EP0154986A2 - Procédé et dispositif pour l'obtention de fumées pauvre en SOx dans des installations d'incinération - Google Patents
Procédé et dispositif pour l'obtention de fumées pauvre en SOx dans des installations d'incinération Download PDFInfo
- Publication number
- EP0154986A2 EP0154986A2 EP85102862A EP85102862A EP0154986A2 EP 0154986 A2 EP0154986 A2 EP 0154986A2 EP 85102862 A EP85102862 A EP 85102862A EP 85102862 A EP85102862 A EP 85102862A EP 0154986 A2 EP0154986 A2 EP 0154986A2
- Authority
- EP
- European Patent Office
- Prior art keywords
- fuel
- sulfur
- additive
- gas
- transport gas
- 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
Links
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L9/00—Treating solid fuels to improve their combustion
- C10L9/10—Treating solid fuels to improve their combustion by using additives
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L9/00—Treating solid fuels to improve their combustion
- C10L9/02—Treating solid fuels to improve their combustion by chemical means
Definitions
- the invention relates to a method and to devices for achieving low-SO x flue gases in combustion plants operated with finely divided carbon-containing fuels, in particular coal, in which the sulfur contained in the fuel is preferably in a finely divided additive.
- Limestone powder (CaC0 3 ), quicklime powder (Ca0) or calcium hydroxide powder (Ca (OH) 2 ) is bound in and then the desulfurized fuel is burned in the combustion chamber and the additive particles loaded with sulfur are sintered with the ash and removed.
- Harmful by-products of fossil fuel combustion are well known.
- One of the main pollutants is sulfur dioxide, from which - according to the current state of technology - around 4 million tons are blown off into the air in the Federal Republic of Germany, whereby power plants and industry are the main causes.
- sulfur dioxide from which - according to the current state of technology - around 4 million tons are blown off into the air in the Federal Republic of Germany, whereby power plants and industry are the main causes.
- the fossil fuel coal contains sulfur either as a mineral accompanying substance, in particular as pyrite (FeS 2 ), or as so-called organic sulfur.
- FeS 2 pyrite
- organic sulfur is part of the coal substance, the type of its binding to the coal is not yet known. According to his appearance in the coal can be desulfurized by mechanical or chemical processes. Both processes are tedious, with the chemical processes requiring particularly high investment and operating costs.
- coal is practically insoluble in common solvents and is therefore not susceptible to attack by selective reagents; Only the "cracking" of the whole structure allows a chemical intervention.
- combustion chamber or the flue gas discharge of the boiler system must consist of materials that tolerate the S0 2 components contained in the flue gas. As a result, the increased price for such materials must be accepted when the boiler system is being designed.
- the effectiveness of desulfurization of flue gas in the boiler depends on a large number of parameters and is highly complex.
- the type of coal, the partial pressure of S0 2 , the excess of oxygen in the flue gas, the reaction temperature or the reaction temperature gradient, the residence time of the additive in the flame zone, the turbulence in the combustion chamber, and the place where the additive is blown in play an important role into the combustion chamber, the speed of the additive blown in and other conditions, all of which are difficult or impossible to control.
- calcium sulfate formed cleaves S0 2 again at temperatures above 1200 ° C.
- the invention has for its object to provide an inexpensive method and devices with which Desulphurise fossil fuels in such a way that when they are burned in the boiler room, significant quantities of SO x no longer arise or can have a harmful effect.
- This object is achieved in that the fuel and the additive are processed in separate disintegration processes, in that an amount of freshly prepared additive corresponding to its sulfur content is then mixed in with the disintegrated fuel, and then this fuel-additive mixture has a controllable positive pressure standing and heated transport gas - while maintaining the mixing - is transported to a reactor designed as a leading section, in which the transport gas pressure suddenly relaxes and in a low-oxygen inert gas atmosphere within a controllable temperature range above the boiling point of sulfur, the residence time of the mixture and the ongoing thermodynamic and reaction-kinetic sulfur transfer process is adapted in which the sulfur is expelled from the fuel and the additives are loaded with the sulfur vapor or the gaseous sulfur compounds, whereupon n the largely sulfur-free fuel blown into the combustion chamber is burned at a temperature at which the loading of the additive particles likewise blown into the combustion chamber with the sulfur vapor or the gaseous sulfur compounds is maintained until sintering.
