DE19532359A1 - Biogas prodn. from high solids biomass - Google Patents

Biogas prodn. from high solids biomass

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Publication number
DE19532359A1
DE19532359A1 DE19532359A DE19532359A DE19532359A1 DE 19532359 A1 DE19532359 A1 DE 19532359A1 DE 19532359 A DE19532359 A DE 19532359A DE 19532359 A DE19532359 A DE 19532359A DE 19532359 A1 DE19532359 A1 DE 19532359A1
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DE
Germany
Prior art keywords
biogas
percolation
biomass
acid buffer
high solids
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
DE19532359A
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German (de)
Other versions
DE19532359C2 (en
Inventor
Hans-Peter Winkler
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.)
WINKLER, HANS-PETER, 39319 WULKOW, DE
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WINKLER HANS PETER
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Priority to DE19532359A priority Critical patent/DE19532359C2/en
Publication of DE19532359A1 publication Critical patent/DE19532359A1/en
Application granted granted Critical
Publication of DE19532359C2 publication Critical patent/DE19532359C2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M23/00Constructional details, e.g. recesses, hinges
    • C12M23/44Multiple separable units; Modules
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/02Biological treatment
    • C02F11/04Anaerobic treatment; Production of methane by such processes
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M21/00Bioreactors or fermenters specially adapted for specific uses
    • C12M21/04Bioreactors or fermenters specially adapted for specific uses for producing gas, e.g. biogas
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M29/00Means for introduction, extraction or recirculation of materials, e.g. pumps
    • C12M29/02Percolation
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12PFERMENTATION OR ENZYME-USING PROCESSES TO SYNTHESISE A DESIRED CHEMICAL COMPOUND OR COMPOSITION OR TO SEPARATE OPTICAL ISOMERS FROM A RACEMIC MIXTURE
    • C12P5/00Preparation of hydrocarbons or halogenated hydrocarbons
    • C12P5/02Preparation of hydrocarbons or halogenated hydrocarbons acyclic
    • C12P5/023Methane
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Abstract

Process for recovering biogas from biomass with a high solids content is carried out using at least 4 separate container modules each acting as a biogas generator and draining into a common drain feeding into a percolation liquor tank. The liquor is treated with an acid buffer and then recycled to be sprayed onto the biomass in the containers.

Description

Stand der TechnikState of the art

Verfahren zur Vergärung von feststoffreicher Biomasse haben das Defizit, daß sie in der Re­ gel zur Übersäuerung im Biogasreaktor neigen, als Folge unterschiedlicher Reaktionsge­ schwindigkeiten bei Hydrolyse, Acetatbildung und Methanisierung. Die Methanisierung mit der geringsten Reaktionsgeschwindigkeit stellt hierbei den prozeßbestimmenden Schritt dar. Ohne zusätzliche Beimpfung mit Methanbildnern werden nur geringe Abbauraten für Koh­ lenstoff und damit geringe Biogasausbeuten realisiert. Hinzu kommt, daß die Vermehrungs­ rate bei den Methanbildnern am geringsten ist.Processes for the fermentation of high-solids biomass have the deficit that they are in the Re gel tend to overacidify in the biogas reactor as a result of different reaction gels Hydrolysis, acetate and methanation rates. The methanization with The slowest reaction rate represents the process-determining step. Without additional inoculation with methane formers, only low degradation rates for Koh lenstoff and thus low biogas yields realized. Add to that the multiplication rate is the lowest among methane formers.

Die Erfindung entsprechend Anspruch stellt eine Lösung dar, wie feststoffreiche Biomasse bei hohen Kohlenstoffabbauraten und damit verbundenen hohen Biogasausbeuten vergoren werden kann. Sie bietet damit die Möglichkeit einer kostengünstigen und damit wirtschaftli­ chen Energieträgerbereitstellung aus nachwachsenden Rohstoffen. Als Beispiele seien hierfür Mais und Gras.- Kleegemische genannt. Einer Vielzahl von Stellungnahmen und Veröffentli­ chungen ist zu entnehmen, daß der Anteil der landwirtschaftlichen Nutzflächen für die Nah­ rungsmittelproduktion immer geringer wird. D.h. das Potential an Flächen für den gezielten Anbau von Biomasse zu Energieerzeugungszwecken wächst. Grundvoraussetzungen sind je­ doch, daß die Biomasse gut vergärbar ist (Kohlenstoff-Stickstoffverhältnis bei 15 bis 35 zu 1 und geringer Ligninanteil), daß das zur Anwendung kommende Verfahren einfach ist und eine hohe Dezentralität ermöglicht.The invention according to claim represents a solution such as high-solids biomass fermented at high carbon degradation rates and the associated high biogas yields can be. It thus offers the possibility of an inexpensive and therefore economical Chen provision of energy from renewable raw materials. As examples of this Corn and grass .-- called clover mixtures. A variety of statements and publications It can be seen that the share of agricultural land for the near food production is getting lower. I.e. the potential of areas for the targeted The cultivation of biomass for energy generation is growing. Basic requirements are each but that the biomass is easily fermentable (carbon-nitrogen ratio at 15 to 35 to 1 and low lignin content) that the method used is simple and enables a high level of decentralization.

