EP0735321A2 - Process and device for purification of noxious exhaust gases by chemical purification - Google Patents

Process and device for purification of noxious exhaust gases by chemical purification Download PDF

Info

Publication number
EP0735321A2
EP0735321A2 EP96102122A EP96102122A EP0735321A2 EP 0735321 A2 EP0735321 A2 EP 0735321A2 EP 96102122 A EP96102122 A EP 96102122A EP 96102122 A EP96102122 A EP 96102122A EP 0735321 A2 EP0735321 A2 EP 0735321A2
Authority
EP
European Patent Office
Prior art keywords
flame
fuel gas
burner
gas
oxygen
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.)
Granted
Application number
EP96102122A
Other languages
German (de)
French (fr)
Other versions
EP0735321B1 (en
EP0735321A3 (en
Inventor
Horst Dr. Reichardt
Lothar Dipl.-Ing. Ritter
Günter Dipl.-Ing. Firkert
Lutz Dipl.-Phys. Labs
Konrad Dipl.-Phys. Gehmlich
Gerold Hofmann
Michael Dipl-Ing. Hentrich
Wido Wiesenberg
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.)
Das-Duennschicht Anlagen Systeme Dresden GmbH
Das Duennschicht Anlagen Systeme GmbH
Original Assignee
Das-Duennschicht Anlagen Systeme Dresden GmbH
Das Duennschicht Anlagen Systeme 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
Family has litigation
First worldwide family litigation filed litigation Critical https://patents.darts-ip.com/?family=7758136&utm_source=google_patent&utm_medium=platform_link&utm_campaign=public_patent_search&patent=EP0735321(A2) "Global patent litigation dataset” by Darts-ip is licensed under a Creative Commons Attribution 4.0 International License.
Application filed by Das-Duennschicht Anlagen Systeme Dresden GmbH, Das Duennschicht Anlagen Systeme GmbH filed Critical Das-Duennschicht Anlagen Systeme Dresden GmbH
Publication of EP0735321A2 publication Critical patent/EP0735321A2/en
Publication of EP0735321A3 publication Critical patent/EP0735321A3/en
Application granted granted Critical
Publication of EP0735321B1 publication Critical patent/EP0735321B1/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/061Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
    • F23G7/065Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating using gaseous or liquid fuel

Definitions

  • the invention relates to a method and devices for cleaning pollutant-containing exhaust gases by chemical reaction in a combustion chamber.
  • waste gases containing pollutants are produced.
  • These exhaust gases include fluorine-containing hydrocarbons or other fluorine compounds.
  • inert gases such as argon or nitrogen are major components of the exhaust gases. Because of the high proportion of such gases, these exhaust gases themselves are usually not combustible.
  • the pollutants or their reaction products have a toxic effect or, due to their harmful effects in the atmosphere, promote ozone depletion and the greenhouse effect.
  • a whole series of methods are known for exhaust gas purification.
  • the cleaning is very often carried out by sorption of the pollutants from the exhaust gas, for example in oxidizing aqueous solution (DE 3342816).
  • Pollutants that are not sorbed in this way or are not efficiently treated can be converted by chemical conversion processes, for example thermal decomposition (EU 0384803) by heating or by burning in an oxygen-containing environment (US Pat. No. 5,183,646). If this is done by burning, exhaust gases with a high proportion of inert gas have to be introduced into a combustion gas flame, for example from a natural gas or hydrogen / oxygen mixture. Harmful secondary products of the conversion are then removed from the exhaust gas, for example by sorption or washing processes.
  • Exhaust gas cleaning is generally a multi-stage process in which partial processes such as thermal decomposition or oxidation, cooling, sorption, hydrolysis and washing out of solid reaction products take place (EP 89 110 875).
  • the exhaust gas is passed in succession, for example, through a device with a combustion chamber and at least one further device, for example one which operates on the washing principle.
  • Devices for purifying exhaust gas have also been proposed, in which the exhaust gas is passed successively through a combustion chamber for combusting the pollutants and a washing chamber, which are structurally combined to form a unit (EP 89 110 875).
  • a disadvantage of such methods and devices with thermal decomposition of the pollutants in a combustion chamber and with a washing chamber are the thermal and electrolytic corrosion of the wall surfaces and other parts, in particular the combustion chamber, under the action of gaseous reaction products from the combustion. This corrosion is critically increased by the high temperature of the burned fuel gas mixture and exhaust gases, especially if these e.g. Hydrogen halides, e.g. HF, and water vapor included.
  • Hydrogen halides e.g. HF
  • an improvement in the efficiency of the cleaning in the direction of a low pollutant content in the cleaned exhaust gas can be achieved by increasing the amount of fuel gas relative to the amount of the supplied exhaust gas, but this route is associated with a critical deterioration in the economy of the exhaust gas cleaning because of the increased fuel gas consumption .
  • the invention has for its object to improve the effectiveness of the purification of exhaust gases by chemical conversion in a fuel gas flame, ie to drastically reduce the percentage of residual pollutants in the cleaned exhaust gas.
  • no unburned constituents of the fuel gas should be contained in the cleaned exhaust gas. In particular, it can be achieved that no secondary pollutants arise during combustion and are released with the cleaned exhaust gas.
  • the object is achieved by a method according to claim 1, 2 and 3 and a device according to claim 4 or 5 .
  • the method assumes that a fuel gas mixture is used in a combustion chamber with a burner to generate a fuel gas flame and that the exhaust gas, which contains the pollutants, in particular fluorine-containing hydrocarbons or other fluorine compounds, is fed into this flame.
  • the chemical conversion of the pollutant components of the exhaust gas takes place in the flame.
  • the burned exhaust gas contains gaseous reaction products of the pollutants.
  • a strongly reducing fame area is created, into which the exhaust gases to be cleaned are fed with the pollutants, on the other hand a strongly oxidizing flame area is created.
  • a strongly reducing flame is created in which the fuel gas mixture of fuel gas and oxygen, for example town gas, natural gas or hydrogen and oxygen, is fed into the burner with an excess of the fuel gas compared to the portion required for stoichiometric combustion and brought to combustion.
  • the exhaust gas usually a mixture of an inert gas (argon or nitrogen) and the fluorine-containing pollutant, such as C 2 F 6 , CHF 3 , SF 6 , NF 3 , is introduced into this flame.
  • the combustion reactions of the fuel gas run in the flame (CH 4th + 2O 2nd ⁇ CO 2nd + 2H 2nd O respectively. 2H 2nd + O 2nd ⁇ 2H 2nd O) and the reactions to Implementation of the pollutant (a possible reaction 1: 2C 2nd F 6 + 14H 2nd ⁇ 4CH 4th + 12HF and as secondary reaction 2: 4CH 4th + 8O 2nd ⁇ 4CO 2nd + 8H 2nd O) in parallel.
  • the reducing flame now contains unused fuel gas (CH 4 and H 2 in the example) and secondary pollutants (CH 4 and HF in the example).
  • the spatially separate feeding of a fuel gas mixture of a different composition into the flame creates, in addition to the reducing flame area primarily created in the burner, a second oxidizing flame area.
  • fuel gases and oxygen with a clear excess of oxygen compared to said conditions, which can burn without residue, air can be supplied as an oxygen supplier or pure oxygen at all.
  • the second oxidizing flame area is characterized by an excess of oxygen.
  • gases from the combusted fuel gas mixture CO 2 , H 2 O
  • unused fuel gas components in the example CH 4 and H 2
  • secondary pollutants in the example HF, CH 4
  • the complete combustion is also given according to the law of mass action, since an excess of oxygen is set in this flame area.
  • the heated inert components of the exhaust gas e.g. N 2
  • the inert combustion products predominantly CO 2 and water vapor
  • the secondary pollutants in the example HF
  • the secondary pollutants are removed in a manner known per se by sorption or hydrolysis.
  • the combustion products are sucked out of the combustion chamber and passed through an aqueous solution, for example in a spray washing device.
  • the method is carried out with a device which essentially consists of a preferably rotationally symmetrical combustion chamber with an annular burner arranged in an end face of the combustion chamber.
  • the fuel and the ring burner separately supplied oxygen or the fuel gas mixture (natural gas / oxygen or hydrogen / oxygen).
  • the fuel gas flame forms on the burner.
  • a feed preferably in the center of the ring burner, supplies the exhaust gas to be cleaned with the pollutants contained therein. Thanks to the central feed, the flue gas is enclosed on all sides by the fuel gas flame, an important prerequisite for effective conversion of pollutants.
  • the additional supply of fuel gas mixture with an excess of oxygen, air or pure oxygen into a ring burner takes place via one or more bores or channels of a second concentric ring.
  • a flame is formed above the burner, with a strongly reducing flame area as the core of the flame above the inner ring of the burner and with a strong one oxidizing flame area as the jacket of the flame over the outer ring of the burner.
  • the additional supply of air or oxygen takes place via one or more inlet channels in the wall the combustion chamber in the area of the ring burner.
  • a flame forms on the ring burner, the core of which is strongly reducing, since a fuel gas mixture with a deficit of oxygen is supplied to the ring burner in the sense mentioned.
  • the flame burns in the combustion chamber in a "jacket" of air or pure oxygen, so that a flame area is also formed in this way around the reducing flame area, which has a strong oxidizing effect.
  • the extraction on the combustion chamber, through which the combustion products are extracted, is dimensioned such that it passes through the holes or channels in the wall. ensures the air supply required for combustion.
  • the additional supply of air or oxygen into the flame area under positive pressure can be metered more precisely through the inlet channels in the wall of the combustion chamber.
  • Fig. 1 shows the device in a schematic longitudinal section.
  • the device according to the invention essentially consists of a cylindrical combustion chamber (1) made of a corrosion-resistant material. It has a diameter of 18 cm and is 60 cm high.
  • annular burner (3) to which the fuel gas mixture of fuel gas and oxygen is fed via a feed (4).
  • the position of the combustion chamber is vertical (other positions, also inclined, are also possible).
  • the ring burner (3) has a diameter of 25 mm.
  • the fuel gas flame (6) forms above the ring channel (5).
  • the exhaust gas with the toxic pollutants is fed to the burner (3) via the feed (7). It enters the fuel gas flame (6) centrally through the bore (8).
  • the burner (3) has an additional feed (9) for a fuel gas mixture of a different composition than that which is let into the feed (4).
  • the tubular connection for the suction (14) through which the combustion gases are either transferred into the exhaust air duct or into devices for carrying out further sub-processes of a multi-stage exhaust gas cleaning.
  • the device is completed by an ignition electrode for the fuel gas mixture and by a monitor (15) which provides sensor signals for optimal control of the device for exhaust gas purification.
  • the exhaust gas consists of approx. 58.5 l / min nitrogen and approx. 1.5 l / min C 2 F 6 as a pollutant.
  • the exhaust gas is fed to the cleaning device through an exhaust pipe.
  • 9 l / min H 2 and 9 l / min O 2 are fed to the inner ring (5) of the ring burner (3).
  • 3 l / min CH 4 and 15 l / min O 2 are additionally fed to the outer ring (10) of the ring burner (3).
  • the flame area (11) of the flame (6) which forms over the annular gap (5) is strongly reducing.
  • the exhaust gas to be cleaned which contains fluorinated hydrocarbon C 2 F 6 as the main pollutant, passes through the bore (8)
  • the pollutant is converted almost completely into CH 4 and HF.
  • the flame temperature is in the range from 1200 to 1400 ° C.
  • the flame region (12) which forms at the annular gap (10) and which envelops the flame region (11) like a jacket is strongly oxidizing.
  • the reactions that preferably take place here are the combustion of CH 4 to CO 2 and water vapor and of H 2 to water vapor.
  • the approximately 1000 ° C hot burned gas mixtures over the flame flow in the direction of arrow (13) perpendicularly from the burner (3) in the direction of the suction (14), from there they are fed to a washing device known per se, in which the gas is below 50 ° C is cooled.
  • the HF part is hydrolyzed.
  • the gas is cleaned, ie practically free of pollutants, released into the environment.
  • the pollutant content is reduced to less than 1% by means of the exhaust gas purification method according to the invention, as a result of which a gas with less than 15 ppm of pollutant enters the exhaust air.

