EP3004570A2 - Procédé de récupération d'eaux usées de processus provenant d'une centrale thermique à vapeur à combustible fossile et centrale thermique à vapeur à combustible fossile - Google Patents

Procédé de récupération d'eaux usées de processus provenant d'une centrale thermique à vapeur à combustible fossile et centrale thermique à vapeur à combustible fossile

Info

Publication number
EP3004570A2
EP3004570A2 EP14758816.4A EP14758816A EP3004570A2 EP 3004570 A2 EP3004570 A2 EP 3004570A2 EP 14758816 A EP14758816 A EP 14758816A EP 3004570 A2 EP3004570 A2 EP 3004570A2
Authority
EP
European Patent Office
Prior art keywords
water
flue gas
steam
fossil
cooling tower
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.)
Withdrawn
Application number
EP14758816.4A
Other languages
German (de)
English (en)
Inventor
Ute AMSLINGER
Anke SÖLLNER
Wolfgang Glück
Peter Widmann
Werner Spies
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.)
Siemens AG
Original Assignee
Siemens AG
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Siemens AG filed Critical Siemens AG
Publication of EP3004570A2 publication Critical patent/EP3004570A2/fr
Withdrawn legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01KSTEAM ENGINE PLANTS; STEAM ACCUMULATORS; ENGINE PLANTS NOT OTHERWISE PROVIDED FOR; ENGINES USING SPECIAL WORKING FLUIDS OR CYCLES
    • F01K25/00Plants or engines characterised by use of special working fluids, not otherwise provided for; Plants operating in closed cycles and not otherwise provided for
    • F01K25/005Plants or engines characterised by use of special working fluids, not otherwise provided for; Plants operating in closed cycles and not otherwise provided for the working fluid being steam, created by combustion of hydrogen with oxygen
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01KSTEAM ENGINE PLANTS; STEAM ACCUMULATORS; ENGINE PLANTS NOT OTHERWISE PROVIDED FOR; ENGINES USING SPECIAL WORKING FLUIDS OR CYCLES
    • F01K13/00General layout or general methods of operation of complete plants
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • C02F1/048Purification of waste water by evaporation
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01KSTEAM ENGINE PLANTS; STEAM ACCUMULATORS; ENGINE PLANTS NOT OTHERWISE PROVIDED FOR; ENGINES USING SPECIAL WORKING FLUIDS OR CYCLES
    • F01K11/00Plants characterised by the engines being structurally combined with boilers or condensers
    • F01K11/02Plants characterised by the engines being structurally combined with boilers or condensers the engines being turbines
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01KSTEAM ENGINE PLANTS; STEAM ACCUMULATORS; ENGINE PLANTS NOT OTHERWISE PROVIDED FOR; ENGINES USING SPECIAL WORKING FLUIDS OR CYCLES
    • F01K21/00Steam engine plants not otherwise provided for
    • F01K21/06Treating live steam, other than thermodynamically, e.g. for fighting deposits in engine
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01KSTEAM ENGINE PLANTS; STEAM ACCUMULATORS; ENGINE PLANTS NOT OTHERWISE PROVIDED FOR; ENGINES USING SPECIAL WORKING FLUIDS OR CYCLES
    • F01K23/00Plants characterised by more than one engine delivering power external to the plant, the engines being driven by different fluids
    • F01K23/02Plants characterised by more than one engine delivering power external to the plant, the engines being driven by different fluids the engine cycles being thermally coupled
    • F01K23/04Plants characterised by more than one engine delivering power external to the plant, the engines being driven by different fluids the engine cycles being thermally coupled condensation heat from one cycle heating the fluid in another cycle
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01KSTEAM ENGINE PLANTS; STEAM ACCUMULATORS; ENGINE PLANTS NOT OTHERWISE PROVIDED FOR; ENGINES USING SPECIAL WORKING FLUIDS OR CYCLES
    • F01K9/00Plants characterised by condensers arranged or modified to co-operate with the engines
    • F01K9/003Plants characterised by condensers arranged or modified to co-operate with the engines condenser cooling circuits