- the disintegration of the fuel for example the coal, is carried out in an inert gas atmosphere in a disintegrator, preferably according to German patent application DE-OS 30 34 849.3, in order to avoid self-ignition of the fuel when it is comminuted.
- the disintegration of the additive also takes place in a disintegrator, but in an independent disintegration ver drive in a normal air or oxygen atmosphere, whereby it is achieved that oxygen accumulates on the additive particles, which favors the subsequent loading of the additive particles with the sulfur vapor or the gaseous sulfur compounds which are expelled from the fuel.
- the fuels and additives prepared in separate disintegration processes are then mixed with one another, with the fine-particle fuel being mixed with a quantity of freshly prepared fine-grained additive corresponding to its sulfur content - in no case deposited, already aged additive powder.
- the mixture of finely divided fuel and highly active additive is then transported through an inert transport gas heated to approximately 500 ° to 600 ° C. to a reactor designed as a leading section, this transport taking place under a controllable excess pressure between 4 and 6 bar.
- This overpressure is necessary to prevent degassing of the fuel in the transport line, the length of which depends on the structural conditions available in front of the combustion chamber. For safety reasons, the disintegration of the fuel and the additive to fine dust is usually not carried out near the combustion chamber.
- the pressure of the hot transport gas (controllable) is suddenly released by the enlarged cross-section of the reaction chamber and the pressure drop is used via a control device to build up a vortex zone, in which the agglomeration-inhibiting and agglomeration-dissolving turbulence temperature and dwell time can be regulated are that the thermodynamic and reaction kinetic process of sulfur transfer from the fuel to the additive can be adapted to the chemo-physical properties of the fuel-additive mixture.
- the fine-grained solid fuel which has largely been freed of its sulfur content, is fed to the burner along with its already released volatile constituents and the sulfur-laden additive particles via a short delivery line behind the lead section, where it is blown into the combustion chamber with combustion air. Due to the already released volatile constituents, the fuel begins to burn out immediately after the burner nozzle. Under certain safety precautions, support torches can therefore be dispensed with.
- the additive By blowing in the very fine-grained additive particles already heated to a temperature between 500 ° and 600 ° C in the lead section into the hot flame zone of the combustion chamber, which begins immediately after the injection nozzle, the additive is sintered almost in shock and thus "sealed" together with the not combustible fiber of the fuel supplied to the ashes.
- the combustion temperature must be driven below 1850 ° C, but above 1250 ° C, so that the shock sintering ensures that sulfur is incorporated into the additive, but the splitting of the sulfur molecules into individual sulfur atoms by thermal energy, which can be explosive, is prevented before sintering. By splitting the sulfur molecules, the binding to the additive is lost due to a spontaneous rejection reaction.
- the new process enables gaseous, or at least gaseous, sulfur compounds to be transferred to an additive. It is important that due to the pressure and temperature control in the lead section, coking of the fuel, i.e. an unwanted complete degassing before the combustion chamber can be prevented.
- the solid additive itself is not flammable, due to its special reactivity it can hold vaporized sulfur or gaseous sulfur compounds at the given combustion temperature spectrum in such a way that desorbation does not take place.
- the advantage here is that the burner, chimney and flue gas outlet can consist of less good material, since they are not - as before - exposed to the aggressive S0 2 influence.
- the mixture of non-degassed, but freed from the sulfur constituents or fuel particles and additive particles with the incorporated sulfur reaches the combustion chamber in a well preheated state and does not extract as much thermal energy from the flame cone as cold-introduced mixtures of coal particles and additive Particles.
- coal can be used as fuel, which is processed in a turbo disintegration process.
- the expulsion of the sulfur from the fuel and the intensive reactions between the expelled sulfur and the additive are promoted according to the invention in that the sulfur transfer process takes place in a vortex zone, the turbulence of which builds up optimal reaction zones.
- the system for achieving low-SO X flue gases in the operation of firing systems for carrying out the method according to the invention with a device for injecting mixtures of fuels and finely divided additive particles into the combustion chamber and with a ash removal system through which - with the ashes - too the sintered additive particles loaded with the sulfur are discharged has a pressure transmitter vessel designed as a buffer for an intimate mixture of fuel and additive particles prepared in separate disintegration processes.
