EP2198200B1 - Post-combustion device, for filtering and reducing emission of particulate as well as optimizing thermal performance and method of operating such a device - Google Patents
Post-combustion device, for filtering and reducing emission of particulate as well as optimizing thermal performance and method of operating such a device Download PDFInfo
- Publication number
- EP2198200B1 EP2198200B1 EP07819054A EP07819054A EP2198200B1 EP 2198200 B1 EP2198200 B1 EP 2198200B1 EP 07819054 A EP07819054 A EP 07819054A EP 07819054 A EP07819054 A EP 07819054A EP 2198200 B1 EP2198200 B1 EP 2198200B1
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- European Patent Office
- Prior art keywords
- post
- combustion
- stage
- catalyst
- burner
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- 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.)
- Not-in-force
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- 238000002485 combustion reaction Methods 0.000 title claims abstract description 35
- 238000001914 filtration Methods 0.000 title claims abstract description 15
- 238000000034 method Methods 0.000 title claims description 5
- 239000007789 gas Substances 0.000 claims abstract description 34
- 239000002028 Biomass Substances 0.000 claims abstract description 9
- 239000002023 wood Substances 0.000 claims abstract description 9
- 239000008188 pellet Substances 0.000 claims abstract description 5
- 239000003054 catalyst Substances 0.000 claims description 24
- 239000000758 substrate Substances 0.000 claims description 14
- 238000010438 heat treatment Methods 0.000 claims description 8
- 229910052751 metal Inorganic materials 0.000 claims description 7
- 239000002184 metal Substances 0.000 claims description 7
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 6
- 239000001301 oxygen Substances 0.000 claims description 6
- 229910052760 oxygen Inorganic materials 0.000 claims description 6
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims description 6
- 238000011045 prefiltration Methods 0.000 claims description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 6
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 5
- 229910002091 carbon monoxide Inorganic materials 0.000 claims description 5
- 239000002245 particle Substances 0.000 claims description 5
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 4
- 230000001413 cellular effect Effects 0.000 claims description 4
- 238000006243 chemical reaction Methods 0.000 claims description 4
- 239000011362 coarse particle Substances 0.000 claims description 3
- 229930195733 hydrocarbon Natural products 0.000 claims description 3
- 150000002430 hydrocarbons Chemical class 0.000 claims description 3
- 239000000463 material Substances 0.000 claims description 3
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 claims description 3
- 229910000510 noble metal Inorganic materials 0.000 claims description 3
- 230000003647 oxidation Effects 0.000 claims description 3
- 238000007254 oxidation reaction Methods 0.000 claims description 3
- 229910052763 palladium Inorganic materials 0.000 claims description 3
- 229910052697 platinum Inorganic materials 0.000 claims description 3
- 230000001105 regulatory effect Effects 0.000 claims description 3
- 229910052703 rhodium Inorganic materials 0.000 claims description 3
- 239000010948 rhodium Substances 0.000 claims description 3
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims description 3
- 229910002092 carbon dioxide Inorganic materials 0.000 claims description 2
- 239000001569 carbon dioxide Substances 0.000 claims description 2
- 239000011248 coating agent Substances 0.000 claims description 2
- 238000000576 coating method Methods 0.000 claims description 2
- 238000005367 electrostatic precipitation Methods 0.000 claims description 2
- 238000002156 mixing Methods 0.000 claims description 2
- 230000003197 catalytic effect Effects 0.000 claims 2
- 239000012716 precipitator Substances 0.000 claims 2
- 238000004140 cleaning Methods 0.000 claims 1
- 230000001788 irregular Effects 0.000 claims 1
- 230000007257 malfunction Effects 0.000 claims 1
- 230000001960 triggered effect Effects 0.000 claims 1
- -1 woodchips Substances 0.000 abstract 1
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 6
- 239000000126 substance Substances 0.000 description 5
- 239000000779 smoke Substances 0.000 description 3
- 230000008901 benefit Effects 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 238000005201 scrubbing Methods 0.000 description 2
- 230000009471 action Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000000567 combustion gas Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000002708 enhancing effect Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 238000009533 lab test Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000011403 purification operation Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000012905 visible particle Substances 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
- F23G5/08—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
- F23G5/14—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion
- F23G5/16—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion in a separate combustion chamber
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/017—Combinations of electrostatic separation with other processes, not otherwise provided for
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/02—Plant or installations having external electricity supply
