WO1999025462A1 - Device for purifying a mercury-containing flue gas - Google Patents

Device for purifying a mercury-containing flue gas Download PDF

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Publication number
WO1999025462A1
WO1999025462A1 PCT/NL1998/000654 NL9800654W WO9925462A1 WO 1999025462 A1 WO1999025462 A1 WO 1999025462A1 NL 9800654 W NL9800654 W NL 9800654W WO 9925462 A1 WO9925462 A1 WO 9925462A1
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Prior art keywords
mercury
flue gas
amalgamable
filter
containing flue
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PCT/NL1998/000654
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French (fr)
Inventor
Anthonius Hendricus Maria Vermeulen
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Priority to AT98954852T priority Critical patent/ATE262972T1/en
Priority to EP98954852A priority patent/EP1032467B1/en
Priority to DE69822869T priority patent/DE69822869T2/en
Priority to JP2000520890A priority patent/JP3948903B2/en
Priority to AU11798/99A priority patent/AU1179899A/en
Priority to DK98954852T priority patent/DK1032467T3/en
Priority to US09/554,760 priority patent/US6699440B1/en
Publication of WO1999025462A1 publication Critical patent/WO1999025462A1/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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    • 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
    • F23J15/006—Layout of treatment plant
    • 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
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/46—Removing components of defined structure
    • B01D53/64—Heavy metals or compounds thereof, e.g. mercury
    • 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
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/75—Multi-step processes
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J2215/00—Preventing emissions
    • F23J2215/60—Heavy metals; Compounds thereof