Lösungsolution

Im folgenden wird das erfindungsgemäße Verfahren anhand der beiliegenden Zeichnung nä­ her erläutert. Die Zeichnung stellt das Verfahrensprinzip dar, hinsichtlich der Geometrie der Container-Module werden keine verfahrenstechnischen Anforderungen gestellt, sie könnten also auch rund sein.In the following, the method according to the invention is shown in the accompanying drawing ago explained. The drawing represents the principle of the process, with regard to the geometry of the Container modules have no procedural requirements, they could so be round too.

Die mit C1-C4 bezeichneten Container- Module werden einstufig, diskontinuierlich und me­ sophil (ca. 35°C) bei einem Trockensubstanzgehalt von 20-40% betrieben. Der Sickersaft der einzelnen Container-Module wird Taktweise, in Abhängigkeit von der Struktur und der Konsistenz des Haufwerkes abgezogen. Über einen gemeinsamen Sammelkanal werden die Sickersäfte dem Säurepuffer zugeführt. Hier erfolgt die Einstellung eines Mischgehaltes an Nährstoffen und Methanbildnern. Dieses Mischprodukt dient als Perkolationsmedium und wird durch ein Verteilersystem über dem Inhalt der Container-Module C1 bis C4 versprüht. Der Container-Modul C1 wird durch diese Vorgehensweise in seinem Nährstoffangebot re­ duziert und in seiner Methanbildneranzahl erhöht. Zugleich wird das ökologische Fenster, daß bedingt durch das Starten der biochemischen Reaktion geöffnet wurde, durch die Me­ thanbildnerspezies belegt, die sich in den Container-Modulen C2 bis C4 durchgesetzt hat. Eine zügige Überführung in einen stabilen Methanbildungsvorgang wird initiiert. Die Container-Module C2 und C3 befinden sich in der Phase der stabilen Methanbildung, d. h. die Nährstoffbereitstellung und die Methanisierung befinden sich hinsichtlich der Reaktionsge­ schwindigkeit in einem ausgewogenen Verhältnis. Im Container-Modul C3 erreicht die Me­ thanbildneranzahl ihr Maximum. Der Sickersaft aus den Container-Modulen C2 und C3 ent­ spricht hinsichtlich seiner Zusammensetzung Nährstoffgehalt und Methanbildneranzahl dem des Säurepuffers. Im Container-Modul C4 wird das Nährstoffangebot durch das Perkolati­ onsmedium erhöht, da die Nährstoffbereitstellung bereits abklingt. Die Gesamtverweilzeit der Biomasse im Reaktor wird hierdurch erhöht, ohne das dabei wesentlich die Gasprodukti­ onsrate (m³ Biogas/m³ Faulraum) sinkt. Dies führt zwangsläufig dazu, daß der Kohlenstoff­ umsatz im Container-Modul C4 erhöht wird.The container modules designated C1-C4 become single-stage, discontinuous and me sophil (approx. 35 ° C) operated with a dry matter content of 20-40%. The seep juice of the individual container modules is intermittent, depending on the structure and the Subtract consistency of the pile. The Infiltration juices are added to the acid buffer. This is where a mixed content is set Nutrients and methane formers. This mixed product serves as a percolation medium and is sprayed through a distribution system over the contents of the container modules C1 to C4. The container module C1 is re through this procedure in its nutrient supply reduced and increased in its methane generator number. At the same time, the ecological window that due to the start of the biochemical reaction was opened by the Me thanbildner species, which has established itself in the container modules C2 to C4. A rapid transition to a stable methane formation process is initiated. The Container modules C2 and C3 are in the phase of stable methane formation, i.e. H. the Nutrient supply and methanation are in terms of the reaction gene  speed in a balanced ratio. In the container module C3, the Me number of formers their maximum. The seepage juice from the container modules C2 and C3 ent speaks with regard to its composition nutrient content and number of methane formers of the acid buffer. In the container module C4, the nutrient supply is provided by the percolati onsmedium increased because the supply of nutrients is already declining. The total dwell time the biomass in the reactor is thereby increased without significantly reducing the gas products onsrate (m³ biogas / m³ digestion) decreases. This inevitably leads to the carbon sales in the container module C4 is increased.

