US20110165526A1 - External preheating of fresh air in solid material furnaces - Google Patents
External preheating of fresh air in solid material furnaces Download PDFInfo
- Publication number
- US20110165526A1 US20110165526A1 US13/059,999 US200913059999A US2011165526A1 US 20110165526 A1 US20110165526 A1 US 20110165526A1 US 200913059999 A US200913059999 A US 200913059999A US 2011165526 A1 US2011165526 A1 US 2011165526A1
- Authority
- US
- United States
- Prior art keywords
- heat
- air
- fresh air
- fresh
- combustion
- 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.)
- Abandoned
Links
- 239000011343 solid material Substances 0.000 title claims abstract description 5
- 238000002485 combustion reaction Methods 0.000 claims abstract description 29
- 238000000034 method Methods 0.000 claims abstract description 18
- 238000010304 firing Methods 0.000 claims description 21
- 239000002028 Biomass Substances 0.000 claims description 15
- 239000000446 fuel Substances 0.000 claims description 11
- 239000002918 waste heat Substances 0.000 claims description 8
- 239000000463 material Substances 0.000 claims description 6
- 239000003245 coal Substances 0.000 claims description 3
- 230000000694 effects Effects 0.000 claims description 3
- 150000003839 salts Chemical class 0.000 claims description 3
- 239000000203 mixture Substances 0.000 claims description 2
- 239000002699 waste material Substances 0.000 claims description 2
- 239000003546 flue gas Substances 0.000 description 12
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 238000005516 engineering process Methods 0.000 description 5
- 239000004449 solid propellant Substances 0.000 description 5
- 238000005260 corrosion Methods 0.000 description 4
- 230000007797 corrosion Effects 0.000 description 4
- 239000004744 fabric Substances 0.000 description 4
- 239000007789 gas Substances 0.000 description 4
- 238000001816 cooling Methods 0.000 description 3
- 238000011161 development Methods 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 230000005611 electricity Effects 0.000 description 2
- 239000013505 freshwater Substances 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 230000005855 radiation Effects 0.000 description 2
- 230000001172 regenerating effect Effects 0.000 description 2
- 239000013535 sea water Substances 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000001311 chemical methods and process Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000010344 co-firing Methods 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 238000010612 desalination reaction Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 239000002803 fossil fuel Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 239000003345 natural gas Substances 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000001681 protective effect Effects 0.000 description 1
- 238000003303 reheating Methods 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 239000010801 sewage sludge Substances 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000010902 straw Substances 0.000 description 1
- 239000008400 supply water Substances 0.000 description 1
Images
Classifications
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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
- F23L15/04—Arrangements of recuperators
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01K—STEAM ENGINE PLANTS; STEAM ACCUMULATORS; ENGINE PLANTS NOT OTHERWISE PROVIDED FOR; ENGINES USING SPECIAL WORKING FLUIDS OR CYCLES
- F01K13/00—General layout or general methods of operation of complete plants
- F01K13/006—Auxiliaries or details not otherwise provided for
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F22—STEAM GENERATION
- F22B—METHODS OF STEAM GENERATION; STEAM BOILERS
- F22B31/00—Modifications of boiler construction, or of tube systems, dependent on installation of combustion apparatus; Arrangements or dispositions of combustion apparatus
- F22B31/0007—Modifications of boiler construction, or of tube systems, dependent on installation of combustion apparatus; Arrangements or dispositions of combustion apparatus with combustion in a fluidized bed
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/30—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having a fluidised bed
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
- F23G5/46—Recuperation of heat
-
- 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
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2206/00—Waste heat recuperation
- F23G2206/20—Waste heat recuperation using the heat in association with another installation
- F23G2206/203—Waste heat recuperation using the heat in association with another installation with a power/heat generating installation
-
- 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
- Y02E20/12—Heat utilisation in combustion or incineration of waste
-
- 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
Definitions
- the invention relates to a method of using the heat in the low-temperature range below 1000° C., preferably below 500° C., in the form of preheated air in a solid-fuel firing system.
- biothermal, solar-thermal, and nuclear power plants for generating electricity that, just like refuse-burning plants and plants that use the waste heat from exothermic chemical processes, are restricted in the maximum temperature achievable in order to convert heat into electricity at a high level of efficiency according to Carnot's theorem.
- the flue gas can generally be cooled down to just above the feed water temperature. Limits are no longer placed on feed water preheating relative to the properties of the water due to the use of supercritical steam. In terms of energy, regenerative fresh-air preheating is required and standard practice; flue gases are thus cooled down further and flue gas losses are minimized. The recycled flue-gas heat directly displaces fuel heat and thus constitutes one of the most effective measures for increasing the efficiency of power plants.
- solid-material firing systems are known in which the combustion material is first combusted substoichiometrically, and the low-calorific gas or flue gas generated in the first step is combusted completely only in the last stage. Air is added in stages to do this.
- This firing technology for solid fuels that is implemented practically, for example in the form of a grate-firing systems, pulverized-fuel firing systems, or firing by spreader stoker firing, allows the real temperatures in the furnace chamber to be reduced, thereby enabling a higher-level of fresh-air preheating to be achieved.