- B03C3/025—Combinations of electrostatic separators, e.g. in parallel or in series, stacked separators or dry-wet separator combinations
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/02—Plant or installations having external electricity supply
- B03C3/04—Plant or installations having external electricity supply dry type
- B03C3/09—Plant or installations having external electricity supply dry type characterised by presence of stationary flat electrodes arranged with their flat surfaces at right angles to the gas stream
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/02—Plant or installations having external electricity supply
- B03C3/04—Plant or installations having external electricity supply dry type
- B03C3/12—Plant or installations having external electricity supply dry type characterised by separation of ionising and collecting stations
-
- 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
- F23G7/06—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
- F23G7/07—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases in which combustion takes place in the presence of catalytic material
-
- 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
- F23G7/10—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of field or garden waste or biomasses
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
- F23J15/022—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material for removing solid particulate material from the gasflow
- F23J15/025—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material for removing solid particulate material from the gasflow using filters
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23L—SUPPLYING AIR OR NON-COMBUSTIBLE LIQUIDS OR GASES TO COMBUSTION APPARATUS IN GENERAL ; VALVES OR DAMPERS SPECIALLY ADAPTED FOR CONTROLLING AIR SUPPLY OR DRAUGHT IN COMBUSTION APPARATUS; INDUCING DRAUGHT IN COMBUSTION APPARATUS; TOPS FOR CHIMNEYS OR VENTILATING SHAFTS; TERMINALS FOR FLUES
- F23L17/00—Inducing draught; Tops for chimneys or ventilating shafts; Terminals for flues
- F23L17/005—Inducing draught; Tops for chimneys or ventilating shafts; Terminals for flues using fans
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2217/00—Intercepting solids
- F23J2217/10—Intercepting solids by filters
- F23J2217/102—Intercepting solids by filters electrostatic
Definitions
- the present finding concerns a post-combustion device, for filtering and reducing emission of particulate as well as optimizing thermal performance, to be used on biomass fuelled burners.
- the heating appliance can be equipped with a chamber with a secondary airflow or a water coil which, upon contact with the combustion exhaust gases, transfers some of the heat from the gases mentioned beforehand to the transfer fluid, thus increasing the appliance's thermal performance (for example as described respectively in the 253.010 and VI2004A000049 Italian patents).
- This patent aims at manufacturing a combustion heating appliance capable of guaranteeing both enhanced thermal performance and low pollution compared to corresponding parameters of similar products already known.
- a device to be applied downstream a burner - to be found in wood, pellet, wood chips, oil seeds and generally biomass fuelled stoves/boilers - comprising at least one mechanical pre-filter (a cyclone filter), at least one smoke ionization chamber, at least one electrostatic collection filter (made of a cellular monolithic catalyst with an impregnated metal substrate), at least one oxygen addition intake to control post-combustion, at least one post-filtration electrostatic chamber, at least one heat exchanger, at least one suction device used to create depression along the entire gases route (burner - cyclone pre-filter - ioniser - collector/catalyst - electrostatic post-filter - heat exchanger).
- a cyclone separator may be used for mechanical pre-filtration operations.
- Such cyclone separator is used to remove heavy visible particles (ash for instance which could end up settling on the catalyst substrate and thus clogging it) from the smoke generated following normal combustion.
- Such particles end up in a removable collection tray under the appliance.
- smoke is channelled into the primary ionizing section, where there is an exhaust gases ionization chamber, made of a metal sheet mesh with a 10 kV electrostatically charged catalyzing substrate, to cause particulate polarisation.
- the electrically charged gases are channelled into an electrostatic filtering collector, made of a catalyst with a previously treated and earthed metal substrate, operating as a post-burner through combustion of the CO (carbon monoxide) previously mixed with oxygen and of the particulate electrostatically collected and applied on the surface of the abovementioned substrate.
- the catalyst serves as a collector in the electrostatic scrubbing process, collecting fine dusts while converting harmful substances - both to health and environment - usually produced by biomass combustion into harmless substances. This occurs through surface chemical reactions taking place onto the heated metal substrate previously coated with noble metals (such as platinum, palladium and rhodium) which cause oxidation of carbon monoxide and other unburned hydrocarbons, converting them into carbon dioxide and water alongside the reduction of nitrogen oxides and fine dusts, commonly referred to as PM 10 , (environmentally friendly outcome).
