[go: up one dir, main page]

GB2470452A - Electrical Energy Generating System - Google Patents

Electrical Energy Generating System Download PDF

Info

Publication number
GB2470452A
GB2470452A GB1004605A GB201004605A GB2470452A GB 2470452 A GB2470452 A GB 2470452A GB 1004605 A GB1004605 A GB 1004605A GB 201004605 A GB201004605 A GB 201004605A GB 2470452 A GB2470452 A GB 2470452A
Authority
GB
United Kingdom
Prior art keywords
biowaste
generator
biogas
electrical energy
processor
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
GB1004605A
Other versions
GB201004605D0 (en
GB2470452B (en
Inventor
Alan Rogers
John Rutt
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.)
CLEAN ENERGY Ltd
INTARK Ltd
Original Assignee
CLEAN ENERGY Ltd
INTARK Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by CLEAN ENERGY Ltd, INTARK Ltd filed Critical CLEAN ENERGY Ltd
Publication of GB201004605D0 publication Critical patent/GB201004605D0/en
Publication of GB2470452A publication Critical patent/GB2470452A/en
Application granted granted Critical
Publication of GB2470452B publication Critical patent/GB2470452B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G7/00Botany in general
    • A01G7/02Treatment of plants with carbon dioxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1456Removing acid components
    • B01D53/1475Removing carbon dioxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1418Recovery of products
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1425Regeneration of liquid absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/84Biological processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L3/00Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
    • C10L3/06Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L3/00Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
    • C10L3/06Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
    • C10L3/10Working-up natural gas or synthetic natural gas
    • C10L3/101Removal of contaminants
    • C10L3/102Removal of contaminants of acid contaminants
    • C10L3/104Carbon dioxide
    • 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
    • C12M43/00Combinations of bioreactors or fermenters with other apparatus
    • C12M43/08Bioreactors or fermenters combined with devices or plants for production of electricity
    • 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
    • C12M45/00Means for pre-treatment of biological substances
    • C12M45/09Means for pre-treatment of biological substances by enzymatic treatment
    • 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
    • C12M47/00Means for after-treatment of the produced biomass or of the fermentation or metabolic products, e.g. storage of biomass
    • C12M47/18Gas cleaning, e.g. scrubbers; Separation of different gases
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2256/00Main component in the product gas stream after treatment
    • B01D2256/24Hydrocarbons
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/302Sulfur oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/304Hydrogen sulfide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/05Biogas
    • 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
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/20Capture or disposal of greenhouse gases of methane
    • 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
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/40Capture or disposal of greenhouse gases of CO2
    • 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
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/59Biological synthesis; Biological purification
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P60/00Technologies relating to agriculture, livestock or agroalimentary industries
    • Y02P60/20Reduction of greenhouse gas [GHG] emissions in agriculture, e.g. CO2

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Wood Science & Technology (AREA)
  • Zoology (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • General Chemical & Material Sciences (AREA)
  • Biomedical Technology (AREA)
  • Biotechnology (AREA)
  • Genetics & Genomics (AREA)
  • General Health & Medical Sciences (AREA)
  • Biochemistry (AREA)
  • Microbiology (AREA)
  • General Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Molecular Biology (AREA)
  • Analytical Chemistry (AREA)
  • Sustainable Development (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Ecology (AREA)
  • Forests & Forestry (AREA)
  • Environmental Sciences (AREA)
  • Botany (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

An electrical energy generating system comprises an electricity generator 4, a biowaste processor 2 and a farm housing 6, wherein the biowaste processor breaks down a biowaste product to a methane-rich biogas and is in fluid communication with both the generator and the farm housing, the system further including gas transport elements which are capable of transporting the biogas to the generator 32 and carbon dioxide 72 to the farm housing; and wherein the system further includes a biogas treatment station 12 located between the biowaste processor and the generator, the treatment station including a scrubber including water adapted to remove CO2from the methane-rich biogas. A method of production of biogas with the apparatus is also disclosed.

