US20150143809A1 - Environmentally friendly and high efficiency solid fuel production method using high-water-content organic waste, and combined heat and power system using same - Google Patents

Environmentally friendly and high efficiency solid fuel production method using high-water-content organic waste, and combined heat and power system using same Download PDF

Info

Publication number
US20150143809A1
US20150143809A1 US14/401,607 US201314401607A US2015143809A1 US 20150143809 A1 US20150143809 A1 US 20150143809A1 US 201314401607 A US201314401607 A US 201314401607A US 2015143809 A1 US2015143809 A1 US 2015143809A1
Authority
US
United States
Prior art keywords
reactor
solid fuel
waste
water
produced
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Abandoned
Application number
US14/401,607
Other languages
English (en)
Inventor
Jae-Hyeon Ha
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Assigned to HA, Jae-Hyeon, TAKASE, JOJI reassignment HA, Jae-Hyeon ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: HA, Jae-Hyeon
Publication of US20150143809A1 publication Critical patent/US20150143809A1/en
Abandoned legal-status Critical Current

Links

Images

Classifications

    • 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
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • 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
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/42Solid fuels essentially based on materials of non-mineral origin on animal substances or products obtained therefrom, e.g. manure
    • 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
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/403Solid fuels essentially based on materials of non-mineral origin on paper and paper waste
    • 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
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/406Solid fuels essentially based on materials of non-mineral origin on plastic
    • 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
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/46Solid fuels essentially based on materials of non-mineral origin on sewage, house, or town refuse
    • 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
    • C10L9/00Treating solid fuels to improve their combustion
    • C10L9/08Treating solid fuels to improve their combustion by heat treatments, e.g. calcining
    • C10L9/086Hydrothermal carbonization
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01KSTEAM ENGINE PLANTS; STEAM ACCUMULATORS; ENGINE PLANTS NOT OTHERWISE PROVIDED FOR; ENGINES USING SPECIAL WORKING FLUIDS OR CYCLES
    • F01K25/00Plants or engines characterised by use of special working fluids, not otherwise provided for; Plants operating in closed cycles and not otherwise provided for
    • F01K25/08Plants or engines characterised by use of special working fluids, not otherwise provided for; Plants operating in closed cycles and not otherwise provided for using special vapours
    • F01K25/14Plants or engines characterised by use of special working fluids, not otherwise provided for; Plants operating in closed cycles and not otherwise provided for using special vapours using industrial or other waste gases
    • 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
    • C10L2200/00Components of fuel compositions
    • C10L2200/04Organic compounds
    • C10L2200/0461Fractions defined by their origin
    • C10L2200/0469Renewables or materials of biological origin
    • 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
    • C10L2270/00Specifically adapted fuels
    • C10L2270/04Specifically adapted fuels for turbines, planes, power generation
    • 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
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/08Drying or removing water
    • 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
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/24Mixing, stirring of fuel components
    • 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
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/28Cutting, disintegrating, shredding or grinding
    • 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
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/48Expanders, e.g. throttles or flash tanks
    • 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
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/50Screws or pistons for moving along solids
    • 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
    • Y02E50/10Biofuels, e.g. bio-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
    • 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

