US20150338094A1 - Waste energy recovery system - Google Patents
Waste energy recovery system Download PDFInfo
- Publication number
- US20150338094A1 US20150338094A1 US14/285,832 US201414285832A US2015338094A1 US 20150338094 A1 US20150338094 A1 US 20150338094A1 US 201414285832 A US201414285832 A US 201414285832A US 2015338094 A1 US2015338094 A1 US 2015338094A1
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- Prior art keywords
- furnace
- cooling water
- smoke
- oil
- water filter
- 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
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- 239000002699 waste material Substances 0.000 title claims abstract description 67
- 238000011084 recovery Methods 0.000 title claims abstract description 20
- 239000000498 cooling water Substances 0.000 claims abstract description 57
- 239000007789 gas Substances 0.000 claims abstract description 54
- 239000000779 smoke Substances 0.000 claims abstract description 38
- 239000000428 dust Substances 0.000 claims abstract description 36
- 239000003921 oil Substances 0.000 claims abstract description 36
- 239000002023 wood Substances 0.000 claims abstract description 24
- 239000003610 charcoal Substances 0.000 claims abstract description 20
- 239000000463 material Substances 0.000 claims abstract description 13
- 238000002485 combustion reaction Methods 0.000 claims abstract description 12
- -1 tree branches Substances 0.000 claims abstract description 9
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 8
- 239000000446 fuel Substances 0.000 claims abstract description 8
- 239000001301 oxygen Substances 0.000 claims abstract description 8
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 8
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 8
- 229910052799 carbon Inorganic materials 0.000 claims description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 7
- 238000001035 drying Methods 0.000 claims description 5
- 238000000746 purification Methods 0.000 claims description 5
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 4
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 4
- 239000004571 lime Substances 0.000 claims description 4
- 239000000843 powder Substances 0.000 claims description 4
- 229910000831 Steel Inorganic materials 0.000 claims description 2
- 239000002253 acid Substances 0.000 claims description 2
- 238000002309 gasification Methods 0.000 claims description 2
- 239000012535 impurity Substances 0.000 claims description 2
- 239000007788 liquid Substances 0.000 claims description 2
- 239000000203 mixture Substances 0.000 claims description 2
- 239000004033 plastic Substances 0.000 claims description 2
- 229920003023 plastic Polymers 0.000 claims description 2
- 229910001220 stainless steel Inorganic materials 0.000 claims description 2
- 239000010935 stainless steel Substances 0.000 claims description 2
- 239000010959 steel Substances 0.000 claims description 2
- 238000003763 carbonization Methods 0.000 claims 1
- 238000010438 heat treatment Methods 0.000 claims 1
- 238000004064 recycling Methods 0.000 abstract description 3
- 239000004071 soot Substances 0.000 abstract description 3
- 239000003570 air Substances 0.000 description 19
- 239000002956 ash Substances 0.000 description 7
- 239000010812 mixed waste Substances 0.000 description 4
- 238000003915 air pollution Methods 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 238000000034 method Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- 229910002091 carbon monoxide Inorganic materials 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 150000002013 dioxins Chemical class 0.000 description 2
- 239000000295 fuel oil Substances 0.000 description 2
- 230000036541 health Effects 0.000 description 2
- 231100000331 toxic Toxicity 0.000 description 2
- 230000002588 toxic effect Effects 0.000 description 2
- 238000010792 warming Methods 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- 235000002918 Fraxinus excelsior Nutrition 0.000 description 1
- 241000282412 Homo Species 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- 241000700605 Viruses Species 0.000 description 1
- 125000003118 aryl group Chemical group 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- 150000004826 dibenzofurans Chemical class 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 239000002737 fuel gas Substances 0.000 description 1
- 239000002920 hazardous waste Substances 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 231100000518 lethal Toxicity 0.000 description 1
- 230000001665 lethal effect Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 230000004083 survival effect Effects 0.000 description 1
Images
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/027—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
- F23G5/0276—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage using direct heating
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/08—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
- F23G5/442—Waste feed arrangements
- F23G5/444—Waste feed arrangements for solid waste
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
- B01D2253/102—Carbon
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/20—Halogens or halogen compounds
- B01D2257/206—Organic halogen compounds
- B01D2257/2064—Chlorine
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
- B01D2258/0291—Flue gases from waste incineration plants
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/002—Separation 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 condensation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/02—Separation 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 adsorption, e.g. preparative gas chromatography
- B01D53/04—Separation 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 adsorption, e.g. preparative gas chromatography with stationary adsorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/26—Drying gases or vapours
- B01D53/261—Drying gases or vapours by adsorption
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2204/00—Supplementary heating arrangements
- F23G2204/10—Supplementary heating arrangements using auxiliary fuel
- F23G2204/101—Supplementary heating arrangements using auxiliary fuel solid fuel
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2209/00—Specific waste
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2900/00—Special features of, or arrangements for incinerators
- F23G2900/50205—Waste pre-treatment by pyrolysis, gasification or cracking followed by condensation of gas into combustible oil or fat
Definitions
- the present invention relates to energy recovery technology and more particularly, to a waste energy recovery system for recovering energy from waste materials, which separates smoke and oil for recycling without emitting soot or using any fuel material that can cause pollution hazards.
