EP0718555A1 - Procédé et dispositif pour la combustion des déchets - Google Patents

Procédé et dispositif pour la combustion des déchets Download PDF

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Publication number
EP0718555A1
EP0718555A1 EP95120113A EP95120113A EP0718555A1 EP 0718555 A1 EP0718555 A1 EP 0718555A1 EP 95120113 A EP95120113 A EP 95120113A EP 95120113 A EP95120113 A EP 95120113A EP 0718555 A1 EP0718555 A1 EP 0718555A1
Authority
EP
European Patent Office
Prior art keywords
waste
microwave
water content
control unit
process control
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
Application number
EP95120113A
Other languages
German (de)
English (en)
Inventor
Albrecht Vogel
Armin Gasch
Gunar Baier
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
ABB Patent GmbH
Original Assignee
ABB Patent GmbH
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by ABB Patent GmbH filed Critical ABB Patent GmbH
Publication of EP0718555A1 publication Critical patent/EP0718555A1/fr
Ceased legal-status Critical Current

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Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/50Control or safety arrangements
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/002Incineration of waste; Incinerator constructions; Details, accessories or control therefor characterised by their grates
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23HGRATES; CLEANING OR RAKING GRATES
    • F23H1/00Grates with solid bars
    • F23H1/02Grates with solid bars having provision for air supply or air preheating, e.g. air-supply or blast fittings which form a part of the grate structure or serve as supports
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23NREGULATING OR CONTROLLING COMBUSTION
    • F23N1/00Regulating fuel supply
    • F23N1/02Regulating fuel supply conjointly with air supply
    • F23N1/022Regulating fuel supply conjointly with air supply using electronic means
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2900/00Special features of, or arrangements for incinerators
    • F23G2900/55Controlling; Monitoring or measuring
    • F23G2900/55011Detecting the properties of waste to be incinerated, e.g. heating value, density
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23NREGULATING OR CONTROLLING COMBUSTION
    • F23N2221/00Pretreatment or prehandling
    • F23N2221/10Analysing fuel properties, e.g. density, calorific
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23NREGULATING OR CONTROLLING COMBUSTION
    • F23N2241/00Applications
    • F23N2241/18Incinerating apparatus

