FI124206B - Process for the treatment of ash and plant for the treatment of ash - Google Patents
Process for the treatment of ash and plant for the treatment of ash Download PDFInfo
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- FI124206B FI124206B FI20125949A FI20125949A FI124206B FI 124206 B FI124206 B FI 124206B FI 20125949 A FI20125949 A FI 20125949A FI 20125949 A FI20125949 A FI 20125949A FI 124206 B FI124206 B FI 124206B
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- ash
- combustion
- flue gases
- gasification
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Classifications
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/46—Gasification of granular or pulverulent flues in suspension
- C10J3/48—Apparatus; Plants
- C10J3/52—Ash-removing devices
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F22—STEAM GENERATION
- F22B—METHODS OF STEAM GENERATION; STEAM BOILERS
- F22B1/00—Methods of steam generation characterised by form of heating method
- F22B1/02—Methods of steam generation characterised by form of heating method by exploitation of the heat content of hot heat carriers
- F22B1/18—Methods of steam generation characterised by form of heating method by exploitation of the heat content of hot heat carriers the heat carrier being a hot gas, e.g. waste gas such as exhaust gas of internal-combustion engines
- F22B1/1838—Methods of steam generation characterised by form of heating method by exploitation of the heat content of hot heat carriers the heat carrier being a hot gas, e.g. waste gas such as exhaust gas of internal-combustion engines the hot gas being under a high pressure, e.g. in chemical installations
- F22B1/1846—Methods of steam generation characterised by form of heating method by exploitation of the heat content of hot heat carriers the heat carrier being a hot gas, e.g. waste gas such as exhaust gas of internal-combustion engines the hot gas being under a high pressure, e.g. in chemical installations the hot gas being loaded with particles, e.g. waste heat boilers after a coal gasification plant
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C10/00—Fluidised bed combustion apparatus
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23L—SUPPLYING AIR OR NON-COMBUSTIBLE LIQUIDS OR GASES TO COMBUSTION APPARATUS IN GENERAL ; VALVES OR DAMPERS SPECIALLY ADAPTED FOR CONTROLLING AIR SUPPLY OR DRAUGHT IN COMBUSTION APPARATUS; INDUCING DRAUGHT IN COMBUSTION APPARATUS; TOPS FOR CHIMNEYS OR VENTILATING SHAFTS; TERMINALS FOR FLUES
- F23L15/00—Heating of air supplied for combustion
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/16—Integration of gasification processes with another plant or parts within the plant
- C10J2300/1625—Integration of gasification processes with another plant or parts within the plant with solids treatment
- C10J2300/1628—Ash post-treatment
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/16—Integration of gasification processes with another plant or parts within the plant
- C10J2300/164—Integration of gasification processes with another plant or parts within the plant with conversion of synthesis gas
- C10J2300/1643—Conversion of synthesis gas to energy
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/16—Integration of gasification processes with another plant or parts within the plant
- C10J2300/1687—Integration of gasification processes with another plant or parts within the plant with steam generation
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/72—Other features
- C10J3/82—Gas withdrawal means
- C10J3/84—Gas withdrawal means with means for removing dust or tar from the gas
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2209/00—Specific waste
- F23G2209/30—Solid combustion residues, e.g. bottom or flyash
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/16—Combined cycle power plant [CCPP], or combined cycle gas turbine [CCGT]
- Y02E20/18—Integrated gasification combined cycle [IGCC], e.g. combined with carbon capture and storage [CCS]
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/34—Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Sustainable Development (AREA)
- Life Sciences & Earth Sciences (AREA)
- Sustainable Energy (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
- Gasification And Melting Of Waste (AREA)
Description
Menetelmä tuhkan käsittelemiseksi ja tuhkan käsittelylaitosMethod for ash treatment and ash treatment plant
Keksintö kohdistuu patenttivaatimuksen 1 johdanto-osan mukaiseen menetelmään tuhkan käsittelemiseksi. Keksintö kohdistuu myös tuhkan käsittely-5 laitokseen, joka on patenttivaatimuksen 6 johdanto-osan mukainen.The invention relates to a method for treating ash according to the preamble of claim 1. The invention also relates to an ash treatment plant according to the preamble of claim 6.