- This pressure transmitter vessel is on the one hand connected to a line for compressed, heated, inert transport gas and on the other hand via an arrangement for loading this transport gas with the mixture of fuel and additive particles, via a further transport line to one for evaporating the sulfur to 500 ° C to 600 ° C heatable lead section Connected: Due to the expansion of the cross-section between the transport line and the preliminary section, a shock-like relaxation of the pressure takes place in this preliminary section. As a result of this and because the residence time of the mixture in the vortex zone within the feed section can be controlled by throttling or deflecting devices and / or sieve plates, one is able to desulfurize practically any fuel according to the invention.
- the temperature within the lead section must be above the equilibrium temperature of sulfur and its steam, preferably between 500 ° C and 600 ° C.
- All control valves, mixing valves, metering or throttling devices can be operated electrically, but also pneumatically or hydraulically, or via a process computer, which controls the entire process in connection with an S0 2 measuring device installed in the flue gas extractor - if necessary also in connection with a Lead distance installed thermometer - can control.
- an optimal desulfurization of the fuel can be made possible without the coal being completely degassed in front of the combustion chamber.
- the parameters for the proper course of the desulfurization process can be optimally set, for example in accordance with the coal, by many control means.
- suitable measuring devices, evaluation circuits and control devices are therefore provided, with the aid of which the reaction temperature in the lead section or in the reactions and the pressure can be optimally adjusted.
- FIG. 1 schematically shows a furnace 1, of which a combustion chamber 2 and a flue gas outlet 6 are shown in simplified form.
- An evaporation pipeline 3 is indicated above the combustion chamber 2, for example.
- a burner device 4 is supplied with combustion air in a conventional manner via a combustion air supply line 11 and a conveying fan 12.
- a dust separator 7 and a conventional SO 2 knife 8 are provided in the flue gas outlet 6.
- the combustor 4 is supplied with the necessary fuel in the form of gas or fuel particles from a lead section 27 via a transport gas line 9, in which finely divided, preferably solid fossil fuels, the bound sulfur is removed.
- the lead section 27 has a double wall 28 which is connected via a heating gas line 26 and a heat exchanger 25 in the combustion chamber 2 and via a further heating gas line 24 to a flue gas extraction 13 in the flue gas outlet 6.
- Inert flue gas is removed via the flue gas extraction 13 behind the dust separator 7 by means of a blower 15, behind which the flue gas line 14 is divided into the already mentioned heating gas line 24 and a transport gas line 16, which will be explained later.
- the heating gas portion of the quantity of flue gas withdrawn is used to heat the lead section 26 to the predetermined one Temperature warmed up.
- pressure and temperature can be regulated so that the sulfur components are expelled from the fuel without the fuel, for example coal, being degassed.
- the temperature of the feed section 27 is kept between 500 ° and 600 ° C., ie above the boiling point of the sulfur.
- the temperature required in each case is regulated by means of temperature controllers known per se, which are not explained in detail here.
- the amount of flue gas extracted by the blower 15 passes via the transport gas line 16 and a suction filter 17 to a compressor 18 and then via a control valve 23 via the control valve 31 into the inlet line 30 or via a branched line to a transport gas inlet 47 at a pressure transmitter vessel 44.
- a heat exchanger 20 for the transport gas is provided parallel to the control valve 23 and, like the heat exchanger 25, can be arranged in the combustion chamber 2.
- the control valve 23 By means of the control valve 23, the temperature of the transport gas, which is branched off for the floating fluidized bed or fluidized bed 29 and also reaches the transport gas inlet 47, can be set or controlled in a manner known per se. It should be noted here that the dedusted flue gases removed from the flue gas outlet already have a not inconsiderable initial temperature. The transport gas therefore does not need to be heated up from the relatively cold ambient temperature.
- the temperature of the transport gas is set between 500 ° and 600 ° C for both purposes.
- the tempe Temperature control is carried out, for example, by an electronic process computer 55 explained later.
- the passing through the 'inlet conduit 30 in the flow path 27 gases are in a conventional, per se known manner to form a floating or vortex.
- a further known metering device 39 can be provided, with which a further influencing of the floating-fluidized or fluidized bed within the advance section 27, for example the pressure within the advance section, is possible.
- the intimately mixed fuel and additive particles are fed to the advance section 27 via a transport gas line 49 from a known pressure transmitter vessel 44 with an inlet seal 45 and an outlet slide valve 46 for secure shut-off, which in turn via a delivery line 42 to one in connection with the present invention not explained, known mixing device for coal dust and additive particles, is connected. Via an additional line 43 with a corresponding control valve 48, additive can be introduced into the delivery line 42 as required.