Landscapes

  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Treating Waste Gases (AREA)
  • Incineration Of Waste (AREA)

Abstract

The device cleans or purifies waste gas containing toxic substances esp. with fluoride carbonated water etc. The method uses chemical conversion in a combustion chamber with a burner for generating a burning gas flame. By spatial separation of the feeding in of gases of different combinations and quantities into the flame a flame region of reduced chemical strength is created. The gas to be cleaned is fed into this region. A strongly oxidised flame region is also formed. The gas is put into this region and then it is passed through the reduced region. The appts. for carrying out this method has a combustion chamber, a ring burner for the burning gas or gas mixture, and a central supply for the toxic waste gas into the burner. One or more inlet channels are arranged in the wall of the chamber near the burner to additionally feed in air or acid.

Description

Die Erfindung betrifft ein Verfahren und Einrichtungen zur Reinigung von schadstoffhaltigen Abgasen durch chemische Umsetzung in einer Brennkammer.The invention relates to a method and devices for cleaning pollutant-containing exhaust gases by chemical reaction in a combustion chamber.

In technischen Anlagen, insbesondere in Anlagen zur chemischen Dampfphasenabscheidung und zum Abtragen oder Abscheiden von Material durch Plasmaprozesse fallen schadstoffhaltige Abgase an. Diese Abgase enthalten u.a. fluorhaltige Kohlenwasserstoffe oder andere Fluorverbindungen. Im allgemeinen sind inerte Gase, wie Argon oder Stickstoff, Hauptbestandteile der Abgase. Diese Abgase sind wegen des hohen Anteils an derartigen Gasen selbst meist nicht brennbar. Die Schadstoffe oder deren Reaktionsprodukte wirken toxisch bzw. fördern aufgrund ihrer schädlichen Wirkung in der Atmossphäre die Ozonzerstörung und den Treibhauseffekt.In technical plants, in particular in plants for chemical vapor phase separation and for the removal or separation of material by means of plasma processes, waste gases containing pollutants are produced. These exhaust gases include fluorine-containing hydrocarbons or other fluorine compounds. In general, inert gases such as argon or nitrogen are major components of the exhaust gases. Because of the high proportion of such gases, these exhaust gases themselves are usually not combustible. The pollutants or their reaction products have a toxic effect or, due to their harmful effects in the atmosphere, promote ozone depletion and the greenhouse effect.

Zur Abgasreinigung sind eine ganze Reihe von Verfahren bekannt. Sehr häufig erfolgt die Reinigung durch Sorption der Schadstoffe aus dem Abgas, z.B. in oxidierender wässriger Lösung (DE 3342816).
Schadstoffe, die auf diese Weise nicht oder wenig effizient sorbiert werden, können durch Verfahren der chemischen Umsetzung, z.B. thermische Zersetzung (EU 0384803) durch Aufheizen oder durch Verbrennen in sauerstoffhaltiger Umgebung (US 5183 646), umgewandelt werden. Geschieht dies durch Verbrennen, müssen Abgase mit hohem Inertgasanteil in eine Brenngasflamme, z.B. aus einem Erdgas- oder Wasserstoff-/Sauerstoffgemisch, eingeführt werden. Schädliche Sekundärprodukte der Umwandlung werden anschließend, z.B durch Sorptions- oder Waschprozesse, aus dem Abgas beseitigt.
A whole series of methods are known for exhaust gas purification. The cleaning is very often carried out by sorption of the pollutants from the exhaust gas, for example in oxidizing aqueous solution (DE 3342816).
Pollutants that are not sorbed in this way or are not efficiently treated can be converted by chemical conversion processes, for example thermal decomposition (EU 0384803) by heating or by burning in an oxygen-containing environment (US Pat. No. 5,183,646). If this is done by burning, exhaust gases with a high proportion of inert gas have to be introduced into a combustion gas flame, for example from a natural gas or hydrogen / oxygen mixture. Harmful secondary products of the conversion are then removed from the exhaust gas, for example by sorption or washing processes.