- noble metals such as platinum, palladium and rhodium
- a secondary electrostatic filter comprising a two-stage electrostatic chamber made of metal sheet with a treated substrate, made up of an ionising section and a collection section, can be arranged downstream the catalyst.
- the electrostatic two-stage chamber mentioned beforehand collects the fine dusts (diameter below 1 ⁇ m) produced during the initial igniting stage of the burner. These fine dusts remain unburned after going through the previous post-combustion group, as this is still inefficient within that ignition period of time due to low temperatures at that stage.
- the secondary electrostatic filter is disabled and its collection surface is cleaned up under the effect of the high temperature of the gases exiting from the post-burner.
- the ideal performance of a bundle heat exchanger can be obtained only by positioning said exchanger after the particulate filtration system, thus allowing the scrubbing of fine dusts. Indeed, were said dusts still present during the thermal exchange stage, they disadvantageously would settle onto the internal walls of the exchanger, thus reducing its performance i.e. external thermal conduction.
- a suction device is fixed at the end of the exhaust gas pipe where gases have already considerably cooled down.
- Such suction device is used to create depression along the canal outlining the entire exhaust gas route, thus starting the suction operation directly from the combustion chamber of the heating appliance.
- the entire system shall be fixed downstream the combustion chamber of the heating appliance. Basically, this is due to the fact that the system should collect burnt gases while they are still flames and at temperatures not below 300-350°C, the maximum value required to neutralise polluting gas substances through the catalyst.
- the device 1 provided for by this finding operates in five stages: in the first stage, mechanical pre-filtration of coarse particulate occurs, as illustrated in the drawing at F1; ( fig. 1 ); in the second stage, oxygen regulated ionization and mixing occurs as illustrated in the drawing at F2; in the third stage, collection of fine dusts alongside conversion and post-combustion of gases occurs with electrostatic precipitation as illustrated in the drawing at F3; in the fourth stage, electrostatic post-filtration of fine particulate occurs as illustrated in the drawing at F4 and in the fifth stage, heat exchange with the external environment occurs as illustrated in the drawing at F5.
- the exhaust gases find their way from the combustion chamber "C” into the mechanical separation filter through the pipe 2.
- Said filter is made of a cyclone 3, which separates coarse particles, which in turn settle in a manually removable tray 4 beneath.
- the combustion gas exits from the upper collector 5 of the cyclone 2 then it undergoes mechanical pre-filtration and addition of oxygen coming from an external source through an intake canal 6 equipped with an automatic gate valve 6.1.
- the gas is channelled through an ionization chamber 8 supplied with a 10 kV positive electric charge, through which it is treated, charging the fine particles still present after the first mechanical filtration stage electrostatically.
- particulate collection is performed in the third stage through the action of the metal substrate of a cellular catalyst 9 earthed with negative charge.
- the substrate mentioned beforehand - treated using noble metals such as platinum, palladium and rhodium - serves to eliminate the unburned substances, cause oxidation of carbon monoxide and unburned hydrocarbons converting them into carbon monoxide and water, alongside reducing nitrogen oxide and PM 10 (environmentally friendly purpose).
- Such two-stage electrostatic chamber 10 made of the same material as the previous cellular catalyst 9, consists of a first stage 10.1 which allows ionization of particles at 7,5 and 10 kV (positive pole) not collected by the catalyst mentioned beforehand, due to low temperature or due to temperature excursions under normal operation conditions (change of temperature/speed, on/off, lack of combustion).
- the two-stage electrostatic chamber 10 also consists of a second stage 10.2 used to collect previously ionised particles, settling the rejected particles of the charged substrate at a 1/3 of the ionization voltage, on the earthed surface.
- the gases are channelled into a high exchange surface tube bundle heat exchanger 12, where heat exchange occurs with environment air/air or air/water and where gas intake occurs from the top towards the bottom while the tube bundle encloses the entire post-combustion group (8,9,10) thus allowing to recover even the heat produced by the previously mentioned post combustion group surface coating, through the circulation of air to perform the heat exchange.
- a suction motor 13 is fixed onto the heat exchanger 12 on the "S" openings. Such suction motor sucks cooled gases keeping the depression along the entire appliance at a constant level and releases said gases.