Abhängig von den eingesetzten Biomassen kann der Säurepuffer als inaktiver Tank oder als eigenständige Biogasanlage im thermophilen Temperaturbereich bei ca. 55°C betrieben wer­ den. Dies hat zur Folge, daß ein höherer Nährstoffumsatz bei geringerer Biogasqualität (Methangehalt) in Kauf genommen werden muß.Depending on the biomass used, the acid buffer can be used as an inactive tank or as independent biogas plant in the thermophilic temperature range at approx. 55 ° C the. This has the consequence that a higher nutrient conversion with lower biogas quality (Methane content) must be accepted.

Erreichte VorteileAchieved advantages

Diese Vorgehensweise führt bei Feststoffvergärverfahren dazu, daß das startbedingte Defizit der zu schnellen Nährstoffbereitstellung durch das prozeßbedingte allmähliche Abklingen der biochemischen Reaktion kompensiert wird. Die Größe des Säurepuffers und die Zeitinterval­ le in denen die einzelnen Reaktoren gestartet werden, ist in erster Linie von der zu vergären­ den Biomasse abhängig. Das beispielhaft angegebene Intervall von 7 Tagen gilt für ein Mais/ Grasgemisch. Eine gezielte Einflußnahme auf den Methanbildungsvorgang in den Container- Modulen C1 bis C4 erfolgt lediglich über den Durchfluß an Perkolationsmedium bei konstan­ tem Füllstand. Hierdurch kann schneller Nährstoff reduziert bzw. angereichert werden.This procedure leads to the start-related deficit in solid fermentation processes the too rapid supply of nutrients due to the process-related gradual decay of the biochemical reaction is compensated. The size of the acid buffer and the time interval le in which the individual reactors are started is primarily fermented by the depending on the biomass. The interval of 7 days given as an example applies to a maize / Grass mixture. A targeted influence on the methane formation process in the container Modules C1 to C4 only take place via the flow of percolation medium at constant level. This allows nutrients to be reduced or enriched more quickly.

Ein zusätzlicher positiver Effekt ist der, daß die Gasverfügbarkeit trotz des diskontinuierli­ chen Betriebs der Container-Module C1 bis C4 nie unter 3/4 der Maximalverfügbarkeit sinkt. Hierdurch wird erreicht, daß die nachgeschaltete Verbrauchseinrichtung BHKW zur Strom- und Wärmebereitstellung ohne große Speichervorhaltung betrieben werden kann.An additional positive effect is that the gas availability despite the discontinuous operation of the container modules C1 to C4 never drops below 3/4 of the maximum availability. This ensures that the downstream CHP unit for electricity and heat supply can be operated without large storage reserves.

Durch dieses einfache Verfahrensprinzip ist es möglich, den technischen Aufwand (Anzahl und Leistung von Pumpen, Ausgestaltung mit Prozeß-, Meß- und Regeltechnik) zu reduzie­ ren.This simple process principle enables the technical effort (number and performance of pumps, design with process, measurement and control technology) to reduce ren.

Claims (5)

1. Verfahren zur Gewinnung von Biogas aus Biomasse mit hohem Feststoffgehalt, dadurch gekennzeichnet, daß mindestens 4 separate Container-Module, die jeder für sich ein eigenständiger Biogasreaktor sind, über das Sumpfprodukt (Sickersaft) und das Perkolationsprodukt mit einem Säurepuffer gekoppelt sind.1. A process for the production of biogas from biomass with a high solids content, characterized in that at least 4 separate container modules, each of which is an independent biogas reactor, are coupled via the bottom product (percolation juice) and the percolation product with an acid buffer. 2. Verfahren nach Anspruch 1, dadurch gekennzeichnet, daß die 4 separaten Con­ tainer-Module zeitversetzt nacheinander gestartet werden und sich dadurch in 4 unter­ schiedlichen Reaktionsphasen der Biogaserzeugung befinden.2. The method according to claim 1, characterized in that the 4 separate Con tainer modules are started one after the other with a time delay and are thus divided into 4 under different reaction phases of biogas production. 3. Verfahren nach Ansprüchen 1 und 2, dadurch gekennzeichnet, daß trotz diskon­ tinuierlichen Betriebs des einzelnen Containers mindestens 3/4 der maximal erzeug­ baren Biogasmenge kontinuierlich verfügbar ist.3. The method according to claims 1 and 2, characterized in that despite discount continuous operation of the individual container produces at least 3/4 of the maximum available amount of biogas is continuously available. 4. Verfahren nach Ansprüchen 1 und 2, dadurch gekennzeichnet, daß die Überführung in die stabile Methanbildungsphase des jeweiligen Startcontainer-Moduls über die Durchflußmenge an Perkolationsmedium bei gleichbleibendem Flüssigkeitsstand gesteuert wird.4. The method according to claims 1 and 2, characterized in that the transfer into the stable methane formation phase of the respective start container module via the Flow rate of percolation medium with constant liquid level is controlled. 5. Verfahren nach Ansprüchen 1 bis 4, dadurch gekennzeichnet, daß der Säurepuffer sowohl als inaktiver Tank, als auch als Biogasreaktor im thermophilen Temperatur­ bereich ausgeführt sein kann.5. Process according to claims 1 to 4, characterized in that the acid buffer both as an inactive tank and as a biogas reactor in thermophilic temperature area can be executed.
DE19532359A 1995-09-01 1995-09-01 Process for the production of biogas from solid biomass Expired - Fee Related DE19532359C2 (en)