- the current garbage incineration technique is to burn a fuel such as energy coal, gas, fuel oil, diesel and plasma, etc., to deliver air using an air blower, to neutralize smoke gas, and to remove solid matters from smoke gas by spraying water and using dust bag, to spray water, enabling treated gas to be discharged into the atmosphere.
- a fuel such as energy coal, gas, fuel oil, diesel and plasma, etc.
- the resource utilization of this garbage incineration technique is only for power generation.
- the average humidity of garbage is normally above 40%.
- the furnace internal temperature of the incinerator must be maintained at a very high level so that the garbage in the furnace can be fully incinerated.
- a large amount of fuel gas, heavy oil, diesel, coal may be used for the incineration of garbage, resulting in a great waste and causing severe air pollution to impact people's health and to accelerate global warming.
- incineration ash emitted by an incinerator contains a large amount of highly toxic aromatic organic chlorides or dioxins. If these harmful substances flow out of the incinerator into the atmosphere, it will directly impact the natural environment or human health, causing a huge social problem.
- the present invention has been accomplished under the circumstances in view. It is the main object of the present invention to provide a waste energy recovery system, which separates smoke and oil for recycling without emitting soot or using any fuel material that can cause pollution hazards.
- a waste energy recovery system of the invention comprises a furnace, at least one cooling water filter, at least one dry purifier and an exhaust fan.
- the furnace, the at least one cooling water filter, the at least one dry purifier and the exhaust fan are connected in series by closed conduits.
- the exhaust fan is disposed near a rear end of the waste energy recovery system.
- the furnace comprises a waste inlet 11 located in a top side thereof for enabling the user to put wastes into the inside of the furnace, an unidirectional airtight cover covered the waste inlet 11 , an ash outlet located in an opposing bottom side thereof for discharge of burnt charcoal and carbonized wastes, an unidirectional airtight cover covered the ash outlet, and at least one air inlet located in the periphery thereof.
- charcoal, tree branches, wood and/or waste wood furniture are put in a bottom side inside the furnace for use as a fuel material, and then assorted wastes are put through the waste inlet 11 into the inside of the furnace, and then an igniter is inserted through one the air inlet into the inside of the furnace to ignite the charcoal, and at the same time, the exhaust fan is turned on to draw air and to create a negative pressure in the furnace, the at least one cooling water filter and the at least one dry purifier so that outside air is drawn through the at least one air inlet into the inside of the furnace, and thus, a limited volume of oxygen is provided for the combustion of the loaded charcoal, tree branches, wood and/or waste wood furniture.
- the burning temperature in the furnace is over 1000° C.
- the loaded charcoal, tree branches, wood and/or waste wood furniture are being smoldered in the furnace due to combustion under lean oxygen, and thus, the loaded wastes in contact with this temperature field of over 1000° C. are immediately decomposed into oil, smoke and dust mixed gas.
- FIG. 1 is a schematic sectional view of a waste energy recovery system in accordance with the present invention.
- FIG. 2 is an elevational view of the waste energy recovery system in accordance with the present invention.
- FIG. 3 is an operational flow chart explaining the operation of the waste energy recovery system in accordance with the present invention.
- the waste energy recovery system comprises a furnace 1 , at least one cooling water filter, at least one dry purifier and an exhaust fan 5 .
- the aforesaid component parts are connected by closed conduits 7 .
- the exhaust fan 5 is disposed near the rear end of the system.