Yksi tapa tuottaa polttoainetta on kaasuttaa hiilipitoista raaka-ainetta, jolloin siitä muodostuu kaasua, joka voidaan polttaa. Raaka-aineina ovat erityisen suosittuja jätemateriaalit, jotka ovat yleensä eloperäistä materiaalia, kuten 10 erilaista puujätettä ja pakkausjätettä (esimerkiksi kartonki ja paperi). Materiaalista käytetään myös nimitystä kierrätyspolttoaine.One way to produce fuel is to gasify a carbonaceous raw material, which produces gas that can be burned. The raw materials are particularly popular waste materials, which are usually organic materials such as 10 different types of wood waste and packaging waste (for example, cardboard and paper). The material is also referred to as recycled fuel.
Kaasutus tapahtuu tavallisesti leijupetikäsittelynä korkeassa lämpötilassa ali-ilmaisissa olosuhteissa. Saatu tuotekaasu soveltuu poltettavaksi esimerkiksi 15 tavanomaisessa voimalaitoskattilassa.The gasification is usually effected as a fluidized bed treatment at elevated temperature under undetermined conditions. The resulting product gas is suitable for combustion in, for example, 15 conventional power plant boilers.
Jätteen kaasutuksessa syntyy lentotuhkaa, joka erotetaan kaasuttimesta tulevasta tuotekaasuvirtauksesta kuumana ns. kuumasuodintuhkana. Tämä tuhka sisältää mm. reagoimatonta hiiltä (nokea), petimateriaalia ja poltto-20 aineen tuhkakomponentteja (mm. alkalimetalleja, raskasmetalleja ja klorideja).The gasification of waste generates fly ash, which is separated from the product gas stream from the gasifier when hot. kuumasuodintuhkana. This ash contains e.g. unreacted carbon (carbon black), bed material, and ash components (including alkali metals, heavy metals, and chlorides) of fuel.
Kuumasuodintuhkassa on runsaasti hiiltä, n. 20 - 30 p-%. Kuumasuo- dintuhkaa ei pystytä kuitenkaan hyötykäyttämään, vaan se joudutaan toimit- 25 tamaan jätteenkäsittelijälle sen muuttamiseksi loppusijoitukseen soveltuvaan muotoon. Suuresta hilipitoisuudesta johtuen kuumasuodintuhka on ongel- ^ majätettä.The hot filter ash is high in carbon, about 20-30% by weight. However, the hot filter ash cannot be recovered, but must be delivered to a waste handler to convert it to a disposal form. Due to the high lecithin content, the hot filter ash is a hazardous waste.
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i g Kuumasuodintuhkan lämpöarvo on hiilipitoisuuden johdosta n. 8-11 MJ/kg.i g Due to its carbon content, the calorific value of the hot filter ash is approximately 8-11 MJ / kg.
i co 30 Jotta tuhkan lämpöarvoa ei menetettäisi ja jätteeksi menevän tuhkan määrää x voitaisiin vähentää, onkin kehitetty prosesseja tuhkan polttamiseksi. Oni co 30 In order to avoid losing the ash calorific value and reducing the amount of ash x that becomes waste, processes have been developed to burn the ash. Is
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esimerkiksi kehitetty CFB-polttolaitteistoa, jossa polton savukaasut johdetaan ^ kaasutuksen tuotekaasua polttavan kattilan jälkeiseen savukaasukanavaan g ennen pussisuodattimia olevaan kohtaan, minkä johdosta niitä jäähdytetään g 35 alle 200 °C:een.for example, a CFB combustion apparatus has been developed in which the combustion flue gases are introduced into the flue gas channel g after the gasification product gas boiler to the point before the bag filters, whereby they are cooled to below 200 ° C.