- this device performs heat exchange and combustion exhaust gas purification operations occupying little space and with maximum performance.
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- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Sustainable Development (AREA)
- Sustainable Energy (AREA)
- Life Sciences & Earth Sciences (AREA)
- Combustion & Propulsion (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Combustion Of Fluid Fuel (AREA)
- Electrostatic Separation (AREA)
- Incineration Of Waste (AREA)
Abstract
Description
- The present finding concerns a post-combustion device, for filtering and reducing emission of particulate as well as optimizing thermal performance, to be used on biomass fuelled burners.
- As it is well known, the main problem regarding the use of combustion heating appliances based on boilers equipped with biomass fuelled burners (wood, pellets, wood chips, oil seeds and other similar material), especially when used for domestic purposes - stoves, boilers and fireplaces - concerns optimising thermal performance (recovery of combustion heat) alongside ensuring least pollution possible (lowest emission of combustion products into the atmosphere).
- According to the current state of the art, there are several stove and fireplace performance enhancement methods. Some of these methods include creating airflows in the fire chamber thus enhancing combustion and consequently reducing emissions (for example as described in the V193A000161 Italian patent). Alternatively, the heating appliance can be equipped with a chamber with a secondary airflow or a water coil which, upon contact with the combustion exhaust gases, transfers some of the heat from the gases mentioned beforehand to the transfer fluid, thus increasing the appliance's thermal performance (for example as described respectively in the 253.010 and
VI2004A000049 - In the document D1
WO2007/036974 A , which is considered to represent the most relevant State of the Art, is disclosed an economizer/environmentally-friendly device; another similar device is described inDE3331545 : it describes a similar device in which the exhausted gases are treated using only an electrostatic filter. - This patent aims at manufacturing a combustion heating appliance capable of guaranteeing both enhanced thermal performance and low pollution compared to corresponding parameters of similar products already known.
- This can be achieved by means of a device to be applied downstream a burner - to be found in wood, pellet, wood chips, oil seeds and generally biomass fuelled stoves/boilers - comprising at least one mechanical pre-filter (a cyclone filter), at least one smoke ionization chamber, at least one electrostatic collection filter (made of a cellular monolithic catalyst with an impregnated metal substrate), at least one oxygen addition intake to control post-combustion, at least one post-filtration electrostatic chamber, at least one heat exchanger, at least one suction device used to create depression along the entire gases route (burner - cyclone pre-filter - ioniser - collector/catalyst - electrostatic post-filter - heat exchanger).
- Constructively, a cyclone separator may be used for mechanical pre-filtration operations. Such cyclone separator is used to remove heavy visible particles (ash for instance which could end up settling on the catalyst substrate and thus clogging it) from the smoke generated following normal combustion. Such particles end up in a removable collection tray under the appliance.
- Then, once the coarse particles are removed through the cyclone separator, smoke is channelled into the primary ionizing section, where there is an exhaust gases ionization chamber, made of a metal sheet mesh with a 10 kV electrostatically charged catalyzing substrate, to cause particulate polarisation. Next, the electrically charged gases are channelled into an electrostatic filtering collector, made of a catalyst with a previously treated and earthed metal substrate, operating as a post-burner through combustion of the CO (carbon monoxide) previously mixed with oxygen and of the particulate electrostatically collected and applied on the surface of the abovementioned substrate.
- More precisely, the catalyst serves as a collector in the electrostatic scrubbing process, collecting fine dusts while converting harmful substances - both to health and environment - usually produced by biomass combustion into harmless substances. This occurs through surface chemical reactions taking place onto the heated metal substrate previously coated with noble metals (such as platinum, palladium and rhodium) which cause oxidation of carbon monoxide and other unburned hydrocarbons, converting them into carbon dioxide and water alongside the reduction of nitrogen oxides and fine dusts, commonly referred to as PM10, (environmentally friendly outcome).
- In addition, when the gases generated by combustion pass through the catalyst mentioned beforehand, not only do they undergo a chemical conversion, but they also trigger a post-combustion process of the of the gases still unburned after the first stage, thus increasing the temperature of the gases (reaching 800°C) exiting from the catalyst mentioned beforehand considerably (heat recovery).
