WO1994029497A1 - Bipolar process for removal of sulfur dioxide from waste gases - Google Patents
Bipolar process for removal of sulfur dioxide from waste gases Download PDFInfo
- Publication number
- WO1994029497A1 WO1994029497A1 PCT/US1994/002224 US9402224W WO9429497A1 WO 1994029497 A1 WO1994029497 A1 WO 1994029497A1 US 9402224 W US9402224 W US 9402224W WO 9429497 A1 WO9429497 A1 WO 9429497A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- process according
- sulfuric acid
- column
- packing material
- gas
- Prior art date
Links
Classifications
-
- 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
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
- B01D53/507—Sulfur oxides by treating the gases with other liquids
-
- 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
- B01D53/32—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by electrical effects other than those provided for in group B01D61/00
- B01D53/326—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by electrical effects other than those provided for in group B01D61/00 in electrochemical cells
-
- C—CHEMISTRY; METALLURGY
- C25—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
- C25B—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
- C25B1/00—Electrolytic production of inorganic compounds or non-metals
- C25B1/01—Products
- C25B1/22—Inorganic acids
Definitions
- the present invention concerns an improved electrolytic process for removing sulfur dioxide (S0 2 ) from a waste gas stream and recovering the sulfur values as sulfuric acid.
- the sources of said waste gas stream include effluent vent, flue or exhaust gases from power plants, sulfuric acid plants, ore roasters, and solid waste incinerators.
- the purpose of the process is to achieve economies of operation, provide a useful byproduct, and minimize environmental pollution.
- the scrubbing zone conveniently is a scrubbing column of conventional design or modified design for passage of a stream of effluent gas therethrough.
- the scrubbing column contains packing material that provides gas-liquid contact surface for the gas stream and the aqueous acid stream. The design of the packing material is critical in order to minimize channeling and thereby achieve greater scrubbing efficiency.
- the packing material is electrically conductive, and it serves both as the gas-liquid contact surface for scrubbing and as the electrochemically active surface of the anode of the electrolytic cell.
- the cathode is located in the electrolytic cell compartment external to the scrubbing column. Electrical contact between the anode and cathode is maintained by the aqueous acid stream flowing through the scrubbing column and the connecting piping leading from the column to the electrolytic cell.
- Hydrogen gas produced at the cathode is kept isolated from the flue gases by means of the aqueous acid seal in the connecting piping.
- hydrogen gas cannot intermix with the flue gases forming potentially explosive mixtures.
- the hydrogen gas formed in the process can be recovered as a useful byproduct for such applications as the production of ammonia.
- the hydrogen can be burned as a fuel in such general uses as steam generation, or it can be used specifically to reheat the flue gases thereby providing buoyancy to the gases for better dispersibility in the atmosphere.
- the methods described for removing sulfur dioxide have serious disadvantages. When both electrodes are installed in the electrolytic cell compartment, large quantities of acid must be recycled between the electrolytic cell and the scrubbing column.
- a further object is to provide a process requiring the minimum investment and offering the lowest operating costs.
- the invention concerns a process for removing sulfur dioxide from effluent vent or flue gas by scrubbing the gas with an aqueous acid stream in a column 10 comprising a confined scrubbing zone and simultaneously subjecting this acid stream, which contains dissolved sulfur dioxide, to electrolysis.
- the confined scrubbing zone contains packing material 20a that is electrically conductive. This packing material both provides gas- liquid contact surface for scrubbing and serves as the electrochemically active surface of a bipolar electrode for the electrolysis reactions.
- the confined scrubbing zone also contains two electrical contacts which are arranged so that the packing material is spaced between the contacts and is in electrical contact with them.
- the electrical contacts 32 and 34 are shown as being located one at the top and the other at the bottom of the column packing material.
- a circulating pump 40 supplies the aqueous acid stream to the scrubbing zone in order to provide effective contact between the gas stream and the liquid phase.
- the concentration of the aqueous acid stream is maintained within set limits by means of makeup water or acid.
- Byproduct acid produced by the process is withdrawn from the system.
- the scrubbing zone consists of a column 10 whose inner walls are manufactured from an electrically conductive material.
- the walls of the column thus serve the dual purposes of confining the process streams and acting as one of the electrical contacts 36.
- the other electrical contact 38 consists of an electrically conductive cylinder that is centered along the vertical axis of the column. In this configuration, the packing material fills an annular space.