Definitions

  • the present invention relates to an environmentally friendly and high efficiency solid fuel production method using a high-water-content organic waste and a combined heat and power system using the same while noticeably reducing bad smell.
  • Organic waste such as sludge, livestock excretions in general is treated using a technology such as incineration, fermentation, direct or indirect drying, etc.
  • incineration it produces dioxin and a lot of harmful substance and requires a large amount of externally supplied energy along with increased installation cost, so the above-mentioned incineration has a disadvantage in that it is not economical.
  • a large amount of energy is required so as to lower the water content from 80% to 15% in the course of direct or indirect drying, and bad smell generates from solid fuel during the drying process and after the drying process.
  • the fermentation it have some problems in that a lot of bad smell generates, and energy efficiency is low, and it takes long time to treat waste water.
  • a technology for developing a solid fuel is going on so as to treat high-water-content organic waste into energy source. In this case, it necessarily needs to lower the water content below 15%.
  • Such a solid fuel process technology is categorized into drying and carbonization. In terms of the total amount of energy, the drying is most preferred. The bad smell generating in the course of the drying and the bad smell generating in the course of the storing and use of the produced fuel become problematic.
  • an environmentally friendly and high efficiency solid fuel production method using a high-water-content organic waste comprising:
  • a waste mixing step where a high-water-content organic waste and a municipal solid waste are inputted and mixed in a Fe-based reactor
  • a hydrolysis step where a mixture of the organic waste and the municipal solid waste is pressurized by adding high temperature vapor into the reactor and is agitated in the pressurized state for thereby hydrolyzing the mixture
  • a depressurization step where the reactor is controlled to remain in normal state after the interior of the reactor is suddenly depressurized by discharging the vapor from the interior of the reactor, and the mixture is crushed by depolymerizing the organic waste treated through the step (b) or by increasing the specific surface area of the municipal solid waste treated through the step (b);
  • a vacuum or differential pressure step where water is eliminated from the reactant treated through the step (c) by providing the vacuum or differential pressure condition to the reactor
  • a solid fuel preparation step where a solid fuel of which the water content is 10 ⁇ 20% is prepared by naturally drying the reactant treated through the step (d).
  • the present invention is characterized in that the solid fuel may be produced by efficiently drying the internal water of the organic waste in such a way to much more effectively degrade the organic matter and bad smell with the aid of the degrading power of vapor radical and the promoted peptone reaction by the Fe reaction catalyst by inputting and mixing high-water-content organic waste and municipal solid waste into a Fe-based reactor and adding high temperature and pressure vapor and in such a way to completely crush and degrade the organic waste based on the sudden depressurization.
  • the present invention makes it possible to produce solid fuel within a short time by greatly enhancing the efficiency of drying in such a way that the non-degraded organic waste is depolymerized through the sudden depressurization after high temperature and pressure vapor is inputted and that the specific surface area is increased by expanding the municipal solid waste.
  • the solid fuel produced according to the present invention may be provided as a good energy source which may substitute fossil energy thanks to its high calorific power. So, it is possible to efficiently generate electricity based on the combined heat and power generator system using the above mentioned energy source.
  • FIG. 1 is a view illustrating a treatment system of a high-water-content organic waste according to the present invention.
  • FIG. 2 is an ion product change and permittivity change curve of water.
  • the present invention is directed to an environmentally friendly and high efficiency solid fuel production method using a high-water-content organic waste which makes it possible to efficiently dry the internal water of the organic waste in such a way to much more effectively degrade the organic matter and bad smell with the aid of the degrading power of vapor radical and the promoted peptone reaction by the Fe reaction catalyst by inputting and mixing high-water-content organic waste and municipal solid waste into a Fe-based reactor and adding high temperature and pressure vapor and in such a way to completely crush and degrade the organic waste based on the sudden depressurization.