Definitions

  • the invention relates to a device for purifying a mercury-containing flue gas, at least comprising dust removing means for removing dust from a flue gas, and a quantity of a regenerable amalgamable material for removing mercury from a flue gas.
  • a filter for removing mercury (Hg) from flue gas which filter comprises a housing with an inlet opening and an outlet opening for gases for purifying and a filter body.
  • the filter body consists of a large number of layers of a thin metal foil covered with a gold layer, between which layers channels are formed for guiding gases for purifying along these layers.
  • electrical heating wires or other means are provided for heating said metal foil and the gold layer deposited thereon to a temperature above 200°C in order to regenerate the filter in si tu . During regeneration of the filter air or another gas is preferably guided through said channels.
  • the known filter is particularly intended for use in combination with a cremation furnace to remove mercury originating from dental fillings.
  • the object of the invention is to provide an operationally reliable purifying device for removing mercury from flue gas , which is particularly suitable for use in combination with a cremation furnace, which can be manufactured and operated at relatively low cost and which can be regenerated in simple manner without expensive provisions being required for this purpose or normal operations having to be discontinued for a protracted period.
  • Amalgamable material is here understood to mean any material which is capable of alloying with mercury or of binding with mercury by adsorption; amalgamated state is understood to mean a state in which the material is alloyed with mercury or has bound with mercury by adsorption.
  • the quantity of amalgamable material is a quantity of amalgamable metal which is accommodated in removable manner in a filter housing which is adapted to guide a mercury-containing flue gas through this filter housing and in contact with this metal.
  • the amalgamable metal is for instance metal selected from the group comprising copper (Cu) , silver (Ag) and gold (Au) .
  • the amalgamable metal is copper (Cu) with sulphur (S) bound thereto, this being obtained for instance from a reaction of copper (Cu) with solid sulphur (S) at a temperature of about 104°C.
  • S sulphur
  • the surface of Cu available for amalgamation is enlarged, while the capacity for binding mercury is further increased by the S, which forms the compound mercury sulphide (HgS) with mercury.
  • the quantity of amalgamable material is a quantity of inorganic amalgamable material which is accommodated in removable manner in a filter housing which is adapted to guide a mercury-containing flue gas through this filter housing and in contact with this material .
  • the quantity of inorganic amalgamable material is poured for instance in powder or granule form into a container with a gas-permeable bottom which fits into a filter housing such that flue gas guided through this housing is guided via the bottom of the container through the quantity of amalgamable material, wherein mercury in the flue gas is bound by this material .
  • the inorganic amalgamable material is a mixture of titanium dioxide (Ti0 2 ) and divanadium pentoxide (V 2 0 5 ) , wherein the quantity of V 2 0 5 in the mixture lies for instance in the region of 4-7% by weight, the Ti0 2 forms a carrier for the V 2 0 5 and/or the carrier of Ti0 2 and the V 2 0 5 carried thereby is provided by particles with a nominal diameter of about 0.8 mm.
  • the quantity of amalgamable material is accommodated for instance in a laminar flow reactor (LFR) for removing mercury from a mercury-containing flue gas guided in a laminar flow through this reactor in contact with this material .
  • LFR laminar flow reactor
  • the quantity of amalgamable material in a device according to the invention is accommodated in a radial flow reactor (RFR) for removing mercury from a mercury-containing flue gas guided in a radial flow through this reactor in contact with this material .
  • RFR radial flow reactor
  • the quantity of amalgamable material is provided in a cylindrical reactor vessel between two internal cylindrical walls, and a flue gas is guided in radial direction from the outer wall through the quantity of amalgamable material to the axis of the cylindrical reactor vessel, wherein a pressure gradient is created over the quantity of amalgamable material which enhances the amalgamation process.
  • the dust removing means comprise a cyclone or an electro-filter placed in a conduit system for a mercury-containing flue gas flow upstream in the device relative to the quantity of amalgamable material.
  • a cyclone which in this respect should also be understood to mean a multi-cyclone and a rotating particle separator, or an electro-filter makes it possible to filter out dust particles from a flue gas at a relatively short distance from the relevant furnace at a temperature which is so high that the flue gas is not saturated with mercury, and all the mercury present in the gas is therefore carried along further downstream in said conduit system to the amalgamable material present in the device .