Description

Electrical Energy Generating System The present invention relates to an electrical energy generating system and in particular a system which minimises so-called "greenhouse gases" being released into the atmosphere.
Current fossil fuel power stations generate electrical energy through the burning of fossil fuels, such as oil and gas. The combustion process generates as a by-product significant amounts of greenhouse gases, such as carbon dioxide, and other atmospheric pollutants, which are released into the atmosphere.
Thus, conventional power stations have a double negative impact on the environment: they consume valuable natural resources and they release pollutants into the atmosphere.
The present invention seeks to address the problems of commercial power stations by using a renewable fuel source to power the generator and to minimise pollutants that are released into the atmosphere.
The present invention provides an electrical energy generating system including an electricity generator, a biowaste processor and a farm housing, wherein the biowaste processor breaks down a biowaste product to a methane-rich biogas and is in fluid communication with both the generator and the farm housing, the system further including gas transport elements which are capable of transporting the biogas to the generator and carbon dioxide to the farm housing; and wherein the system further includes a biogas treatment station located between the biowaste processor and the generator, the treatment station including a scrubber including water adapted to remove carbon dioxide from the methane-rich biogas.
The biowaste processor generates a methane-rich biogas from a biowaste source and is suitably a biodigester or a pyrolysis apparatus for biowaste. In an embodiment of the invention, the biowaste processor is a biodigester.
Biodigesters are known in the art and convert appropriate biowaste to a methane-rich gas via microbial action. Thus the generator is effectively powered by biowaste which is renewable, and not by natural resources such as fossil fuels.
The pyrolysis apparatus pyrolyses a biowaste product to generate the methane-rich biogas.
In addition, the system utilises the carbon dioxide by-product of the biodigester and/or the generator to produce a carbon dioxide-rich environment in the farm housing. This minimises the amount of this greenhouse gas that is released into the atmosphere. In addition it enhances the growth of the crops, which thrive in a carbon dioxide-rich environment.
The system should operate in a way which is carbon neutral or in some cases, carbon negative.
Definitions: Biodigester: a reactor which is capable of generating a methane-rich gas from organic waste products via the action of micro-organisms, e.g. bacteria.
Biogas: the gas derived from the biodigester which is used to power the generator.
Biowaste: a carbon-rich organic waste, typically derived from animal or plant waste.
Digestate: the non-gaseous output from the biodigester.
The biowaste processor may include a plurality of individual units which may be linked in series or in parallel to provide sufficient biogas to power the generator.
In an embodiment of the invention, the biowaste processor is a biodigester.
In a further embodiment of the invention, the biodigester includes a pre-treatment station which is adapted to break down lignin in the biowaste prior to the biodigester being fuelled with the biowaste.
Lignin in the biowaste is difficult for the biodigester to degrade. As such, too much lignin may cause the biodigester to stall, which in turn stops or severely limits the output of the generator. In order for the biodigester to operate at optimum efficiency, it is therefore useful to break down the lignin content of the biowaste.
Lignin is indigestible by animal enzymes, but some fungi and bacteria are able to secrete ligninases which can bidegrade the polymer. Thus, the pre-treatment station may comprise fungi and/or bacteria which secrete one or more ligninases.
Lignin is suitably broken down by an aerobic process typically found in mushroom production. As such, the pre-treatment station may include a mushroom farm. In such an embodiment, the lignin-rich biowaste is used as part of a growing medium for the mushrooms where the ligninases secreted by the mushrooms break down the lignin content in the biowaste which is then used as a fuel for the biodigester after the mushrooms have been harvested.
The embodiment described immediately above provides an additional feature to the system in that the mushrooms generated as part of the process to break down lignin in the biowaste can then be sold.
The invention includes a biogas treatment station located between the generator and the biowaste processor, wherein the biogas treatment station suitably includes a gas input in fluid communication with the processor and a gas output in fluid communication with the generator and the treatment station outputs a desired ratio of gases for powering the generator from the gas mixture received from the processor.
Certain generators operate more efficiently with a fuel which contains more methane as a volume percentage than is generated by the biowaste processor. In such cases, it is desired to increase the volume percentage of methane in the biogas fuel for the generator. Such an increase in the amount of methane is achieved by the biogas treatment station.
The volume percentage of methane in the biogas fuel for the generator is increased by removing carbon dioxide from the gas output of the biowaste processor. This is achieved by washing the gas output from the processor with water, which is capable of dissolving carbon dioxide in preference to methane. Thus, the biogas treatment station may include a scrubber containing water.
The skilled person will appreciate that the water scrubber will also remove an amount of certain other non-methane gases from the biogas, such as hydrogen sulphide and sulphur dioxide, for
example.