22
Suomalaisessa patentissa Fl 110266 on esitetty menetelmä käsitellä kaasutuksen tuotekaasun nokipitoisia kiintoaineita jo kaasutuslaitoksessa. Tässä menetelmässä paljon nokea sisältävä tuhka, joka on erotettu tuotekaasu-virrasta, johdetaan hapettimena toimivaan leijukerrosreaktoriin, jossa se pol-5 tetaan 800...900°C:n lämpötilassa hiilen hapettamiseksi hiilidioksidiksi. Polton savukaasut johdetaan takaisin kaasuttimeen sekundääriseksi kaasu-tuskaasuksi. Tätä ennen savukaasuista erotetaan tuhkaa.Finnish patent Fl 110266 discloses a method for treating sooty solids in the gasification product gas already in the gasification plant. In this process, the high carbon black ash, which is separated from the product gas stream, is fed to a fluidized bed reactor as an oxidizer, where it is incinerated at 800 to 900 ° C to oxidize the carbon to carbon dioxide. The combustion flue gases are recycled back to the carburettor as secondary gasification gas. Before this, ash is separated from the flue gases.
Tällainen savukaasujen kierrättäminen on ratkaisuna kuitenkin ongelmallista, 10 koska hapetuksesta tuleva lisäkaasuvirta sisältää runsaasti happea, mikä vaikeuttaa kaasutusprosessin hallintaa. Myös kapasiteetti laskee, koska savukaasuvirta, joka lisää inerttiä virtausta kaasuttimen läpi, syö osan kapasiteetista.However, such flue gas recycling is problematic as a solution 10 because the auxiliary gas stream from oxidation is rich in oxygen which complicates the control of the gasification process. Capacity also decreases because the flue gas stream, which increases the inert flow through the carburetor, consumes part of the capacity.
15 Julkaisussa WO 03/055962 on esitetty kaasutuksesta saadun tuhkan poltto CFB-polttoreaktorissa, josta savukaasut johdetaan kaasuttimesta tulevan tuotekaasun joukkoon, jonka mukana ne kulkeutuvat tuotekaasun jääh-dyttimen ja tuhkan suodattimen kautta tuotekaasua polttavaan kattilaan. Julkaisun mukaan polttoreaktorista tulevaan savukaasuvirtaukseen pyritään 20 saamaan myös tuhkapartikkeleita, joiden avulla sidotaan tuotekaasussa olevaa tervaa, jotta se ei tarttuisi tuotekaasun jäähdyttimeen.WO 03/055962 discloses incineration of the ash from the gasification in a CFB combustion reactor, where the flue gases are introduced into the product gas from the gasifier, where they are transported through the product gas cooler and the ash filter to the product gas burning boiler. According to the publication, it is also sought to obtain ash particles in the flue gas stream from the combustion reactor which bind the tar in the product gas so that it does not adhere to the product gas cooler.
Keksinnön tarkoituksena on esittää menetelmä, jolla poltetaan hiilipitoisia kaasutusprosessista tulevia kuumasuodintuhkia hiilen (noen) vähentämiseksi 25 ja poltosta saadut savukaasut käsitellään yksinkertaisella ratkaisulla, jolla niitä voidaan hyödyntää entistä paremmin.It is an object of the present invention to provide a process for burning carbonaceous hot filter ash from a gasification process to reduce carbon (soot) and treating the flue gases from the combustion with a simple solution that can be better utilized.
° Tämän tarkoituksen toteuttamiseksi keksinnön mukaiselle menetelmälle on i g tunnusomaista pääasiassa se, mikä on esitetty oheisen patenttivaati- i co 30 muksen 1 tunnusmerkkiosassa. 1 2 3 4 5 2In order to accomplish this purpose, the process according to the invention is characterized essentially by what is shown in the characterizing part of the appended claim co 30. 1 2 3 4 5 2
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Kaasutusprosessin tuotekaasusta erotettu tuhka hapetetaan leijupetipoltos-^ sa, ja polton tuottamat savukaasut johdetaan kaasutusprosessin tuotekaasua 4 g polttavan kattilan (pääkattilan) palamisilman joukkoon.The ash separated from the product gas of the gasification process is oxidized in fluidized bed combustion, and the flue gases produced by combustion are introduced into the combustion air of a 4 g boiler (main boiler) product of the gasification process.