- Advantageously, according to the finding, a secondary electrostatic filter, comprising a two-stage electrostatic chamber made of metal sheet with a treated substrate, made up of an ionising section and a collection section, can be arranged downstream the catalyst.
- The electrostatic two-stage chamber mentioned beforehand collects the fine dusts (diameter below 1 µm) produced during the initial igniting stage of the burner. These fine dusts remain unburned after going through the previous post-combustion group, as this is still inefficient within that ignition period of time due to low temperatures at that stage. Once the post-burner reaches the temperature required for regular operation, the secondary electrostatic filter is disabled and its collection surface is cleaned up under the effect of the high temperature of the gases exiting from the post-burner.
- Then, the gases mentioned beforehand, purified and considerably hot exiting from the catalyst, pass through a heat exchanger thus recovering the greater part of the heat held in the post-burner gases. This heat exchanger is used to produce hot water or heated air for the environment.
- Exploiting the maximum thermally conductive surface, the ideal performance of a bundle heat exchanger can be obtained only by positioning said exchanger after the particulate filtration system, thus allowing the scrubbing of fine dusts. Indeed, were said dusts still present during the thermal exchange stage, they disadvantageously would settle onto the internal walls of the exchanger, thus reducing its performance i.e. external thermal conduction.
- Lastly, a suction device is fixed at the end of the exhaust gas pipe where gases have already considerably cooled down. Such suction device is used to create depression along the canal outlining the entire exhaust gas route, thus starting the suction operation directly from the combustion chamber of the heating appliance.
- The entire system shall be fixed downstream the combustion chamber of the heating appliance. Basically, this is due to the fact that the system should collect burnt gases while they are still flames and at temperatures not below 300-350°C, the maximum value required to neutralise polluting gas substances through the catalyst.
- Practically, laboratory tests have proved that upon final exit, not only are the exhaust gases free of polluting dusts (environmental benefit) but they also transfer most of their heat compared to the traditional systems (energy saving).
- This finding shall be explained in details through a description of a possible embodiment, as illustrative but not limiting examples, with the help the annexed drawings, wherein:
-
fig.1 illustrates a front elevation view of the device according to the finding; -
fig.2 illustrates a side view of the abovementioned device, partially cross-sectioned by line II-II offig.1 ; -
fig.3 illustrates an overall view of the filtering group; -
fig.4 illustrates an exploded view of the group according tofig 3 ; -
fig.5 illustrates a cross-section, according to line V-V offig 4 , under the filtering group; -
fig. 6 illustrates a cross-section, according to line VI-VI offig 3 , under the filtering group; -
fig.7 illustrates a block diagram of how the device operates according to the finding; - From the operational point of view, the
device 1 provided for by this finding operates in five stages: in the first stage, mechanical pre-filtration of coarse particulate occurs, as illustrated in the drawing at F1; (fig. 1 ); in the second stage, oxygen regulated ionization and mixing occurs as illustrated in the drawing at F2; in the third stage, collection of fine dusts alongside conversion and post-combustion of gases occurs with electrostatic precipitation as illustrated in the drawing at F3; in the fourth stage, electrostatic post-filtration of fine particulate occurs as illustrated in the drawing at F4 and in the fifth stage, heat exchange with the external environment occurs as illustrated in the drawing at F5. - As illustrated by the drawings, in the first operational stage, the exhaust gases find their way from the combustion chamber "C" into the mechanical separation filter through the
pipe 2. Said filter is made of acyclone 3, which separates coarse particles, which in turn settle in a manuallyremovable tray 4 beneath. - Subsequently, the combustion gas exits from the
upper collector 5 of thecyclone 2 then it undergoes mechanical pre-filtration and addition of oxygen coming from an external source through anintake canal 6 equipped with an automatic gate valve 6.1. - Next, in the second stage, by means of a
pipe 7, the gas is channelled through anionization chamber 8 supplied with a 10 kV positive electric charge, through which it is treated, charging the fine particles still present after the first mechanical filtration stage electrostatically. - After that, particulate collection is performed in the third stage through the action of the metal substrate of a
cellular catalyst 9 earthed with negative charge. - Through surface post-combustion of the substrate at high temperatures, the substrate mentioned beforehand - treated using noble metals such as platinum, palladium and rhodium - serves to eliminate the unburned substances, cause oxidation of carbon monoxide and unburned hydrocarbons converting them into carbon monoxide and water, alongside reducing nitrogen oxide and PM10 (environmentally friendly purpose).