Bei der Abgasreinigung handelt es sich in der Regel um einen mehrstufigen Prozeß, bei dem Teilprozesse, wie thermische Zersetzung oder Oxidation, Kühlung, Sorption , Hydrolyse und Auswaschen fester Reaktionsprodukte ablaufen (EP 89 110 875). Dazu wird das Abgas nacheinander z.B. durch eine Einrichtung mit einer Brennkammer und mindestens eine weitere Einrichtung, z.B. eine solche, die nach dem Waschprinzip wirkt, geleitet. Es sind auch Einrichtungen zur Reinigung von Abgas vorgeschlagen worden, bei denen das Abgas nacheinander durch eine Brennkammer zur Verbrennung der Schadstoffe und eine Waschkammer geleitet wird, die konstruktiv zu einer Einheit zusammengefaßt sind (EP 89 110 875).Exhaust gas cleaning is generally a multi-stage process in which partial processes such as thermal decomposition or oxidation, cooling, sorption, hydrolysis and washing out of solid reaction products take place (EP 89 110 875). For this purpose, the exhaust gas is passed in succession, for example, through a device with a combustion chamber and at least one further device, for example one which operates on the washing principle. Devices for purifying exhaust gas have also been proposed, in which the exhaust gas is passed successively through a combustion chamber for combusting the pollutants and a washing chamber, which are structurally combined to form a unit (EP 89 110 875).

Ein Nachteil solcher Verfahren und Einrichtungen mit thermischer Zersetzung der Schadstoffe in einer Brennkammer und mit einer Waschkammer sind die thermische und elektrolytische Korrosion der Wandflächen und anderer Teile, insbesondere der Brennkammer unter der Wirkung gasförmiger Reaktionsprodukte der Verbrennung. Kritisch erhöht wird diese Korrosion durch die hohe Temperatur der verbrannten Brenngasmischung und Abgase, insbesondere wenn diese z.B. Halogenwasserstoffe, wie z.B. HF, und Wasserdampf enthalten.A disadvantage of such methods and devices with thermal decomposition of the pollutants in a combustion chamber and with a washing chamber are the thermal and electrolytic corrosion of the wall surfaces and other parts, in particular the combustion chamber, under the action of gaseous reaction products from the combustion. This corrosion is critically increased by the high temperature of the burned fuel gas mixture and exhaust gases, especially if these e.g. Hydrogen halides, e.g. HF, and water vapor included.

Diesen Nachteil kann man eliminieren, wenn in einer einzigen Reaktionskammer Teilprozesse der Reinigung kombiniert zur Wirkung gebracht werden,in dem das verbrannte Abgas durch eine feinverteilte Flüssigkeit (Sorptions- bzw. Kühlmittel) geführt wird oder mit einem solchen Flüssigkeitsfilm an den Wandflächen der Brennkammer in Kontakt gebracht wird (DE 43 200 44). Die beiden zuletzt genannten Lösungen haben jedoch eine geringe Effizienz in Ihrer Reinigungswirkung , wenn man sie für Abgase mit fluorierten Kohlenwasserstoffen und mit anderen Fluorverbindungen anwendet. Bei vertretbarem Verbrauch von Brenngas enthalten die gereinigten Abgase noch kritisch hohe Anteile an Schadstoffen. Die Kühlung der Reaktorwände verringert zwar deren Korrosion, führt aber eher zur Verschlechterung der Effizienz der Reinigung. Eine Verbesserung der Effizienz der Reinigung in Richtung eines niedrigen Schadstoffgehaltes im gereinigten Abgas, kann zwar in gewissem Umfang durch Erhöhung der Brenngasmenge relativ zu Menge des zugeführten Abgases erzielt werden, jedoch ist dieser Weg wegen des erhöhten Brenngasverbrauches mit einer kritischen Verschlechterung der Ökonomie der Abgasreinigung verbunden.This disadvantage can be eliminated if partial cleaning processes are combined in a single reaction chamber, in which the burned exhaust gas is passed through a finely divided liquid (sorbent or coolant) or in contact with such a liquid film on the wall surfaces of the combustion chamber brought (DE 43 200 44). However, the last two solutions mentioned have a low efficiency in their cleaning effect when used for exhaust gases with fluorinated hydrocarbons and with other fluorine compounds. With justifiable consumption of fuel gas, the cleaned exhaust gases still contain critically high proportions of pollutants. The cooling of the reactor walls reduces their corrosion, but rather leads to a deterioration in the efficiency of the cleaning. To a certain extent, an improvement in the efficiency of the cleaning in the direction of a low pollutant content in the cleaned exhaust gas can be achieved by increasing the amount of fuel gas relative to the amount of the supplied exhaust gas, but this route is associated with a critical deterioration in the economy of the exhaust gas cleaning because of the increased fuel gas consumption .

Da in der Brenngasflamme mit Abgaszufuhr im allgemeinen mehrere Reaktionen ablaufen, deren wichtigste Ergebnisse die Verbrennung des Brenngases (z.B. Erdgas oder Wasserstoff) unter der Einwirkung des mit zugeführten Sauerstoffes zum Zwecke der thermischen Aktivierung der Schadgase und die chemische Umsetzung der Schadgase in hydrolisierbare und absorbierbare bzw. unschädliche Verbindungen sind, ist aufgrund der Reaktionskinetik nicht zu erwarten, daß die gewünschte Umsetzung des Schadgases vollständig erfolgt. Dies gilt insbesondere auch, wenn alle Reaktanden (Brenngas, Sauerstoff und Schadgas) im stöchiometrischen Verhältnis zugeführt werden. Infolge des Inertgasanteiles im Schadgas wird die Reaktionskinetik ungünstig beeinflußt und damit die Umsetzung des Schadgases anteilmäßig weiter verringert.Since several reactions generally take place in the fuel gas flame with exhaust gas supply, the most important results of which are the combustion of the fuel gas (e.g. natural gas or hydrogen) under the influence of the oxygen supplied for the purpose of thermal activation of the harmful gases and the chemical conversion of the harmful gases into hydrolyzable and absorbable or Because of the reaction kinetics, harmless compounds are not to be expected that the desired conversion of the harmful gas takes place completely. This also applies in particular if all reactants (fuel gas, oxygen and harmful gas) are supplied in a stoichiometric ratio. As a result of the proportion of inert gas in the harmful gas, the reaction kinetics are adversely affected and the proportion of the conversion of the harmful gas is further reduced.

Eine Erhöhung des Brenngasanteiles im Brenngasgemisch ( EP-A-0347 753 ) gegenüber dem stöchiometrischen Verhältnis für alle zugeführten Reaktanden, verbessert zwar die Schadstoffumsetzung, insbesondere bei fluorhaltigen Kohlenwasserstoffen, führt jedoch zum Ausstoß unverbrannter, auch schädlicher Brenngase aus der Reinigungsanlage. Eine Erhöhung des Sauerstoffanteils im Brenngasgemisch gegenüber dem stöchiometrischen Verhältnis führt andererseits zur kritischen Verschlechterung der Schadstoffumsetzung für fluorhaltige Abgase und damit zu unvertretbar hohen restlichen Schadstoffanteilen im gereinigten Abgas.An increase in the proportion of fuel gas in the fuel gas mixture (EP-A-0347 753) compared to the stoichiometric ratio for all reactants supplied does improve the conversion of pollutants, in particular in the case of fluorine-containing hydrocarbons, but leads to the emission of unburned, even harmful, fuel gases from the cleaning system. An increase in the oxygen content in the fuel gas mixture compared to the stoichiometric ratio leads on the other hand to the critical deterioration of the pollutant conversion for fluorine-containing exhaust gases and thus to an unacceptably high residual pollutant content in the cleaned exhaust gas.

Der Erfindung liegt die Aufgabe zugrunde, die Wirksamkeit der Reinigung von Abgasen durch chemische Umsetzung in einer Brenngasflamme zu verbesern, d.h. den prozentualen Restanteil an Schadstoffen im gereinigten Abgas drastisch zu reduzieren. Außerdem besteht die Aufgabe zu sichern, daß bei der Reaktion in der Brenngasflamme entstehende Zwischenprodukte effektiv verbrannt werden. Weiterhin sollen auch keine unverbrannten Bestandteile des Brenngases im gereinigten Abgas enthalten sein. Insbesondere ist zu erreichen, daß bei der Verbrennung keine sekundären Schadstoffe entstehen und mit dem gereinigten Abgas abgegeben werden. The invention has for its object to improve the effectiveness of the purification of exhaust gases by chemical conversion in a fuel gas flame, ie to drastically reduce the percentage of residual pollutants in the cleaned exhaust gas. There is also the task of ensuring that intermediate products formed during the reaction in the fuel gas flame are effectively burned. Furthermore, no unburned constituents of the fuel gas should be contained in the cleaned exhaust gas. In particular, it can be achieved that no secondary pollutants arise during combustion and are released with the cleaned exhaust gas.