- the furnace 1 comprises a waste inlet 11 located in a top side thereof for enabling the user to put wastes 15 into the inside of the furnace 1 , an unidirectional airtight cover 111 covered the waste inlet 11 , an ash outlet 12 located in an opposing bottom side thereof for discharge of burnt charcoal 141 and carbonized wastes 151 , an unidirectional airtight cover 121 covered the ash outlet 12 , and at least one air inlet 13 located in the periphery thereof.
- the burning temperature in the furnace 1 can be over 1000° C., however, due to combustion under lean oxygen, the charcoal 14 , tree branches, wood and/or waste wood furniture are being smoldered in the furnace 1 . At this time, the wastes 15 in contact with this temperature field of over 1000° C. are immediately decomposed into oil, smoke and dust mixed gas 16 .
- a part of the tar in the oil, smoke and dust mixed gas 16 is removed when the oil, smoke and dust mixed gas 16 flows over the hot carbon layer of over 1000° C., and then the temperature of the oil, smoke and dust mixed gas 16 is lowered when it flows through the raceway in the furnace 1 into the at least one cooling water filter. After entered the at least one cooling water filter, the oil, smoke and dust mixed gas 16 is cooled down to room temperature and then separated into crude tar 162 and inflammable gas 161 .
- the charcoal 14 and the top-sided wastes 15 in the furnace 1 are carbonized and maintained in shape, but not in ashes, and thus, the discharged burnt charcoal 141 can be used as a fuel for combustion again. If wood or waste wood furniture are put in the furnace 1 for combustion, it can be carbonized into burnt charcoal 141 for combustion again. After discharged out of the ash outlet 12 , the carbonized wastes 151 can be crushed and used as organic fertilizers. Further, the quantity of the at least one cooling water filter and the quantity of the at least one dry purifier can be changed to fit different needs. In the present preferred embodiment, two cooling water filters and two dry purifiers are used.
- a cooling water circulating pipe 21 extends through the first cooling water filter 2 to guide a circulating flow of cooling water for heat exchange with the oil, smoke and dust mixed gas 16 that flows from the furnace 1 through the closed conduit 7 into the first cooling water filter 2 in contact with the outside surface of the cooling water circulating pipe 21 , enabling the oil, smoke and dust mixed gas 16 to be cooled down.
- most crude tar 162 in the oil, smoke and dust mixed gas 16 is cooled down to fall to the bottom side in the first cooling water filter 2 and then guided out of the first cooling water filter 2 through a bottom-sided crude tar discharge pipe 23 for collection, and the rest oil, smoke and dust mixed gas 16 keeps flowing through another closed conduit 7 into the second cooling water filter 3 .
- the second cooling water filter 3 has a cooling water pipe 31 connected thereto for guiding external cooling water 32 into the second cooling water filter 3 for direct contact with the oil, smoke and dust mixed gas 16 .
- the oil, smoke and dust mixed gas 16 is secondarily cooled down, causing the rest crude tar 162 in the oil, smoke and dust mixed gas 16 to float on the surface of the cooling water 32 in the second cooling water filter 3 and then guided out of the second cooling water filter 3 through another crude tar discharge pipe 33 for collection, enabling the rest inflammable gas 161 to flow through another closed conduit 7 into the first dry purifier 4 where the filter material 41 in the first dry purifier 4 such as active carbon or HePa filter media removes micro dust and water moisture from the inflammable gas 16 to perform a primary drying and purification process.
- the filter material 41 in the first dry purifier 4 such as active carbon or HePa filter media removes micro dust and water moisture from the inflammable gas 16 to perform a primary drying and purification process.
- the inflammable gas 161 flows out of the first dry purifier 4 through another closed conduit 7 into the second dry purifier 6 where the filter material 61 in the second dry purifier 6 such as active carbon or HePa filter media removes micro dust and water moisture from the inflammable gas 161 to perform a secondary drying and purification process, and the purified inflammable gas 161 is then guided by gas pipes 62 to burner stoves for application.
- the purified inflammable gas 161 can also be converted by an external liquefaction equipment into liquid inflammable gas for storage and application. If the active carbons in the first dry purifier 4 and second dry purifier 6 have a large amount of impurities adhered thereto after a long period of application, they can be delivered to the furnace 1 and heat carbonized for repeated use.
- a manifold 22 is connected between the second cooling water filter 3 and the furnace 1 . If the moisture content of the wastes 15 in the furnace 1 , the manifold 22 can be opened to guide the heated cooling water 32 from the second cooling water filter 3 into the furnace 1 to increase the moisture content of the wastes 15 .
