WO2010102854A1 - Verfahren und anlage zur verwertung von biomasse sowie blockheizkraftwerk - Google Patents
Verfahren und anlage zur verwertung von biomasse sowie blockheizkraftwerk Download PDFInfo
- Publication number
- WO2010102854A1 WO2010102854A1 PCT/EP2010/051063 EP2010051063W WO2010102854A1 WO 2010102854 A1 WO2010102854 A1 WO 2010102854A1 EP 2010051063 W EP2010051063 W EP 2010051063W WO 2010102854 A1 WO2010102854 A1 WO 2010102854A1
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- WO
- WIPO (PCT)
- Prior art keywords
- dryer
- heat
- heat exchanger
- pyrolysis
- stage
- 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.)
- Ceased
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/10—Treatment of sludge; Devices therefor by pyrolysis
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/13—Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/18—Treatment of sludge; Devices therefor by thermal conditioning
-
- 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 OR C10K; LIQUIFIED PETROLEUM GAS; USE OF ADDITIVES TO FUELS OR FIRES; FIRE-LIGHTERS
- C10L3/00—Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B23/00—Heating arrangements
- F26B23/001—Heating arrangements using waste heat
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B23/00—Heating arrangements
- F26B23/10—Heating arrangements using tubes or passages containing heated fluids, e.g. acting as radiative elements; Closed-loop systems
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/06—Sludge reduction, e.g. by lysis
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/10—Energy recovery
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B2200/00—Drying processes and machines for solid materials characterised by the specific requirements of the drying goods
- F26B2200/18—Sludges, e.g. sewage, waste, industrial processes, cooling towers
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P70/00—Climate change mitigation technologies in the production process for final industrial or consumer products
- Y02P70/10—Greenhouse gas [GHG] capture, material saving, heat recovery or other energy efficient measures, e.g. motor control, characterised by manufacturing processes, e.g. for rolling metal or metal working
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/40—Valorisation of by-products of wastewater, sewage or sludge processing
Definitions
- the invention concerns a process for the utilization of biogenous mass, in particular of clear sludge, in which the gas to be utilized is first dried and then thermally decomposed for the purpose of producing pyrolysis gas in a pyrolysis reactor. Furthermore, the invention relates to a plant for recycling biogenic mass.
- biogenic mass thereby falls the actual “biomass” according to biomass regulation, i. Plant residues, wastes and by-products of plant and animal origin, biowaste, waste wood, etc., as well as recycled process waste and municipal and industrial sewage sludge.
- the present invention seeks to provide a method and a plant for the recovery of biogenic mass, in particular of sewage sludge indicate which or which with high efficiency based on the energy content of the introduced biogenic mass in relation to the Recycling generated energy can be operated.
- the object is achieved with a method for utilization of biogenic mass, in particular of sewage sludge, according to the preamble of claim 1, characterized in that the material is thermally dried in at least two consecutively arranged dryer stages, wherein the waste heat downstream in the transport direction of the goods dryer stage Process heat is used for each upstream dryer bank.
- the particular advantage of the method according to the invention is that by using the waste heat of the downstream dryer stage as useful heat in the upstream dryer stage, the energy to be applied for the required drying of the biogenic mass can be minimized, so that the example in a combustion of the pyrolysis obtained pyrolysis gas energy significantly above the expended for the drying of the biogenic mass energy, which was previously not possible with comparable methods of the prior art. Calculations by the applicant have shown in this context that a
- the at least two dryer stages preferably comprise at least one low-temperature dryer as upstream dryer stage and at least one high-temperature dryer as downstream dryer stage.
- the waste heat of the high-temperature stage of the low-temperature stage is provided as process heat in a cascaded drying process and thus made usable in the system, ie in the intrinsic process.
- further dryer stages can occur, so that a dryer cascade of a plurality of dryer stages can be formed, in which preferably the next higher and nacnordinated in the transport direction of the material to be dried arranged dryer stage their Abwarme upstream dryer stage or the upstream dryer stages with lower temperature than process heat provides.
- the heat of the exhaust gases of the pyrolysis reactor firing Stutzbrenners is additionally used as process heat in the upstream dryer stage and / or the downstream dryer stage.