Definitions

  • the present invention relates to a steam power plant withmém and flue gas cleaning plant, and a wastewater treatment plant for process wastewater and in particular the recovery of process water.
  • the invention further relates to a method for operating a steam power plant with cooling tower and flue gas cleaning system.
  • a steam power plant essentially comprises a fired boiler, a steam turbine, a water-steam cycle, a condenser, a cooling tower and a flue gas purification plant.
  • deionized water is used, which is produced in a demineralization plant using ion exchange resins.
  • the deionized water is vaporized in the steam generator and sent to the steam turbine where it is depressurized.
  • the released during relaxation energy is transmitted via a wave to the generator.
  • the expanded steam is then fed to a condenser and the liquid phase condenses.
  • an evacuation system is connected to the condenser which generates a vacuum when the steam power plant starts up in the condenser and maintains it during operation.
  • the vacuum increases steam turbine efficiency and removes non-condensable gases from the liquid stream.
  • the impurities and additives include, in particular, ammonia, calcium, magnesium, sodium, potassium, chlorides, nitrates, sulfates (sulfuric acid) and silica.
  • the working medium contaminated by impurities or additives must be discharged as process wastewater from the water-steam cycle, since the impurities are in direct opposition to reuse as a working medium in the water-steam cycle.
  • Ammonia serves as an alkalizing agent for conditioning the feedwater.
  • the addition of ammonia makes it possible to increase the pH of the working medium, which reduces the relative corrosion rate of the feedwater. Since the distribution coefficient of ammonia in liquids and steam differs, locally significantly increased ammonia concentrations can occur in system parts with evaporation and condensation processes.
  • Process wastewater accumulates at various points in the steam power plant. A large part of contaminated water is obtained in the form of blowdown from the boiler drums in the evacuation system. When starting up and shutting down, shortages (due to dosing of working medium) and multiple stocks (due to discharge of working medium) of the working medium must be compensated. Furthermore, process waste water is produced by taking water samples and leaks in the water-steam cycle. Due to the aforementioned loss of water, the water-steam cycle must be continuous with demineralized water
  • Dewatering for example, during operation from longer closed pipelines, in which condensate has accumulated. For this purpose, the relevant pipes are opened briefly and thus dewatered. In doing so, water is lost to the water cycle, which is recirculated by additional water (deionized water). must be led. Dewatering also occurs particularly frequently when starting and stopping the steam power plant, since, for example, when the steam power plant is shut down, the steam in the water cycle gradually condenses and the resulting liquid water must not stand in the plant components, in particular in the heating surfaces. When driving off, more water is dewatered from the water cycle than is refilled until no more water is added at the end.
  • the process wastewater from the water-steam cycle is returned, depending on the quality, back into the water-steam cycle, discharged into the cooling tower or the industrial wastewater system.
  • An exemplary state-of-the-art fossil-fueled steam power plant with 2x1050 MW, a natural draft cooling tower and a wet limestone flue gas cleaning plant, produces up to 100,000 tons of process wastewater per year during basic load operation, which has to be discharged into public waters. Almost half of this is accounted for by the cooling tower.
  • the object of the invention is therefore to specify a steam power plant in which the total water consumption of a steam power plant is minimized, the pollutant capacity in the remaining wastewater, in particular the wastewater of the flue gas cleaning plant, and the consumption of demineralized / demineralized water is minimized.
  • the object of the invention is also to provide a method for operating a steam power plant, in which the total water consumption is minimized.
  • the fossil-fueled steam power plant includes a water-steam circuit, a cooling water circuit, a cooling tower and a flue gas cleaning system.
  • a fossil-fired steam generator, a steam turbine, and a capacitor are connected in the cooling water circuit.
  • a cooling tower and the condenser are interconnected in such a way that relaxed steam from the water-steam cycle in the condenser can be condensed by heat exchange with the cooling water circuit.
  • the flue gas from the fossil-fueled steam generator can be cleaned, eg by carbon dioxide (C0 2 ).
  • a process water can be supplied to the flue gas purification plant, and a process waste water can be diverted from it.
  • the flue gas cleaning system is connected to the cooling water circuit in such a way that the process water required for the flue gas cleaning can be removed from the cooling water circuit.