- the invention adds 3% strongly alkaline lime powder to the mixed wastes 15 .
- the content of the strongly alkaline lime powder can be adjusted subject to the amount of plastics in the mixed wastes 15 .
- the furnace 1 can be selected from the material group of class 310 stainless steel, acid resistant steels and firebricks for direct contact with the wastes 15 .
Landscapes
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
A waste energy recovery system includes a furnace for the combustion of charcoal, tree branches, wood and/or waste wood furniture under lean oxygen, cooling water filters, dry purifiers, and an exhaust fan for creating a negative pressure in the furnace, the cooling water filters and the dry purifiers such that the loaded charcoal, tree branches, wood and/or waste wood furniture are smoldered in the furnace and decomposed into oil, smoke and dust mixed gas, enabling the oil, smoke and dust mixed gas to be cooled down and separated into crude tar and inflammable gas after entered the cooling water filters. Thus, the waste energy recovery system effectively separates smoke and oil for recycling without emitting soot or using any fuel material that can cause pollution hazards.
Description
- 1. Field of the Invention
- The present invention relates to energy recovery technology and more particularly, to a waste energy recovery system for recovering energy from waste materials, which separates smoke and oil for recycling without emitting soot or using any fuel material that can cause pollution hazards.
- 2. Description of the Related Art
- With the continuous development of modern technology, commercial and industrial prosperity keeps going. However, widely use of a variety of petrochemical products generates a large amount of hazardous wastes, complicating waste treatment. Because of lack in waste garbage disposal technology, severe secondary air pollution problems are seen in many countries around the word.
- Mixed wastes produced by humans around the world may contain very complex organic and inorganic substances and a large amount of lethal bacteria and viruses. Except landfill and incineration, there is no other better ways to dispose of garbage. However, disposing of garbage by landfill or incineration is the planet's largest source of pollution because it can severely pollute soil, water and air, and its harm to the ecological environment of the earth and human life is unprecedented. Effective scientific waste treatment and pollution prevention job is now a matter that admits of no delay.
- The current garbage incineration technique is to burn a fuel such as energy coal, gas, fuel oil, diesel and plasma, etc., to deliver air using an air blower, to neutralize smoke gas, and to remove solid matters from smoke gas by spraying water and using dust bag, to spray water, enabling treated gas to be discharged into the atmosphere. The resource utilization of this garbage incineration technique is only for power generation.
- The average humidity of garbage is normally above 40%. Thus, the furnace internal temperature of the incinerator must be maintained at a very high level so that the garbage in the furnace can be fully incinerated. In order to accelerate incineration, a large amount of fuel gas, heavy oil, diesel, coal may be used for the incineration of garbage, resulting in a great waste and causing severe air pollution to impact people's health and to accelerate global warming.
- Moreover, with the popularity of chemicals, incineration ash emitted by an incinerator contains a large amount of highly toxic aromatic organic chlorides or dioxins. If these harmful substances flow out of the incinerator into the atmosphere, it will directly impact the natural environment or human health, causing a huge social problem.
- Further, hydrogen chloride (HCl), oxygen (O2) and carbon monoxide (CO) generated after incineration can be synthesized with heavy metals or residual carbon to generate toxic dioxins and polychlorinated dibenzofurans, leading to huge social problems. However, the conventional garbage treatment incineration technique cannot solve the above-mentioned problems.
- According to the WHO reports, environmental and air pollution has caused further serious problems affecting human survival. Therefore, the WHO requests all countries around the world to commit to pollution improvement for the slowing of global warming.
- The present invention has been accomplished under the circumstances in view. It is the main object of the present invention to provide a waste energy recovery system, which separates smoke and oil for recycling without emitting soot or using any fuel material that can cause pollution hazards.