- a throttle device 38 is provided in front of the outlet slide 46.
- All control valves preferably the control valves 23, 31, 48, but also the throttle device 38, can be influenced, for example, by means of an electronic process computer, generally designated 55, by the S0 2 knife 8 in the flue gas outlet 6, possibly also by the temperature in the lead section , so that the reactions in the upstream section, ie the desulfurization of the fuel and the incorporation of the sulfur components into the additive particles, take place fully under the control of the electronic process computer 55.
- the temperature control via the electronic process computer 55 can be influenced by a thermometer 21 arranged, for example, in the lead section 27 by acting on the control valves 23 and / or 31.
- the electronic process computer 55 is also operatively connected to the metering devices 38, 39 in order to influence the dwell time in the lead section 27. Without changing anything at the core of the invention;
- the control or regulation of the fuel desulfurization in front of the combustion chamber 2 can also be carried out by other control initiations or by hand.
- a metering device 34 and a throttle valve 59 are provided in front of and behind the lead section 27, which are also connected to the electronic process computer 55. With these control elements, the dwell time in the lead section 27 and also the internal pressure conditions can be precisely controlled.
- 1 shows a very general process flow diagram to explain the new process for the desulfurization of fuel and a device suitable therefor. It is important that 4 short lines are provided between the lead section 27 and the burner device so that fuel and additive cannot cool down and agglomerate. 1 shows that with relatively simple means the new fuel desulfurization process can be used advantageously with the aid of the device explained both on new combustion plants and also on existing combustion plants 1. In all applications, extensive or complete desulphurization of the fuel particles takes place in front of the burner device 4. As a result, the s0 2 emissions in the combustion chamber and in the flue gas outlet 6 as well as the resulting contamination and destruction of these parts of the boiler system are reduced to a minimum. completely avoided. The S0 2 is not blown off into the atmosphere.
- a new feature of the first exemplary embodiment is that a storage container 19 for compressed transport gas is provided in the transport gas line 16 behind the compressor 18, and a control valve 54 for the transport gas is connected to the outlet thereof.
- an oxygen meter 56 can be provided which, when the oxygen content in the conveying gas line 16 becomes too high, switches an inert gas source 50 on and off via a control valve 51 in order to introduce more or less inert gas into the Inject transport gas line 16. This ensures that the mixture of fuel and additive particles cannot ignite before or in the lead section.
- the transport gas line 16 divides behind a further control valve 52.
- a bypass line 41 is guided over a heating device 37, in which the conveying gas is heated.
- a line 40 branches off for normal-temperature conveying gas, which reunites with the bypass line 41 upstream of the transport gas inlet 47 into the pressure transmitter vessel 44.
- the control valve 52 and the mixing valve 53 can be actuated by the electronic process computer 55, which can be influenced by the SO 2 knife 8, in order to adjust the temperature of the transport gas for the intimately mixed fuel and additive particles.
- the heating device 37 can be arranged in the combustion chamber 2. In the present exemplary embodiment, it is installed in a double wall 36 of a fluidized bed reactor 32, which is heated via the heating gas line 26, in which a regulating valve 58 is provided, which can be controlled, for example, by a thermometer 57 in the fluidized bed reactor 32.
- the temperature in the fluidized bed reactor is set depending on the fuels fired. In principle, the temperature has to be regulated so high that the sulfur components certainly escape from the fuel particles. It is advantageous if the temperature inside the fluidized bed reactor is above the boiling point of sulfur. Quick and good results can be achieved if the temperature inside the fluidized bed reactor is kept between 500 ° and 600 ° C.
- An inlet 33 of the fluidized bed reactor 32 is connected to the outlet of the pressure transmitter vessel 44 via a metering device 34 connected to the process computer 55 and / or via a metering device 39 and via the transport gas line 49.
- a throttling or deflection device 38 is arranged within the temperature-controlled fluidized bed reactor 32, behind which a fluidized bed 35 is formed from the transport gas loaded with the intimately mixed fuel and additive particles.
- the sulfur components are driven out of the fuel and taken up by the additive.