  • the present invention is directed to a solid fuel production method using a high-water-content organic waste, which includes (a) a waste mixing step where a high-water-content organic waste and a municipal solid waste are inputted and mixed in a Fe-based reactor; (b) a hydrolysis step where a mixture of the organic waste and the municipal solid waste is pressurized by adding high temperature vapor into the reactor and is agitated in the pressurized state for thereby hydrolyzing the mixture; (c) a depressurization step where the reactor is controlled to remain in normal state after the interior of the reactor is suddenly depressurized by discharging the vapor from the interior of the reactor, and the mixture is crushed by depolymerizing the organic waste treated through the step (b) or by increasing the specific surface area of the municipal solid waste treated through the step (b); (d) a vacuum or differential pressure step where water is eliminated from the reactant treated through the step (c) by providing the vacuum or differential pressure condition to the reactor; and (e) a solid fuel preparation step where a solid fuel
  • the step (a) is a step where high-water-content organic waste and municipal solid waste are inputted and mixed in a Fe-based reactor.
  • the high-water-content organic waste is one or at least one selected from the group consisting of livestock excretions, sewage sludgy, and food waste and contains more than 80% of water content, and the municipal solid waste preferably contains kind of paper and plastics.
  • the municipal solid waste containing such paper and plastics each having increased specific surface area reacts while expanding together with the organic waste which was depolymerized by means of the depressurization in the depressurization step, so the drying efficiency may be maximized.
  • the plastics-based municipal solid waste which is a kind of a petroleum-based organic substance is contained, it is possible to enhance the low calorific power of the produced solid fuel.
  • the municipal solid waste contains 50 ⁇ 55% by weigh of paper, and 40 ⁇ 45% by weight of plastics.
  • the high-water-content organic waste and the municipal solid waste are inputted and mixed at a ratio of 3.5 ⁇ 4:0.5 ⁇ 1.
  • the high-water-content organic waste and the municipal solid waste are inputted and mixed in the reactor at a filling ratio of 70 ⁇ 90%. Since high temperature and pressure vapor may be supplied from outside the reactor even though the waste, which will be treated, is inputted into the reactor at such high charging rate, and the contact-based reaction with the saturated vapor can be maintained, so that it is possible to enhance the efficiency of reaction in the highest process capacity of the wastes.
  • the step (b) is a step where a mixture of the organic waste and the municipal solid waste is pressurized by supplying high temperature of vapor into the reactor, and the mixture is agitated in the pressurized state and is hydrolyzed.
  • the substance belonging to the organic waste is degraded and depolymerized by the pressurization, and the bad smell containing sulfuric acid is degraded, so the water content of the organic waste may be greatly lowered thanks to the high temperature while eliminating bad smell.
  • the mixture may be agitated and undergo the hydrolysis reaction after the internal pressure of the reactor is made to 20 ⁇ 25 atm by supplying the vapor of 200 ⁇ 250° C. into the reactor.
  • the ion product reaction is most active at the temperature of 200 ⁇ 250° C. and shows 1,000 times higher activity as compared with the room temperature. Since the permittivity lowers to 1 ⁇ 3 ⁇ 1 ⁇ 4 as compared with the room temperature, a potential difference occurs between the ions, which would result in increased organic substance degradation performance. If it is below the range of the above temperature and pressure, it is hard to obtain the desired effect, and when it is above the range of the above temperature and pressure, the loss in energy may occur.
  • step (b) of the present invention since the supply of the vapor is performed using a boiler which is connected to the reactor, the organic waste in the reactor comes into contact with the vapor from the boiler and physically and chemically reacts for thereby greatly enhancing the efficiency of the reaction without any procedure where the water changes to high temperature water in such a way that it is sprayed while coming into direct contact with the low temperature organic waste.
  • the vapor since the vapor is supplied using the externally supplied boiler, any phenomenon where it reacts with high temperature water does not occur, so the reaction may be maintained even when the amount of the waste increases. Therefore, the mixture of the waste, which will be treated, is charged up to 70 ⁇ 90% of the reactor, thus causing a contact-based reaction with the vapor.
  • the efficiency of the reaction may be greatly enhanced thanks to the catalyst reaction of Fe, in particular the promoted peptone reaction in the region where the saturated vapor occupies in the reactor, and an organic membrane of 1 ⁇ 2 mm is formed in the inner side of the reactor based on the process and operation of the reactor, so it is possible to prevent any corrosion due to NaCl, etc.
  • the step (c) of the present invention is a step where the reactor is controlled to remain in normal state after the pressure inside of the reactor is suddenly depressurized by discharging the vapor from the interior of the reactor, so that the organic waste treated through the step (b) is depolymerized or the specific surface area of the municipal solid waste treated through the step (b) is increased, and the municipal solid waste is crushed, more specifically, the step (c) is a step where the reactant pressurized by high temperature vapor is suddenly depressurized, and the volume of increased, thus depolymerizing the reactant or crushing the reactant.