The water may be under pressure and/or be within a controlled temperature range as desired to dissolve the carbon dioxide. Suitably, the gas output from the processor is bubbled through the water. The water within the scrubber may be a static pool or it may be a flow of water. Accordingly, the scrubber may include a water inlet and a water outlet such that the water flows through the scrubber from the inlet to the outlet.
The system may be used to provide environmentally-friendly power for a specific site, or it may be used to provide power to a local or national power grid, or any combination of these. Accordingly, the generator may be connected to a local or national power grid.
In addition to fuelling the generator, the system may provide surplus methane or methane-rich biogas which may be utilised as a fuel for, say, a boiler/heater, stored for later use or sold as a fuel source.
The farm housing is typically an enclosed structure which houses crops being grown. The structure is suitably enclosed as this minimises the amount of carbon dioxide which is allowed to enter the atmosphere. As crops tend to require light for growth, the structure may be formed at least partly from glass. For example, the farm housing may be a greenhouse.
The crops grown within the farm housing need not be limited to traditional plant crops such as flowers, fruits and vegetables, but may include algae, plankton, etc. Any surplus carbon dioxide from the system may be purified and/or stored for later use or sold as a by-product.
In a still further embodiment of the invention, the processor is a biodigester which includes a digestate conditioning station in which the spent biowaste is conditioned for use as a fertiliser. The digestate conditioning station typically includes a dryer which is adapted to dry the digestate. The dryer may include for example a source of heated air and a blower to direct the hot air flow over the digestate. The conditioning station may also include a grinder or pelletiser to powder or pelletise the dried digestate. A powdered or pelletised form of the dried digestate is a useful form for packaging, storage and transportation.
The system may include a catalytic converter downstream of the generator to minimise further any environmental impact of the system. In such an embodiment, the exhaust gases of the generator pass through the catalytic converter where the nitrogen oxides are broken down and carbon monoxide is oxidised to carbon dioxide, which may then be captured by a scrubbing process similar to that described above. The carbon dioxide removed from the generator exhaust may be combined with the carbon dioxide removed from the biogas and fed into the farm housing.
The generator typically produces heat as a by-product of burning the biogas and this heat is usually dissipated using a coolant system, suitably containing water as a coolant. However, this heat may be used to generate additional power by the use of a waste heat generator system. Such systems typically operate on the principals of the Rankine cycle and include a refrigerant which is heated by the waste heat from the generator to form a heated pressurised vapour, which is then used to drive an electric generator. The vapour is then cooled and condensed back to a liquid to re-start the cycle.
Thus, the generator may include a cooling system, such as a water coolant system, coupled to a waste heat generator which is operable to convert the heat to electrical energy.
To increase the efficiency of the cooling system for the generator, the cooling fluid may be further cooled between the waste heat generator and being returned to the biogas-powered generator. This may be achieved by using geothermal cooling, such as, for example, passing the coolant fluid through a heat exchanger located underground in an aquifer.
Additionally or alternatively, the heat produced by the biogas-powered generator may be used to dry the digestate. Furthermore, the waste heat may be used in a local heating system, for example to heat the farm housing.
According to a second aspect of the invention, there is provided a method of powering a generator, the method including charging a biowaste processor with biowaste, isolating from the processor a methane-rich biogas, removing a percentage of the carbon dioxide from the biogas via a scrubber containing water, fuelling the generator with the isolated biogas and supplying excess carbon dioxide to a farm housing.
As mentioned above, where the processor is a biodigester, the presence of lignin in the biowaste may have a detrimental effect on the efficiency of the biodigester. As such, the method may include a step in which the biowaste is pre-treated to reduce the lignin content therein to an acceptable level.
The pre-treatment step may include subjecting the lignin-rich biowaste to a source of bacteria and/or fungi which are capable of secreting one or more ligninases for a period of time sufficient to reduce the lignin content to a desired level.
In an embodiment of the invention, the lignin content is reduced by an aerobic process using fungi-produced ligninases, such as is found in mushroom farms. The mushrooms may be sold to increase operating revenues of the system.
In order to increase the volume percentage of methane in the biogas used to power the generator, the method includes a biogas conditioning step in which carbon dioxide is removed from the output gas of the biowaste processor. Thus, the conditioning step includes passing the biogas through a scrubber containing water. The removal of carbon dioxide is achieved by the use of water as a solvent, which preferentially dissolves gases such as carbon dioxide compared with methane. The water-based scrubber may also dissolve other non-methane gases, such as hydrogen sulfide and sulfur dioxide, which further increases the volume percentage of methane in the biogas.
Where the solvent is water, this is suitably used at a temperature between 2 and 15°C to wash the gas. The gas may be washed by bubbling it through the water.
Carbon dioxide has a greater solubility in water in the temperature range 2 to 15°C, suitably 2 to 6°C, more suitably about 4°C. Accordingly, water in this temperature range is able to dissolve a greater amount of carbon dioxide. Additionally or alternatively, the water may be pressurised to increase the carbon dioxide capable of being dissolved therein. The water pressure may be 1 to 200 kPa (0.01 to 2 bar).