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DE19532359C2 DE19532359C2 (en) 2001-02-01

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Cited By (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0934998A2 (en) * 1998-02-09 1999-08-11 Manfred Prof. Dr. Hoffmann Method and device for the methanation of biomasses
DE19828889A1 (en) * 1998-06-19 1999-12-23 Schulte Siering Eberhard Biogas production by co-fermentation of harvested crops and organic waste
DE19947339A1 (en) * 1999-10-01 2001-04-12 Wolfgang Tentscher Agricultural methane generator reactor has sub-surface inlet accelerating fermentation
DE19951929A1 (en) * 1999-10-28 2001-05-10 Xaver Lipp Process for the recovery of a gaseous energy carrier, especially methane comprises crushing plant raw material, filling the raw material into a digestion container and collecting the energy carrier produced
DE102004053615B3 (en) * 2004-11-03 2006-05-18 Brandenburgische Technische Universität Cottbus Degradation of biogenic material
EP1749883A1 (en) * 2005-08-05 2007-02-07 agraferm technologies AG Biogas plant and module for a biogas plant
DE102006040799A1 (en) * 2006-08-31 2008-03-20 Arno Fudel Production of biogas by fermentation, involves alternate liquid build-up with an intermittent rhythm between complete overage of substrate and transfer of bacteria-rich fermentation liquid to parallel fermenters
WO2009000309A1 (en) * 2007-06-27 2008-12-31 MEISSNER, Jan, A. Biogas plant with solids fermentation and methane production in the recirculating percolate tank
DE102010017818A1 (en) 2010-02-17 2011-08-18 Meissner, Jan A. Process and plant for the production of CBM (Compressed BioMethane) as greenhouse gas-free fuel
EP2428559A1 (en) * 2010-09-10 2012-03-14 Pöttinger Entsorgungstechnik GmbH & Co. KG Biogas assembly, method for its operation and reactor unit for same
EA016292B1 (en) * 2008-12-23 2012-03-30 Бикон Энерджи Текнолоджиз Гмбх Унд Ко.Кг Biogas plant for methanizing biomass having a high solids fraction
US8759083B2 (en) 2006-02-21 2014-06-24 Bekon Energy Technologies Gmbh & Co., Kg Bioreactor for methanization of biomass having a high solids fraction
DE102014011479A1 (en) * 2014-07-31 2016-02-04 Christoph Bürger New process for the fermentation of biogenic energy sources
EP3354718A1 (en) * 2017-01-30 2018-08-01 HERBST Umwelttechnik GmbH Device and method for creating biogas
CN112661366A (en) * 2020-12-22 2021-04-16 湖南军信环保股份有限公司 Method and system for cooperative sludge dewatering treatment of aged leachate of refuse landfill

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE102008015609A1 (en) 2008-03-26 2009-10-01 Markus Dallinger Producing biogas e.g. methane gas during a multi-step process from solid biomass e.g. solid dung, comprises carrying out a hydrolysis process and an acidification process and then a methane formation process in a spatially separated manner
DE102014011447A1 (en) 2014-08-07 2016-02-11 S+B Service Und Betrieb Gmbh Combined Hydrolysis Fermentation Apparatus

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EP0152730A1 (en) * 1983-12-15 1985-08-28 L'Etat belge, représenté par le Secrétaire Général des Services de la Programmation de la Politique Scientifique Process for the preparation of methane by anaerobic digestion of organic materials
DE4409487A1 (en) * 1993-10-09 1995-04-13 Steffen Ingenieurgesellschaft Process and system for the fermentation of biogenic/organic crude waste
DE4444462A1 (en) * 1994-11-29 1996-06-20 Haase Energietech Gmbh Anaerobic digestion of organic material