Erfindungsgemäß wird die Aufgabe durch ein Verfahren nach Anspruch 1, 2 und 3 und eine Einrichtung nach Anspruch 4 oder 5 gelöst. According to the invention the object is achieved by a method according to claim 1, 2 and 3 and a device according to claim 4 or 5 .

Das Verfahren geht davon aus, daß in einer Brennkammer mit einem Brenner zur Erzeugung einer Brenngasflamme ein Brenngasgemisch genutzt wird und daß in diese Flamme das Abgas, welches die Schadstoffe, insbesondere fluorhaltige Kohlenwasserstoffe oder andere Fluorverbindungen enthält, zugeführt wird. In der Flamme erfolgt die chemische Umsetzung der Schadstoffanteile des Abgases. Das verbrannte Abgas enthält gasförmige Reaktionsprodukte der Schadstoffe. The method assumes that a fuel gas mixture is used in a combustion chamber with a burner to generate a fuel gas flame and that the exhaust gas, which contains the pollutants, in particular fluorine-containing hydrocarbons or other fluorine compounds, is fed into this flame. The chemical conversion of the pollutant components of the exhaust gas takes place in the flame. The burned exhaust gas contains gaseous reaction products of the pollutants.

Erfindungsgemäß wird durch räumliche Trennung der Einspeisung von Gasen unterschiedlicher Zusammensetzung und Menge in die Brenngasflamme einerseits ein stark reduzierender Fammenbereich geschaffen, in den die zu reinigenden Abgase mit den Schadstoffen eingespeist werden, andererseits wird ein stark oxidierender Flammenbereich geschaffen. Zunächst wird eine stark reduzierende Flamme geschaffen, in dem das Brenngasgemisch aus Brenngas und Sauerstoff, z.B. Stadtgas, Erdgas oder Wasserstoff und Sauerstoff, mit einem Überschuß des Brenngases gegenüber dem, zur stöchiometrischen Verbrennung notwendigem Anteil, in den Brenner eingespeist und zur Verbrennung gebracht wird. Gegenüber dem stöchiometrischen Verhältnis des Brenngasgemisches, beispielsweise CH4: O2 = 1 : 2 oder H2: O2 = 2 : 1, die ohne Rückstand an Brenngas (CH4 bzw. H2) verbrennen können ,wird ein reduzierender Flammenbereich durch einen Überschuß an Wasserstoff in der Brenngasflamme erreicht, in dem im Brenngasgemisch das Verhältnis der Anteile wasserstoffhaltiger Komponenten erhöht wird, im Beispiel Veränderung der Verhältnisse in Richtung CH4: O2= 1 : 1 bzw. H2: O2 = 4 : 1. Die mit einem Überschuß an Brenngas betriebene Flamme erzeugt die notwendige Energie zur Aktivierung der Reaktanden und zum Aufbrechen der chemischen Bindungen. In diese Flamme wird das Abgas, in der Regel ein Gemisch aus einem inerten Gas (Argon oder Stickstoff) und dem fluorhaltigen Schadstoff, wie z.B. C2F6, CHF3, SF6, NF3, eingebracht. In der Flamme laufen die Verbrennungsreaktionen des Brenngases (CH 4 + 2O 2 → CO 2 + 2H 2 O

Figure imgb0001
bzw. 2H 2 + O 2 → 2H 2 O)
Figure imgb0002
und die Reaktionen zur Umsetzung des Schadstoffes (eine mögliche Reaktion 1: 2C 2 F 6 + 14H 2 → 4CH 4 + 12HF
Figure imgb0003
und als sekundäre Reaktion 2: 4CH 4 + 8O 2 → 4CO 2 +8H 2 O)
Figure imgb0004
parallel ab. According to the invention , by spatially separating the feed of gases of different composition and quantity into the fuel gas flame, on the one hand a strongly reducing fame area is created, into which the exhaust gases to be cleaned are fed with the pollutants, on the other hand a strongly oxidizing flame area is created. First, a strongly reducing flame is created in which the fuel gas mixture of fuel gas and oxygen, for example town gas, natural gas or hydrogen and oxygen, is fed into the burner with an excess of the fuel gas compared to the portion required for stoichiometric combustion and brought to combustion. Compared to the stoichiometric ratio of the fuel gas mixture, for example CH 4 : O 2 = 1: 2 or H 2 : O 2 = 2: 1, which can burn without residue of fuel gas (CH 4 or H 2 ), a reducing flame area is created by a Excess hydrogen in the fuel gas flame is reached by increasing the ratio of the proportions of hydrogen-containing components in the fuel gas mixture, in the example changing the ratios in the direction of CH 4 : O 2 = 1: 1 or H 2 : O 2 = 4: 1 Flame operated with an excess of fuel gas generates the energy required to activate the reactants and break the chemical bonds. The exhaust gas, usually a mixture of an inert gas (argon or nitrogen) and the fluorine-containing pollutant, such as C 2 F 6 , CHF 3 , SF 6 , NF 3 , is introduced into this flame. The combustion reactions of the fuel gas run in the flame (CH 4th + 2O 2nd → CO 2nd + 2H 2nd O
Figure imgb0001
respectively. 2H 2nd + O 2nd → 2H 2nd O)
Figure imgb0002
and the reactions to Implementation of the pollutant (a possible reaction 1: 2C 2nd F 6 + 14H 2nd → 4CH 4th + 12HF
Figure imgb0003
and as secondary reaction 2: 4CH 4th + 8O 2nd → 4CO 2nd + 8H 2nd O)
Figure imgb0004
in parallel.

Infolge der besagten Zusammensetzung des Brenngasgemisches ist zunächst nicht nur seine Verbrennung unvollständig, sondern von den Reaktionen zur Umsetzung des Schadgases wird das Reaktionsgleichgewicht in der Brenngasflamme in Richtung der Reduktion (im angenommenen Beispiel Reaktion 1) verschoben. Ursache dafür ist der Überschuß von Wasserstoff im Reaktionsraum, so daß das Massenwirkungsgesetz in Richtung der vollständigen Umsetzung des Schadstoffes (im Beispiel C2F6 in HF) wirkt. Die möglichst vollständige Umsetzung des Schadstoffes ist das Ziel der Reinigung, um den prozentualen Anteil von Schadstoff im Abgas so gering wie möglich zu erzielen.As a result of the composition of the fuel gas mixture, not only is its combustion incomplete, but the reaction equilibrium in the combustion gas flame is shifted from the reactions to the conversion of the harmful gas in the direction of the reduction (in the assumed example reaction 1). The reason for this is the excess of hydrogen in the reaction space, so that the law of mass action acts in the direction of the complete conversion of the pollutant (in the example C 2 F 6 in HF). The most complete implementation of the pollutant is the goal of cleaning in order to achieve the lowest possible percentage of pollutant in the exhaust gas.

In der reduzierend wirkenden Flamme sind aber jetzt unverbrauchtes Brenngas (im Beispiel CH4 und H2) und sekundäre Schadstoffe (im Beispiel CH4 und HF) enthalten.However, the reducing flame now contains unused fuel gas (CH 4 and H 2 in the example) and secondary pollutants (CH 4 and HF in the example).

Durch die räumlich getrennte Einspeisung eines Brenngasgemisches anderer Zusammensetzung in die Flamme wird neben dem reduzierenden, im Brenner primär geschaffenen Flammenbereich, ein zweiter oxidierender Flammenbereich geschaffen. Es können dazu Brenngase und Sauerstoff mit einem deutlichen Überschuß an Sauerstoff, gegenüber besagten Verhältnissen, die ohne Rückstand verbrennen können, Luft als Sauerstofflieferant oder überhaupt reiner Sauerstoff zugeführt werden.The spatially separate feeding of a fuel gas mixture of a different composition into the flame creates, in addition to the reducing flame area primarily created in the burner, a second oxidizing flame area. For this purpose, fuel gases and oxygen with a clear excess of oxygen, compared to said conditions, which can burn without residue, air can be supplied as an oxygen supplier or pure oxygen at all.