- To achieve this and other objects of the present invention, a waste energy recovery system of the invention comprises a furnace, at least one cooling water filter, at least one dry purifier and an exhaust fan. The furnace, the at least one cooling water filter, the at least one dry purifier and the exhaust fan are connected in series by closed conduits. The exhaust fan is disposed near a rear end of the waste energy recovery system. The furnace comprises a
waste inlet 11 located in a top side thereof for enabling the user to put wastes into the inside of the furnace, an unidirectional airtight cover covered thewaste inlet 11, an ash outlet located in an opposing bottom side thereof for discharge of burnt charcoal and carbonized wastes, an unidirectional airtight cover covered the ash outlet, and at least one air inlet located in the periphery thereof. During application, charcoal, tree branches, wood and/or waste wood furniture are put in a bottom side inside the furnace for use as a fuel material, and then assorted wastes are put through the waste inlet 11 into the inside of the furnace, and then an igniter is inserted through one the air inlet into the inside of the furnace to ignite the charcoal, and at the same time, the exhaust fan is turned on to draw air and to create a negative pressure in the furnace, the at least one cooling water filter and the at least one dry purifier so that outside air is drawn through the at least one air inlet into the inside of the furnace, and thus, a limited volume of oxygen is provided for the combustion of the loaded charcoal, tree branches, wood and/or waste wood furniture. Subject to the functioning of the exhaust fan to draw air and the functioning of the at least one air inlet of the furnace to intake air, the burning temperature in the furnace is over 1000° C., and the loaded charcoal, tree branches, wood and/or waste wood furniture are being smoldered in the furnace due to combustion under lean oxygen, and thus, the loaded wastes in contact with this temperature field of over 1000° C. are immediately decomposed into oil, smoke and dust mixed gas. At this time, a part of the tar in the oil, smoke and dust mixed gas is removed when the oil, smoke and dust mixed gas flows over the hot carbon layer of over 1000° C., and then the temperature of the oil, smoke and dust mixed gas is lowered when the oil, smoke and dust flows through an internal raceway in the furnace into the at least one cooling water filter, and thus, the oil, smoke and dust mixed gas is cooled down to room temperature and then separated into crude tar and inflammable gas after entered the at least one cooling water filter. -
FIG. 1 is a schematic sectional view of a waste energy recovery system in accordance with the present invention. -
FIG. 2 is an elevational view of the waste energy recovery system in accordance with the present invention. -
FIG. 3 is an operational flow chart explaining the operation of the waste energy recovery system in accordance with the present invention. - Referring to
FIGS. 1-3 , a waste energy recovery system in accordance with the present invention is shown. The waste energy recovery system comprises afurnace 1, at least one cooling water filter, at least one dry purifier and anexhaust fan 5. The aforesaid component parts are connected by closedconduits 7. Theexhaust fan 5 is disposed near the rear end of the system. Thefurnace 1 comprises awaste inlet 11 located in a top side thereof for enabling the user to putwastes 15 into the inside of thefurnace 1, anunidirectional airtight cover 111 covered thewaste inlet 11, anash outlet 12 located in an opposing bottom side thereof for discharge ofburnt charcoal 141 andcarbonized wastes 151, anunidirectional airtight cover 121 covered theash outlet 12, and at least oneair inlet 13 located in the periphery thereof. In application, putcharcoal 14, tree branches, wood and/or waste wood furniture in a bottom side inside thefurnace 1 for use as a fuel material, and then put assortedwastes 15 through thewaste inlet 11 into the inside of thefurnace 1, and then insert an igniter through oneair inlet 13 into the inside of thefurnace 1 to ignite thecharcoal 14, and at the same time, turn on theexhaust fan 5 to draw air, creating a negative pressure in thefurnace 1, the at least one cooling water filter and the at least one dry purifier to suck in outside air through theair inlet 13 into the inside of thefurnace 1, and thus a limited volume of oxygen can be provided for the combustion of thecharcoal 14, tree branches, wood and/or waste wood furniture. Subject to the functioning of theexhaust fan 5 to draw air and the functioning of the at least oneair inlet 13 of thefurnace 1 to intake air, the burning temperature in thefurnace 1 can be over 1000° C., however, due to combustion under lean oxygen, thecharcoal 14, tree branches, wood and/or waste wood furniture are being smoldered in thefurnace 1. At this time, thewastes 15 in contact with this temperature field of over 1000° C. are immediately decomposed into oil, smoke and dust mixedgas 16. A part of the tar in the oil, smoke and dust mixedgas 16 is removed when the oil, smoke and dust mixedgas 16 flows over the hot carbon layer of over 1000° C., and then the temperature of the oil, smoke and dust mixedgas 16 is lowered when it flows through the raceway in thefurnace 1 into the at least one cooling water filter. After entered the at least one cooling water filter, the oil, smoke and dust mixedgas 16 is cooled down to room temperature and then separated intocrude tar 162 andinflammable gas 161. - When smoldered in the