The water may be static within the scrubber, i.e. the scrubber may contain a pool of water through which the biogas is bubbled, or a flow of water may pass through the scrubber or be cycled through the scrubber. Thus, the scrubber may include a water inlet and a water inlet and the water may flow through the scrubber from the inlet to the outlet.
The system may also include a carbon dioxide release step in which the water is warmed to release the dissolved carbon dioxide from the water. The non-dissolved carbon dioxide can then be collected and pumped into the farm housing or may be compressed for storage.
Alternatively, the carbon dioxide-rich water may be used directly on the crops being grown in the farm housing.
In addition to removing excess carbon dioxide from the biogas, the system may also include an exhaust gas conversion step, in which the exhaust gases from the generator are passed through a catalytic converter. The conversion step may further include a scrubbing step to remove carbon dioxide from the exhaust gases downstream of the catalytic converter.
For embodiments where the biowaste processor is a biodigester, the digestate from the biodigester may be used as a fertiliser. To provide the digestate in a more suitable form for use as a fertiliser, it may be conditioned. Thus, the method may include a step of conditioning the digestate. The conditioning step may include drying the digestate, for example by the use of a heated airflow.
Additionally or alternatively, it may include a step of grinding or pelletising the digestate.
The present invention will now be described, by way of example only, with reference to the accompanying drawing, which shows a schematic representation of an electrical energy generating system according to the invention.
Figure 1 shows a schematic representation of an electrical energy generating system according to the invention. The system includes a biodigester 2 which is a conventional "plug-type" biodigester which contains appropriate bacteria to generate a methane-rich biogas from a biowaste source 8.
The biogas source 8 is either fed directly into the biodigester 2 via paths 20 and 22a if it contains a relatively low lignin content, or it is fed into a mushroom farm 10 via paths 20 and 22b if the lignin content is relatively high. The mushrooms in the mushroom farm 10 secrete one or more ligninases which decomposes at least some of the lignin to a form which can be converted to biogas within the biodigester 2. The mushroom farm includes two outputs: a more acceptable biowaste which is fed into the biodigester as shown by step 24, and a crop of mushrooms which are harvested according to step 26.
The biogas produced within the biodigester 2 is carried by a conduit 30 to a biogas treatment station 12.
In addition to the bio gas, the biodigester 2 produces a digestate, which is the spent biowaste after it has been subjected to bacterial decomposition in the biodigester 2. The digestate is conveyed from the biodigester 2 to a digestate conditioning station 18 via step 40. The digestate is dried and pelletised within the conditioning station 18 and the digestate pellets are output via step 42, where they can be packaged and sold as fertiliser.
The biogas treatment station 12 scrubs the biogas with chilled water at 4°C which is fed into the biogas treatment station 12 under pressure from a water source 16 via a conduit 34. The scrubbing of the biogas with the chilled pressurised water removes a percentage of carbon dioxide from the biogas which effectively increases the percentage of methane in the biogas. The methane-rich biogas is carried from the biogas treatment station 12 to an electricity generator 4 via a conduit 32.
The water from the biogas treatment station 12 is carried to a degassing station 70 via a conduit 36 where the water is allowed to warm and is de-pressurised to release at least some of the carbon dioxide which was dissolved therein. The carbon dioxide is then carried to a greenhouse 6 via a conduit 72 and the water is carried to the greenhouse 6 via a conduit 74.
The greenhouse maintains an atmosphere which is rich in carbon dioxide and moisture and outputs crops which thrive in such environments via step 62.
The generator 4 receives the methane-enriched biogas which is used as fuel to generate electricity, which is output from the generator via path 50. The generator may be electrically connected to one or more electrical apparatus located nearby or it may be electrically connected to a local or national power grid.
The exhaust gases are carried by an exhaust conduit 54 to an exhaust gas conversion station 14 which includes a catalytic converter (not shown) which converts carbon monoxide from the generator to carbon dioxide and breaks down nitrogen oxide compounds. The gases downstream of the catalytic converter are scrubbed with chilled pressurised water in a similar process to the biogas treatment station 12 and the carbon dioxide-rich water is carried to the greenhouse 6 via a conduit 58, where the carbon dioxide is released from the water into the greenhouse atmosphere and the water is used for irrigation. The non-dissolved gases downstream of the catalytic converter are vented to the atmosphere via an exhaust port 56.
The generator 4 is cooled by a water cooling system. Relatively cool water is carried to the generator 4 from the greenhouse 6 via a conduit 60 and passed around the generator 4 where heat from the generator 4 is absorbed by the water. The heated water is then output from the generator 4 via a conduit 52, where is may be recycled through the system via a radiator (not shown).
The skilled person will appreciate that various features of the above-described schematic representation of the invention can be varied within the scope of the invention as claimed. In particular, various components of the system, for example pumps, valves, control systems, etc. are not described in detail as these are well known in the field of fluid transfer. In addition, details of the biodigester, the generator, the greenhouse, etc. are not provided, as these individually are known components.