- the dwell time required for this can be controlled via the metering device 34 and / or via the metering device 39, but also with the aid of a throttle valve 59 behind the lead section 27, for example by the electronic process computer 55. Due to the temperature control, the sudden drop in pressure and the adjustable dwell time, the additive is loaded with the sulfur components.
- the process control then causes either the control valve 48 to enter more additive powder into the line 42, to extend the residence time in the fluidized bed reactor, to increase the reaction temperature or to change the pressure difference between the transport line 49 and the lead section 27.
- An additional quantity of additive particles can be entered in the delivery line 42 for the intimately mixed fuel and additive particles via an additional line 43 and a control valve 48.
- the control valve 48 is likewise connected to the electronic process computer 55 in order to always ensure the excess of additive particles in the mixture which is necessary for the desulfurization. It is advantageous if at least four times the amount of sulfur of additive particles incorporated in the fuel is available for the integration of the sulfur components.
- the plants shown in FIGS. 1 and 2 can also be combined with one another if the fuel used requires that a residual desulfurization of the fuel must be carried out behind the fluidized bed reactor 32 in a reaction zone 27 before harmful combustion of the sulfur to S0 2 takes place in the combustion chamber 2.
- coal dust particles are used as fuel, which, for example, by means of the turbo disintegration process with impact speeds of over 100 m / sec. and a grain size of 50% under 40 u has been prepared from coal if possible.
- Particularly good results are achieved when the carbon particles are processed at impact speeds of over 200 m / sec. he follows.
- coal particle surfaces are then not compressed, as is the case, for example, when the coal is comminuted in ball mills, but "broken up" in preparation for a more effective desulfurization.
- the temperature and pressure control practiced in the leading sections according to the invention only cause the sulfur constituents to be expelled, but not a simultaneous full degassing of the fuel. Fuel particles guided into the boiler room 2 over the short distance between the lead section and the burner chamber are therefore not coked, but rather fully-fledged, sulfur-free fuel.
- Highly active sulfur-binding additives for example limestone powder, quicklime powder or calcium hydroxide powder, are also obtained.
- additive particles do not have a compacted surface, as is the case with comminution in ball mills, but a surface with a broken structure that is highly active. It can saturate faster with the expelled sulfur components at the temperatures maintained and during the adjustable dwell time.
- the device according to the invention allows it to be adjusted to different fuels without difficulty.
- One is able to vary the constituents of fuel particles in the mixture and also to optimally adapt the temperature control and the dwell time in the leading sections to the fuel and its sulfur content.
- low-oxygen gas is already available for the pneumatic conveyance. The mixture cannot ignite. If the oxygen content in the transport gas nevertheless exceeds the values to be observed for safety reasons, inert gas can also be added to the transport gas removed from the flue gas.
- the additives are processed in a normal air or oxygen atmosphere in which oxygen can accumulate on the additive particles, which contributes significantly to the activation of the additive particles and promotes the binding of the sulfur components to the additive.
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
- Treating Waste Gases (AREA)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AT85102862T ATE42110T1 (de) | 1984-03-13 | 1985-03-13 | Verfahren und vorrichtung zum erzielen sox-armer rauchgase in feuerungsanlagen. |
Applications Claiming Priority (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE3409014 | 1984-03-13 | ||