Definitions

  • the invention relates to a method and a device for incinerating waste according to the preamble of claims 1 and 9.
  • Waste as fuel is very inhomogeneous in its composition. Their properties such as calorific value, ignitability and burning rate fluctuate in a very wide range.
  • Waste is incinerated, which consists, for example, of organic residual waste, industrial waste, wood, stones, plastics, glass, ceramics, paper and cardboard.
  • the waste is provided for incineration in such a combination that it always contains a certain amount of combustible components.
  • the waste intended for incineration is available in different sizes. In addition, they have different proportions of water, which must be taken into account when burning.
  • the compositions and chemical-physical properties of fuels such as coal, gas and oil are known. In contrast to the waste mentioned above, it is easily possible to optimize an incineration plant for these fuels.
  • Incineration plants for waste have so far mostly been operated with a low degree of automation.
  • a control room is provided, which is looked after by at least one surgeon.
  • the operator is responsible for adapting the combustion control to the fuel that is produced. He is dependent on his personal observation of the combustion process.
  • at least one video camera is provided, which is arranged above the combustion chamber. Corrective interventions in the combustion process can, however, only be made retrospectively, ie when a change in the composition of the waste to be incinerated has become noticeable through a change in the quality of the incineration. Then it is usually too late for corrective interventions. Such a combustion process will always fluctuate more or less strongly around its optimal operating point.
  • EP-A-0 317 731 it is proposed to observe the area of the waste application on the combustion grate with optical radiation receivers, which are preceded by optical filters which selectively detect the electromagnetic radiation emitted by H 2 O or CO 2 molecules.
  • the indicator for the water content of the waste obtained in this way is fed to the control device as a disturbance variable for controlling the combustion.
  • a signal is obtained which provides information about the water content of the waste before the waste is incinerated, so that the combustion parameters can be adapted directly to the incinerating waste.
  • a disadvantage of this process is that the time from the drop in the waste in the drop zone to the incineration on the grate is too short for changes in the combustion parameters to have a positive effect.
  • the dead times in this process are of the order of 30 to 60 minutes.
  • the transport time from the waste disposal area to the main incineration zone is in the range of 10 minutes.
  • the water content of the waste is only determined from the water evaporating on the surface. The water contained in the waste is not recorded and can therefore not be taken into account when controlling the combustion.
  • EP-A-0 352 620 describes a method in which the grate on which the waste is incinerated is observed with the aid of a video camera.
  • the video image obtained is automatically processed by means of a computer.
  • Information about the course of the combustion such as, for example, the temperature distribution and the location of the main fire zone, is derived from the signals obtained from this and is then fed to the process control system as a control variable.
  • the invention is therefore based on the object of demonstrating a method which enables a forward-looking manner of incinerating waste of all kinds, so that it is known even before the incidental waste is incinerated which parameters the furnace is to be set to.
  • the invention is also based on the object of demonstrating a device with which this method can be carried out.
  • a corresponding device for incinerating waste is disclosed in claim 9.
  • incinerate waste The best way to incinerate waste is to determine the composition or nature of the waste before incineration, and to ensure that its incineration is fully tailored to this information.
  • One of the most important factors for optimal combustion is knowledge of the water content of the waste. If the water content of waste due for incineration is known both on its surface and in its interior, the incineration can be controlled in advance without major problems.
  • the water content of the waste to be incinerated is determined a few minutes before incineration with the aid of microwave signals.
  • the determination of the water content of the waste takes place in the allocation shaft, in such a timely manner that the information obtained is completely available during incineration.
  • microwave signals are emitted perpendicular to the direction of conveyance of the allocation shaft, in which the waste is transported to a grate provided for incineration.
  • the water content of the waste causes signal weakening and / or phase changes in these microwave signals. These are evaluated to determine the water content in the waste.
  • microwave signals are transmitted from a first inner wall of the allocation shaft to the opposite wall and received there.
  • the microwaves sent through the waste experience a signal weakening and / or phase change.
  • the water content of the waste just examined is then determined from this by comparing the transmitted and received microwave signals.
  • the information signals obtained are forwarded to a process control unit.
  • microwave signals can also be transmitted perpendicular to the conveying direction of the allocation shaft and the microwave signals reflected on the waste can be evaluated for the determination of the water content.
  • the information signals determined from this are also fed to the process control unit.
  • a standing microwave can be formed between two opposite walls of the allocation shaft and the water content of the waste can be evaluated in a corresponding manner from the signal weakening and / or phase change of this standing microwave.
  • the microwave signals that are required for the upgrading are forwarded to evaluation units. The measured values determined by these evaluation units are stored in the process control unit.
  • the device for incinerating waste is equipped with an allocation shaft, which is followed by a feed slide. It is used to convey the amount of waste to be incinerated to a grate provided for this purpose, to which air is fed to maintain the incineration.
  • At least one, preferably a plurality of microwave transmitters and microwave receivers, which are connected to at least one evaluation unit, are installed in the allocation shaft.
  • the signal outputs of the evaluation units are connected to a process control unit. This is intended for controlling the air supply to the grate.
  • four combined microwave transmission / reception modules are provided in at least two planes ⁇ and ⁇ that are perpendicular to one another and perpendicular to the conveying direction of the allocation shaft.
  • Two combined microwave transmission / reception modules are installed at a defined distance from each other on a first inner wall of the allocation shaft.
  • the two other combined microwave transmitter / receiver modules belonging to the same level are installed on the opposite wall in such a way that two combined microwave transmitter / receiver modules are arranged opposite each other on a straight line perpendicular to the conveying direction of the distribution shaft.
  • the device 1 shown in FIG. 1 for the combustion of all types of waste comprises an allocation shaft 2, a feed slide 3 and a grate 4, a measuring device 5, three evaluation units for microwave signals 15, 16 and 17, and a process control unit 18.
  • the in a dimensioning section 30 of the distribution shaft 2 waste 20 are provided for incineration on the grate 4 in about 20 to 30 minutes.
  • the measuring device 5 is provided in the dimensioning section 30 of the distribution shaft 2, which in the exemplary embodiment shown here is equipped with five microwave transmitters or receivers 6S, 6E, 7S, 7E and 8.