- the underlying principle of the invention is extended to the effect that the waste heat of the pyrolysis reactor, which is also at a significantly higher temperature level compared with a high-temperature drying stage, is made available to one or more dryer stages as process heat.
- the waste heat of a downstream process stage is made available as process heat to the upstream process stages of lower temperature than process heat.
- the heat of the hot pyrolysis gas produced in the pyrolysis reactor can also be used as process heat in the upstream dryer stage and / or in the downstream dryer stage.
- the high thermal energy content of the pyrolysis gas can be supplied to the dryer stages upstream of the pyrolysis reactor as process heat, whereby the efficiency of the overall process is further increased.
- the pyrolysis gas produced in the pyrolysis reactor is a
- Energy conversion unit a fuel cell which directly converts the chemical Epergie content of the pyrolysis gas into electrical energy is considered as well as a heat engine driving a generator, in particular a gas turbine, an internal combustion engine or a Stirling engine.
- the heat of the exhaust gases of the heat engine can be used as process heat in the upstream dryer stage and / or the downstream dryer stage according to a further embodiment of the invention for further increasing the process efficiency.
- each of the at least two dryer stages is supplied with process heat via its own heat exchanger circuit, in particular a thermal oil circuit.
- the waste heat of the downstream dryer stage in particular in the form of vapors, i. in the form of a vapor-air mixture, be passed through a heat exchanger integrated into the heat exchanger circuit of the upstream dryer stage to erfmdungsgeatii to use them as process heat for the upstream dryer strand.
- the exhaust gases of its exhaust gases are used as process heat for the upstream dryer stage and / or the downstream dryer stage, this can be done practically by passing the exhaust gases of the heat engine through an exhaust gas heat exchanger integrated into the heat exchanger circuit of the respective dryer stage become. Special is it is possible to first pass the exhaust gases through an integrated in the 9,tragernikla ⁇ f the downstream dryer stage hot exhaust gas heat exchanger, whereupon they are then passed through an integrated in the Warrretragerniklauf the upstream Dryerst jfe heat exchanger.
- the vapors flowing out of a dryer stage can also at least partially provide the required process heat for this dryer stage, and some of the vapors are first compressed while supplying energy, and then heated: and then condensed into a heat exchanger circuit of the respective dryer stage integrated heat exchanger; wherein the enthalpy of condensation is delivered to the heat exchanger circuit and heats the heat transfer medium.
- the waste heat of the dryer stage nacn type of heat pump is lifted by compression to a higher Temperaturmveau and then fed as Nutzwarme via a functioning as a condenser heat exchanger again m the dryer stage with process wareworth supplying heat transfer circuit.
- a portion of the pyrolysis gas generated in the pyrolysis reactor is used as fuel for the burner of an integrated into the heat exchanger circuit of the upstream and / or the downstream dryer stage boiler, in particular a Thermalolkessels.
- the boiler is preferably arranged in the heat exchanger circuit of the downstream dryer stage and the exhaust gases of the boiler burner are then by a in the Warpietragernikank the upstream dryer stage integrated heat exchanger passed.
- the energy content of the branched pyrolysis gas is used for both of the at least two dryer stages in a particularly efficient manner.
- a part of the pyrolysis gas produced in the pyrolysis reactor is used as fuel for the nozzle burner of the pyrolysis reactor itself.
- the system can be operated substantially independently of other fuels.
- the pyrolysis coke produced during the pyrolysis of the dried material is fed to a gasifier and the lean gas produced there by gasification is fed to the nozzle burner for the pyrolysis reactor as fuel.
- Vornchtupgsileig the above-mentioned object is achieved with a plant for the recovery of biogenic mass, in particular sewage sludge, according to the preamble of claim 17, characterized in that the drying device comprises at least two in Transport ⁇ citung the goods successively arranged dryer stages which are gekopoelt together so that the Abwarme the downstream in the transport direction of the goods dryer stage is used as Nutzwarme for each upstream dryer devisr.