  • fig. 1 shows a diagram of an embodiment of a purifying device according to the invention in a configuration in which the device is used for selective purifying of flue gas from a cremation furnace.
  • Fig. 1 shows schematically a flue gas purifying device which is connected to the chimney 2 of a cremation furnace (not shown) which is closable with a control valve 1.
  • the flue gas purifying device is composed successively of a cyclone 3, a fine dust filter 4, the outlet opening of which is in contact with an amalgam filter 6 and an activated carbon filter 7 via a conduit 13 in which a heat exchanger 10 and a fan 5 are accommodated.
  • the figure further shows a collecting tube 12 under cyclone 3 for collecting dust, and an inlet opening 8 for cooling air closable by a control valve 9.
  • the operation of the purifying device is as follows. It is known that during a cremation mercury from dental fillings is released about 10 to 50 minutes after the beginning of the cremation process for a period lasting about 30 minutes. The release of mercury is detected in the device using a suitable mercury sensor (not shown) , whereupon control valve 1 is closed using a per se known circuit and the flue gas is guided via chimney 2 through cyclone 3, where hot dust particles are collected in dust tube 12, and the hot flue gas purified of coarse dust particles is guided by means of fan 5 via a fine dust filter 4 through a conduit 13 along a heat exchanger 10 to the amalgam filter 6.
  • the temperature of the flue gas in amalgam filter 6 is brought to about 150°C using heat exchanger 10 and optionally by drawing in cold ambient air via inlet opening 8.
  • an amalgam filter 6 in which the amalgamable material is for instance copper, silver or gold, about 90% of the quantity of mercury present in the flue gas is bound.
  • the remaining amount of mercury is absorbed in the activated carbon filter 7, which is impregnated with for instance sulphur (S) or potassium iodide (KI) .
  • S sulphur
  • KI potassium iodide
  • dioxins and furans present in the flue gas are also bound in activated carbon filter 7.
  • Fine dust filter 4 is periodically cleaned when the device is not in use by blowing compressed air therethrough in counter flow as according to the direction of arrow 11, wherein dust which has been blown loose is collected in dust tube 12 of cyclone 3.
  • the filter body of amalgam filter 6 is periodically replaced in fast and simple manner by a new or regenerated filter body.
  • the amalgam filter 6 has a modular assembly.
  • a filter body with bound mercury is heated in an oven at a temperature of about 850°C, wherein mercury is released which is carried along by a gas flow and collected in a cooler where it condenses at a temperature of about -30°C.
  • the amount of mercury captured in a filter amounts at a rough estimate to about 750 grams after 250 cremations which in normal circumstances are carried out in a crematorium in a period of six months.
  • a laminar flow reactor (LFR) of a modular type can be used, wherein an easily exchangeable filter body is filled with particles of a porous structure and a nominal diameter of about 0.8 mm, composed of titanium dioxide (Ti0 2 ) and 4-7% by weight of divanadium pentoxide (V 2 0 5 ) , wherein the Ti0 2 forms a carrier for the V 2 0 5 present in a quantity of 4-7% by weight.
  • a material is commercially available from CRI Catalyst Company U.K. Ltd., and is supplied under the name "Catalyst SO96" as catalyst for reducing nitrogen oxides (N0 X ) .
  • Catalyst SO96 as catalyst for reducing nitrogen oxides (N0 X ) .
  • the purifying device according to the invention is particularly suitable for use in combination with a cremation furnace, but that use of the device is not limited thereto.
  • the following experiments demonstrate the action of said composition V 2 0 5 /Ti0 2 ("Catalyst S096") as mercury- assimilating material.
  • Example 1 In a through-flow tube with a diameter of 1 cm mercury vapour-containing air with an Hg concentration of more than 2000 ⁇ g/m 3 was guided at a temperature of 22°C, an air pressure of 1013 mBar and a relative humidity of 50% for 0.5 hour through a sample of 5g V 2 0 5 /Ti0 2 "Catalyst S096" and subsequently via a plastic Tygon hose with dust filter to a UV mercury vapour meter, The measured Hg concentration after guiding of the air through the sample of V 2 0 5 /Ti0 2 amounted to 25 ⁇ g/m 3 , which corresponds to a mercury reduction of more than 98.75%.
  • Example 3 The experiment described under example 1 was repeated under wholly identical conditions. The measured Hg concentration after guiding of the air through the sample of V 2 0 5 /Ti0 2 amounted to 5 ⁇ g/m 3 , which corresponds to a mercury reduction of more than 99.75%.
  • Example 4
  • Comparative example 4 The experiment described under example 1 was repeated wherein the sample of V 2 0 5 /Ti0 2 was replaced by a sample of 7g silver wool with a wire thickness of 0.05 mm under otherwise identical conditions.
  • the measured Hg concentration after guiding of the air through the sample amounted to 1 ⁇ g/m 3 , which corresponds to a mercury reduction of more than 99.95%.