  • the amount of waste 20 that is loaded onto the grate 4 for incineration corresponds to the amount of waste that can be filled into the dimensioning section 30 of the allocation shaft 2.
  • a microwave transmitter 6S is installed on the first inner wall 2A of the allocation shaft 2 and a microwave receiver 6E is installed on the opposite inner wall 2B at the same height as the microwave transmitter 6S.
  • a standing microwave is formed between these two microwave devices 6S and 6E. From the signal weakening and / or phase changes of this standing microwave, the water content of the wastes 20 transported into the dimensioning section 30 can be determined with the aid of the evaluation unit 15. A signal with the information about the water content is forwarded from the evaluation unit 15 to the process control unit 18.
  • a microwave transmitter 7S is installed on the inside of the wall 2a, as seen in the conveying direction of the allocation shaft 2, from which the vertical through the in the Dimensioning section 30 of the allocation shaft 2 to be transported waste 20 microwaves.
  • the microwave signals passing through the wastes 20 are received by the microwave receiver 7E installed on the inside of the wall 2B at the same level as the microwave transmitter 7S.
  • the evaluation unit 16 to which the microwave transmitter 7S and the microwave receiver 7E are connected, the water content in the waste 20 is determined from the signal weakening and / or phase change of the received microwave signals compared to the transmitted microwave signals.
  • the measured values are transmitted from the evaluation unit 16 to the process control unit 18.
  • a combined microwave transmitter / receiver module 8 is also installed at a defined distance below the microwave transmitter 7S on the inner wall 2A of the allocation shaft 2. This sends out microwave signals.
  • the microwave signals reflected at the waste 20 are received again by the module 8.
  • the microwave signals sent and received by the module 8 are fed to the evaluation unit 17. This determines measured values from the signal weakening and / or phase change between the transmitted and the reflected microwave signals, which are passed on to the process control unit 18. All measurement signals transmitted from the evaluation units to the process control unit 18 are stored there. They are available for the combustion of the waste 20 for controlling the air supply to the grate 4.
  • the waste 20 contained in the allocation shaft 2 is conveyed onto the grate 4 for incineration with the aid of the feed slide 3.
  • the amount of waste 20 that is loaded onto the grate 4 corresponds to the amount of waste that is currently in the dimensioning section 30 of the allocation shaft 2.
  • the dimensioning section 30 comprises only that part of the allocation shaft 2 in which the microwave transmitters and receivers 6S, 7S, 7E, and 8 are arranged.
  • the feed slide 3 is also controlled by the process control unit 18.
  • An air damper 19L which is installed in a pipeline 19, is also controlled by the process control unit 18. This opens into channels 19K on the underside of the grate 4, from where the amount of air required for optimal combustion is supplied from the grate 4.
  • the measuring device 5 here has eight combined microwave transmitter / receiver modules 7, 8, 9, 10, 11, 12, 13, 14 .
  • four combined microwave transmission / reception modules 7, 8, 9, 10, 11, 12, 13 and 14 are arranged in two planes ⁇ and ⁇ , which are perpendicular to one another and perpendicular to the conveying direction of the distribution shaft 2. As shown in FIG.
  • microwave transmission / reception modules 7 and 9 are at a defined distance from one another on the inside of the wall 2A of the allocation shaft 2 and the two other microwave transmission / reception modules 8 and 10 also belonging to the plane ⁇ opposite inside of the wall 2B installed so that two microwave transmitter / receiver modules 7 and 8 are arranged on a straight line perpendicular to the conveying direction of the allocation shaft 2 opposite each other.
  • the microwave transmission / reception modules 11, 12, 13 and 14 belonging to the plane ⁇ are arranged.
  • FIG. 3 shows the change in a microwave signal over the course of a minute.
  • the microwave signal D is transmitted by the microwave transmission / reception module 7 and received by the microwave transmission / reception module 8.
  • the microwave transmission / reception modules 7 and 8 During this one minute there will be waste 20 bypassed the microwave transmission / reception modules 7 and 8 and the dimensioning section 30 is filled with them. From the decrease in the intensity of the microwave D, it can be clearly seen that the waste 20 which is being guided past is initially dry, but the water content of the subsequent waste 20 is constantly increasing.
  • FIG. 4 shows the course over time of a microwave R, which was emitted by the microwave transmission / reception module 7 in a manner reflected by the waste 20 that was passed. The reflected microwave is again received by the microwave transmission / reception module 7.
  • the reflected microwave signal R also shows that the first bypassed wastes 20 initially dry and the subsequent wastes 20 have a considerable water content, which also leads to a weakening of the reflected microwave signal.
  • FIGS. 5, 6, 7 and 8 show several measurements carried out with the microwave transmission / reception modules 7, 8, 9, 10, 11, 12, 13, 14 can be used to clearly determine whether the wastes are loaded with water, or whether the change in the microwaves is caused by metallic wastes which are directed past the measuring device 5.
  • FIG. 5 shows the microwave signal 7R reflected on the metallic waste 21 during the time t1 to t2, which is received by the microwave transmitter / receiver module 7 and was also transmitted by the latter.
  • the reflected microwave 7R show a clear amplification, which it experienced when reflecting on the metallic waste 21.
  • the microwave signals 7T emitted by the microwave transmission / reception module 7 are weakened by the metallic waste and are received in this form by the microwave transmission / reception module 8.
  • the metallic piece of waste 21 passes the microwave transmission / reception modules 11 and 12.
  • the transmission and reception module 11 emitted by the microwave transmission / reception module Transceiver module 12 received microwave signal 11T through the metallic piece of waste 21 weakened, while the microwave signal 11R emitted by the microwave transmission / reception module 11 and reflected by the metallic waste 21 was amplified.
  • microwave signals 9T and 9R or 13T and 13R transmitted, transmitted, received or reflected by the microwave transmission / reception modules 9 and 10 or 13 and 14 have no changes, as can be seen from FIGS. 7 and 8 is. This means that non-metallic wastes 22 were transported past the microwave transmitter / receiver modules 9, 10, 13 and 14.
  • the evaluation units which are connected to the microwave transmitter / receiver modules 7, 8, 9, 10, 11, 12, 13 and 14, are subject to greatly modified transmitted or reflected microwave signals 7T and 7R and 11T and 11R and on the other hand unchanged transmitted or reflected microwave signals 9T, 9R and 13T and 13R, the evaluation units which are connected to the microwave transmitter / receiver modules 7, 8, 11, 12 can recognize that a large metallic piece of waste 21 is conveyed into the design section 30. This means that the measurement of the water content must be suspended in the time t1 to t4. They therefore do not give any information signals to the process control unit (not shown here). This receives only the information signals from the evaluation units, which are connected to the microwave transmission / reception modules 9, 10, 13, 14.
  • the process control unit is designed such that in this case it stores the water content of the waste 22, or if the water content of the waste 22 is too low, it does not store the information. This means that the control of the supply of air for the combustion of these wastes 21 and 22 is tracked according to a value permanently stored in the process control unit.