- 1 is a block diagram of a plant for generating electrical energy from clear sludge
- FIG. 2 shows a block diagram of the low-temperature dryer with thermal oil circuit m in a preferred embodiment
- Fig. 3 shows the pyrolysis reactor of the system of FIG. 1 in a preferred embodiment
- Fxg. 4 is a flowchart illustrating a process for recycling sludge.
- the plant 1 shown schematically as a block diagram for generating electrical energy from clear sludge as a biogenic mass comprises a drying device 1, by means of which the clear sludge introduced into the plant at a delivery point Ia is transported and thereby dried.
- the drying apparatus is divided into two dryer stages, namely a low-temperature dryer 3 and a high-temperature dryer 4. It is possible to add further dryer stages (not shown here).
- a pyrolysis reactor 2 is arranged, which is a Stutzbrenner 2a is fired.
- a Stutzbrenner 2a is fired.
- Drying device 1 dried sludge thermally decomposed, pyrolysis gas, (usually consisting of nitrogen, carbon dioxide, hydrogen, carbon monoxide and higher hydrocarbons) and obtained as a further products pyrolysis and not recyclable ash.
- pyrolysis gas usually consisting of nitrogen, carbon dioxide, hydrogen, carbon monoxide and higher hydrocarbons
- the pyrolysis gas escapes: from the pyrolysis reactor 2 via a line 25 and reaches a heat engine, in this case a gas turbine 5, which in turn is connected to a generator 5a for generating electrical energy.
- a heat engine in this case a gas turbine 5, which in turn is connected to a generator 5a for generating electrical energy.
- a gas turbine an internal combustion engine, a Stirling engine or a fuel cell, which converts the chemical energy of the pyrolysis gas directly into electrical energy, can be provided.
- the low-temperature dryer 3 as well as the high-temperature dryer 4 comprise as individual drying stages of the drying apparatus 1 each a heat exchanger circuit, in this case a thermal oil circuit 30, 40, which supplies the respective dryer stage 3, 4 with process heat.
- Therroalolniklaufe 30, 40 are coupled to each other (not m Fig. 1 shown), which is particularly advantageous when commissioning the system to achieve a rapid drying of sewage sludge to achieve a steady state operation.
- a Tnermalolkessel 41 for heating the Thermaiols and a heat exchanger 42 are arranged one behind the other.
- the thermal oil boiler 41 in turn comprises a nozzle burner 41 a, the fuel supply line 43 with the Pyrolysis gas line 25 connected xst. Accordingly, the nozzle burner 41a is operated directly with the pyrolysis gas generated in the pyrolysis reactor 2 as fuel.
- the heat exchanger 42 circulating in the thermal oil circuit 40 Thermaiol is additionally heated by the effluent via an exhaust pipe 52 from the gas turbine 5 hot aegas.
- the thermal oil circuit 30 of the low-temperature dryer 3 in the present case a total of five heat exchanger 31 to 35 are arranged one behind the other.
- the heat exchanger 31 is flowed through by the exhaust gases of the burner 41 a of the thermal oil circuit 41 arranged in the thermal oil boiler 41.
- the residual heat of the effluent from the heat exchanger 31 exhaust gas escapes as loss of heat.
- the heat exchanger 32 in turn is flowed through by the exhaust gases of the gas turbine 5, after they have already flowed through the arranged in the thermal oil circuit 40 heat exchanger 42.
- the connection of the heat exchanger 42, 32 indicated only by the symbols C-C.
- the residual heat of the exhaust gases of the gas turbine escapes after flowing through the heat exchanger 32, wherein the circulating in the thermal oil circuit 30 T ⁇ ermalol further heats up, again as loss of heat.
- the thermals of the thermal oil circuit 30 are further cooled by the exhaust gases of the stalk burner 2a of the
- Pyrolysis reactor 2 heated. For this purpose, they flow through the exhaust pipe 23 and m the integrated heat exchanger 33 in the line.
- conduit 44 through which the vapors emerging from the high-temperature dryer 4 flow, with the Heat exchanger 34 of the Thern ⁇ alolnikanks 30 connected so that the vapors flow through the heat exchanger 34 and release their heat energy partially to the thermal oil.
