WO1999025462A1 - Device for purifying a mercury-containing flue gas - Google Patents
Device for purifying a mercury-containing flue gas Download PDFInfo
- 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
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- mercury
- flue gas
- amalgamable
- filter
- containing flue
- 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.)
- Ceased
Links
Classifications
-
- 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%.
Landscapes
- 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
Description
Claims
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. |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO1999025462A1 true WO1999025462A1 (en) | 1999-05-27 |
Family
ID=19766036
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/NL1998/000654 Ceased WO1999025462A1 (en) | 1997-11-19 | 1998-11-12 | Device for purifying a mercury-containing flue gas |
Country Status (11)
| Country | Link |
|---|---|
| US (1) | US6699440B1 (en) |
| EP (1) | EP1032467B1 (en) |
| JP (1) | JP3948903B2 (en) |
| AT (1) | ATE262972T1 (en) |
| AU (1) | AU1179899A (en) |
| DE (1) | DE69822869T2 (en) |
| DK (1) | DK1032467T3 (en) |
| ES (1) | ES2217598T3 (en) |
| NL (1) | NL1007579C2 (en) |
| PT (1) | PT1032467E (en) |
| WO (1) | WO1999025462A1 (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109843415A (en) * | 2016-08-18 | 2019-06-04 | 太平洋绿色科技股份有限公司 | Integrated wet scrubbing system |
| EP1624963B1 (en) * | 2003-04-23 | 2019-11-27 | Midwest Energy Emissions Corporation | Method of removal of mercury and other pollutant species from flue gas streams generated during the burning of fossil fuels |
Families Citing this family (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| AU2005240594B2 (en) * | 2004-04-29 | 2009-10-01 | Solucorp Industries, Ltd. | Air pollution control |
| US7704461B2 (en) * | 2004-06-01 | 2010-04-27 | Illinois Institute Of Technology | Virtual sorbent bed systems and methods of using same |
| US8202482B2 (en) * | 2006-07-26 | 2012-06-19 | Babcock-Hitachi Kabushiki Kaisha | Apparatus for removing of trace of toxic substance from exhaust gas and method of operating the same |
| JP5094468B2 (en) * | 2007-03-01 | 2012-12-12 | 日本エンバイロケミカルズ株式会社 | Method for removing mercury vapor from gas |
| US8069703B1 (en) * | 2007-11-30 | 2011-12-06 | The United States Of America As Represented By The United States Department Of Energy | Semi-continuous detection of mercury in gases |
| JP2009240883A (en) * | 2008-03-31 | 2009-10-22 | Ihi Corp | Method and device of removing mercury |
| US8876958B2 (en) | 2011-12-15 | 2014-11-04 | Clariant Corporation | Composition and process for mercury removal |
| US9381492B2 (en) | 2011-12-15 | 2016-07-05 | Clariant Corporation | Composition and process for mercury removal |
| US10730012B2 (en) | 2014-07-25 | 2020-08-04 | Chemical and Metal Technologies LLC | Extraction of target materials using CZTS sorbent |
| US9675933B2 (en) * | 2014-07-25 | 2017-06-13 | Chemical And Metal Technologies, Llc | Emissions contaminant capture and collection device and method of use |
| US10888836B2 (en) | 2014-07-25 | 2021-01-12 | Chemical and Metal Technologies LLC | Extraction of target materials using CZTS sorbent |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1992016284A1 (en) * | 1991-03-18 | 1992-10-01 | Stiftelsen Centrum För Dentalteknik Och Biomaterial I Huddinge | Filter for the purification of gases |
| EP0629431A1 (en) * | 1993-06-18 | 1994-12-21 | Boliden Contech Ab | A method for extracting gaseous contaminants from a gas, and apparatus therefore |
Family Cites Families (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE2656803C2 (en) * | 1975-12-18 | 1986-12-18 | Institut Français du Pétrole, Rueil-Malmaison, Hauts-de-Seine | Process for removing mercury from a gas or liquid |
| DE4034498A1 (en) * | 1990-09-06 | 1992-03-12 | Metallgesellschaft Ag | METHOD FOR SEPARATING HEAVY METALS AND DIOXINES FROM COMBUSTION EXHAUST GASES |
| FR2668465B1 (en) * | 1990-10-30 | 1993-04-16 | Inst Francais Du Petrole | PROCESS FOR REMOVAL OF MERCURY OR ARSENIC IN A FLUID IN THE PRESENCE OF A MASS OF MERCURY AND / OR ARSENIC CAPTATION. |
| DE4127075A1 (en) * | 1991-08-16 | 1993-02-18 | Nymic Anstalt | METHOD FOR CLEANING LOADED EXHAUST GAS FROM COMBUSTION PLANTS |
| US5409522A (en) * | 1994-04-20 | 1995-04-25 | Ada Technologies, Inc. | Mercury removal apparatus and method |
| JP3480596B2 (en) * | 1994-05-10 | 2003-12-22 | 三井鉱山株式会社 | Dry desulfurization denitrification process |
-
1997
- 1997-11-19 NL NL1007579A patent/NL1007579C2/en not_active IP Right Cessation
-
1998
- 1998-11-12 DE DE69822869T patent/DE69822869T2/en not_active Expired - Fee Related
- 1998-11-12 JP JP2000520890A patent/JP3948903B2/en not_active Expired - Fee Related
- 1998-11-12 PT PT98954852T patent/PT1032467E/en unknown
- 1998-11-12 DK DK98954852T patent/DK1032467T3/en active
- 1998-11-12 EP EP98954852A patent/EP1032467B1/en not_active Expired - Lifetime
- 1998-11-12 WO PCT/NL1998/000654 patent/WO1999025462A1/en not_active Ceased
- 1998-11-12 ES ES98954852T patent/ES2217598T3/en not_active Expired - Lifetime
- 1998-11-12 AT AT98954852T patent/ATE262972T1/en not_active IP Right Cessation
- 1998-11-12 AU AU11798/99A patent/AU1179899A/en not_active Abandoned
- 1998-11-19 US US09/554,760 patent/US6699440B1/en not_active Expired - Fee Related
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1992016284A1 (en) * | 1991-03-18 | 1992-10-01 | Stiftelsen Centrum För Dentalteknik Och Biomaterial I Huddinge | Filter for the purification of gases |
| EP0629431A1 (en) * | 1993-06-18 | 1994-12-21 | Boliden Contech Ab | A method for extracting gaseous contaminants from a gas, and apparatus therefore |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP1624963B1 (en) * | 2003-04-23 | 2019-11-27 | Midwest Energy Emissions Corporation | Method of removal of mercury and other pollutant species from flue gas streams generated during the burning of fossil fuels |
| CN109843415A (en) * | 2016-08-18 | 2019-06-04 | 太平洋绿色科技股份有限公司 | Integrated wet scrubbing system |
Also Published As
| Publication number | Publication date |
|---|---|
| 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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