Der zweite oxidierende Flammenbereich ist durch einen Überschuß an Sauerstoff charakterisiert. In ihn strömen aus dem reduzierend wirkenden Flammenbereich neben Gasen des verbrannten Brenngasgemisches (CO2, H2O) noch unverbrauchte Brenngasanteile (im Beispiel CH4 und H2 und sekundäre Schadstoffe (im Beispiel HF, CH4), die jetzt vollständig oxidiert bzw. verbrannt werden. Die vollständige Verbrennung ist auch nach dem Massenwirkungsgesetz gegeben, da in diesem Flammenbereich ein Überschuß an Sauerstoff eingestellt ist.The second oxidizing flame area is characterized by an excess of oxygen. In addition to gases from the combusted fuel gas mixture (CO 2 , H 2 O), unused fuel gas components (in the example CH 4 and H 2 and secondary pollutants (in the example HF, CH 4 ), which now completely oxidize or The complete combustion is also given according to the law of mass action, since an excess of oxygen is set in this flame area.

Aus dem oxidierenden Flammenbereich strömen die erhitzten inerten Bestandteile des Abgases (z.B. N2), die inerten Verbrennungsprodukte (vorwiegend CO2 und Wasserdampf) und die sekundären Schadstoffe (imBeispiel HF). Die sekundären Schadstoffe werden in an sich bekannter Weise durch eine Sorption oder Hydrolyse beseitigt. Im einfachsten Fall werden dazu die Verbrennungsprodukte aus der Brennkammer abgesaugt und durch eine wässerige Lösung, z.B. in einer Sprühwascheinrichtung geführt.The heated inert components of the exhaust gas (e.g. N 2 ), the inert combustion products (predominantly CO 2 and water vapor) and the secondary pollutants (in the example HF) flow out of the oxidizing flame area. The secondary pollutants are removed in a manner known per se by sorption or hydrolysis. In the simplest case, the combustion products are sucked out of the combustion chamber and passed through an aqueous solution, for example in a spray washing device.

Das Verfahren wird mit einer Einrichtung ausgeführt, die im wesentlichen aus einer vorzugsweise rotationssymmetrischen Brennkammer mit einem, in einer Stirnfläche der Brennkammer angeordneten Ringbrenner, besteht. Dem Ringbrenner wird das Brenngas und getrennt Sauerstoff oder das Brenngasgemisch zugeführt (Erdgas/Sauerstoff oder Wasserstoff/Sauerstoff). Am Brenner bildet sich die Brenngasflamme aus. Durch eine Zuführ, vorzugsweise im Zentrum des Ringbrenners,wird das zu reinigende Abgas, mit den darin enthaltenen Schadstoffen zugeführt. Durch die zentrale Zuführ ist das Abgas allseitig von der Brenngasflamme umschlossen, eine wichtige Voraussetzung für die effektive Schadstoffumsetzung. The method is carried out with a device which essentially consists of a preferably rotationally symmetrical combustion chamber with an annular burner arranged in an end face of the combustion chamber. The fuel and the ring burner separately supplied oxygen or the fuel gas mixture (natural gas / oxygen or hydrogen / oxygen). The fuel gas flame forms on the burner. A feed, preferably in the center of the ring burner, supplies the exhaust gas to be cleaned with the pollutants contained therein. Thanks to the central feed, the flue gas is enclosed on all sides by the fuel gas flame, an important prerequisite for effective conversion of pollutants.

Erfindungsgemäß erfolgt die zusätzliche Zuführ von Brenngasgemisch mit einem Überschuß an Sauerstoff, von Luft oder reinem Sauerstoff in einen Ringbrenner über eine oder mehrere Bohrungen oder Kanäle eines zweiten konzentrischen Ringes. Bei dem Betrieb des Brenners mit den besagten zwei konzentrischen Ringen für die Zuführ von Brenngasgemischen mit Sauerstoffdefizit bzw, mit Sauerstoffüberschuß bildet sich über dem Brenner eine Flamme aus, mit einem stark reduzierenden Flammenbereich als Kern der Flamme über dem inneren Ring des Brenners und mit einem stark oxidierenden Flammenbereich als Mantel der Flamme über dem äußeren Ring des Brenners.According to the invention , the additional supply of fuel gas mixture with an excess of oxygen, air or pure oxygen into a ring burner takes place via one or more bores or channels of a second concentric ring. When the burner is operated with the said two concentric rings for supplying fuel gas mixtures with an oxygen deficit or with an excess of oxygen, a flame is formed above the burner, with a strongly reducing flame area as the core of the flame above the inner ring of the burner and with a strong one oxidizing flame area as the jacket of the flame over the outer ring of the burner.

In einer anderen erfindungsgemäßen Ausführung der Einrichtung mit einem an sich bekannten Ringbrenner mit einem Ring für die Zuführ des Brenngasgemisches mit erhöhtem Brenngasanteil und mit einer zentralen Zufuhr für das schadstoffhaltige Abgas, erfolgt die zusätzliche Zufuhr von Luft oder Sauerstoff über ein oder mehrere Einlaßkanäle in der Wand der Brennkammer im Bereich des Ringbrenners. Am Ringbrenner bildet sich eine Flamme aus, deren Kern stark reduzierend ist, da dem Ringbrenner ein Brenngasgemisch mit einem Defizit an Sauerstoff im besagten Sinne zugeführt wird. Die Flamme brennt in der Brennkammer in einem "Mantel" von Luft bzw. reinem Sauerstoff, so daß sich auch auf diese Weise um den reduzierend wirkenden Fammenbereich ein Flammenbereich ausbildet, der stark oxidierend wirkt.In another embodiment of the device according to the invention with a ring burner known per se with a ring for supplying the fuel gas mixture with an increased fuel gas content and with a central supply for the pollutant-containing exhaust gas, the additional supply of air or oxygen takes place via one or more inlet channels in the wall the combustion chamber in the area of the ring burner. A flame forms on the ring burner, the core of which is strongly reducing, since a fuel gas mixture with a deficit of oxygen is supplied to the ring burner in the sense mentioned. The flame burns in the combustion chamber in a "jacket" of air or pure oxygen, so that a flame area is also formed in this way around the reducing flame area, which has a strong oxidizing effect.

Die Absaugung an der Brennkammer, durch die die Verbrennungsprodukte abgesaugt werden, wird derart dimensioniert, daß sie über die Bohrungen oder Kanäle in der Wand. die für die Verbrennung erforderliche Luftzuführ gewährleistet.The extraction on the combustion chamber, through which the combustion products are extracted, is dimensioned such that it passes through the holes or channels in the wall. ensures the air supply required for combustion.

Exakter kann die zusätzliche Zuführ von Luft oder Sauerstoff in den Flammenbereich unter Überdruck durch die Einlaßkanäle in der Wand der Brennkammer dosiert werden.The additional supply of air or oxygen into the flame area under positive pressure can be metered more precisely through the inlet channels in the wall of the combustion chamber.

Die Erfindung wird im folgenden anhand eines Verfahrensbeispiels und anhand der Zeichnung Fig. 1 einer bevorzugten Ausführungsform der Einrichtung näher erläutert. Die Fig. 1 zeigt die Einrichtung in einem schematischen Längsschnitt. The invention is explained in more detail below with the aid of a method example and with reference to the drawing Fig. 1 of a preferred embodiment of the device . Fig. 1 shows the device in a schematic longitudinal section.