- the heat exchanger 35 is arranged in the thermal oil circuit 30 of the low-temperature dryer 3. This is flowed through by the hot pyrolysis gases flowing out of the pyrolysis reactor 2, these giving off a portion of their heat to the thermal oil.
- Fig. 2 is a block diagram of the
- Low-temperature dryer 3 shown according to a particularly preferred embodiment.
- a further heat exchanger 37 is integrated in thermal oil circuit 30 of the low-temperature dryer 3.
- the heat exchangers 31 to 35 described above are not shown in FIG. 2. The from the
- Low-temperature dryers 3 exhaust vapors are compressed according to the arrangement of Fig. 2 in a compressor 36, wherein they are raised to a higher temperature level, and then flow as a condensed vapor stream through line 38 in the heat exchanger 37, which acts as a condensation heat exchanger. Accordingly, the vapors are liquefied when flowing through the heat exchanger 37, wherein the heat of condensation is released to the circulating in the thermal oil circuit 30 Thermaiol.
- this design which roughly corresponds to the functional principle of a heat pump, additional process heat for the drying process in the low-temperature dryer 3 can be provided in a very efficient manner by the application of additional energy in the compressor.
- FIG. 3 is shown in the form of a further block diagram of the pyrolysis reactor 2 of the system of FIG. 1 in a particularly preferred embodiment.
- the already known from the block diagram of Fig. 1 components carry corresponding reference numerals.
- the peculiarity of the arrangement shown in FIG. 3 consists in the fact that the pyrolysis coke produced in the course of the pyrolysis is discharged from the reactor through a conduit 24 and fed to a gasifier stage 26 where the pyrolysis coke gasifies in a manner known per se from the prior art becomes.
- the resulting lean gas is purified in a purification stage 27 and then fed to the support burner 2a of the pyrolysis reactor 2 as an additional fuel.
- the efficiency of the overall process is further increased because other pyrolysis products, in this case the pyrolysis, is used as an energy source in the process.
- the dry sludge to be dried with a dry matter content of about 25% by weight - the remaining 75 wt .-% are formed by water - placed in the system and transported in the Kfiedertemperaturtrockner 3 and pre-dried. There he is dried so far that he leaves the
- Low temperature dryer 3 has a dry matter content of about 40%.
- the low-temperature dryer 3 is supplied by the Thermal ⁇ lniklauf 30 with the necessary process heat. Afterwards the pre-dried Well required in the high-temperature dryer 4 and dried to the final degree of drying.
- the vapors produced in the high-temperature dryer 4 are thereby passed via the line 44 m to the heat exchanger 34 provided in the thermal oil circuit 30 of the low-temperature dryers 3, where they release a portion of their heat to the thermal oil circulating in the thermal oil circuit 30.
- the waste heat of the downstream in the transport direction of the goods dryer stage namely the waste heat of the high-temperature dryer 4, as process heat for the upstream dryer stage, ie the low-temperature dryer 3, thus used.
- the dried to a dry matter content of about 85% Good is then introduced into the pyrolysis reactor 2, where the material is preferably thermally decomposed in a two-stage pyrolysis under exclusion of oxygen, as known from the prior art.
- the heat required for this purpose is generated by the support burner 2a.
- the burner exhaust gas produced in this case is supplied via line 23 to the heat exchanger 33 provided in the thermal oil circuit 30 of the low-temperature dryer 3, so that the heat of the burner exhaust gases is used as process heat in a dryer stage, in this case in the low-temperature dryer 3.
- the pyrolysis gas generated in the pyrolysis reactor 2 leaves the pyrolysis reactor 2 via the line 25 and first passes through a dust separator 21, where dust still contained in the pyrolysis gas stream are separated.
- the pyroxylic gas subsequently flows through the heat exchanger 35, so that the heat in the pyrolysis reactor 2 Pyrolysis gas generated in turn is supplied as process heat this dryer stage.
- parts of the pyrolysis gas stream are diverted from the line 25 into the lines 22, 43.
- the introduced into the line 22 pyrolysis gas is used as fuel for firing the support burner 2a of the pyrolysis reactor 2, while introduced into the line 43 portion is supplied as fuel to the support burner 41a of 41 arranged in the thermal circuit 40 of the cooking temperature dryer 4 thermal oil boiler.