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  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Combustion & Propulsion (AREA)
  • Incineration Of Waste (AREA)
EP95120113A 1994-12-22 1995-12-19 Procédé et dispositif pour la combustion des déchets Ceased EP0718555A1 (fr)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DE4446022A DE4446022A1 (de) 1994-12-22 1994-12-22 Verfahren und Vorrichtung zur Verbrennung von Abfällen
DE4446022 1994-12-22

Publications (1)

Publication Number Publication Date
EP0718555A1 true EP0718555A1 (fr) 1996-06-26

Family

ID=6536746

Family Applications (1)

Application Number Title Priority Date Filing Date
EP95120113A Ceased EP0718555A1 (fr) 1994-12-22 1995-12-19 Procédé et dispositif pour la combustion des déchets

Country Status (6)

Country Link
EP (1) EP0718555A1 (fr)
JP (1) JPH08233242A (fr)
KR (1) KR960024012A (fr)
DE (1) DE4446022A1 (fr)
NO (1) NO306645B1 (fr)
TW (1) TW289789B (fr)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009065726A1 (fr) * 2007-11-19 2009-05-28 Siemens Ag Österreich Procédé de régulation d'un dispositif de chauffe à combustible solide
WO2011055015A1 (fr) * 2009-11-06 2011-05-12 Senfit Oy Mesure de l'humidité
EP2522905A3 (fr) * 2011-05-13 2014-11-19 Clyde Bergemann Drycon Gmbh Procédé et dispositif d'actionnement d'un dispositif de convoyage pour des cendres