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • General Chemical & Material Sciences (AREA)
  • Biomedical Technology (AREA)
  • Health & Medical Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Removal Of Specific Substances (AREA)
  • Gas Separation By Absorption (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

Device for purifying a mercury-containing flue gas, at least comprising dust removing means for removing dust from a flue gas, and a quantity of a regenerable amalgamable material for removing mercury from a flue gas, which device is adapted for removal therefrom in amalgamated state of the quantity of amalgamable material for the purpose of regenerating this material, wherein the material is provided in a manner such that it can be regenerated in amalgamated state outside the device.

Description

DEVICE FOR PURIFYING A MERCURY-CONTAINING FLUE GAS
The invention relates to a device for purifying a mercury-containing flue gas, at least comprising dust removing means for removing dust from a flue gas, and a quantity of a regenerable amalgamable material for removing mercury from a flue gas.
From the international patent publication WO 92/16284 is known a filter for removing mercury (Hg) from flue gas, which filter comprises a housing with an inlet opening and an outlet opening for gases for purifying and a filter body. The filter body consists of a large number of layers of a thin metal foil covered with a gold layer, between which layers channels are formed for guiding gases for purifying along these layers. In the known filter electrical heating wires or other means are provided for heating said metal foil and the gold layer deposited thereon to a temperature above 200°C in order to regenerate the filter in si tu . During regeneration of the filter air or another gas is preferably guided through said channels. The known filter is particularly intended for use in combination with a cremation furnace to remove mercury originating from dental fillings. Due to the heating installation required for regenerating the gold foil and the cooling device inherently associated therewith which enables condensation of the mercury coming from the filter and released during regeneration, the filter is expensive to purchase and its complexity makes operation vulnerable. Replacement of the filter body requires disassembly of the electrical heating cables and the filter housing, which may necessitate a prolonged and usually unexpected and therefore undesirable interruption in operations. The object of the invention is to provide an operationally reliable purifying device for removing mercury from flue gas , which is particularly suitable for use in combination with a cremation furnace, which can be manufactured and operated at relatively low cost and which can be regenerated in simple manner without expensive provisions being required for this purpose or normal operations having to be discontinued for a protracted period.
These objectives are achieved, and other advantages obtained, with a purifying device of the type stated in the preamble, which device is adapted according to the invention for removal therefrom in amalgamated state of the quantity of amalgamable material for the purpose of regenerating this material, wherein the material is provided in a manner such that it can be regenerated in amalgamated state outside the device.
Amalgamable material is here understood to mean any material which is capable of alloying with mercury or of binding with mercury by adsorption; amalgamated state is understood to mean a state in which the material is alloyed with mercury or has bound with mercury by adsorption.
In an embodiment of a purifying device according to the invention the quantity of amalgamable material is a quantity of amalgamable metal which is accommodated in removable manner in a filter housing which is adapted to guide a mercury-containing flue gas through this filter housing and in contact with this metal. The amalgamable metal is for instance metal selected from the group comprising copper (Cu) , silver (Ag) and gold (Au) .
In an advantageous embodiment the amalgamable metal is copper (Cu) with sulphur (S) bound thereto, this being obtained for instance from a reaction of copper (Cu) with solid sulphur (S) at a temperature of about 104°C. By binding S to Cu the surface of Cu available for amalgamation is enlarged, while the capacity for binding mercury is further increased by the S, which forms the compound mercury sulphide (HgS) with mercury.
It has been found that mercury-containing copper with sulphur bound thereto can be regenerated in simple manner in a vacuum oven at a temperature of about 550°C, wherein formed HgS decomposes into Hg and S, and Hg which has been taken up into Cu with the formation of a CuHg alloy is released. In a subsequent embodiment of a purifying device according to the invention the quantity of amalgamable material is a quantity of inorganic amalgamable material which is accommodated in removable manner in a filter housing which is adapted to guide a mercury-containing flue gas through this filter housing and in contact with this material .