- the chemical energy contained in the pyrolysis gas produced in the pyrolysis reactor 2 is used to maintain the overall process in a particularly efficient manner.
- the pyrolysis gas flowing through the conduit 25 is then introduced into the gas turbine 5 and incinerated there, the gas turbine 5 driving a generator 5a.
- the exhaust gases of the gas turbine are supplied through line 52 to heat exchanger 42 arranged in thermal oil circuit 40 of high-temperature dryer 4 and subsequently to heat exchanger 32 disposed in thermal oil circuit 30 of low-temperature dryer 3, so that the heat contained in the exhaust gas of the gas turbine is again used as process heat to both dryer stages 3 4 is provided.
- the principle is thus realized, in a multi-stage process with each increasing process temperature, the waste heat of a process step of certain temperature one or more upstream process steps lower temperature than Provide process heat to increase the overall efficiency of the overall process.
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- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Sustainable Development (AREA)
- General Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Treatment Of Sludge (AREA)
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
Claims
Priority Applications (7)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| EP20100704343 EP2406190B1 (de) | 2009-03-13 | 2010-01-29 | Verfahren und anlage zur verwertung von biomasse sowie blockheizkraftwerk |
| RU2011141417/05A RU2011141417A (ru) | 2009-03-13 | 2010-01-29 | Способ, и установка для переработки биогенной массы, и теплоэлектроцентраль |
| CN201080011526XA CN102348649A (zh) | 2009-03-13 | 2010-01-29 | 利用生物质的装置和方法以及中央供暖站 |
| CA 2755375 CA2755375A1 (en) | 2009-03-13 | 2010-01-29 | Method and system for utilising biomass and block-type thermal power plant |
| US13/256,111 US20120111715A1 (en) | 2009-03-13 | 2010-01-29 | Method and System for Utilizing Biomass and Block-Type Thermal Power Plant |
| JP2011553369A JP2012520166A (ja) | 2009-03-13 | 2010-01-29 | バイオマスの利用方法および利用システムおよびブロック型熱発電プラント |
| BRPI1009134A BRPI1009134A2 (pt) | 2009-03-13 | 2010-01-29 | processo e sistema para o aproveitamento de biomassa e instalação de aquecimento de bloco |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DE200910012668 DE102009012668A1 (de) | 2009-03-13 | 2009-03-13 | Verfahren und Anlage zur Verwertung von Biomasse |
| DE102009012668.6 | 2009-03-13 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2010102854A1 true WO2010102854A1 (de) | 2010-09-16 |
Family
ID=41796474
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/EP2010/051063 Ceased WO2010102854A1 (de) | 2009-03-13 | 2010-01-29 | Verfahren und anlage zur verwertung von biomasse sowie blockheizkraftwerk |
Country Status (10)
| Country | Link |
|---|---|
| US (1) | US20120111715A1 (de) |
| EP (1) | EP2406190B1 (de) |
| JP (1) | JP2012520166A (de) |
| KR (1) | KR20110137345A (de) |
| CN (1) | CN102348649A (de) |
| BR (1) | BRPI1009134A2 (de) |
| CA (1) | CA2755375A1 (de) |
| DE (1) | DE102009012668A1 (de) |
| RU (1) | RU2011141417A (de) |
| WO (1) | WO2010102854A1 (de) |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE102009012668A1 (de) * | 2009-03-13 | 2010-09-16 | E.On Anlagenservice Gmbh | Verfahren und Anlage zur Verwertung von Biomasse |