- Known examples include the straw firing in the power plant in Aved ⁇ re, Denmark, and the substitute fuel power plant in Södertälje, Sweden with multistage addition of air.
- the object of this invention is to provide a method comprising an optimized firing technology for priority solid fuels having the capability of maximum internal and external fresh-air preheating.
- the basic idea of this invention consists in combining fresh-air preheating with a grate-firing system comprising substoichiometric combustion and multiple air staging, or with circulating fluidized-bed firing.
- a grate-firing system comprising substoichiometric combustion and multiple air staging, or with circulating fluidized-bed firing.
- what is used for firing are solid fuels such as biomass, industrial or municipal wastes, coal, or mixtures of these materials.
- Geothermal heat, solar-thermal heat, or heat from refuse incineration and waste heat from exothermic processes are preferably used to effect preheating of the fresh air.
- waste heat that can be considered is unused district heat during warm-weather periods, for example during the summer.
- preheating the air to 80° C. to 150° C. can be achieved that, based on the preheating potential, enables energy to be exploited that otherwise would remain unused.
- energy can be introduced from solar collectors into an efficient combustion process of a modern biomass power plant, even at northern latitudes, which energy is usable there at an efficiency of more than 35% for generating electric power.
- the waste heat in combustion processes that can be obtained from the flue gas can be used effectively for fresh-air preheating, an approach that is more effective than using this energy for condensate heating in the water-steam circuit.
- preheated fresh air is added in staged fashion, where the combustion process is effected for an extended period of time substoichiometrically, while the combustible material is only burned completely during the last stages.
- a mean is temperature of approximately 900° C. can be maintained in a grate-type combustion system by adding additional air as secondary, tertiary, quarternary, and quinternary air, which action should in idealized terms obtain a temperature between 850° C. and 950° C.
- Circulating fluidized-bed combustion represents the best available combustion technology for fresh-air preheating.
- cooling is effected by the circulating ash through a fluidized-bed cooler, thereby enabling up to 80% of the rated thermal input to be exploited by cooling ash at an optimum temperature level of 500° C. to 750° C.
- Fresh-air preheating of up to a maximum of 750° C. is possible for primary air, and up to 1000° C. for secondary air, with circulating fluidized-bed combustion.
- Solar towers for example together with fields of heliostats for concentrating radiation and receivers are known from the area of solar thermal energy, where these either directly preheat air to temperatures of 700° C. to 1000° C., or also use a thermal oil circuit with output temperatures of almost 400° C., or use the current state of the art with molten salt to achieve an output temperature of 565° C. so as to enable implementation of external fresh-air preheating.
- FIGS. 1-3 are schematic diagrams depicting facilities for implementing the method according to the invention.
- FIG. 1 illustrates a combination of a solar-thermal plant and with biomass-fired circulating fluidized-bed combustion ZWS. Radiation is reflected in a solar field 1 . 2 to a solar tower 1 . 1 that preheats the air to 300° C. to 700° C., the air being then delivered as preheated fresh air to a circulating fluidized-bed combustion facility 1 . 3 . The heat thus generated is transferred through a fluidized-bed cooler and a waste-heat superheater to saturated steam, after which the superheated steam is passed to a turbine 1 . 13 to generate power. The condensate returns through a preheater to the feed water pump. The flue gas is cooled in an air preheater 1 .
- the flue gas temperature being reduced from 350° C. down to values around 130° C. so as to allow for flue gas cleaning and minimize flue gas losses.
- the fresh air delivered through the air preheater 1 . 7 to the solar tower is preheated to approximately 300° C.
- the residual heat contained in the flue gas leaving the fabric filter is used to dry the biomass in another air preheater, this biomass being subsequently delivered as fuel to the circulating fluidized-bed combustion facility ZWS.
- FIG. 2 illustrates the combination of the above-mentioned facility with solar seawater desalinization (MED).
- MED solar seawater desalinization
- the fresh water is produced is sufficient for irrigating the biomass production area, thereby enabling the biomass used for reheating to be generated locally on site.
- parabolic troughs 2 . 2 are provided that are filled with thermal oil that is heated to approximately 390° C., and used in the customary way to generate steam and to partially superheat the steam.
- the last superheating stage is provided by the combustion facility that in turn is operated with external solar fresh-air preheating.
- the live steam fed to the turbines is at a temperature of 540° C. at a pressure of 150 bar.
- the fresh air is preheated by the flue gas in a heat exchanger to around 165° C.
- the preheated air is further heated to 350° C. by hot thermal oil from a parabolic trough solar field.
- a grate-firing system with multiple air staging functions as the combustion furnace, where preheated fresh air is delivered in each added-air supply.
- biomass serves as the fuel.
- Another example of an application is the use of waste heat from a small-scale refuse incineration facility to preheat the secondary air of a coal-fired power plant after fresh-air preheating within the power plant.