  • the flue gas cleaning plant is connected to a wastewater treatment plant comprising an evaporator for the discharge of process wastewater.
  • a purified process waste water can be generated by the wastewater treatment plant.
  • the invention is based on the consideration, on the one hand to use water from the cooling water circuit for flue gas cleaning, and on the other hand to clean the contaminated by the flue gas cleaning process wastewater by evaporation in Ab- water treatment plant, so that a clean process wastewater is produced.
  • the raw water demand of the steam power plant can be reduced by the amount of additional water required by the flue gas cleaning system.
  • Lower water consumption or optimized water treatment can also reduce chemical consumption, making the plant's environmental footprint more resource-efficient.
  • the distillate is of high purity and can be reused in the power plant. It is possible to introduce the distillate into the raw water tank or into the permeate tank of the demineralization plant. The heavily polluted wastewater from the flue gas cleaning is completely processed by the evaporation. The raw water requirement and the wastewater volume of the power plant are thus reduced.
  • the flue gas cleaning system is connected to the cooling water circuit after the cooling tower such that cooling tower drainage water is used as process water for the flue gas cleaning.
  • Cooling tower sewage is wastewater that is a major requirement in a power plant with a cooling tower as contaminated process water and is therefore always available. This reduces the total amount of wastewater, as the process water in the flue gas cleaning system is additionally thickened.
  • the thickening can also be considered disadvantageous depending on local guidelines and specifications or requirements, since the process wastewater in the flue gas cleaning plant is repeatedly thickened.
  • the salt and heavy metal load and the pollutant input through the flue gas cleaning in the process wastewater can be very high.
  • An improved and preferred embodiment of the fossil-fired steam power plant therefore proposes to supply the flue gas cleaning plant with a process water which is connected from the cooling water circuit upstream of the cooling tower and upstream of a cooling tower additional water treatment plant.
  • This process water has not yet been processed in the cooling tower auxiliary water treatment plant and is therefore untreated.
  • the advantage here is that the water is simply thickened in the flue gas cleaning system and therefore limits for chloride, sulfate and heavy metals can be easily complied with.
  • the additional chloride entry into the process waste water by precipitation with FeC13 in the cooling tower auxiliary water treatment is eliminated. Because the
  • Cooling tower slurry is not used here, this can be thickened higher.
  • the additional amount of water for the cooling tower is reduced because less is slurried. This reduces the water consumption of the steam power plant.
  • the required purity of the gypsum produced during operation of the steam power plant in the cooling water circuit is not used here, this can be thickened higher.
  • the additional amount of water for the cooling tower is reduced because less is slurried. This reduces the water consumption of the steam power plant.
  • the flue gas purification system is connected to the cooling water circuit in front of the cooling tower with a cooling tower auxiliary water treatment plant, so that a prepared for use in the cooling tower cooling tower water can be used as process water for flue gas cleaning.
  • a prepared for use in the cooling tower cooling tower water can be used as process water for flue gas cleaning.
  • treated coolant additive water is used as process water This is simply thickened, which makes it easier to comply with limits.
  • precipitation with FeC13 inridgetumzusatzwassers the chloride content of the water is slightly increased. Since the cooling tower slurry is no longer used, it can be thickened. This reduces the amount of makeup water added to the cooling tower as it is less likely to drain. This reduces the water consumption of the power plant. This measure may also be necessary if the total volume of waste water discharged into the forerunner is fixed.
  • the waste water treatment plant is connected to a full desalination plant connected in the water-steam cycle.
  • a purified process waste water from the wastewater treatment plant in the demineralizer can be introduced.
  • the purified process wastewater contributes to make-up in the water-steam cycle, whereby on the one hand raw water is saved for make-up, and on the other hand, the demineralizer is relieved because less deionized water (deionized) must be generated.
  • the wastewater treatment plant is connected to a cooling tower auxiliary water treatment plant connected to the cooling water circuit.
  • a purified process wastewater from the wastewater treatment plant can be introduced into the cooling tower auxiliary wastewater treatment plant.