| DE102011005065A1 (de) * | 2011-03-03 | 2012-09-06 | Siemens Aktiengesellschaft | Thermische Behandlung von Biomasse |
| CN102875000A (zh) * | 2011-07-12 | 2013-01-16 | 北大工学院绍兴技术研究院 | 一种污泥干燥室 |
| ITTO20120452A1 (it) * | 2012-05-25 | 2013-11-26 | Tm E S P A Termomeccanica Ecologi A | Impianto e procedimento per il trattamento di fanghi. |
| PL2774894T3 (pl) * | 2013-03-08 | 2016-03-31 | Aquatec Proyectos Para El Sector Del Agua S A U | Ciągły sposób termicznej hydrolizy materiału organicznego oraz instalacja umożliwiająca realizację sposobu |
| CN103146403B (zh) * | 2013-03-22 | 2014-05-21 | 清华大学 | 能量自给的生物质热解系统和方法 |
| ITPD20130230A1 (it) * | 2013-08-08 | 2015-02-09 | Ronda Engineering Srl | Impianto e metodo per il trattamento di composti organici |
| TWI507366B (zh) * | 2014-05-21 | 2015-11-11 | Leaderman & Associates Co Ltd | 污泥處理裝置 |
| CN104329923B (zh) * | 2014-10-24 | 2016-06-15 | 中盈长江国际新能源投资有限公司 | 利用电厂烟气余热干燥生物质燃料的方法及其设备 |
| DE102015002671A1 (de) * | 2015-03-03 | 2016-09-22 | Eisenmann Se | Temperieranlage mit Wärmekraftmaschine |
| US11215360B2 (en) * | 2015-08-18 | 2022-01-04 | Glock Ökoenergie Gmbh | Method and device for drying wood chips |
| FR3052544B1 (fr) * | 2016-06-08 | 2020-12-04 | Haffner Energy | Dispositif de deshydratation |
| FR3052545B1 (fr) * | 2016-06-09 | 2018-06-15 | Haffner Energy | Dispositif de sechage |
| WO2018073344A1 (en) * | 2016-10-20 | 2018-04-26 | Hsl Energy Holding Aps | Plant and process for production of hot water from humid air |
| RU2632444C1 (ru) * | 2017-01-25 | 2017-10-04 | Общество с ограниченной ответственностью "ЭКОС ИНВЕСТ" | Система и способ переработки осадка сточных вод |
| CN107741150A (zh) * | 2017-10-31 | 2018-02-27 | 江苏天舒电器股份有限公司 | 一种无霜、多变量耦合型热泵热风炉的控制系统及其控制方法 |
| CN111777299B (zh) * | 2020-06-30 | 2022-02-18 | 中国石油大学(华东) | 一种基于单螺杆膨胀机的含油污泥热解能量回收系统 |
| US11982444B2 (en) * | 2020-11-09 | 2024-05-14 | Guangdong University Of Technology | System for disposing high-moisture mixed waste composed of kitchen garbage and water-containing sludge |
| EP4480927A1 (de) * | 2023-06-21 | 2024-12-25 | PBTechnology, s.r.o | Behandlung von flüssigkeiten zur veränderung ihrer eigenschaften |
| FR3165794A1 (fr) * | 2024-08-29 | 2026-03-06 | Suez International | Procédé et installation de pyrocarbonisation de matières organiques et notamment de déchets organiques |
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- 2010-01-29 WO PCT/EP2010/051063 patent/WO2010102854A1/de not_active Ceased
- 2010-01-29 CA CA 2755375 patent/CA2755375A1/en not_active Abandoned
- 2010-01-29 RU RU2011141417/05A patent/RU2011141417A/ru not_active Application Discontinuation
- 2010-01-29 CN CN201080011526XA patent/CN102348649A/zh active Pending
- 2010-01-29 EP EP20100704343 patent/EP2406190B1/de not_active Not-in-force
- 2010-01-29 US US13/256,111 patent/US20120111715A1/en not_active Abandoned
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Also Published As
| Publication number | Publication date |
|---|---|
| KR20110137345A (ko) | 2011-12-22 |
| CA2755375A1 (en) | 2010-09-16 |
| JP2012520166A (ja) | 2012-09-06 |
| US20120111715A1 (en) | 2012-05-10 |
| CN102348649A (zh) | 2012-02-08 |
| EP2406190A1 (de) | 2012-01-18 |
| DE102009012668A1 (de) | 2010-09-16 |
| EP2406190B1 (de) | 2013-04-03 |
| BRPI1009134A2 (pt) | 2016-03-08 |
| RU2011141417A (ru) | 2013-04-20 |
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