Claims (18)

  1. Claims 1. An electrical energy generating system including an electricity generator, a biowaste processor and a farm housing, wherein the biowaste processor breaks down a biowaste product to a methane-rich biogas and is in fluid communication with both the generator and the farm housing, the system further including gas transport elements which are capable of transporting the biogas to the generator and carbon dioxide to the farm housing; and wherein the system further includes a biogas treatment station located between the biowaste processor and the generator, the treatment station including a scrubber including water adapted to remove carbon dioxide from the methane-rich biogas.
  2. 2. An electrical energy generating system according to Claim 1, wherein the biowaste processor is a biodigester and the system includes a pre-treatment station which breaks down the lignin in the biowaste prior to the biodigester being fuelled with the biowaste.
  3. 3. An electrical energy generating system according to Claim 2, wherein the pre-treatment station includes a mushroom farm.
  4. 4. An electrical energy generating system according to any of Claims 1 to 3, wherein the biogas treatment station removes a pre-determined percentage of carbon dioxide from the biogas.
  5. 5. An electrical energy generating system according to any of Claims 1 to 4, wherein the scrubber includes a flow of water.
  6. 6. An electrical energy generating system according to any preceding claim, wherein the generator is electrically connected to a local or national power grid.
  7. 7. An electrical energy generating system according to any preceding claim, wherein the farm housing is a greenhouse or glass enclosure within which crops are grown.
  8. 8. An electrical energy generating system according to Claim 7, wherein the crops are selected from plants, plankton and algae.
  9. 9. An electrical energy generating system according to any preceding claim, wherein the biowaste processor is a biodigester and the system includes a digestate conditioning station in which the spent biowaste is conditioned for use as a fertiliser.
  10. 10. An electrical energy generator system according to any preceding claim, wherein the generator includes a coolant system coupled to a waste heat generator.
  11. 11. A method of powering a generator, the method including charging a biowaste processor with biowaste, isolating from the processor a methane-rich biogas, removing a percentage of the carbon dioxide from the biogas via a scrubber including water, fuelling the generator with the isolated biogas and supplying excess carbon dioxide to a farm housing.
  12. 12. A method according to Claim 11, wherein the biowaste processor is a biodigester and the biowaste is pre-treated to reduce the lignin therein to an acceptable limit prior to being charged into the biodigester.
  13. 13. A method according to Claim 12, wherein the lignin is broken down by an aerobic process.
  14. 14. A method according to any of Claims 11 to 13, wherein the water is between 2 and 15°C.
  15. 15. A method according to any of Claims 11 to 14, wherein the scrubber includes a water inlet and a water outlet and the water flows from the inlet to the outlet.
  16. 16. A method according to any of claims 11 to 14, wherein the biowaste processor is a biodigester and the method further includes the step of conditioning the digestate for use as a fertiliser.
  17. 17. An electrical energy generating system substantially as described herein with reference to the accompanying drawings.
  18. 18. A method of powering a generator substantially as described herein with reference to the accompanying drawings.
GB1004605.0A 2009-03-19 2010-03-19 Electrical energy generating system Expired - Fee Related GB2470452B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
GBGB0904661.6A GB0904661D0 (en) 2009-03-19 2009-03-19 Electrical energy generating system