  • the wastewater treatment plant is still connected to the condensate purification plant, the evacuation system and the sampling for the introduction of contaminated process wastewater from the water-steam cycle in the wastewater treatment plant. All process wastewater from the condensate treatment plant is returned to the water-steam cycle via the wastewater treatment plant. The process wastewater that is produced when starting up for boiler flushing is thereby regained. As boiler flushing is done with deionized water, the quality of the rejected process waste water is good.
  • the auxiliary boiler is also fed with deionized water, which is why the quality of the process waste water (blowdown) is high.
  • deionized water In the process wastewater of the auxiliary boiler, increased ion concentrations and contamination by iron particles are to be expected.
  • the demineralized plant Due to the recirculation of the condensate produced by evaporation in the wastewater treatment plant to the full demineralization plant, the demineralized plant has to process up to 75,200 tons per year of less deionized water in the exemplified steam power plant. Of this, approximately 15,000 tonnes per year are attributable to the recoverable process wastewater from boiler flushing and the startup, approx. 4,300 tonnes per year to the recoverable sludge from the
  • Auxiliary boilers up to 6,000 tons per year of process waste water from the sampling, and about 50,000 tons per year on recovery from the condenser.
  • the traceable in the water-steam cycle streams have minor impurities (eg iron particles and ammonia).
  • these flows must therefore be cleaned via the condensate purification system. This can be done by feeding into the standpipe of the condenser before the condensate cleaning system.
  • the maximum operating temperature of the ion exchangers in the condensate cleaning system must be observed.
  • the recirculated streams may need to be cooled first. The service life of the condensate cleaning system is reduced by the higher ion load.
  • the process-oriented object of the invention is solved by the features of claim 8.
  • the method of operating a fossil-fired steam power plant includes a steam power plant having a water-steam cycle, a cooling water circuit, a flue gas purification plant, and a cooling tower. In the water-steam cycle, a fossil-fired steam generator, a steam turbine, and a capacitor is connected, wherein in the
  • the flue gas purification system is supplied with a cooling tower blow-off water as process water, which is taken from the cooling water circuit to the cooling tower.
  • the flue gas purification system is supplied with a untreated cooling tower water to be treated as process water, which is supplied to the cooling flue water. Water cycle in front of the cooling tower and before a Kuhlturmzusatzwasseraufleungsstrom is removed.
  • the flue gas purification system is supplied to a prepared cooling tower water as process water, which is taken from the cooling water circuit upstream of the cooling tower of a cooling tower auxiliary water treatment plant.
  • the purified process waste water is passed from the wastewater treatment plant in a connected in the water-steam circuit desalination plant.
  • the purified process wastewater from the wastewater treatment plant is fed into a cooling tower auxiliary water treatment plant connected in the cooling water circuit.
  • the process in the wastewater treatment plant still contaminated from the water-steam cycle process wastewater from the condensate purification system, the evacuation system and the sampling initiated.
  • FIG. 2 shows a first embodiment of the fossil-fired steam power plant according to the invention with the use ofdeturmabschlemmigan as process water for
  • Flue gas cleaning a second embodiment of the fossil-fired steam power plant according to the invention with use of untreated cooling tower water as process water for flue gas cleaning
  • a third embodiment of the invention fossil-fired steam power plant with use of treated cooling tower water as process water for flue gas cleaning a fossil-fired steam power plant with cooling tower and flue gas cleaning system with process wastewater recovery.
  • 1 shows schematically a fossil-fired steam power plant 1 with cooling tower 7 and flue gas cleaning system 8 according to the prior art.
  • the fossil-fired steam power plant 1 comprises a largely closed water-steam circuit 2 and an open cooling water circuit 6.
  • water from the tower auxiliary water treatment plant 16 is deionized in a de-digestion plant 19 using ion exchange resins.
  • a contaminated process waste water 26 resulting from reverse osmosis is conducted back into the public waters via a receiving water 27.
  • a demineralized 28 formed in the demineralizer 19 is supplied to the water-steam circuit 2.
  • the deionized water 28 is evaporated in a fossil-fired steam generator 3.
  • the formed steam is expanded in a steam turbine, not shown. Subsequently, the expanded steam is condensed in a condenser.
  • the water-steam circuit 2 includes an evacuation system 21.
  • the condensate is fed to a condensate purification system 20 and subjected to mechanical cleaning.