furnace 1 over 1000° C., thecharcoal 14 and the top-sided wastes 15 in thefurnace 1 are carbonized and maintained in shape, but not in ashes, and thus, the dischargedburnt charcoal 141 can be used as a fuel for combustion again. If wood or waste wood furniture are put in thefurnace 1 for combustion, it can be carbonized intoburnt charcoal 141 for combustion again. After discharged out of theash outlet 12, thecarbonized wastes 151 can be crushed and used as organic fertilizers. Further, the quantity of the at least one cooling water filter and the quantity of the at least one dry purifier can be changed to fit different needs. In the present preferred embodiment, two cooling water filters and two dry purifiers are used. - Further, a cooling
water circulating pipe 21 extends through the firstcooling water filter 2 to guide a circulating flow of cooling water for heat exchange with the oil, smoke and dust mixedgas 16 that flows from thefurnace 1 through the closedconduit 7 into the firstcooling water filter 2 in contact with the outside surface of the coolingwater circulating pipe 21, enabling the oil, smoke and dust mixedgas 16 to be cooled down. At this time, mostcrude tar 162 in the oil, smoke and dust mixedgas 16 is cooled down to fall to the bottom side in the firstcooling water filter 2 and then guided out of the firstcooling water filter 2 through a bottom-sided crudetar discharge pipe 23 for collection, and the rest oil, smoke and dust mixedgas 16 keeps flowing through another closedconduit 7 into the secondcooling water filter 3. The secondcooling water filter 3 has acooling water pipe 31 connected thereto for guidingexternal cooling water 32 into the secondcooling water filter 3 for direct contact with the oil, smoke and dust mixedgas 16. At this time, the oil, smoke and dust mixedgas 16 is secondarily cooled down, causing the restcrude tar 162 in the oil, smoke and dust mixedgas 16 to float on the surface of thecooling water 32 in the secondcooling water filter 3 and then guided out of the secondcooling water filter 3 through another crudetar discharge pipe 33 for collection, enabling the restinflammable gas 161 to flow through another closedconduit 7 into the firstdry purifier 4 where thefilter material 41 in the firstdry purifier 4 such as active carbon or HePa filter media removes micro dust and water moisture from theinflammable gas 16 to perform a primary drying and purification process. After through the primary drying and purification process, theinflammable gas 161 flows out of the firstdry purifier 4 through another closedconduit 7 into the seconddry purifier 6 where thefilter material 61 in the seconddry purifier 6 such as active carbon or HePa filter media removes micro dust and water moisture from theinflammable gas 161 to perform a secondary drying and purification process, and the purifiedinflammable gas 161 is then guided bygas pipes 62 to burner stoves for application. The purifiedinflammable gas 161 can also be converted by an external liquefaction equipment into liquid inflammable gas for storage and application. If the active carbons in the firstdry purifier 4 and seconddry purifier 6 have a large amount of impurities adhered thereto after a long period of application, they can be delivered to thefurnace 1 and heat carbonized for repeated use. - Further, a
manifold 22 is connected between the secondcooling water filter 3 and thefurnace 1. If the moisture content of thewastes 15 in thefurnace 1, themanifold 22 can be opened to guide the heatedcooling water 32 from the secondcooling water filter 3 into thefurnace 1 to increase the moisture content of thewastes 15. - Further, during combustion gasification of the
mixed wastes 15, a large amount of superacidic gas mixture will be generated, causing smoke oil viscosity to plug the pipeline and to corrode the e furnace and pipe materials. In order to eliminate this problem, the invention adds 3% strongly alkaline lime powder to the mixedwastes 15. The content of the strongly alkaline lime powder can be adjusted subject to the amount of plastics in the mixed wastes 15. Further, thefurnace 1 can be selected from the material group of class 310 stainless steel, acid resistant steels and firebricks for direct contact with thewastes 15. - Although particular embodiments of the invention have been described in detail for purposes of illustration, various modifications and enhancements may be made without departing from the spirit and scope of the invention. Accordingly, the invention is not to be limited except as by the appended claims.