Patent Citations (3)

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Publication number Priority date Publication date Assignee Title
EP0152730A1 (en) * 1983-12-15 1985-08-28 L'Etat belge, représenté par le Secrétaire Général des Services de la Programmation de la Politique Scientifique Process for the preparation of methane by anaerobic digestion of organic materials
DE4409487A1 (en) * 1993-10-09 1995-04-13 Steffen Ingenieurgesellschaft Process and system for the fermentation of biogenic/organic crude waste
DE4444462A1 (en) * 1994-11-29 1996-06-20 Haase Energietech Gmbh Anaerobic digestion of organic material

Cited By (23)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0934998A2 (en) * 1998-02-09 1999-08-11 Manfred Prof. Dr. Hoffmann Method and device for the methanation of biomasses
EP0934998A3 (en) * 1998-02-09 2000-02-09 Manfred Prof. Dr. Hoffmann Method and device for the methanation of biomasses
DE19828889A1 (en) * 1998-06-19 1999-12-23 Schulte Siering Eberhard Biogas production by co-fermentation of harvested crops and organic waste
DE19947339A1 (en) * 1999-10-01 2001-04-12 Wolfgang Tentscher Agricultural methane generator reactor has sub-surface inlet accelerating fermentation
DE19947339B4 (en) * 1999-10-01 2005-02-24 Tentscher, Wolfgang, Dr. Process and plant for the production and treatment of biogas
DE19951929A1 (en) * 1999-10-28 2001-05-10 Xaver Lipp Process for the recovery of a gaseous energy carrier, especially methane comprises crushing plant raw material, filling the raw material into a digestion container and collecting the energy carrier produced
DE102004053615B3 (en) * 2004-11-03 2006-05-18 Brandenburgische Technische Universität Cottbus Degradation of biogenic material
EP1749883A1 (en) * 2005-08-05 2007-02-07 agraferm technologies AG Biogas plant and module for a biogas plant
US8759083B2 (en) 2006-02-21 2014-06-24 Bekon Energy Technologies Gmbh & Co., Kg Bioreactor for methanization of biomass having a high solids fraction
DE102006040799A1 (en) * 2006-08-31 2008-03-20 Arno Fudel Production of biogas by fermentation, involves alternate liquid build-up with an intermittent rhythm between complete overage of substrate and transfer of bacteria-rich fermentation liquid to parallel fermenters
US9963665B2 (en) 2007-06-27 2018-05-08 Jan A. Meissner Biogas plant and process for the production of biogas from ligneous renewable resources
WO2009000309A1 (en) * 2007-06-27 2008-12-31 MEISSNER, Jan, A. Biogas plant with solids fermentation and methane production in the recirculating percolate tank
EA016292B1 (en) * 2008-12-23 2012-03-30 Бикон Энерджи Текнолоджиз Гмбх Унд Ко.Кг Biogas plant for methanizing biomass having a high solids fraction
US8236554B2 (en) 2008-12-23 2012-08-07 Bekon Energy Technologies Gmbh & Co., Kg Biogas plant for methanizing biomass having a high solids fraction
DE102010017818A1 (en) 2010-02-17 2011-08-18 Meissner, Jan A. Process and plant for the production of CBM (Compressed BioMethane) as greenhouse gas-free fuel
WO2011101137A1 (en) 2010-02-17 2011-08-25 Meissner, Jan A. Method and system for the production of cbm (compressed biomethane) as a greenhouse gas-reduced fuel
EP2428559A1 (en) * 2010-09-10 2012-03-14 Pöttinger Entsorgungstechnik GmbH & Co. KG Biogas assembly, method for its operation and reactor unit for same
DE102014011479A1 (en) * 2014-07-31 2016-02-04 Christoph Bürger New process for the fermentation of biogenic energy sources
EP3354718A1 (en) * 2017-01-30 2018-08-01 HERBST Umwelttechnik GmbH Device and method for creating biogas
WO2018138368A1 (en) * 2017-01-30 2018-08-02 Herbst Umwelttechnik Gmbh Method and device for producing biogas
US11312932B2 (en) 2017-01-30 2022-04-26 Herbst Umwelttechnik Gmbh Method and device for producing biogas
CN112661366A (en) * 2020-12-22 2021-04-16 湖南军信环保股份有限公司 Method and system for cooperative sludge dewatering treatment of aged leachate of refuse landfill
CN112661366B (en) * 2020-12-22 2022-07-05 湖南军信环保股份有限公司 Method and system for cooperative sludge dewatering treatment of aged leachate of refuse landfill

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