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE19723298A1 (de) * 1997-06-04 1998-12-10 Abb Patent Gmbh Verfahren zur Steuerung der Mischungsgüte bei der Müllverbrennung
DE19917572A1 (de) * 1999-04-19 2000-10-26 Abb Alstom Power Ch Ag Verfahren zur automatischen Einstellung der Feuerung einer Müllverbrennungsanlage
DE102010031528B4 (de) * 2010-07-19 2013-04-25 Klaus Seeger System zur Bestimmung eines Energiegehalts eines festen Brennstoffs und Verwendung des Systems
WO2013107509A1 (fr) * 2012-01-18 2013-07-25 Heinrich Unland Système permettant de déterminer la valeur énergétique d'un combustible
DE102017120222B3 (de) 2017-09-01 2018-11-29 Technische Universität Dresden Verfahren und System zur Prognose einer Brennstoffzusammensetzung bei der thermischen Verwertung von Abfall
JP2020094734A (ja) * 2018-12-12 2020-06-18 Jfeエンジニアリング株式会社 火格子式廃棄物焼却炉及び火格子式廃棄物焼却炉による廃棄物焼却方法
DE102020124544A1 (de) 2020-09-21 2022-03-24 Fraunhofer-Gesellschaft zur Förderung der angewandten Forschung eingetragener Verein Verfahren und Anlage zum thermischen Verwerten von festem Brennstoff in einem Reaktionsraum

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DD203398A1 (de) * 1981-12-23 1983-10-19 Martin Weber Verfahren und anordnung zur messung des wassergehaltes von rohbraunkohle
DE3805637A1 (de) * 1987-10-29 1989-05-11 Still Otto Gmbh Verfahren und vorrichtung zur kontinuierlichen messung der feuchte eines feinkoernigen schuettgutes
WO1990007110A1 (fr) * 1988-12-14 1990-06-28 Buehler Ag Maschinenfabrik Procede et dispositif de mesure en continu de l'humidite d'un produit en vrac
EP0415582A2 (fr) * 1989-08-14 1991-03-06 Westinghouse Electric Corporation Méthode et appareil pour modeler l'écoulement dans une soute pour une meilleure combustion ou autre fonctionnement d'une installation

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DD203398A1 (de) * 1981-12-23 1983-10-19 Martin Weber Verfahren und anordnung zur messung des wassergehaltes von rohbraunkohle
DE3805637A1 (de) * 1987-10-29 1989-05-11 Still Otto Gmbh Verfahren und vorrichtung zur kontinuierlichen messung der feuchte eines feinkoernigen schuettgutes
WO1990007110A1 (fr) * 1988-12-14 1990-06-28 Buehler Ag Maschinenfabrik Procede et dispositif de mesure en continu de l'humidite d'un produit en vrac
EP0415582A2 (fr) * 1989-08-14 1991-03-06 Westinghouse Electric Corporation Méthode et appareil pour modeler l'écoulement dans une soute pour une meilleure combustion ou autre fonctionnement d'une installation

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009065726A1 (fr) * 2007-11-19 2009-05-28 Siemens Ag Österreich Procédé de régulation d'un dispositif de chauffe à combustible solide
WO2011055015A1 (fr) * 2009-11-06 2011-05-12 Senfit Oy Mesure de l'humidité
CN102612647A (zh) * 2009-11-06 2012-07-25 圣菲特公司 湿度测量
US8725284B2 (en) 2009-11-06 2014-05-13 Senfit Oy Moisture measurement
CN102612647B (zh) * 2009-11-06 2016-01-06 圣菲特公司 湿度测量
EP2522905A3 (fr) * 2011-05-13 2014-11-19 Clyde Bergemann Drycon Gmbh Procédé et dispositif d'actionnement d'un dispositif de convoyage pour des cendres

Also Published As

Publication number Publication date
TW289789B (fr) 1996-11-01
NO955225D0 (no) 1995-12-21
NO306645B1 (no) 1999-11-29
JPH08233242A (ja) 1996-09-10
DE4446022A1 (de) 1996-06-27
NO955225L (no) 1996-06-24
KR960024012A (ko) 1996-07-20

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