Claims (6)
1. A waste energy recovery system, comprising a furnace, at least one cooling water filter, at least one dry purifier and an exhaust fan, wherein:
said furnace, said at least one cooling water filter, said at least one dry purifier and said exhaust fan are connected in series by closed conduits; said exhaust fan is disposed near a rear end of the waste energy recovery system; said furnace comprises a waste inlet located in a top side thereof for enabling the user to put wastes into the inside of said furnace, an unidirectional airtight cover covered said waste inlet, an ash outlet located in an opposing bottom side thereof for discharge of burnt charcoal and carbonized wastes, an unidirectional airtight cover covered said ash outlet, and at least one air inlet located in the periphery thereof; charcoal, tree branches, wood and/or waste wood furniture are put in a bottom side inside said furnace for use as a fuel material, and assorted wastes are put through said waste inlet into the inside of said furnace, and an igniter is inserted through one said air inlet into the inside of said furnace to ignite the charcoal, and at the same time, said exhaust fan is turned on to draw air and to create a negative pressure in said furnace, said at least one cooling water filter and said at least one dry purifier so that outside air is drawn through said at least one air inlet into the inside of said furnace and thus a limited volume of oxygen is provided for the combustion of the loaded charcoal, tree branches, wood and/or waste wood furniture; subject to the functioning of said exhaust fan to draw air and the functioning of said at least one air inlet of said furnace to intake air, the burning temperature in said furnace is over 1000° C., and the loaded charcoal, tree branches, wood and/or waste wood furniture are being smoldered in said furnace due to combustion under lean oxygen, and thus, the loaded wastes in contact with this temperature field of over 1000° C. are immediately decomposed into oil, smoke and dust mixed gas, at this time, a part of the tar in the oil, smoke and dust mixed gas is removed when the oil, smoke and dust mixed gas flows over the hot carbon layer of over 1000° C., and then the temperature of the oil, smoke and dust mixed gas is lowered when the oil, smoke and dust flows through an internal raceway in said furnace into said at least one cooling water filter, and thus, the oil, smoke and dust mixed gas is cooled down to room temperature and then separated into crude tar and inflammable gas after entered said at least one cooling water filter.
2. The waste energy recovery system as claimed in claim claim 1 , wherein said at least one cooling water filter comprises a first cooling water filter and a second cooling water filter, said first cooling water filter having a cooling water circulating pipe inserted therethrough for the circulation of a cooling water so that the generated oil, smoke and dust mixed gas flows out of said furnace through one said closed conduit into said first cooling water filter to contact with the periphery of said cooling water circulating pipe for heat exchange where a major part of crude tar in the oil, smoke and dust mixed gas is cooled down to fall to a bottom side in said first cooling water filter and then to flow out of said first cooling water filter through a bottom-sided crude tar discharge pipe for collection.
3. The waste energy recovery system as claimed in claim 1 , wherein said dry purifier comprises a first dry purifier and a second dry purifier; said second cooling water filter has a cooling water pipe connected thereto for guiding external cooling water into said cooling water filter for direct contact with the oil, smoke and dust mixed gas so that the oil, smoke and dust mixed gas is secondarily cooled down, causing the rest crude tar in the oil, smoke and dust mixed gas to float on the surface of the cooling water in said second cooling water filter and then guided out of said second cooling water filter through another said crude tar discharge pipe for collection, and the rest inflammable gas flows through another said closed conduit into said first dry purifier where internal filter materials of active carbon and/or HePa filter media in said first dry purifier removes micro dust and water moisture from the inflammable gas to perform a primary drying and purification process, and then flows out of said first dry purifier through another said closed conduit into said second dry purifier where internal filter materials of active carbon and/or HePa filter media in said second dry purifier removes micro dust and water moisture from the inflammable gas to perform a secondary drying and purification process, and the purified inflammable gas is then guided by gas pipes to burner stoves for application or converted by an external liquefaction equipment into liquid inflammable gas for storage and application.
4. The waste energy recovery system as claimed in claim 3 , wherein when the active carbons in said first dry purifier have a large amount of impurities adhered thereto after a long period of application, the active carbons are removed from said second dry purifier and delivered to said furnace for heating and carbonization for repeated use.
5. The waste energy recovery system as claimed in claim 1 , wherein 3% strongly alkaline lime powder is added to the wastes been put in said furnace for combustion gasification to prevent generation of a large amount of superacidic gas mixture that is capable of causing smoke oil in gas to become viscous, plugging pipelines being connected to said furnace and corroding said furnace, and the percentage of the strongly alkaline lime powder is adjustable subject to the amount of plastics in the wastes been put in said furnace; said furnace is selected from the material group of class 310 stainless steel, acid resistant steels and firebricks for direct contact with the wastes.