5 355 35
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Sen lisäksi että kaasutuksen kuumasuodintuhkan hiilipitoisuutta saadaan laskettua, loppusijoitettavaa massaa vähennettyä ja tuhkan lämpösisältö 3 käytetyksi hyväksi, savukaasut jotka sisältävät CO:ta, voidaan polttaa kaasutuslaitoksen pääkattilassa johtamalla ne ensin pääkattilan palamisilman joukkoon. Tuhkan poltosta peräisin olevaa savukaasujen lämpösisältöä voidaan samalla käyttää palamisilman esilämmitykseen. Pääkattilassa CO 5 hapettuu.In addition to lowering the carbon content of the gasification hot filter ash, reducing the mass to be disposed of, and utilizing the thermal content of the ash 3, the flue gases containing CO can first be burned in the main boiler combustion air. At the same time, the heat content of the flue gases from the ash combustion can be used to preheat the combustion air. In the main boiler CO 5 oxidizes.
Tuhkan poltosta peräisin olevat savukaasut edullisesti suodatetaan ennen niiden johtamista kattilan palamisilman joukkoon, jolloin niistä voidaan erottaa vielä mukana oleva hienompi tuhkafraktio.The flue gases from ash combustion are preferably filtered before being introduced into the combustion air of the boiler, whereby the finer ash fraction still present can be separated from them.
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Keksintöä selostetaan seuraavassa lähemmin viittaamalla oheiseen piirustukseen, joka on tuhkan käsittelylaitoksen prosessikaavio.The invention will now be described in more detail with reference to the accompanying drawing, which is a process diagram of an ash treatment plant.
Kaasutusprosessi on sinänsä tunnettu, eikä sitä ole esitetty sen tarkemmin. 15 Raaka-aineena on tavallisimmin ns. kierrätyspolttoaine, joka on erilaista yhdyskuntajätettä ja teollisuusjätettä, yleensä energiantuotantoon sopivaa hiilipitoista kiinteää polttoainetta.The gasification process is known per se and is not described in further detail. 15 The most common raw material is so-called. recycled fuel, which is a different type of municipal and industrial waste, usually a carbonaceous solid fuel suitable for power generation.
Polttoaineen kaasutuksessa saadun palamiskykyisen tuotekaasun virtauk-20 sesta erotettua lentotuhkaa käsitellään piirustuksen esittämässä laitoksessa. Normaalisti tällainen laitos on samassa voimalaitoksessa kuin itse kaasutin ja tuotekaasua polttava voimalaitoksen pääkattila, jolla tuotetaan energiaa. Kaasutusprosessia ja siitä erotetun tuhkan (kuumasuodintuhkan) syöttöä laitoksen raaka-aineeksi on esitetty katkoviivalla. Tätä tuhkaa, joka sisältää 25 paljon kaasutetusta polttoaineesta peräisin olevaa reagoimatta jäänyttä hiiltä (nokea), syötetään leijupetireaktoriin 1, jossa tapahtuu palaminen reaktoriin ^ syötetyn happipitoisen polttoilman (nuoli A) johdosta. Leijupetireaktorissa on ° myös kiinteää petimateriaalia (hiekka, kalkkikivi tms), jota voidaan lisätä i § tarpeen vaatiessa Reaktori 1 on muurattu eli täysin lämpöeristetty CFB- i co 30 reaktori (kiertoleijureaktori), jossa ei ole lämmönvaihtopintoja. Polton lämpö- x tila reaktorissa on alle 900°C, ja se säädetään halutuksi ilmakertoimella.Fly ash separated from the flow of combustible product gas obtained from gasification of fuel is treated in the plant shown in the drawing. Normally, such a plant is located in the same power plant as the gasifier itself and the main boiler of the power plant burning the product gas, which produces energy. The gasification process and the supply of ash (hot filter ash) separated from it as a raw material for the plant are shown in dashed lines. This ash, which contains 25 unreacted carbon (soot) from the gasified fuel, is fed to the fluidized bed reactor 1, which is burned by the oxygen-containing combustion air (arrow A) supplied to the reactor. The fluidized bed reactor also contains solid bed material (sand, limestone, etc.) which can be added if required Reactor 1 is a bricked or fully heat-insulated CFB-i30 reactor (circulating fluidized bed reactor) with no heat exchange surfaces. The combustion temperature in the reactor is below 900 ° C and is adjusted to the desired air coefficient.