DE19843409014 DE3409014C1 (de) | 1984-03-13 | 1984-03-13 | Verfahren und Vorrichtung zum Erzielen SO↓x↓-armer Rauchgase in Feuerungsanlagen |
DE3508650 | 1984-03-13 | ||
DE19853508650 DE3508650C1 (de) | 1985-03-12 | 1985-03-12 | Verfahren und Vorrichtung zum Erzielen SO↓x↓-armer Rauchgase in Feuerungsanlagen |
Publications (3)
Publication Number | Publication Date |
---|---|
EP0154986A2 true EP0154986A2 (fr) | 1985-09-18 |
EP0154986A3 EP0154986A3 (en) | 1985-12-11 |
EP0154986B1 EP0154986B1 (fr) | 1989-04-12 |
Family
ID=25819253
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP85102862A Expired EP0154986B1 (fr) | 1984-03-13 | 1985-03-13 | Procédé et dispositif pour l'obtention de fumées pauvre en SOx dans des installations d'incinération |
Country Status (4)
Country | Link |
---|---|
US (1) | US4635572A (fr) |
EP (1) | EP0154986B1 (fr) |
CS (1) | CS268518B2 (fr) |
YU (1) | YU45705B (fr) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB2196984A (en) * | 1986-09-18 | 1988-05-11 | Dopco Danish Oil Processing Co | Oil based additive for reduction of combustion formed nitrous gases |
Families Citing this family (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4895081A (en) * | 1987-04-08 | 1990-01-23 | General Signal Corporation | Gravimetric feeder, especially adapted for use in a calorimetry system |
US4846081A (en) * | 1987-04-08 | 1989-07-11 | General Signal Corporation | Calorimetry system |
US4809190A (en) * | 1987-04-08 | 1989-02-28 | General Signal Corporation | Calorimetry system |
US4893315A (en) * | 1987-04-08 | 1990-01-09 | General Signal Corporation | Calorimetry system |
DE3933374A1 (de) * | 1989-10-06 | 1991-04-18 | Metallgesellschaft Ag | Verfahren zur aufgabe von kohle-filterschlamm |
US5203267A (en) * | 1991-01-22 | 1993-04-20 | New Clear Energy, Inc. | Method and apparatus for disposing of waste material |
US5368616A (en) * | 1993-06-11 | 1994-11-29 | Acurex Environmental Corporation | Method for decreasing air pollution from burning a combustible briquette |
US5425316A (en) * | 1993-10-12 | 1995-06-20 | Nce Concepts, Ltd. | Method and apparatus for controlling a waste disposal system |
DE19706606A1 (de) * | 1997-02-20 | 1998-08-27 | Babcock Anlagen Gmbh | Verfahren zur Regelung der Temperatur in thermischen Abfallbehandlunganlagen und Abfallbehandlunganlage |
US6319717B1 (en) * | 1998-07-24 | 2001-11-20 | Lacount Robert B. | Thermal acid base accounting in mine overburden |
US20070031311A1 (en) * | 2003-06-23 | 2007-02-08 | Anthony Edward J | Regeneration of calcium oxide or calcium carbonate from waste calcium sulphide |
US20040258592A1 (en) * | 2003-06-23 | 2004-12-23 | Anthony Edward J. | Regeneration of calcium oxide or calcium carbonate from waste calcium sulphide |
IT1404132B1 (it) * | 2011-02-18 | 2013-11-15 | Cooperativa Autotrasportatori Fiorentini C A F Societa Cooperativa A R L | Produzione di idrocarburi da pirolisi di gomme. |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3949684A (en) * | 1973-08-29 | 1976-04-13 | Copeland Systems, Inc. | Method for oxidation of sulfur-containing substances |
US4111755A (en) * | 1975-10-30 | 1978-09-05 | Mcdowell-Wellman Engineering Company | Method of producing pelletized fixed sulfur fuel |
EP0043471A1 (fr) * | 1980-07-03 | 1982-01-13 | Deutsche Kommunal-Anlagen Miete GmbH | Procédé pour la fixation dans le résidu de substances formant des acides, qui résultent de la pyrolyse de déchets contenant des matières organiques |
US4395975A (en) * | 1982-01-22 | 1983-08-02 | Ashworth Robert A | Method for desulfurization and oxidation of carbonaceous fuels |
DE3325570A1 (de) * | 1983-07-15 | 1985-01-24 | Wolf-Rüdiger 4130 Moers Naß | Verfahren und vorrichtung zum entschwefeln von feststoffe enthaltenden substanzen |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE2807076C3 (de) * | 1978-02-18 | 1980-06-04 | Rheinisch-Westfaelisches Elektrizitaetswerk Ag, 4300 Essen | Verfahren zur Reduzierung der Schwefelemission von Kesselfeuerungen |
DE3036504C2 (de) * | 1980-09-27 | 1983-08-18 | Rheinische Braunkohlenwerke Ag, 5000 Koeln | Verfahren zum Entfernen von fluor- und/oder schwefelreichen Schadstoffen aus gasförmigen und flüssigen Medien |