6. The waste energy recovery system as claimed in claim 1 , further comprising a manifold connected between said second cooling water filter and said furnace, and openable to guide the heated cooling water from said second cooling water filter into said furnace to increase the moisture content of the wastes when the moisture content of the wastes in said furnace is low.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US14/285,832 US20150338094A1 (en) | 2014-05-23 | 2014-05-23 | Waste energy recovery system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US14/285,832 US20150338094A1 (en) | 2014-05-23 | 2014-05-23 | Waste energy recovery system |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| US20150338094A1 true US20150338094A1 (en) | 2015-11-26 |
Family
ID=54555772
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US14/285,832 Abandoned US20150338094A1 (en) | 2014-05-23 | 2014-05-23 | Waste energy recovery system |
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| Country | Link |
|---|---|
| US (1) | US20150338094A1 (en) |
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105674291A (en) * | 2016-03-21 | 2016-06-15 | 安徽未名生物环保有限公司 | Device for domestic waste treatment |
| CN105674288A (en) * | 2016-03-21 | 2016-06-15 | 安徽未名生物环保有限公司 | Device used for waste incineration |
| CN105674280A (en) * | 2016-03-21 | 2016-06-15 | 安徽未名生物环保有限公司 | Solid-liquid-gas three-state cooperative garbage pyrolysis treatment system |
| CN105782982A (en) * | 2016-03-21 | 2016-07-20 | 安徽未名生物环保有限公司 | Intelligent garbage disposal system |
| CN106090927A (en) * | 2016-07-28 | 2016-11-09 | 严志谋 | Innoxious incinerator |
| CN106322386A (en) * | 2016-09-09 | 2017-01-11 | 缪卫东 | Paint slag pyrolysis process and device thereof |
| CN107388262A (en) * | 2017-07-27 | 2017-11-24 | 重庆盎瑞悦科技有限公司 | A kind of harmlessness disposing method of comprehensive utilization of high saliferous chemical engineering sludge |
| CN109931617A (en) * | 2018-07-04 | 2019-06-25 | 华北电力大学(保定) | A kind of innoxious incineration treatment of garbage technique |
| CN109990301A (en) * | 2019-04-11 | 2019-07-09 | 宇恒(南京)环保装备科技有限公司 | A kind of method of oil pollutant negative pressure reverse combustion equipment and oil recovery |
| CN111721111A (en) * | 2020-06-30 | 2020-09-29 | 龙南县中利再生资源开发有限公司 | A kind of phosphor powder waste roaster |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4682985A (en) * | 1983-04-21 | 1987-07-28 | Rockwell International Corporation | Gasification of black liquor |
-
2014
- 2014-05-23 US US14/285,832 patent/US20150338094A1/en not_active Abandoned
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4682985A (en) * | 1983-04-21 | 1987-07-28 | Rockwell International Corporation | Gasification of black liquor |
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105674291A (en) * | 2016-03-21 | 2016-06-15 | 安徽未名生物环保有限公司 | Device for domestic waste treatment |
| CN105674288A (en) * | 2016-03-21 | 2016-06-15 | 安徽未名生物环保有限公司 | Device used for waste incineration |
| CN105674280A (en) * | 2016-03-21 | 2016-06-15 | 安徽未名生物环保有限公司 | Solid-liquid-gas three-state cooperative garbage pyrolysis treatment system |
| CN105782982A (en) * | 2016-03-21 | 2016-07-20 | 安徽未名生物环保有限公司 | Intelligent garbage disposal system |
| CN106090927A (en) * | 2016-07-28 | 2016-11-09 | 严志谋 | Innoxious incinerator |
| CN106322386A (en) * | 2016-09-09 | 2017-01-11 | 缪卫东 | Paint slag pyrolysis process and device thereof |
| CN107388262A (en) * | 2017-07-27 | 2017-11-24 | 重庆盎瑞悦科技有限公司 | A kind of harmlessness disposing method of comprehensive utilization of high saliferous chemical engineering sludge |
| CN109931617A (en) * | 2018-07-04 | 2019-06-25 | 华北电力大学(保定) | A kind of innoxious incineration treatment of garbage technique |
| CN109990301A (en) * | 2019-04-11 | 2019-07-09 | 宇恒(南京)环保装备科技有限公司 | A kind of method of oil pollutant negative pressure reverse combustion equipment and oil recovery |
| CN111721111A (en) * | 2020-06-30 | 2020-09-29 | 龙南县中利再生资源开发有限公司 | A kind of phosphor powder waste roaster |
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