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j? Polttoprosessin tuottamat savukaasut kulkevat syklonin 2 kautta, jossa c\j savukaasujen mukana kulkeutunut kiinteä aines erottuu kiertoleijureaktorin ° 35 paluukiertoon. Sen jälkeen kun paluukierron aines on erottunut, savukaasut kulkeutuvat savukasukanavaa 3 pitkin lämmönvaihtimen 4 kautta, jossa niiden lämpötila lasketaan n. 400°C:een. Suodatus on yleensä edullista 4 suorittaa lämpötila-alueella 300 - 550°C. Koska savukaasut jäähdytetään vain n. 400°C:een, suurta lämmönvaihdinta (jäähdytintä) ei tarvita.j? The flue gases produced by the combustion process pass through cyclone 2, where the solid material entrained in the flue gases is separated into the circulating fluidized bed reactor ° 35 return circuit. After the return material has been separated, the flue gases are transported along the flue duct 3 via a heat exchanger 4 where their temperature is lowered to about 400 ° C. Filtration is generally preferred 4 to be carried out at a temperature in the range 300 to 550 ° C. Because the flue gases are only cooled to about 400 ° C, no large heat exchanger (cooler) is required.
Tuhkan karkeampi jae poistetaan leijupetireaktorista 1 alakautta pohjatuh-5 kana, ja hienompi jae, joka ei erotu syklonissa 2 kiertoleijureaktorin paluu-kiertoon, kulkeutuu savukaasujen mukana savukaasukanavaa 3 pitkin lämmönvaihtimen 4 kautta tuhkanerottimeen 5, jossa tuhka erotetaan. Tuhkanerotin on kaasusuodatin, jossa hieno tuhkajae erotetaan suodattamalla. Kaasusuodattin on ns. kuumasuodin, esimerkiksi kuitukeraaminen 10 suodin.The coarser fraction of ash is removed from the fluidized bed reactor 1 below the bottom ash chicken 5, and the finer fraction which is not separated in cyclone 2 into the circulating fluidized bed reactor return passes along the flue gas channel 3 through the heat exchanger 4 to the ash separator 5. The ash separator is a gas filter where the fine ash is separated by filtration. The gas filter is so called. a heat filter, for example a fiber-ceramic filter 10.
Lämmönvaihtimen 4 avulla voidaan ottaa talteen tuhkan hiilen poltosta saatua energiaa, ja samalla savukaasujen lämpötila saadaan laskettua suodatukselle sopivaksi. Lämmönvaihtimessa 4 lämmönvaihto tapahtuu 15 epäsuoralla periaatteella, eli lämpö siirtyy ilman suoraa kontaktia savukaasuista lämmönsiirtoväliaineeseen.By means of the heat exchanger 4, the energy obtained from the combustion of the ash coal can be recovered, while the temperature of the flue gases can be lowered to be suitable for filtration. In heat exchanger 4, heat exchange takes place on the 15 indirect principles, i.e., heat is transferred without direct contact from the flue gases to the heat transfer medium.
Tuhkanerottimen 5 jälkeen savukaasukanava 3 liittyy kaasutuslaitoksen pääkattilalle 8 palamisilmaa tuovaan palamisilmakanavaan 6. Savukaasu-20 kanavassa 3 tulevat savukaasut sekoittuvat näin palamisilman joukkoon esilämmittäen samalla sitä. Palamisilmakanavaa 6 pitkin savukaasut ja palamisilma kulkeutuvat pääkattilan 8 polttoprosessiin, johon tuodaan polttoaineeksi tuotekaasua kanavaa 7 pitkin kaasutusprosessista. 1 Lämmönvaihto palamisilmakanavassa 6 tapahtuu siis suorakontaktilla kaasumaisten väliaineiden välillä. Savukaasut yhdistetään palamisilman virtauk-^ seen edullisesti niin aikaisin, että ne ovat sekoittuneet palamisilmaan ja ™ palamisilman lämpötila on tasoittunut siinä vaiheessa, kun palamisilma g injektoidaan pääkattilaan 8.After the ash separator 5, the flue gas duct 3 is connected to the combustion air duct 6 which supplies combustion air to the main boiler 8 of the gasification plant. Along the combustion air duct 6, the flue gases and combustion air are conveyed to the combustion process of the main boiler 8, where product gas is fed through the duct 7 from the gasification process. 1 The heat exchange in the combustion air duct 6 thus takes place by direct contact between gaseous media. Preferably, the flue gases are connected to the combustion air stream so early that they are mixed with the combustion air and the? Combustion air temperature is stabilized at the time when the combustion air g is injected into the main boiler 8.