The quantity of inorganic amalgamable material is poured for instance in powder or granule form into a container with a gas-permeable bottom which fits into a filter housing such that flue gas guided through this housing is guided via the bottom of the container through the quantity of amalgamable material, wherein mercury in the flue gas is bound by this material .
In an advantageous embodiment of a purifying device according to the invention the inorganic amalgamable material is a mixture of titanium dioxide (Ti02) and divanadium pentoxide (V205) , wherein the quantity of V205 in the mixture lies for instance in the region of 4-7% by weight, the Ti02 forms a carrier for the V205 and/or the carrier of Ti02 and the V205 carried thereby is provided by particles with a nominal diameter of about 0.8 mm.
In a device according to the invention the quantity of amalgamable material is accommodated for instance in a laminar flow reactor (LFR) for removing mercury from a mercury-containing flue gas guided in a laminar flow through this reactor in contact with this material .
In a particularly advantageous embodiment the quantity of amalgamable material in a device according to the invention is accommodated in a radial flow reactor (RFR) for removing mercury from a mercury-containing flue gas guided in a radial flow through this reactor in contact with this material . In a radial flow reactor in a device according to the invention the quantity of amalgamable material is provided in a cylindrical reactor vessel between two internal cylindrical walls, and a flue gas is guided in radial direction from the outer wall through the quantity of amalgamable material to the axis of the cylindrical reactor vessel, wherein a pressure gradient is created over the quantity of amalgamable material which enhances the amalgamation process. In a very advantageous embodiment of a device according to the invention the dust removing means comprise a cyclone or an electro-filter placed in a conduit system for a mercury-containing flue gas flow upstream in the device relative to the quantity of amalgamable material. Use of a cyclone, which in this respect should also be understood to mean a multi-cyclone and a rotating particle separator, or an electro-filter makes it possible to filter out dust particles from a flue gas at a relatively short distance from the relevant furnace at a temperature which is so high that the flue gas is not saturated with mercury, and all the mercury present in the gas is therefore carried along further downstream in said conduit system to the amalgamable material present in the device .
The invention will be elucidated hereinbelow on the basis of an embodiment and with reference to the drawing.
In the drawing fig. 1 shows a diagram of an embodiment of a purifying device according to the invention in a configuration in which the device is used for selective purifying of flue gas from a cremation furnace. Fig. 1 shows schematically a flue gas purifying device which is connected to the chimney 2 of a cremation furnace (not shown) which is closable with a control valve 1. The flue gas purifying device is composed successively of a cyclone 3, a fine dust filter 4, the outlet opening of which is in contact with an amalgam filter 6 and an activated carbon filter 7 via a conduit 13 in which a heat exchanger 10 and a fan 5 are accommodated. The figure further shows a collecting tube 12 under cyclone 3 for collecting dust, and an inlet opening 8 for cooling air closable by a control valve 9. The operation of the purifying device is as follows. It is known that during a cremation mercury from dental fillings is released about 10 to 50 minutes after the beginning of the cremation process for a period lasting about 30 minutes. The release of mercury is detected in the device using a suitable mercury sensor (not shown) , whereupon control valve 1 is closed using a per se known circuit and the flue gas is guided via chimney 2 through cyclone 3, where hot dust particles are collected in dust tube 12, and the hot flue gas purified of coarse dust particles is guided by means of fan 5 via a fine dust filter 4 through a conduit 13 along a heat exchanger 10 to the amalgam filter 6. The temperature of the flue gas in amalgam filter 6 is brought to about 150°C using heat exchanger 10 and optionally by drawing in cold ambient air via inlet opening 8. With an amalgam filter 6 in which the amalgamable material is for instance copper, silver or gold, about 90% of the quantity of mercury present in the flue gas is bound. The remaining amount of mercury is absorbed in the activated carbon filter 7, which is impregnated with for instance sulphur (S) or potassium iodide (KI) . In addition to the mercury remnant, dioxins and furans present in the flue gas are also bound in activated carbon filter 7. Fine dust filter 4 is periodically cleaned when the device is not in use by blowing compressed air therethrough in counter flow as according to the direction of arrow 11, wherein dust which has been blown loose is collected in dust tube 12 of cyclone 3. The filter body of amalgam filter 6 is periodically replaced in fast and simple manner by a new or regenerated filter body. For this purpose the amalgam filter 6 has a modular assembly. A filter body with bound mercury is heated in an oven at a temperature of about 850°C, wherein mercury is released which is carried along by a gas flow and collected in a cooler where it condenses at a temperature of about -30°C. The amount of mercury captured in a filter amounts at a rough estimate to about 750 grams after 250 cremations which in normal circumstances are carried out in a crematorium in a period of six months.