- There is a two-stage
electrostatic chamber 10, directly coupled with thecatalyst 9. This chamber, completing the fourth stage, is used to collect fine dusts (diameter below 1 µm) produced during the initial igniting stage of the burner and not neutralised during the previous phase in that thecatalyst 9 has not yet reached the required temperature. - Such two-stage
electrostatic chamber 10, made of the same material as the previouscellular catalyst 9, consists of a first stage 10.1 which allows ionization of particles at 7,5 and 10 kV (positive pole) not collected by the catalyst mentioned beforehand, due to low temperature or due to temperature excursions under normal operation conditions (change of temperature/speed, on/off, lack of combustion). The two-stageelectrostatic chamber 10 also consists of a second stage 10.2 used to collect previously ionised particles, settling the rejected particles of the charged substrate at a 1/3 of the ionization voltage, on the earthed surface. - In the fifth stage, through a
pipe 11, the gases are channelled into a high exchange surface tubebundle heat exchanger 12, where heat exchange occurs with environment air/air or air/water and where gas intake occurs from the top towards the bottom while the tube bundle encloses the entire post-combustion group (8,9,10) thus allowing to recover even the heat produced by the previously mentioned post combustion group surface coating, through the circulation of air to perform the heat exchange. - A
suction motor 13, is fixed onto theheat exchanger 12 on the "S" openings. Such suction motor sucks cooled gases keeping the depression along the entire appliance at a constant level and releases said gases. - The descriptions above show the benefits achieved through the use of the device provided for by this finding. In particular, this device performs heat exchange and combustion exhaust gas purification operations occupying little space and with maximum performance.
- Obviously, the device herein described may be made according to different embodiments, depending on the dimensions and type of components used, provided that such methods comply with the following claims.
Claims (15)
- POST-COMBUSTION DEVICE USED FOR FILTERING AND REDUCING EMISSION OF HARMFUL PARTICULATE as well as OPTIMIZING THERMAL PERFORMANCE, to be used on biomass, wood, pellet, wood chips, oil seeds and other similar products fuelled burners, especially for domestic use appliance such as stoves and fireplaces,
said device (1) being characterised in that
it comprises at least one mechanical cyclone filter (3), at least one primary ionization chamber (8), at least one catalytic post-combustion precipitator or a grounded catalyst (9), at least one two-stage electrostatic filter (10), at least one heat exchanger (12) and at least one suction device (13) aimed at creating a depression along the gases route
and at releasing said gases. - DEVICE, according to claim 1 characterised in that it serves as a post-burner and in that it is positionable downstream the combustion chamber "C" of a biomass fuelled heating appliance.
- DEVICE, according to claim 2 characterised in that it serves as a filtration system for particulate generated by the combustion of biomass.
- DEVICE, in according to claim 2 characterised in that the catalyst (9) is of the metal monolithic kind, with a cellular substrate impregnated with noble metals such as platinum, palladium or rhodium, which cause oxidation of carbon monoxide and unburned hydrocarbons converting them into carbon dioxide and water.
- DEVICE, according to claim 3, characterised in that the ionization chamber (8) has a 10 kV electric charge and it is positioned before the catalyst (9).
- DEVICE, according to claim 3 characterised in that the post-combustion inside the catalyst is optimised through addition of oxygen directly from an external source through a pipe (6) equipped with a self-regulated valve (6.1).
- DEVICE, according to claim 1, characterised in that the catalyst (1), being earthed, serves as an element collector for fine dusts.
- DEVICE, according to claim 4 characterised in that the primary ionization causes settling of particulate in the catalyst substrate, even when the latter has not reached required post-combustion operation temperatures.
- DEVICE, one or more of the previous claims characterised in that the two-stage electrostatic filter (10), positioned after the catalytic post-burner (9) is of the two-stage type with double voltage (10 kV - 7.5 kV) and it consists of an ionising section (10.1) and a collection section (10.2), which prevents leakage of particles from the catalyst (9).
- DEVICE, according to claim 8 characterised in that the two-stage electrostatic filter (10) is positioned after the catalyst (9), and is made of the same material as the abovementioned catalyst, thus avoiding ongoing manual cleaning of the precipitator positioned after the ionising section (10.1) through surface combustion of the particulate deposited on the substrate, triggered by the high temperature of the gas produced by the previous post-combustion.