Publications (3)

Publication Number Publication Date
GB201004605D0 GB201004605D0 (en) 2010-05-05
GB2470452A true GB2470452A (en) 2010-11-24
GB2470452B GB2470452B (en) 2013-08-07

Family

ID=40637554

Family Applications (2)

Application Number Title Priority Date Filing Date
GBGB0904661.6A Ceased GB0904661D0 (en) 2009-03-19 2009-03-19 Electrical energy generating system
GB1004605.0A Expired - Fee Related GB2470452B (en) 2009-03-19 2010-03-19 Electrical energy generating system

Family Applications Before (1)

Application Number Title Priority Date Filing Date
GBGB0904661.6A Ceased GB0904661D0 (en) 2009-03-19 2009-03-19 Electrical energy generating system

Country Status (1)

Country Link
GB (2) GB0904661D0 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20220177827A1 (en) * 2019-03-08 2022-06-09 Hitachi Zosen Inova Ag Biogas plant and biogas treatment
WO2023161404A1 (en) * 2022-02-25 2023-08-31 Fld Technologies Gmbh Method for removing and immobilising carbon dioxide from the atmosphere and/or a waste gas
WO2024192474A1 (en) * 2023-03-21 2024-09-26 Cenagen Pty Ltd Waste processing method and system

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB175978A (en) * 1921-02-26 1923-06-20 Henry August Mueller Method of treating peat
US4566278A (en) * 1984-10-29 1986-01-28 Force Louis W Methane - carbon dioxide scrubbing method and system
WO2008138114A1 (en) * 2007-05-10 2008-11-20 Marshall Richard M A process and apparatus for assisting the extraction and processing of biodiesel oil using oil-bearing and other organic feedstock
CN101314780A (en) * 2007-05-29 2008-12-03 黄卫东 Method for producing methyl hydride and electricity with solar energy