  • the drying time may be shortened because such municipal solid waste is reacted with the water-content organic matter and is dried, thus greatly enhancing the efficiency of the drying.
  • the pressure is suddenly depressurized so that the atmosphere may become 0.9 ⁇ 1.1 atm by discharging the vapor inside of the reactor for 10 ⁇ 120 seconds.
  • the step (d) of the present invention is a step where the moisture is eliminated from the reactant treated through the step (c) by adopting the vacuum or differential pressure condition to the reactor. It is preferred that the moisture is eliminated by 5 ⁇ 10% from the reactant treated through the step (c) by adopting the vacuum or differential pressure condition or 10 ⁇ 15 minutes to the reactor using the vacuum pump connected to the reactor.
  • the step (e) of the present invention is a step where the reactant treated through the step (d) is naturally dried for thereby producing solid fuel of which the water content is 10 ⁇ 20%. It is preferred that the solid fuel having low calorific power of above 5,000 kcal/kg is produced.
  • the present invention relates to the combined heat and power generator system using the solid fuel produced using the above-described method.
  • the present invention provides the combined heat and power generator system characterized in that the solid fuel (RDF) is produced from high-water-content organic waste and municipal solid waste, and superheated vapor is produced by supplying the solid fuel to the RDF-based burner and boiler, and electricity may be generated by the steam-based power generation system which uses the superheated vapor.
  • RDF solid fuel
  • superheated vapor is produced by supplying the solid fuel to the RDF-based burner and boiler, and electricity may be generated by the steam-based power generation system which uses the superheated vapor.
  • a batch reactor made of a Fe material and having a dimension of 5 m 3 was manufactured.
  • 3.5 tons of livestock excretions of which the water-content was 80 ⁇ 85% and 0.5 ⁇ 1 tones of paper Municipal Solid Waste (MSW) were inputted into the reactor as soon as possible, and the input port of the top of the reactor was closed.
  • MSW Municipal Solid Waste
  • the livestock and the MSW were mixed, and vapor of 210° C. was supplied for the internal pressure of the reactor to become 23 atm.
  • the inputted saturated vapor or superheated vapor reached the reaction condition within about 3 ⁇ 5 minutes in the vapor supply-dedicated boiler of the top of the previously prepared reactor, so the supply of the vapor was stopped.
  • the supplied vapor and target waste were agitated at 10 ⁇ 15 rpm so that the supplied vapor and target waste physically and chemically reacted.
  • the saturated vapor or superheated vapor was intermittently supplied so as to maintain the atmosphere of 23 atm at 210° C.
  • the above-described state was maintained for 30 ⁇ 60 minutes depending on the physical property of the treatment target in order for the peptone reaction to take place enough based on the catalyst operation by the vapor, the treatment target organic matter and the Fe-based reactor.
  • the organic matter and the organic cell or MSW which had not been degraded during the above-mentioned reaction, were depolymerized or crushed by quickly discharging the vapor through the vapor discharge port by opening the pressure reducing valve until the pressure became the atmospheric pressure (1-atm) within 2 minutes.
  • About 5 ⁇ 10% of the total water of the reactant was eliminated by performing the vacuum (differential pressure) process for about 10 ⁇ 15 minutes using the external vacuum (differential pressure) pump so as to eliminate the water from the reactant in the reactor under the high vacuum or differential pressure condition after the processes for depolymerizing and crushing the reactant.
  • the product produced after the reaction was moved to the natural drying place and was naturally dried, so that the final solid fuel of which the water content was 15% was produced.
  • the solid fuel was produced by the method of the first exemplary embodiment, wherein the solid fuel was produced without adding the municipal solid waste (MSW).
  • MSW municipal solid waste
  • the solid fuel was produced by the method of the first exemplary embodiment, wherein the solid fuel was produced without performing a process for suddenly depressurizing by discharging the vapor after the pressurization.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Combustion & Propulsion (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)
US14/401,607 2012-05-17 2013-05-15 Environmentally friendly and high efficiency solid fuel production method using high-water-content organic waste, and combined heat and power system using same Abandoned US20150143809A1 (en)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
KR10-2012-0052662 2012-05-17
KR1020120052662A KR101313314B1 (ko) 2012-05-17 2012-05-17 고함수 유기성 폐기물을 이용한 친환경·고효율의 고형연료 제조방법 및 이를 이용한 열병합 발전 시스템
PCT/KR2013/004323 WO2013172661A1 (ko) 2012-05-17 2013-05-15 고함수 유기성 폐기물을 이용한 친환경·고효율의 고형연료 제조방법 및 이를 이용한 열병합 발전 시스템