US4547351A (en) * | 1984-05-01 | 1985-10-15 | The United States Of America As Represented By The United States Department Of Energy | Flue gas desulfurization |
-
1985
- 1985-03-11 US US06/710,127 patent/US4635572A/en not_active Expired - Fee Related
- 1985-03-13 YU YU39885A patent/YU45705B/sh unknown
- 1985-03-13 EP EP85102862A patent/EP0154986B1/fr not_active Expired
- 1985-03-13 CS CS851759A patent/CS268518B2/cs unknown
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3949684A (en) * | 1973-08-29 | 1976-04-13 | Copeland Systems, Inc. | Method for oxidation of sulfur-containing substances |
US4111755A (en) * | 1975-10-30 | 1978-09-05 | Mcdowell-Wellman Engineering Company | Method of producing pelletized fixed sulfur fuel |
EP0043471A1 (fr) * | 1980-07-03 | 1982-01-13 | Deutsche Kommunal-Anlagen Miete GmbH | Procédé pour la fixation dans le résidu de substances formant des acides, qui résultent de la pyrolyse de déchets contenant des matières organiques |
US4395975A (en) * | 1982-01-22 | 1983-08-02 | Ashworth Robert A | Method for desulfurization and oxidation of carbonaceous fuels |
DE3325570A1 (de) * | 1983-07-15 | 1985-01-24 | Wolf-Rüdiger 4130 Moers Naß | Verfahren und vorrichtung zum entschwefeln von feststoffe enthaltenden substanzen |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB2196984A (en) * | 1986-09-18 | 1988-05-11 | Dopco Danish Oil Processing Co | Oil based additive for reduction of combustion formed nitrous gases |
GB2196984B (en) * | 1986-09-18 | 1990-08-15 | Dopco Danish Oil Processing Co | Method for the reduction of environment-injurious components in flue gas, and a product for the execution of the method |
Also Published As
Publication number | Publication date |
---|---|
CS268518B2 (en) | 1990-03-14 |
EP0154986A3 (en) | 1985-12-11 |
EP0154986B1 (fr) | 1989-04-12 |
US4635572A (en) | 1987-01-13 |
CS175985A2 (en) | 1989-06-13 |
YU45705B (sh) | 1992-07-20 |
YU39885A (en) | 1988-04-30 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
EP0154986B1 (fr) | Procédé et dispositif pour l'obtention de fumées pauvre en SOx dans des installations d'incinération | |
DE2440543A1 (de) | Verfahren zur verbrennung von abfalltreibstoffen und -explosivstoffen | |
DE2931214C2 (de) | Verfahren und Vorrichtung zur Trocknung und Feinmahlung von Kohle | |
DE60008970T2 (de) | In der Zementherstellung anwendbarer Verbrennungsprozess | |
DE2633789B2 (de) | Verfahren und Vorrichtung zur . Herstellung von Petrolkokskalzinat | |
DE2621220A1 (de) | Verfahren zur behandlung von materialien und ofensystem zur waermebehandlung von materialien | |
DE2815461A1 (de) | Verfahren und vorrichtung zur thermischen behandlung von feinkoernigem gut mit heissen gasen | |
DE2611213B2 (de) | Verfahren und Anlage zur Herstellung von Ziegeln, insbesondere von Klinkern aus einer Mischung, in die ein aus insbesondere Steinkohlenkraftwerken stammender Flugstaub eingesetzt wird | |
DE2610015A1 (de) | Verfahren und vorrichtung zum brennen von kalkstein | |
DE3508650C1 (de) | Verfahren und Vorrichtung zum Erzielen SO↓x↓-armer Rauchgase in Feuerungsanlagen | |
EP1918015A1 (fr) | Equilibrage des gaz de fumées dans des installations de combustion de déchets | |
DE3324411C2 (fr) | ||
DE3409014C1 (de) | Verfahren und Vorrichtung zum Erzielen SO↓x↓-armer Rauchgase in Feuerungsanlagen | |
DE4041746C2 (de) | Verfahren zur Verbrennung von Explosivstoffen | |
DE1218927B (de) | Vorrichtung zum thermischen Behandeln von Magnesit, Dolomit und Kalk und Verfahren zu deren Betrieb | |
DE3036957C2 (fr) | ||
EP0089075B1 (fr) | Méthode pour la combustion des éléments combustibles de gaz d'échappement de fours tournants | |
DE2951104C2 (de) | Verfahren zur Herabsetzung des Anteils an Stiickoxiden im Abgas von Schmelzfeuerungen sowie Anlage zur Durchführung des Verfahrens | |
DE4139348C1 (en) | Removing sulphurous fumes from combustion gases - by mixing fuel with calcium carbonate, calcium hydroxide and calcium oxide, and spraying hot combustion gas with water | |
DE19859053C2 (de) | Verfahren zur Verbrennung von Säureharzteer in einer stationären Wirbelschichtfeuerung | |
DE2354513C3 (de) | Verfahren zur thermischen Behandlung von verunreinigten Salzlösungen | |