cö 30 i Savukaasujen sisältämä hiilimonoksidi hapettuu hiilidioksidiksi pääkattilan 8cö 30 i The carbon monoxide contained in the flue gases is oxidized to carbon dioxide in the main boiler 8
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polttoprosessissa. Tuhkan polton suuresta ilmakertoimesta johtuen savukaa-? sut sisältävät myös runsaasti happea.the combustion process. Due to the high air coefficient of ash incineration, Sut is also rich in oxygen.
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C\1 g 35 Ainetaseista voidaan arvioida, että tuhkanpolton savukaasujen määrä on korkeintaan 10% pääkattilan 8 palamisilmasta (massasuhteena ilmaistuna).C \ 1 g 35 From the material balances, it can be estimated that the amount of flue gases from ash combustion does not exceed 10% of the combustion air (expressed as a mass ratio) of the main boiler 8.
Claims (9)
Priority Applications (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
FI20125949A FI124206B (en) | 2012-09-13 | 2012-09-13 | Process for the treatment of ash and plant for the treatment of ash |
EP13836774.3A EP2895580A4 (en) | 2012-09-13 | 2013-09-13 | A method for processing ash, and an ash processing plant |
PCT/FI2013/050891 WO2014041250A1 (en) | 2012-09-13 | 2013-09-13 | A method for processing ash, and an ash processing plant |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
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FI20125949 | 2012-09-13 | ||
FI20125949A FI124206B (en) | 2012-09-13 | 2012-09-13 | Process for the treatment of ash and plant for the treatment of ash |
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FI20125949A FI20125949A (en) | 2014-03-14 |
FI124206B true FI124206B (en) | 2014-05-15 |
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FI20125949A FI124206B (en) | 2012-09-13 | 2012-09-13 | Process for the treatment of ash and plant for the treatment of ash |
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EP (1) | EP2895580A4 (en) |
FI (1) | FI124206B (en) |
WO (1) | WO2014041250A1 (en) |
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EP0227196B1 (en) * | 1985-12-27 | 1990-08-08 | Shell Internationale Researchmaatschappij B.V. | Oxidation of flyash |
DE19539946C2 (en) * | 1995-10-26 | 2002-03-28 | Linde Gas Ag | Method and device for the integrated disposal of filter dusts in thermal treatment plants |
DE19729114A1 (en) * | 1997-07-08 | 1999-01-14 | Metallgesellschaft Ag | Heat treatment method for fine dust in exhaust fumes |
FI112952B (en) * | 2001-12-21 | 2004-02-13 | Foster Wheeler Energia Oy | Methods and devices for gasification of carbonaceous material |
EP1772511A1 (en) * | 2004-06-01 | 2007-04-11 | Japan Science and Technology Agency | Solid-fuel gasification system |
US20070295250A1 (en) * | 2006-06-27 | 2007-12-27 | Bool Lawrence E | Oxygen-enhanced combustion of unburned carbon in ash |
FI124422B (en) * | 2011-03-14 | 2014-08-29 | Valmet Power Oy | Method for ash treatment and ash treatment plant |
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2012
- 2012-09-13 FI FI20125949A patent/FI124206B/en not_active IP Right Cessation
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2013
- 2013-09-13 EP EP13836774.3A patent/EP2895580A4/en not_active Withdrawn
- 2013-09-13 WO PCT/FI2013/050891 patent/WO2014041250A1/en active Application Filing
Also Published As
Publication number | Publication date |
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EP2895580A4 (en) | 2016-04-20 |
FI20125949A (en) | 2014-03-14 |
WO2014041250A1 (en) | 2014-03-20 |
EP2895580A1 (en) | 2015-07-22 |
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