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20080050800A1 (en) * 2006-08-23 2008-02-28 Mckeeman Trevor Method and apparatus for a multi-system bioenergy facility
DE102008038502A1 (en) * 2008-08-20 2010-02-25 Dieter Freinecker Method for generating and distributing energies by using lignocellulose-containing raw material, by delivering the raw material into a station, and pretreating and processing the raw material to liquid fermentation substrate in the station

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB175978A (en) * 1921-02-26 1923-06-20 Henry August Mueller Method of treating peat
US4566278A (en) * 1984-10-29 1986-01-28 Force Louis W Methane - carbon dioxide scrubbing method and system
WO2008138114A1 (en) * 2007-05-10 2008-11-20 Marshall Richard M A process and apparatus for assisting the extraction and processing of biodiesel oil using oil-bearing and other organic feedstock
CN101314780A (en) * 2007-05-29 2008-12-03 黄卫东 Method for producing methyl hydride and electricity with solar energy

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20220177827A1 (en) * 2019-03-08 2022-06-09 Hitachi Zosen Inova Ag Biogas plant and biogas treatment
WO2023161404A1 (en) * 2022-02-25 2023-08-31 Fld Technologies Gmbh Method for removing and immobilising carbon dioxide from the atmosphere and/or a waste gas
WO2024192474A1 (en) * 2023-03-21 2024-09-26 Cenagen Pty Ltd Waste processing method and system

Also Published As

Publication number Publication date
GB201004605D0 (en) 2010-05-05
GB2470452B (en) 2013-08-07
GB0904661D0 (en) 2009-04-29

Similar Documents

Publication Publication Date Title
US20090301399A1 (en) Fish and plant factory
JP2012520166A (en) Biomass utilization method and utilization system, and block-type thermoelectric power plant
CN112430469A (en) Greenhouse heat supply and carbon dioxide collecting system based on biomass pyrolysis technology
JP2005341953A (en) Greenhouse cultivation plant residue reuse cogeneration system
JP2010213587A (en) Plant cultivation system by greenhouse
US20090031698A1 (en) Liquid and Solid Biofueled Combined Heat and Renewable Power Plants
CN110073855A (en) A kind of distributed energy-Agricultural recycling economy system and method
GB2470452A (en) Electrical Energy Generating System
WO2012038680A1 (en) Electrical energy generating system
CN113813774A (en) Carbon capture-algae/plant culture carbon fixation system
JP2011240238A (en) Anaerobic bioreactor
JP5036938B2 (en) Organic waste combined treatment apparatus including combination of biogas production apparatus and biodiesel production apparatus, and organic waste treatment method using the same
CN108651285A (en) Utilize pig manure to realize intelligent pig farm of cogeneration on spot
CN106536924B (en) Closed-loop data center and organic life ecosystem
JP2022180705A (en) Environmental control device for greenhouse cultivation
JP2019196859A (en) Method of drying plant biomass fuel, and biomass power generation facility
CN104071748A (en) Matter energy transformation station
CN109082316B (en) Biogas purification and fertilizer production integrated system and method using renewable ammonia water
WO2012131414A1 (en) Zero carbon dioxide and heat emission integrated system of power generation from natural/renewable energy sources, organic waste reclamation and commodities production and method of conduction
Górecki et al. Biomass energy potential: green energy for the university of Warmia and Mazury in Olsztyn
TWI869795B (en) Gasification power generation method and gasification power generation system
US20240102403A1 (en) Process for utilizing waste heat and carbon dioxide from the production of low, neutral, and/or negative carbon intensity hydrogen from electrolysis
TW202438766A (en) Gasification power generation method and gasification power generation system
CN205372508U (en) Totally enclosed control system of living beings
CN204787420U (en) Antithetical couplet that utilizes biomass power generation supplies system

Legal Events

Date Code Title Description
PCNP Patent ceased through non-payment of renewal fee

Effective date: 20190319