- the refuse incineration is effected as stationary fluidized-bed combustion for mechanically dewatered sewage sludge that requires a high level of internal fresh-air preheating. Almost all of the combustion heat can be transferred by thermal oil or molten salt at temperatures of 300° C.-500° C., and used to effect fresh-air preheating for the coal-fired power plant.
- the gross efficiency of refuse incineration approximately matches that of the coal-fired power plant.
Landscapes
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Air Supply (AREA)
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
- Processing Of Solid Wastes (AREA)
Applications Claiming Priority (5)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DE102008048097.5 | 2008-09-19 | ||
| DE102008048097 | 2008-09-19 | ||
| DE102008064321.1 | 2008-12-20 | ||
| DE102008064321A DE102008064321A1 (de) | 2008-09-19 | 2008-12-20 | Externe Frischluftvorwärmung bei Feststofffeuerungen |
| PCT/DE2009/001224 WO2010031374A2 (fr) | 2008-09-19 | 2009-08-31 | Préchauffage d'air frais externe pour des foyers à combustible solide |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| US20110165526A1 true US20110165526A1 (en) | 2011-07-07 |
Family
ID=41719958
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US13/059,999 Abandoned US20110165526A1 (en) | 2008-09-19 | 2009-08-31 | External preheating of fresh air in solid material furnaces |
Country Status (4)
| Country | Link |
|---|---|
| US (1) | US20110165526A1 (fr) |
| EP (1) | EP2405196A1 (fr) |
| DE (1) | DE102008064321A1 (fr) |
| WO (1) | WO2010031374A2 (fr) |
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| US20120255471A1 (en) * | 2011-04-11 | 2012-10-11 | Hitachi, Ltd. | Solar Boiler System |
| US20130042857A1 (en) * | 2010-04-29 | 2013-02-21 | Mario Magaldi | Storing and transport device and system with high efficiency |
| US20130269631A1 (en) * | 2010-12-21 | 2013-10-17 | Inbicon A/S | Steam Delivery System for Biomass Processing |
| CN103836609A (zh) * | 2013-12-04 | 2014-06-04 | 成信绿集成股份有限公司 | 一种电厂锅炉烟气粉尘的减排系统 |
| US10081556B2 (en) * | 2008-04-15 | 2018-09-25 | Morningside Venture Investments Limited | Systems and methods for water reclamation |
| CN114738725A (zh) * | 2022-05-06 | 2022-07-12 | 西安交通大学 | 煤基固体废弃物预热直燃及余热梯级利用系统、操作方法 |
| US20250012439A1 (en) * | 2013-11-07 | 2025-01-09 | Gate 5 Energy Partners, Inc. | Thermal sludge to energy transformer |
| CN120008065A (zh) * | 2025-04-07 | 2025-05-16 | 临沂市阳光热力有限公司 | 一种用于工业锅炉的空气预热装置 |
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| GB0909061D0 (en) * | 2009-05-27 | 2009-07-01 | Doosan Babcock Energy Ltd | System for heat a primary air stream |
| DE102013203089A1 (de) * | 2013-02-25 | 2014-08-28 | Dürr Systems GmbH | Verbrennungsanlage, Werkstückbehandlungsanlage und Verfahren zum Betreiben einer Verbrennungsanlage |
| CN107270374A (zh) * | 2017-05-09 | 2017-10-20 | 北京万机汇机电工程技术有限公司 | 一种熔盐储热式集中供暖系统 |
| DE102018201172A1 (de) * | 2018-01-25 | 2019-07-25 | Siemens Aktiengesellschaft | Verbrennungsanlage mit Restwärmenutzung |
| DE102019125615A1 (de) * | 2019-09-24 | 2021-03-25 | Steuerungsbau Hanswille GmbH | Verbrennungsvorrichtung |
| CN113217939B (zh) * | 2021-04-28 | 2022-10-25 | 西安热工研究院有限公司 | 一种塔式太阳能提高垃圾电站进风温度及燃料热值的系统 |
| CN113446619A (zh) * | 2021-06-24 | 2021-09-28 | 华能秦煤瑞金发电有限责任公司 | 一种冷风蒸汽加热装置 |
| CN115013099B (zh) * | 2022-06-01 | 2023-06-27 | 昆明理工大学 | 一种生物质能与csp结合的新能源发电系统、运行方法 |
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2008
- 2008-12-20 DE DE102008064321A patent/DE102008064321A1/de not_active Withdrawn
-
2009
- 2009-04-11 EP EP09005279A patent/EP2405196A1/fr not_active Withdrawn
- 2009-08-31 WO PCT/DE2009/001224 patent/WO2010031374A2/fr not_active Ceased
- 2009-08-31 US US13/059,999 patent/US20110165526A1/en not_active Abandoned
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Also Published As
| Publication number | Publication date |
|---|---|
| WO2010031374A3 (fr) | 2012-01-26 |
| EP2405196A1 (fr) | 2012-01-11 |
| DE102008064321A1 (de) | 2010-04-01 |
| WO2010031374A2 (fr) | 2010-03-25 |
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