Publications (1)

Publication Number Publication Date
US20150143809A1 true US20150143809A1 (en) 2015-05-28

Family

ID=49456985

Family Applications (1)

Application Number Title Priority Date Filing Date
US14/401,607 Abandoned US20150143809A1 (en) 2012-05-17 2013-05-15 Environmentally friendly and high efficiency solid fuel production method using high-water-content organic waste, and combined heat and power system using same

Country Status (6)

Country Link
US (1) US20150143809A1 (es)
KR (1) KR101313314B1 (es)
CN (1) CN104508093A (es)
ES (1) ES2526716B1 (es)
RU (1) RU2586332C1 (es)
WO (1) WO2013172661A1 (es)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP3453240A4 (en) * 2016-04-19 2020-01-15 Caraball Ugarte, José PURINE PROCESSING PROCESS FOR OBTAINING A HIGH CALORIFIC POWER PRODUCT
CN114433596A (zh) * 2022-01-25 2022-05-06 上海汉怡环保科技有限公司 一种有机质垃圾处理工艺

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106753676A (zh) * 2017-01-03 2017-05-31 苏州草宝能源科技有限公司 一种高温湿法干燥生活垃圾的方法
CN109943380A (zh) * 2019-02-22 2019-06-28 佐古猛 一种固体燃料制造方法及制造装置
KR102107704B1 (ko) * 2019-05-22 2020-05-07 주식회사 네오디아 하수 슬러지를 이용한 연료 제조장치
JP7285729B2 (ja) * 2019-08-08 2023-06-02 三菱重工業株式会社 廃棄物処理装置
CN110564431B (zh) * 2019-09-10 2024-07-12 上海环境卫生工程设计院有限公司 一种湿垃圾脱水热解方法及系统
CN111112276A (zh) * 2019-11-25 2020-05-08 林赞德 废弃物处理方法
KR102198208B1 (ko) 2020-07-13 2021-01-04 채재우 고함수 웨이스트 재활용 및 소각장치
KR102319903B1 (ko) * 2020-12-03 2021-11-01 하재현 생활 쓰레기 가수 분해 펠렛 연료화 시스템

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004044492A1 (en) * 2002-11-14 2004-05-27 David Systems Technology, S.L. Method and device for integrated plasma-melt treatment of wastes
WO2008130260A1 (en) * 2007-04-18 2008-10-30 Sgc Energia Sgps, S.A. Waste to liquid hydrocarbon refinery system

Family Cites Families (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1079834C (zh) * 1994-12-07 2002-02-27 受控的环境系统有限公司 城市固体废物处理设备和商用乳酸的生产方法
KR100356966B1 (en) * 2002-04-16 2002-10-19 Halla Engineering & Ind Develo Apparatus and method for integrated treatment of garbage and livestock excretions by two stage anaerobic digestion
JP4913366B2 (ja) * 2005-06-21 2012-04-11 株式会社ネオス 難分解性有機ハロゲン化合物の処理方法
AU2006303016B2 (en) * 2005-10-17 2013-03-28 Ab-Cwt, Llc Process of conversion of organic and non-organic waste materials into useful products
KR100841335B1 (ko) * 2007-03-08 2008-06-26 한국에너지기술연구원 중압증기를 이용한 축산분뇨 또는 유기성폐기물 건조장치 및 이를 이용한 축산분뇨 또는 유기성폐기물의 건조방법과 이러한 축산분뇨 또는 유기성폐기물 건조장치를 이용한 축산분뇨 또는 유기성폐기물의 고효율 건조/가스화를 포함하는 열병합장치
RU2326900C1 (ru) * 2007-04-20 2008-06-20 Валерий Григорьевич Лурий Способ переработки органических углеродсодержащих отходов и углеродсодержащие формовки
WO2009072454A1 (ja) * 2007-12-03 2009-06-11 Cdm Consulting Co., Ltd バイオマスの処理方法
US8057639B2 (en) * 2008-02-28 2011-11-15 Andritz Inc. System and method for preextraction of hemicellulose through using a continuous prehydrolysis and steam explosion pretreatment process
JP2010106133A (ja) * 2008-10-30 2010-05-13 Kubota Kankyo Service Kk 廃棄物の燃料化方法および装置
KR101243605B1 (ko) * 2009-11-24 2013-03-18 델타 떠모 에너지 인크 열수분해에 의한 폐기물 처리와 고효율 에너지를 생산하는 방법및 장치

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004044492A1 (en) * 2002-11-14 2004-05-27 David Systems Technology, S.L. Method and device for integrated plasma-melt treatment of wastes
WO2008130260A1 (en) * 2007-04-18 2008-10-30 Sgc Energia Sgps, S.A. Waste to liquid hydrocarbon refinery system