Die erfindungsgemäße Einrichtung besteht im wesentlichen aus einer zylindrischen Brennkammer (1) aus einem korrosionsbeständigen Material. Sie hat 18 cm Durchmesser und ist 60 cm hoch. Im Bereich einer Stirnfläche (2) der Brennkammer (1) ist ein Ringbrenner (3) angeordnet, dem das Brenngasgemisch aus Brenngas und Sauerstoff über eine Zufuhr (4) zugeführt wird. Im Beispiel ist dieLage der Brennkammer vertikal (andere Lagen,auch schräge, sind ebenso möglich). Der Ringbrenner (3) hat einen Durchmesser von 25 mm. Über dem Ringkanal (5) bildet sich die Brenngasflamme (6) aus. Das Abgas mit den toxischen Schadstoffen wird dem Brenner (3) über die Zufuhr (7) zugeführt. Es tritt durch die Bohrung (8) zentral in die Brenngasflamme (6) ein. The device according to the invention essentially consists of a cylindrical combustion chamber (1) made of a corrosion-resistant material. It has a diameter of 18 cm and is 60 cm high. In the area of an end face (2) of the combustion chamber (1) there is an annular burner (3) to which the fuel gas mixture of fuel gas and oxygen is fed via a feed (4). In the example, the position of the combustion chamber is vertical (other positions, also inclined, are also possible). The ring burner (3) has a diameter of 25 mm. The fuel gas flame (6) forms above the ring channel (5). The exhaust gas with the toxic pollutants is fed to the burner (3) via the feed (7). It enters the fuel gas flame (6) centrally through the bore (8).

Der Brenner (3) besitzt eine zusätzliche Zufuhr (9) für ein Brenngasgemisch anderer Zusammensetzung als die, die in die Zufuhr (4) eingelassen wird.The burner (3) has an additional feed (9) for a fuel gas mixture of a different composition than that which is let into the feed (4).

An der Brennkammer ist der rohrförmige Anschluß für die Absaugung (14 ), durch die die Verbrennungsgase entweder in den Abluftkanal oder in Einrichtungen zur Durchführung weiterer Teilprozesse einer mehrstufigen Abgasreinigung überführt werden.At the combustion chamber is the tubular connection for the suction (14) through which the combustion gases are either transferred into the exhaust air duct or into devices for carrying out further sub-processes of a multi-stage exhaust gas cleaning.

Die Einrichtung wird komplettiert durch eine Zündelektrode für das Brenngasgemisch und durch einen Monitor (15), der Sensorsignale zur optimalen Steuerung der Einrichtung zur Abgasreinigung liefert.The device is completed by an ignition electrode for the fuel gas mixture and by a monitor (15) which provides sensor signals for optimal control of the device for exhaust gas purification.

Beispiel für die Ausführung des Verfahrens:Example of the execution of the procedure:

In einer Plasma-Ätzanlage zum Abtragen von Siliziumoxidschichten auf Siliziumscheiben fallen 60 l/min Abgas an. Das Abgas besteht aus ca 58,5 l/min Stickstoff und ca 1,5 l/min C2F6 als Schadstoff. Das Abgas wird der Reinigungseinrichtung durch eine Abgasleitung zugeführt. In der Brennkammer (1) werden dem inneren Ring (5) des Ringbrenners (3) 9 l/min H2 und 9 l/min O2 zugeführt. Dem äußeren Ring (10) des Ringbrenners (3) werden zusätzlich 3 l/min CH4 und 15 l/min O2 zugeführt. Der sich über dem Ringspalt (5) ausbildende Flammenbereich (11) der Flamme (6) ist stark reduzierend In diesen stark reduzierenden Flammenbereich (11), wird das zu reinigende Abgas, daß als hauptsächlichen Schadstoff Fluorkohlenwasserstoff C2F6 enthält, durch die Bohrung (8) eingelassen.In diesem reduzierenden Flammenbereich (11) wird der Schadstoff praktisch vollständig in CH4 und HF umgesetzt. Die Flammtemperatur liegt im Bereich von 1200 bis 1400°C.In a plasma etching system for removing silicon oxide layers on silicon wafers, 60 l / min of exhaust gas are produced. The exhaust gas consists of approx. 58.5 l / min nitrogen and approx. 1.5 l / min C 2 F 6 as a pollutant. The exhaust gas is fed to the cleaning device through an exhaust pipe. In the combustion chamber (1) 9 l / min H 2 and 9 l / min O 2 are fed to the inner ring (5) of the ring burner (3). 3 l / min CH 4 and 15 l / min O 2 are additionally fed to the outer ring (10) of the ring burner (3). The flame area (11) of the flame (6) which forms over the annular gap (5) is strongly reducing. In this strongly reducing flame area (11), the exhaust gas to be cleaned, which contains fluorinated hydrocarbon C 2 F 6 as the main pollutant, passes through the bore (8) In this reducing flame area (11) the pollutant is converted almost completely into CH 4 and HF. The flame temperature is in the range from 1200 to 1400 ° C.

Der sich am Ringspalt (10) ausbildende Flammenbereich (12), der den Flammenbereich (11) wie einen Mantel umhüllt, ist stark oxidierend. Die hier vorzugsweise ablaufende Reaktionen sind die Verbrennung von CH4 zu CO2 und Wasserdampf und von H2 zu Wasserdampf. Die etwa 1000°C heißen verbrannten Gasgemische über der Flamme strömen in Pfeilrichtung (13) senkrecht vom Brenner (3) in Richtung der Absaugung (14), von dort werden sie einer an sich bekannten Wascheinrichtung zugeführt,in der das Gas auf unter 50°C abgekühlt wird. Der HF-Anteil wird hydrolisiert. Das Gas wird wird gereinigt, d.h. praktisch schadstoffrei, an die Umgebung abgegeben. Es wird eine Reduzierung des Schadstoffgehalts mit Hilfe des erfindungsgemäßen Verfahrens zur Abgasreinigung auf weniger als 1% erreicht, infolgedessen gelangt ein Gas mit weniger als 15 ppm Schadstoff in die Abluft.The flame region (12) which forms at the annular gap (10) and which envelops the flame region (11) like a jacket is strongly oxidizing. The reactions that preferably take place here are the combustion of CH 4 to CO 2 and water vapor and of H 2 to water vapor. The approximately 1000 ° C hot burned gas mixtures over the flame flow in the direction of arrow (13) perpendicularly from the burner (3) in the direction of the suction (14), from there they are fed to a washing device known per se, in which the gas is below 50 ° C is cooled. The HF part is hydrolyzed. The gas is cleaned, ie practically free of pollutants, released into the environment. The pollutant content is reduced to less than 1% by means of the exhaust gas purification method according to the invention, as a result of which a gas with less than 15 ppm of pollutant enters the exhaust air.

Claims (5)