DE3320049A1 (de) | Verfahren zum betreiben einer wirbelschichtfeuerung | |
DE3334686A1 (de) | Verfahren und vorrichtung zur thermischen behandlung von grobkoernigen und/oder stueckigen materialien | |
DE2753390A1 (de) | Teilweiser ersatz von brennoel durch rohe mineral- oder pflanzenkohle bei der zementherstellung im trockenverfahren | |
DE1948154A1 (de) | Verfahren zur Verfeuerung von festen Brennstoffen und Vorrichtung zur Durchfuehrung dieses Verfahrens |
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 |
Designated state(s): AT BE CH FR GB IT LI LU NL SE |
|
PUAL | Search report despatched |
Free format text: ORIGINAL CODE: 0009013 |
|
AK | Designated contracting states |
Designated state(s): AT BE CH FR GB IT LI LU NL SE |
|
17P | Request for examination filed |
Effective date: 19860605 |
|
17Q | First examination report despatched |
Effective date: 19870826 |
|
GRAA | (expected) grant |
Free format text: ORIGINAL CODE: 0009210 |
|
AK | Designated contracting states |
Kind code of ref document: B1 Designated state(s): AT BE CH FR GB IT LI LU NL SE |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: NL Effective date: 19890412 Ref country code: IT Free format text: LAPSE BECAUSE OF FAILURE TO SUBMIT A TRANSLATION OF THE DESCRIPTION OR TO PAY THE FEE WITHIN THE PRESCRIBED TIME-LIMIT;WARNING: LAPSES OF ITALIAN PATENTS WITH EFFECTIVE DATE BEFORE 2007 MAY HAVE OCCURRED AT ANY TIME BEFORE 2007. THE CORRECT EFFECTIVE DATE MAY BE DIFFERENT FROM THE ONE RECORDED. Effective date: 19890412 |
|
REF | Corresponds to: |
Ref document number: 42110 Country of ref document: AT Date of ref document: 19890415 Kind code of ref document: T |
|
GBT | Gb: translation of ep patent filed (gb section 77(6)(a)/1977) | ||
ET | Fr: translation filed | ||
NLV1 | Nl: lapsed or annulled due to failure to fulfill the requirements of art. 29p and 29m of the patents act | ||
PLBE | No opposition filed within time limit |
Free format text: ORIGINAL CODE: 0009261 |
|
STAA | Information on the status of an ep patent application or granted ep patent |
Free format text: STATUS: NO OPPOSITION FILED WITHIN TIME LIMIT |
|
REG | Reference to a national code |
Ref country code: CH Ref legal event code: PUE Owner name: CITADEL INVESTMENTS LIMITED |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: AT Effective date: 19900313 |
|
26N | No opposition filed | ||
REG | Reference to a national code |
Ref country code: FR Ref legal event code: TP |
|
REG | Reference to a national code |
Ref country code: GB Ref legal event code: 732 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: GB Payment date: 19930312 Year of fee payment: 9 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: SE Payment date: 19930322 Year of fee payment: 9 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: LU Payment date: 19930325 Year of fee payment: 9 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: FR Payment date: 19930329 Year of fee payment: 9 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: BE Payment date: 19930514 Year of fee payment: 9 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: CH Payment date: 19930610 Year of fee payment: 9 |
|
EPTA | Lu: last paid annual fee | ||
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: LU Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 19940313 Ref country code: GB Effective date: 19940313 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: SE Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 19940314 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: LI Effective date: 19940331 Ref country code: CH Effective date: 19940331 Ref country code: BE Effective date: 19940331 |
|
BERE | Be: lapsed |
Owner name: KASA-TECHNOPLAN G.M.B.H. Effective date: 19940331 |
|
GBPC | Gb: european patent ceased through non-payment of renewal fee |
Effective date: 19940313 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: FR Effective date: 19941130 |
|
REG | Reference to a national code |
Ref country code: CH Ref legal event code: PL |
|
REG | Reference to a national code |
Ref country code: FR Ref legal event code: ST |
|
EUG | Se: european patent has lapsed |
Ref document number: 85102862.1 Effective date: 19941010 |