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP3453240A4 (en) * 2016-04-19 2020-01-15 Caraball Ugarte, José PURINE PROCESSING PROCESS FOR OBTAINING A HIGH CALORIFIC POWER PRODUCT
CN114433596A (zh) * 2022-01-25 2022-05-06 上海汉怡环保科技有限公司 一种有机质垃圾处理工艺

Also Published As

Publication number Publication date
KR101313314B1 (ko) 2013-09-30
RU2586332C1 (ru) 2016-06-10
CN104508093A (zh) 2015-04-08
ES2526716A2 (es) 2015-01-14
ES2526716B1 (es) 2015-11-17
ES2526716R1 (es) 2015-02-04
WO2013172661A1 (ko) 2013-11-21

Similar Documents

Publication Publication Date Title
US20150143809A1 (en) Environmentally friendly and high efficiency solid fuel production method using high-water-content organic waste, and combined heat and power system using same
Ahmad et al. The outlook of the production of advanced fuels and chemicals from integrated oil palm biomass biorefinery
Atelge et al. A critical review of pretreatment technologies to enhance anaerobic digestion and energy recovery
Carrere et al. Review of feedstock pretreatment strategies for improved anaerobic digestion: From lab-scale research to full-scale application
Shah et al. Biomass pretreatment technologies
Karuppiah et al. Biomass pretreatment for enhancement of biogas production
Basak et al. Advances in physicochemical pretreatment strategies for lignocellulose biomass and their effectiveness in bioconversion for biofuel production
Nazari et al. Recent advances in energy recovery from wastewater sludge
JP5334388B2 (ja) 食品廃棄物および汚泥からのエネルギー回収システム
Scherzinger et al. Thermal pre-treatment options to enhance anaerobic digestibility–A review
Maryam et al. Enhancing methane production from dewatered waste activated sludge through alkaline and photocatalytic pretreatment
Balasundaram et al. Energy feasibility and life cycle assessment of sludge pretreatment methods for advanced anaerobic digestion
Yin et al. Fermentative hydrogen production from waste sludge solubilized by low-pressure wet oxidation treatment
KR101584621B1 (ko) 하수슬러지를 연료화하기 위한 혼합건조장치 및 하수슬러지 연료탄의 제조방법
Hu et al. Polyols and polyurethane foams from acid‐catalyzed biomass liquefaction by crude glycerol: Effects of crude glycerol impurities
Zhi et al. A review of hydrothermal carbonization of municipal sludge: Process conditions, physicochemical properties, methods coupling, energy balances and life cycle analyses
CN102826730A (zh) 一种厌氧消化污泥热水解和超声波联合预处理方法
KR100991483B1 (ko) 마이크로웨이브 건조장치와 열전매체유를 이용한 바이오매스의 건조방법
Periyasamy et al. Biogas recovery from sludge
Colla et al. Waste biomass and blended bioresources in biogas production
KR20140132615A (ko) 고함수 유기성 폐기물 건조장치, 그를 이용한 고함수 유기성 폐기물의 고형연료 제조방법 및 고함수 유기성 폐기물의 에너지화를 위한 전처리 방법
Lam et al. Pretreatment and thermochemical and biological processing of biomass
JP2003103299A (ja) 高濃度汚泥の処理方法及びその装置
Byun et al. Evaluation of non-thermal effects by microwave irradiation in hydrolysis of waste-activated sludge
KR20150035290A (ko) 유기물을 이용한 바이오메탄 제조방법

Legal Events

Date Code Title Description
AS Assignment

Owner name: HA, JAE-HYEON, KOREA, REPUBLIC OF

Free format text: ASSIGNMENT OF ASSIGNORS INTEREST;ASSIGNOR:HA, JAE-HYEON;REEL/FRAME:034282/0645

Effective date: 20141113

Owner name: TAKASE, JOJI, JAPAN

Free format text: ASSIGNMENT OF ASSIGNORS INTEREST;ASSIGNOR:HA, JAE-HYEON;REEL/FRAME:034282/0645

Effective date: 20141113

STCB Information on status: application discontinuation

Free format text: ABANDONED -- FAILURE TO RESPOND TO AN OFFICE ACTION