  • a sampling 22 is seen before, can be removed through the water samples from the water-steam Kreislaus 2 continuously. Some of the water samples are mixed with chemicals.
  • the process wastewater 23 from the condensate cleaning system 20 is particularly heavily contaminated and must be supplied to an external Ent supply.
  • the heavily contaminated process wastewater 23 from the evacuation system 21, the heavily contaminated samples from the sampling 22, and the heavy contaminated process effluents 23 from the scavenging of the steam generator 3 when starting the steam generator 3 are returned to the raw water tank 24.
  • the slightly contaminated process effluents 30 from the auxiliary steam generator 29 and the condensate formed during startup in the condenser 5 are conducted into the cooling tower 7. Not shown is the return of clean condensate from the condenser 5 in the steam generator. 3
  • the cleaned in the cooling tower addition water treatment plant 16 water is passed into the condensate capacitor 5, and there guided with the expanded steam in indi rect heat exchange.
  • the steam condenses and the water in the cooling water circuit 6 heats up.
  • the warmer te water from the cooling water circuit is led to the cooling tower 7, wherein it is sprayed, and by evaporation and convection with the air, gives off heat to the ambient air.
  • the cooling tower 7 leaves a cooled down cooling water, which is discharged via the receiving water 27 into the public waters.
  • the cooling tower auxiliary water treatment plant 16 is also
  • the process water 9 contaminated in the flue gas purification system 8 by the introduction of flue gas residues is likewise discharged into the receiving water 27 as process waste water 10.
  • FIGS. 2 to 4 each show embodiments of the invention according to the invention, each having a raw water tank 24, a cooling tower auxiliary water treatment plant 16, a cooling tower 7, a flue gas purification plant 8, a wastewater treatment plant 13 comprising an evaporator 12, and a receiving water 27.
  • the raw water tank 24 raw water 25 is supplied from a public body of water, and stored in it. From the raw water tank 24, the raw water 25 is then passed into the cooling tower auxiliary water treatment plant 16, and processed in this. The treated water is subsequently passed through the cooling water circuit 6 with the expanded steam in the condenser in the heat exchange, which is not shown here in detail. The thereby warming cooling water is then fed to the cooling tower 7. The cooling tower leaves a cooled downdeturmabschlemmigan, which is discharged into the receiving water 27. 2 shows an embodiment of the invention according to the invention, wherein the flue gas cleaning plant 8 is supplied with the cooling tower blowdown water as process water 9, which is taken from the cooling water circuit 6 after the cooling tower 7.
  • the polluted process wastewater 10 leaving the flue gas purification plant 8 is fed to the wastewater treatment plant 13.
  • the remainingdeturmabschlämmigan from the cooling tower 7 is passed into the receiving water 27.
  • 3 shows a preferred embodiment of the invention, wherein the flue gas cleaning system 8 is fed to be treated untreated cooling tower water 17 as process water 9, which is taken from the cooling water circuit 6 before the cooling tower 7 and before a cooling tower auxiliary water treatment plant 16.
  • FIG 4 shows a further alternative embodiment of the invention, wherein the flue gas cleaning system 8 is fed a prepared cooling tower water 18 as process water 9, which is taken from the cooling water circuit 6 before the cooling tower 7 a cooling tower auxiliary water treatment plant 16.
  • FIG. 5 shows a fossil-fired steam power plant 1 with cooling tower 7 and flue gas cleaning plant 8 with process wastewater recovery.
  • a wastewater treatment plant 13 is provided in addition to the contaminated process wastewater from the cooling water circuit 11 and the heavily contaminated process waste water from the water-steam cycle 23rd be cleaned up.
  • the wastewater treatment plant 13 the contaminated process wastewater 10 is supplied from the flue gas cleaning system 8.
  • the wastewater treatment plant 13 the heavily contaminated process wastewater 23 from the water-steam cycle 2 from the condensate cleaning system 20, from the evacuation system 21, the sampling 22, and incurred during startup of the steam generator 3, heavily contaminated process effluents 23 from the rinsing of the steam generator - Gers 3 supplied.
  • a separate wastewater stream of the wastewater treatment plant 13 continue the slightly contaminated process effluents 30 from the water-steam cycle 2 and the condensate formed during startup in the condenser 5 fed. Not shown is the return of clean condensate from the condenser 5 in the steam generator. 3
  • the polluted process effluents are evaporated, whereby a condensate 32 and a solid 31 are formed.
  • the condensate 32 is returned either back to the cooling tower additional water treatment plant 16 or the demineralizer 19 depending on the requirement or mode of operation.

