2 aufgegeben. Unmittelbar darüber werden mit, bezogen auf die Feststoffmenge, hochstens 100 Gew.-%, vorzugsweise hochstens 15 Gew.-%, die Reststoffe überschichtet und das ganze dann mit Unterwind unter Bildung von Schlacke verbrannt. Dieser Schlacke wird die Flugasche aus der Trockenentstaubung beigegeben. Die naß aufgenommene Schlacke wird in der Bauindustrie verwendet.The mode of operation of the device described can easily be seen in the figure. The pre-dewatered capture materials are dried in the dryer 6 to a residual water content of at least 25% by weight, in particular 20% by weight, based on the amount of capture material. This drying can be dried by heating with at least a part of the water vapor generated and / or with at least a part of the combustion gases generated during the combustion of the capture and residual materials. The exhaust air produced in the latter case is then subjected to post-combustion together with the combustion gases in the
Claims (9)
- A process for the disposal of trash substance and foreign materials arising during waste paper recycling in the paper and carton industries, the trash substance being partly dewatered, characterised in that the partly dewatered trash substance is further dried to a residual water content not exceeding 25% by weight of the trash substance and then continuously laid out on a grate, covered with a layer of foreign materials and incinerated with under-grate blast, to form a clinker.
- A process as in Claim 1, characterised in that the waste gases from the incineration of the trash substance and foreign materials are utilized as a source of waste heat, more particularly for steam production.
- A process as in Claim 1 or 2, characterised in that the partly dewatered trash substance is dried to a residual water content not exceeding 20% by weight of the trash substance.
- A process as in Claim 2 or 3, characterised in that the partly dewatered trash substance is pre-dried by heating with at least a proportion of the steam produced.
- A process as in any of Claims 1 to 4, characterised in that the partly dewatered trash substance is dried with the aid of at least a proportion of the waste gas produced by incinerating the trash substance and foreign materials.
- A process as in Claim 5, characterised in that the spent air arising from the drying of the trash substance is subjected to after-burning together with the waste gases arising from the incineration of the trash substance and foreign materials.
- A process as in any of Claims 1 to 6, characterised in that the dried trash substance on the grate is covered with a layer of foreign materials not exceeding 100% by weight of its solids content, and more particularly not exceeding 15% by weight of its solids content, and subjected to incineration.
- A process as in any of Claims 1 to 7, characterised in that the fly ash contained in the waste gases from the incineration of the trash substance and foreign materials is incorporated in the clinker.
- A process as in any of Claims 1 to 8, characterised in that the clinker is utilized as a building material.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AT89102100T ATE99400T1 (en) | 1988-06-24 | 1989-02-08 | PROCESS FOR DISPOSAL OF COLLECTION AND WASTE MATERIALS GENERATED DURING THE RECYCLING OF WASTE PAPER IN THE PAPER AND BOARD INDUSTRY. |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE3821318 | 1988-06-24 | ||
DE3821318 | 1988-06-24 |
Publications (3)
Publication Number | Publication Date |
---|---|
EP0347519A2 EP0347519A2 (en) | 1989-12-27 |
EP0347519A3 EP0347519A3 (en) | 1991-06-12 |
EP0347519B1 true EP0347519B1 (en) | 1993-12-29 |
Family
ID=6357150
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP89102100A Expired - Lifetime EP0347519B1 (en) | 1988-06-24 | 1989-02-08 | Process for eliminating waste products resulting from the recycling of waste paper in the paper and cardboard industry |
Country Status (3)
Country | Link |
---|---|
EP (1) | EP0347519B1 (en) |
AT (1) | ATE99400T1 (en) |
DE (2) | DE8915578U1 (en) |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
ES2065259B1 (en) * | 1993-02-05 | 1995-09-16 | De Menezes Junior Antoni Teles | GARBAGE INCINERATOR. |
EP0627597B1 (en) * | 1993-06-03 | 1996-07-24 | Oschatz Gmbh | Method for the combustion of waste products resulting from the production of paper |
DE4337420A1 (en) * | 1993-06-03 | 1994-12-08 | Oschatz Gmbh | Process for burning trapping materials from paper production |
CN105465799B (en) * | 2016-01-01 | 2018-08-17 | 广州环峰能源科技股份有限公司 | A kind of dregs of a decoction biomass fuel multi-fuel fired boiler |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CH424058A (en) * | 1965-05-26 | 1966-11-15 | Ulrich Reusser Peter | Method of burning sludge |
US3573202A (en) * | 1970-03-05 | 1971-03-30 | Fort Howard Paper Co | Process for reduction of water pollution due to domestic and industrial wastes |
FR2123635A5 (en) * | 1971-01-26 | 1972-09-15 | Socea | |
JPS59156956A (en) * | 1983-02-28 | 1984-09-06 | 株式会社ノダ | Manufacture of inorganic construction material from incineration ash |
-
1989
- 1989-02-08 DE DE8915578U patent/DE8915578U1/de not_active Expired - Lifetime
- 1989-02-08 EP EP89102100A patent/EP0347519B1/en not_active Expired - Lifetime
- 1989-02-08 AT AT89102100T patent/ATE99400T1/en not_active IP Right Cessation
- 1989-02-08 DE DE89102100T patent/DE58906529D1/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
---|---|
DE8915578U1 (en) | 1990-11-08 |
EP0347519A2 (en) | 1989-12-27 |
DE58906529D1 (en) | 1994-02-10 |
ATE99400T1 (en) | 1994-01-15 |
EP0347519A3 (en) | 1991-06-12 |
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