As an alternative to an amalgam filter 6 with copper, silver or gold, a laminar flow reactor (LFR) of a modular type can be used, wherein an easily exchangeable filter body is filled with particles of a porous structure and a nominal diameter of about 0.8 mm, composed of titanium dioxide (Ti02) and 4-7% by weight of divanadium pentoxide (V205) , wherein the Ti02 forms a carrier for the V205 present in a quantity of 4-7% by weight. Such a material is commercially available from CRI Catalyst Company U.K. Ltd., and is supplied under the name "Catalyst SO96" as catalyst for reducing nitrogen oxides (N0X) . Use of this material in a device according to the invention offers the advantage that nitrogen oxides are also removed from a flue gas, which is a legal requirement in some countries for flue gas purifying installations for cremation furnaces.
It is noted that the purifying device according to the invention is particularly suitable for use in combination with a cremation furnace, but that use of the device is not limited thereto. The following experiments demonstrate the action of said composition V205/Ti02 ("Catalyst S096") as mercury- assimilating material. Example 1 In a through-flow tube with a diameter of 1 cm mercury vapour-containing air with an Hg concentration of more than 2000 μg/m3 was guided at a temperature of 22°C, an air pressure of 1013 mBar and a relative humidity of 50% for 0.5 hour through a sample of 5g V205/Ti02 "Catalyst S096" and subsequently via a plastic Tygon hose with dust filter to a UV mercury vapour meter, The measured Hg concentration after guiding of the air through the sample of V205/Ti02 amounted to 25 μg/m3, which corresponds to a mercury reduction of more than 98.75%.
Example 2
The experiment described under example 1 was repeated at a temperature of 100 °C under otherwise identical conditions. The measured Hg concentration after guiding of the air through the sample of V205/Ti02 amounted to 250 μg/m3, which corresponds to a mercury reduction of more than 87.50%.
Example 3 The experiment described under example 1 was repeated under wholly identical conditions. The measured Hg concentration after guiding of the air through the sample of V205/Ti02 amounted to 5 μg/m3 , which corresponds to a mercury reduction of more than 99.75%. Example 4
The experiment described under example 1 was repeated wherein the mercury vapour-containing air was guided through the sample for 10 hours under otherwise identical conditions. The measured Hg concentration after guiding of the air through the sample of V2Os/Ti02 amounted to 1 μg/m3, which corresponds to a mercury reduction of more than 99.95%.
Comparative example 1
The experiment described under example 1 was repeated wherein the sample of V205/Ti02 was replaced by a rod-like sample of 6g active carbon with a length of 3 mm under otherwise identical conditions. The measured Hg concentration after guiding of the air through the sample amounted to 5 μg/m3, which corresponds to a mercury reduction of more than 99.75%.
Comparative example 2
The experiment described under example 1 was repeated wherein the sample of V2Os/Ti02 was replaced by a 3 mm-long rod-like sample of 6g of active carbon which was impregnated with 5% potassium iodide (KI) under otherwise identical conditions. The Hg concentration after guiding of the air through the sample was not measurable, which corresponds with a mercury reduction of about 100%.
Comparative example 3
The experiment described under comparative example 2 was repeated wherein the mercury vapour-containing air was guided over the sample for 200 hours under otherwise identical conditions . The Hg concentration after guiding of the air through the sample was not measurable, which corresponds with a mercury reduction of about 100%.
Comparative example 4 The experiment described under example 1 was repeated wherein the sample of V205/Ti02 was replaced by a sample of 7g silver wool with a wire thickness of 0.05 mm under otherwise identical conditions. The measured Hg concentration after guiding of the air through the sample amounted to 1 μg/m3, which corresponds to a mercury reduction of more than 99.95%.
Comparative example 5
The experiment described under comparative example 4 was repeated wherein the mercury vapour-containing air was guided through the sample for 10 hours under otherwise identical conditions. The measured Hg concentration after guiding of the air through the sample amounted to 700 μg/m3, which corresponds to a mercury reduction of more than 62.50%. The results of the above described experiments are collected in table 1.
Table 1. Results mercury reduction from mercury vapour- containing air
Figure imgf000011_0001
* at a temperature of 100°C