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Combustion & Propulsion (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Hydrology & Water Resources (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)
  • Treating Waste Gases (AREA)
  • Engine Equipment That Uses Special Cycles (AREA)
  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)

Abstract

L'invention concerne un procédé pour faire fonctionner une centrale thermique à vapeur à combustible fossile (1), ainsi qu'une centrale thermique à vapeur à combustible fossile (1) comprenant un circuit eau-vapeur (2), un circuit d'eau de refroidissement (6), une installation d'épuration des gaz de fumée (8) et une tour de refroidissement (7). Un générateur de vapeur à combustible fossile (3), une turbine à vapeur (4) et un condenseur (5) sont montés dans le circuit eau-vapeur (2). La tour de refroidissement (7) et le condenseur (5) sont raccordés dans le circuit d'eau de refroidissement (6) de telle sorte que la vapeur détendue provenant du circuit eau-vapeur (2) puisse être condensée dans le condenseur (5) par échange de chaleur avec le circuit d'eau de refroidissement. Les gaz de fumée provenant du générateur de vapeur à combustible fossile (3) sont épurés dans l'installation d'épuration des gaz de fumée (8), cette dernière étant alimentée en eau de processus (9) à cet effet. L'installation d'épuration des gaz de fumée (8) rejette des eaux usée de processus (10). Selon l'invention, l'installation d'épuration des gaz de fumée (8) est reliée au circuit d'eau de refroidissement (6) de telle sorte que l'eau de processus nécessaire à l'installation d'épuration des gaz de fumée (8) puisse être prélevée dans le circuit d'eau de refroidissement (6). Pour évacuer les eaux usées de processus polluées (11), l'installation d'épuration des gaz de fumée (8) est en outre reliée à une installation de traitement des eaux usées (13) qui comprend un évaporateur (12) et au moyen de laquelle des eaux usées de processus épurées (14) peuvent être produites.
EP14758816.4A 2013-08-30 2014-08-21 Procédé de récupération d'eaux usées de processus provenant d'une centrale thermique à vapeur à combustible fossile et centrale thermique à vapeur à combustible fossile Withdrawn EP3004570A2 (fr)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DE102013217335 2013-08-30
PCT/EP2014/067824 WO2015028387A2 (fr) 2013-08-30 2014-08-21 Procédé de récupération d'eaux usées de processus provenant d'une centrale thermique à vapeur à combustible fossile et centrale thermique à vapeur à combustible fossile

Publications (1)

Publication Number Publication Date
EP3004570A2 true EP3004570A2 (fr) 2016-04-13

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EP14758816.4A Withdrawn EP3004570A2 (fr) 2013-08-30 2014-08-21 Procédé de récupération d'eaux usées de processus provenant d'une centrale thermique à vapeur à combustible fossile et centrale thermique à vapeur à combustible fossile

Country Status (5)

Country Link
US (1) US20160208658A1 (fr)
EP (1) EP3004570A2 (fr)
JP (1) JP2016536518A (fr)
KR (1) KR20160047548A (fr)
WO (1) WO2015028387A2 (fr)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112321030A (zh) * 2020-11-30 2021-02-05 西安西热控制技术有限公司 一种火电厂水汽处理工艺

Citations (2)

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DE2613205A1 (de) * 1976-03-27 1977-10-06 Saarbergwerke Ag Verfahren zum reinigen von rauchgasen
DE4114333A1 (de) * 1991-05-02 1992-11-05 Buss Ag Verfahren zur aufarbeitung von anorganisch belasteten abwaessern mit verfestigung des reststoffes ohne bindemittel, insbesondere abwaessern von rauchgasreinigungsanlagen und vorrichtung zur durchfuehrung des verfahrens

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Publication number Priority date Publication date Assignee Title
US5018457A (en) * 1989-06-16 1991-05-28 Crown Andersen, Inc. Waste treatment system
US5658361A (en) * 1995-09-12 1997-08-19 Arencibia, Jr.; Jose P. Apparatus for purifying hot flue gas and for recovering thermal energy therefrom
ITPR20010080A1 (it) * 2001-11-19 2003-05-19 Amps Spa Procedimento per la condensazione di vapore proveniente
DE102009035062A1 (de) * 2009-07-28 2011-02-10 Rwe Power Ag Verfahren zum Betrieb eines Dampfturbinenkraftwerks sowie Einrichtung zur Erzeugung von Dampf
JP5704937B2 (ja) * 2011-01-31 2015-04-22 三菱日立パワーシステムズ株式会社 二酸化炭素分離回収装置を備えた火力発電システム

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2613205A1 (de) * 1976-03-27 1977-10-06 Saarbergwerke Ag Verfahren zum reinigen von rauchgasen
DE4114333A1 (de) * 1991-05-02 1992-11-05 Buss Ag Verfahren zur aufarbeitung von anorganisch belasteten abwaessern mit verfestigung des reststoffes ohne bindemittel, insbesondere abwaessern von rauchgasreinigungsanlagen und vorrichtung zur durchfuehrung des verfahrens

Also Published As

Publication number Publication date
WO2015028387A2 (fr) 2015-03-05
JP2016536518A (ja) 2016-11-24
WO2015028387A3 (fr) 2015-04-30
KR20160047548A (ko) 2016-05-02
US20160208658A1 (en) 2016-07-21

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