Verfahren zur Reinigung von schadstoffhaltigen Abgasen, insbesondere mit fluorhaltigen Kohlenwasserstoffen und anderen Fluorverbindungen durch chemische Umsetzung in einer Brennkammer mit einem Brenner zur Erzeugung einer Brenngasflamme, dadurch gekennzeichnet, daß durch räumliche Trennung der Einspeisung von Gasen unterschiedlicher Zusammensetzung und Menge in die Brenngasflamme einerseits ein chemisch stark reduzierender Flammenbereich geschaffen wird, in den die zu reinigenden Abgase eingespeist werden und andererseits ein stark oxidierender Flammenbereich geschaffen wird, in den die Abgase gelangen, nach dem sie durch den reduzierenden Flammenbereich geströmt sind.Process for the purification of pollutant-containing exhaust gases, in particular with fluorine-containing hydrocarbons and other fluorine compounds, by chemical reaction in a combustion chamber with a burner for producing a fuel gas flame, characterized in that, on the one hand, a chemically strong gas is separated by spatially separating the feed of gases of different compositions and amounts into the combustion gas flame reducing flame area is created, into which the exhaust gases to be cleaned are fed and, on the other hand, a strongly oxidizing flame area is created, into which the exhaust gases enter after they have flowed through the reducing flame area. Verfahren nach Anspruch 1, dadurch gekennzeichnet, daß der reduzierende Flammenbereich durch Zufuhr eines Brenngases und Sauerstoff oder eines Brenngasgemisches mit einem Überschuß an Wasserstoff erzeugt wird und daß der oxidierende Flammenbereich durch zusätzliche Zufuhr von einem Brenngasgemisch mit einem Überschuß von Sauerstoff, von reinem Sauerstoff oder von Luft in die Flamme erzeugt wird.A method according to claim 1, characterized in that the reducing flame area is generated by supplying a fuel gas and oxygen or a fuel gas mixture with an excess of hydrogen, and in that the oxidizing flame area is produced by additional supply of a fuel gas mixture with an excess of oxygen, pure oxygen or Air is created in the flame. Verfahren nach Anspruch 1 und 2, dadurch gekennzeichnet, daß schädliche Reaktionsprodukte der Verbrennung in den besagten zwei Flammenbereichen durch nachfolgende Sorption und / oder Hydrolyse beseitigt werden.Process according to claims 1 and 2, characterized in that harmful reaction products of the combustion in said two flame areas are eliminated by subsequent sorption and / or hydrolysis. Einrichtung zur Ausführung des Verfahrens nach Anspruch 1 bis 3 mit einer Brennkammer, einem Ringbrenner für das Brenngas oder das Brenngasgemisch und einer zentralen Zuführ für das schadstoffhaltige Abgas in den Ringbrenner, dadurch gekennzeichnet, daß für eine zusätzliche Zufuhr von einem Brenngas oder Brenngasgemisch mit einem Überschuß an Sauerstoff am Ringbrenner, oder für eine zusätzliche Zufuhr von reinem Sauerstoff, ein zweiter konzentrischer Ring mit ein oder mehreren Bohrungen oder mit einem Kanal an dem Ringbrenner angeordnet wird.Device for carrying out the method according to claims 1 to 3 with a combustion chamber, a ring burner for the fuel gas or the fuel gas mixture and a central feed for the pollutant-containing exhaust gas in the ring burner, characterized in that for an additional supply of a fuel gas or fuel gas mixture with an excess of oxygen on the ring burner, or for an additional supply of pure oxygen, a second concentric ring with one or more holes or with a channel on the ring burner is arranged. Einrichtung zur Ausführung des Verfahrens nach Anspruch 1 bis 3, mit einer Brennkammer, einem Ringbrenner für das Brenngas oder das Brenngasgemisch und einer zentralen Zufuhr für das schadstoffhaltige Abgas in den Ringbrenner, dadurch gekennzeichnet, daß für die zusätzliche Zufuhr von Luft oder Sauerstoff in der Wand der Brennkammer im Bereich des Ringbrenners ein oder mehrere Einlaßkanäle angeordnet werden.Device for carrying out the method according to claim 1 to 3, with a combustion chamber, a ring burner for the fuel gas or the fuel gas mixture and a central feed for the pollutant-containing exhaust gas in the ring burner, characterized in that for the additional supply of air or oxygen in the wall one or more inlet channels are arranged in the combustion chamber in the area of the ring burner.
EP96102122A 1995-03-30 1996-02-14 Process for purification of noxious exhaust gases by chemical conversion Expired - Lifetime EP0735321B1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DE19511644 1995-03-30
DE19511644A DE19511644A1 (en) 1995-03-30 1995-03-30 Process and device for cleaning pollutant-containing exhaust gases by chemical conversion

Publications (3)

Publication Number Publication Date
EP0735321A2 true EP0735321A2 (en) 1996-10-02
EP0735321A3 EP0735321A3 (en) 1997-03-26
EP0735321B1 EP0735321B1 (en) 2000-04-12

Family

ID=7758136

Family Applications (1)

Application Number Title Priority Date Filing Date
EP96102122A Expired - Lifetime EP0735321B1 (en) 1995-03-30 1996-02-14 Process for purification of noxious exhaust gases by chemical conversion

Country Status (2)

Country Link
EP (1) EP0735321B1 (en)
DE (2) DE19511644A1 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0768109A2 (en) * 1995-10-16 1997-04-16 Teisan Kabushiki Kaisha Exhaust gas treatment unit and process
EP0819887A3 (en) * 1996-06-19 1998-10-28 Osaka Sanso Kogyo Limited Combusting Exhaust Gas
EP1291069A1 (en) * 2001-08-30 2003-03-12 DAS-DÜNNSCHICHT ANLAGEN SYSTEME GmbH DRESDEN Process and apparatus for purifying waste gases, particularly fluor-containing, by means of a burner with separated introduction of feed gases
US7462333B2 (en) * 2002-04-11 2008-12-09 Das-Dunnschicht Anlagen Systeme Gmbh Dresden Device for the purification of exhaust gases consisting of fluorine-containing compounds in a combustion reactor
CN107191933A (en) * 2017-06-13 2017-09-22 武汉理工大学 A kind of Plasma Assisted Combustion formula multi-hole medium combustion system

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE29712026U1 (en) * 1997-07-09 1998-11-12 EBARA Germany GmbH, 63452 Hanau Burner for the combustion of exhaust gases with at least one condensable component
CN106642161A (en) * 2016-12-29 2017-05-10 江门市崖门新财富环保工业有限公司 Oxygen-enriched combustion device

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1986001131A1 (en) * 1984-08-17 1986-02-27 American Combustion, Inc. Method and apparatus for flame generation
EP0262561A2 (en) * 1986-09-29 1988-04-06 Mitsubishi Jushi Engineering Co., Ltd. Method of burning waste gases from semiconductor-manufacturing processes and an apparatus for burning the waste gases
EP0285485A1 (en) * 1987-03-18 1988-10-05 L'air Liquide, Societe Anonyme Pour L'etude Et L'exploitation Des Procedes Georges Claude Method and device for destroying toxic gaseous effluents
EP0311317A2 (en) * 1987-10-06 1989-04-12 Toyo Sanso Co., Ltd. Combustion method for specific exhaust gases containing deleterious substances

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE3529309A1 (en) * 1985-08-16 1987-03-19 Hoechst Ag DEVICE FOR THE COMBUSTION OF HYDROCARBONS
DE3802504A1 (en) * 1988-01-28 1989-08-10 Wistra Thermoprozesstech Burner
DD273008A1 (en) * 1988-06-15 1989-11-01 Elektromat Veb DEVICE FOR CLEANING EXHAUST GASES FROM LOW PRESSURE PROCESSES
US5267850A (en) * 1992-06-04 1993-12-07 Praxair Technology, Inc. Fuel jet burner

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1986001131A1 (en) * 1984-08-17 1986-02-27 American Combustion, Inc. Method and apparatus for flame generation
EP0262561A2 (en) * 1986-09-29 1988-04-06 Mitsubishi Jushi Engineering Co., Ltd. Method of burning waste gases from semiconductor-manufacturing processes and an apparatus for burning the waste gases
EP0285485A1 (en) * 1987-03-18 1988-10-05 L'air Liquide, Societe Anonyme Pour L'etude Et L'exploitation Des Procedes Georges Claude Method and device for destroying toxic gaseous effluents
EP0311317A2 (en) * 1987-10-06 1989-04-12 Toyo Sanso Co., Ltd. Combustion method for specific exhaust gases containing deleterious substances

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0768109A2 (en) * 1995-10-16 1997-04-16 Teisan Kabushiki Kaisha Exhaust gas treatment unit and process
EP0768109A3 (en) * 1995-10-16 1997-12-17 Teisan Kabushiki Kaisha Exhaust gas treatment unit and process
US5891404A (en) * 1995-10-16 1999-04-06 Teisan Kabushiki Kaisha Exhaust gas treatment unit
EP0819887A3 (en) * 1996-06-19 1998-10-28 Osaka Sanso Kogyo Limited Combusting Exhaust Gas
EP1291069A1 (en) * 2001-08-30 2003-03-12 DAS-DÜNNSCHICHT ANLAGEN SYSTEME GmbH DRESDEN Process and apparatus for purifying waste gases, particularly fluor-containing, by means of a burner with separated introduction of feed gases
US7462333B2 (en) * 2002-04-11 2008-12-09 Das-Dunnschicht Anlagen Systeme Gmbh Dresden Device for the purification of exhaust gases consisting of fluorine-containing compounds in a combustion reactor
DE10304489B4 (en) * 2002-04-11 2014-07-31 Das Environmental Expert Gmbh Device for purifying exhaust gases containing fluorine-containing compounds in a low-nitrogen-oxide combustion reactor
CN107191933A (en) * 2017-06-13 2017-09-22 武汉理工大学 A kind of Plasma Assisted Combustion formula multi-hole medium combustion system