Claims

1. Device for purifying a mercury-containing flue gas, at least comprising dust removing means for removing dust from a flue gas, and a quantity of a regenerable amalgamable material for removing mercury from a flue gas, characterized in that the device is adapted for removal therefrom in amalgamated state of the quantity of amalgamable material for the purpose of regenerating this material and the material is provided in a manner such that it can be regenerated in amalgamated state outside the device.
2. Device as claimed in claim 1, characterized in that the quantity of amalgamable material is a quantity of amalgamable metal which is accommodated in removable manner in a filter housing which is adapted to guide a mercury- containing flue gas through this filter housing and in contact with this metal .
3. Device as claimed in claim 2, characterized in that the metal is selected from the group comprising copper (Cu) , silver (Ag) and gold (Au) . . Device as claimed in claim 3 , characterized in that the metal is copper (Cu) with sulphur (S) bound thereto.
5. Device as claimed in claim 4, characterized in that the copper with sulphur bound thereto is obtained from a reaction of copper (Cu) with solid sulphur (S) at a temperature of about 104°C.
6. Device as claimed in claim 1, characterized in that the quantity of amalgamable material is a quantity of inorganic amalgamable material which is accommodated in removable manner in a filter housing which is adapted to guide a mercury-containing flue gas through this filter housing and in contact with this material.
7. Device as claimed in claim 6, characterized in that the inorganic amalgamable material is a composition of titanium dioxide (Ti02) and divanadium pentoxide (V205) .
8. Device as claimed in claim 7, characterized in that the quantity of V205 in the composition lies in the region of 4-7% by weight. 9. Device as claimed in claim 7 or 8 , characterized in that the Ti02 forms a carrier for the V205.
10. Device as claimed in claim 9, characterized in that the carrier of Ti02 and the V205 carried thereby is provided by particles with a nominal diameter of about 0.8 mm.
11. Device as claimed in any of the claims 1-10, characterized in that the quantity of amalgamable material is accommodated in a laminar flow reactor (LFR) for removing mercury from a mercury-containing flue gas which is guided in a laminar flow through this reactor in contact with this material .
12. Device as claimed in any of the claims 1-10, characterized in that the quantity of amalgamable material is accommodated in a radial flow reactor (RFR) for removing mercury from a mercury-containing flue gas guided in a radial flow through this reactor in contact with this material .
13. Device as claimed in any of the foregoing claims, characterized in that the dust removing means comprise a cyclone or an electro-filter placed in a conduit system for a mercury-containing flue gas flow upstream in the device relative to the quantity of amalgamable material.
PCT/NL1998/000654 1997-11-19 1998-11-12 Device for purifying a mercury-containing flue gas Ceased WO1999025462A1 (en)

Priority Applications (7)

Application Number Priority Date Filing Date Title
AT98954852T ATE262972T1 (en) 1997-11-19 1998-11-12 DEVICE FOR PURIFYING A GAS CONTAINING MERCURY
EP98954852A EP1032467B1 (en) 1997-11-19 1998-11-12 Device for purifying a mercury-containing flue gas
DE69822869T DE69822869T2 (en) 1997-11-19 1998-11-12 DEVICE FOR CLEANING A MERCURY-CONTAINING GAS
JP2000520890A JP3948903B2 (en) 1997-11-19 1998-11-12 Equipment for purifying flue gas containing mercury
AU11798/99A AU1179899A (en) 1997-11-19 1998-11-12 Device for purifying a mercury-containing flue gas
DK98954852T DK1032467T3 (en) 1997-11-19 1998-11-12 Device for cleaning a mercury containing flue gas
US09/554,760 US6699440B1 (en) 1997-11-19 1998-11-19 Device for purifying a mercury-containing flue gas

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
NL1007579 1997-11-19
NL1007579A NL1007579C2 (en) 1997-11-19 1997-11-19 Installation for the selective cleaning of gases from a cremation oven.

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EP1032467A1 (en) 2000-09-06
ES2217598T3 (en) 2004-11-01
US6699440B1 (en) 2004-03-02
ATE262972T1 (en) 2004-04-15
AU1179899A (en) 1999-06-07
EP1032467B1 (en) 2004-03-31
DE69822869D1 (en) 2004-05-06
JP3948903B2 (en) 2007-07-25
NL1007579C2 (en) 1999-05-20
DE69822869T2 (en) 2005-04-21
JP2001523547A (en) 2001-11-27
DK1032467T3 (en) 2004-07-12
PT1032467E (en) 2004-07-30

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