- DEVICE, according to one or more of the previous claims characterised in that the electrostatic filter (10) performs filtration operations withholding any dusts and gases produced due to poor post-combustion, irregular operation of the heating appliance or malfunctions during burner on/off operations.
- DEVICE, according to one or more of the previous claims characterised in that the heat exchanger (12) is a tube bundle exchanger with gas intake from the top towards the bottom thus allowing heat to spread over the entire surface of the same exchanger.
- DEVICE, according to one or more of the previous claims characterised in that the heat exchanger (12) encloses the post-burner group (8,9,10) thus allowing to recover even the heat produced by the surface coating of the same post-burner through air circulation within the same post-burner.
- METHOD OF operating a DEVICE according to one of more of the previous claims, characterised in that the device (1) provided for by this finding operates in five stages: a first stage (F1), where mechanical pre-filtration of coarse particles occurs; a second stage (F2) where oxygen regulated ionization and mixing occurs; a third stage (F3), where collection of fine dusts occurs alongside conversion and post-combustion of gases with electrostatic precipitation; a fourth stage (F4), where electrostatic post-filtration of fine particulate occurs; a fifth stage (F5) where heat exchange with the external environment occurs.
- HEATING APPLIANCE, such as a wood, pellet, wood chip, oil seeds and generally biomass fuelled stove/burner characterised in that it is equipped with the energy saving/environmentally friendly device (1) made according to one or more of claims 1 to 13.
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
PCT/EP2007/008986 WO2009049647A1 (en) | 2007-10-17 | 2007-10-17 | Post-combustion device, for filtering and reducing emission of particulate as well as optimizing thermal performance |
Publications (2)
Publication Number | Publication Date |
---|---|
EP2198200A1 EP2198200A1 (en) | 2010-06-23 |
EP2198200B1 true EP2198200B1 (en) | 2012-06-27 |
Family
ID=39365514
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP07819054A Not-in-force EP2198200B1 (en) | 2007-10-17 | 2007-10-17 | Post-combustion device, for filtering and reducing emission of particulate as well as optimizing thermal performance and method of operating such a device |
Country Status (3)
Country | Link |
---|---|
EP (1) | EP2198200B1 (en) |
CA (1) | CA2704157A1 (en) |
WO (1) | WO2009049647A1 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
AT515897B1 (en) * | 2014-04-03 | 2016-03-15 | Gilles En Und Umwelttechnik Gmbh & Co Kg | boiler |
Family Cites Families (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE3331545A1 (en) | 1983-08-13 | 1985-02-28 | Ferdinand Lentjes, Dampfkessel- und Maschinenbau, 4000 Düsseldorf | Process and plant for reducing the pollutant emission in flue gases of furnaces |
DE3601378A1 (en) * | 1986-01-18 | 1987-07-23 | Degussa | METHOD FOR PURIFYING OXIDES OF NITROGEN AND EXHAUST GASES CONTAINING SULFUR FROM COMBUSTION PLANTS |
US5233934A (en) * | 1992-08-20 | 1993-08-10 | Wahlco Environmental Systems, Inc. | Control of NOx reduction in flue gas flows |
DE102005023580A1 (en) * | 2005-05-18 | 2006-11-23 | Fev Motorentechnik Gmbh | Heat generator useful as an auxiliary heating unit for a vehicle comprises a particulate filter or oxidation catalyst mounted immediately downstream of a burner |
ITPD20050281A1 (en) | 2005-09-28 | 2007-03-29 | Nonox Ltd | METHOD AND DEVICE TO DAMAGE THE POLLUTING COMPONENTS PRESENT IN THE EXHAUST FUMES OF A COMBUSTION THERMO-GENERATOR |
-
2007
- 2007-10-17 CA CA2704157A patent/CA2704157A1/en not_active Abandoned
- 2007-10-17 EP EP07819054A patent/EP2198200B1/en not_active Not-in-force
- 2007-10-17 WO PCT/EP2007/008986 patent/WO2009049647A1/en active Application Filing
Also Published As
Publication number | Publication date |
---|---|
CA2704157A1 (en) | 2009-04-23 |
EP2198200A1 (en) | 2010-06-23 |
WO2009049647A1 (en) | 2009-04-23 |
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