Also Published As

Publication number Publication date
EP0735321B1 (en) 2000-04-12
EP0735321A3 (en) 1997-03-26
DE59604931D1 (en) 2000-05-18
DE19511644A1 (en) 1996-10-02

Similar Documents

Publication Publication Date Title
DE3513731C2 (en)
DD273386A5 (en) METHOD FOR WASHING THE HOT EXHAUST FLOW FROM A STEAM GENERATOR SYSTEM OR A CEMENT OVEN
DE19731062A1 (en) Process for removing sulfur oxides from flue gases
WO1995000805A1 (en) Exhaust gas cleaning process and installation
EP0309742B1 (en) Process for removal of nitrogen oxides from a flue gas stream
DE3512922A1 (en) METHOD AND DEVICE FOR PURIFYING EXHAUST GASES
EP0735321B1 (en) Process for purification of noxious exhaust gases by chemical conversion
DE60131826T2 (en) Disposal of fluorine-containing substances from gas streams
DE2259763A1 (en) DEVICE FOR CLEANING GASES CONTAINING NITROGEN OXIDES
WO1984004053A1 (en) Method and installation for the purification of combustion gas from domestic heatings, combustion engines or similar heatings
WO1999062621A1 (en) Method for purifying process waste gases
DE10304489B4 (en) Device for purifying exhaust gases containing fluorine-containing compounds in a low-nitrogen-oxide combustion reactor
DE4204603C2 (en) Device for the multi-stage, catalytic combustion of nitrogenous gases
DE3629688C2 (en) Processes for cleaning smoke and other industrial gases
EP1291069B1 (en) Process and apparatus for purifying waste gases, particularly fluor-containing, by means of a burner with separated introduction of feed gases
EP0735322B1 (en) Process and device for purification of noxious exhaust gases by chemical conversion in a flame and hot surfaces
EP0107144B1 (en) Process for the removal of air contaminants from waste gases, especially from flue gases, by condensation
EP0487834A1 (en) Oxidative washing process for cleaning waste gases
EP0735320B1 (en) Process and device for purification of noxious exhaust gases by chemical conversion
DD273009A1 (en) METHOD FOR CLEANING EXHAUST GASES FROM CVD PROCESSES
WO2003085321A1 (en) Device for the purification of exhaust gases consisting of fluorine-containing compounds in a combustion reactor
DE2920691C2 (en) Process for the preparation of pollutant compounds
DE4119630A1 (en) Flue gas purificn. - by wet scrubbing with induced oxidn. of toxic matter and sulphur di:oxide to harmless prod. suitable for dumping or reprocessing
DE4101497A1 (en) METHOD FOR THERMALLY RECONSTRUCTING AMMONIUM SULPHATE-BASED RECIPES, ESPECIALLY AMMONIUM SULPHATE-BASED WASTEWATER
AT380799B (en) METHOD AND DEVICE FOR ABSORPTION OF A GAS RESISTING FROM A CHEMICAL REACTION, MADE OF NITROGEN OXIDS OF THE GENERAL FORMULA NO X AND WATER VAPOR

Legal Events

Date Code Title Description
PUAI Public reference made under article 153(3) epc to a published international application that has entered the european phase

Free format text: ORIGINAL CODE: 0009012

AK Designated contracting states

Kind code of ref document: A2

Designated state(s): BE CH DE ES FR GB IE IT LI NL

PUAL Search report despatched

Free format text: ORIGINAL CODE: 0009013

AK Designated contracting states

Kind code of ref document: A3

Designated state(s): BE CH DE ES FR GB IE IT LI NL

17P Request for examination filed

Effective date: 19970429

17Q First examination report despatched

Effective date: 19990604

GRAG Despatch of communication of intention to grant

Free format text: ORIGINAL CODE: EPIDOS AGRA

GRAG Despatch of communication of intention to grant

Free format text: ORIGINAL CODE: EPIDOS AGRA

GRAH Despatch of communication of intention to grant a patent

Free format text: ORIGINAL CODE: EPIDOS IGRA

RTI1 Title (correction)

Free format text: PROCESS FOR PURIFICATION OF NOXIOUS EXHAUST GASES BY CHEMICAL CONVERSION

GRAH Despatch of communication of intention to grant a patent

Free format text: ORIGINAL CODE: EPIDOS IGRA

GRAA (expected) grant

Free format text: ORIGINAL CODE: 0009210

AK Designated contracting states

Kind code of ref document: B1

Designated state(s): BE CH DE ES FR GB IE IT LI NL

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: NL

Free format text: LAPSE BECAUSE OF FAILURE TO SUBMIT A TRANSLATION OF THE DESCRIPTION OR TO PAY THE FEE WITHIN THE PRESCRIBED TIME-LIMIT

Effective date: 20000412

Ref country code: ES

Free format text: THE PATENT HAS BEEN ANNULLED BY A DECISION OF A NATIONAL AUTHORITY

Effective date: 20000412

REG Reference to a national code

Ref country code: CH

Ref legal event code: EP

REF Corresponds to:

Ref document number: 59604931

Country of ref document: DE

Date of ref document: 20000518

REG Reference to a national code

Ref country code: IE

Ref legal event code: FG4D

Free format text: GERMAN

ET Fr: translation filed
ITF It: translation for a ep patent filed

Owner name: STUDIO TORTA S.R.L.

GBT Gb: translation of ep patent filed (gb section 77(6)(a)/1977)

Effective date: 20000703

NLV1 Nl: lapsed or annulled due to failure to fulfill the requirements of art. 29p and 29m of the patents act
PLBQ Unpublished change to opponent data

Free format text: ORIGINAL CODE: EPIDOS OPPO

PLBI Opposition filed

Free format text: ORIGINAL CODE: 0009260

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: IE

Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES

Effective date: 20010205

PLBF Reply of patent proprietor to notice(s) of opposition

Free format text: ORIGINAL CODE: EPIDOS OBSO

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: LI

Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES

Effective date: 20010228

Ref country code: CH

Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES

Effective date: 20010228

Ref country code: BE

Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES

Effective date: 20010228

REG Reference to a national code

Ref country code: IE

Ref legal event code: FD4D

26 Opposition filed

Opponent name: CENTROTHERM ELEKTRISCHE ANLAGEN GMBH & CO.

Effective date: 20010112

PLBF Reply of patent proprietor to notice(s) of opposition

Free format text: ORIGINAL CODE: EPIDOS OBSO

BERE Be: lapsed

Owner name: DUNNSCHICHT ANLAGEN SYSTEME G.M.B.H. DRESDEN DAS

Effective date: 20010228

REG Reference to a national code

Ref country code: CH

Ref legal event code: PL

REG Reference to a national code

Ref country code: GB

Ref legal event code: IF02

RTI2 Title (correction)

Free format text: PROCESS FOR PURIFICATION OF NOXIOUS EXHAUST GASES BY CHEMICAL CONVERSION

PLBO Opposition rejected

Free format text: ORIGINAL CODE: EPIDOS REJO

PGFP Annual fee paid to national office [announced via postgrant information from national office to epo]

Ref country code: GB

Payment date: 20020122

Year of fee payment: 7

RTI2 Title (correction)

Free format text: PROCESS FOR PURIFICATION OF NOXIOUS EXHAUST GASES BY CHEMICAL CONVERSION

PGFP Annual fee paid to national office [announced via postgrant information from national office to epo]

Ref country code: FR

Payment date: 20020221

Year of fee payment: 7

PLBN Opposition rejected

Free format text: ORIGINAL CODE: 0009273

STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: OPPOSITION REJECTED

27O Opposition rejected

Effective date: 20020202

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: GB

Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES

Effective date: 20030214

GBPC Gb: european patent ceased through non-payment of renewal fee
PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: FR

Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES

Effective date: 20031031

REG Reference to a national code

Ref country code: FR

Ref legal event code: ST

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: IT

Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES

Effective date: 20050214

PGFP Annual fee paid to national office [announced via postgrant information from national office to epo]

Ref country code: DE

Payment date: 20140424

Year of fee payment: 19

REG Reference to a national code

Ref country code: DE

Ref legal event code: R119

Ref document number: 59604931

Country of ref document: DE

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: DE

Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES

Effective date: 20150901