- FIGURE 1 is a diagrammatic view of the scrubber/electrolyzer in which the packing material serves as both the contact surface for scrubbing and the bipolar electrode.
- a pump is provided to circulate acid through the scrubber;
- FIGURE 2 is another embodiment in which a centrally located cylinder and the inner wall of the column serve as electrical contacts.
- Electrolysis is an effective and efficient way to convert sulfurous acid to sulfuric acid when sulfurous acid is formed by stripping sulfur dioxide from waste gases that contain relatively low concentrations of sulfur dioxide.
- the theoretical potential required for this reaction is 0.2 volts, but because of electrode polarization, the applied voltage must be increased to about 0.6 volts before significant reaction takes place.
- additional voltage is required in order to overcome the electrical resistance of the acid in the electrolysis cell.
- electrolysis of water commences to form oxygen and hydrogen. Under normal operations, the applied voltage can be adjusted to permit the electrolysis of sulfurous acid but to avoid the electrolysis of water.
- the present invention makes use of a bipolar electrode in the form of the column packing.
- Bipolar electrodes are well known in the art. Such an electrode is comprised of a bed of solid particles or bodies which forms a medium of relatively low electrical conductivity. In conventional use, a liquid electrolyte flows through the bed. At the same time a direct current is passed through the particles of the bed, forming oppositely charged sites on the surfaces. The desired electrochemical reactions take place at these charged sites.
- the bipolar cell used in the present invention differs from conventional design. Instead of passing a liquid electrolyte through the bed so that the particles are completely immersed, the flue or vent gas containing the sulfur dioxide flows through the bed. The solid particles or bodies are wetted by a film of acid which is sprayed or otherwise distributed on the particulate bed.
- Certain characteristics of the particulate bed are favorable for bipolarity. Relatively high electrical resistance at the contact points between particles in the bed is desired. Particles that have sharp edges and are loosely packed are helpful in this regard.
- the particles should be fabricated from materials with comparatively poor electrical conductivity. Thus, graphite is preferred in this application.
- Duriron a ferro silicon alloy that is well known for its corrosion resistance in acid media.
- the voltage applied across the packed bed will depend on its electrical characteristics and its geometry. Because of the multiplicity of electrically charged sites, the applied voltage will surpass that needed for a single cell, namely, 0.6 volts. The voltage actually used will depend on the design parameters mentioned above and on such operating conditions as the current required to electrolyze all of the sulfurous acid formed. In essence, a bipolar electrode is equivalent to an electrical circuit containing a multitude of conventional cells in series. An advantage of this arrangement is that the applied voltage does not need to be stepped down so far and the current is correspondingly reduced.
- the hydrogen gas released at the electrode will enter the flue gas stream.
- the concentration of hydrogen gas resulting from this source will be small.
- the hydrogen gas concentration in the exiting flue gas is limited by the level of sulfur dioxide initially present in the gas.
- the process is used to scrub flue gases generated by the burning of high sulfur coal or vent gases released from contact sulfuric acid plants, the resulting hydrogen concentration will typically be in the order of 0.2 percent. This value is substantially below the explosive limit for hydrogen in dry air, namely 18 percent.
- FIG. 1 Flue gas enters at the top of the scrubbing column 10 and flows concurrently with the acid down the column. In this manner, column loadings can be increased over the expected gas flow rates for counter-current operations.
- a circulating pump 40 supplies sufficient acid to the column 10 to wet the column packing 20a.
- Figure 2 Another preferred embodiment of the invention is shown in Figure 2.
- the inner wall 36 of the column 10 and a centrally located cylinder 38 serve as electrical contacts and replace the electrical contacts at the top and bottom of the packing.
- Byproduct sulfuric acid is removed from the system during operation of the herein described embodiments of the process.
- Make-up water or acid is supplied to the acid stream as required to maintain the acid concentration within certain limits.
- the selected concentration of the acid is a compromise between competing requirements.
- the electrical conductivities of aqueous sulfuric acid are greatest in the range of 20 weight percent to 40 weight percent. At lower and higher concentrations, the conductivities are reduced but still appreciable within the range of 5 weight percent to 93 weight percent. Balancing the need to maximize the electrical conductivity of the acid is the desire to produce byproduct acid of maximum strength. Concentrated acid has greater utility than weak acid and also is cheaper to ship on an equivalent acid basis. Because the present invention uses a bipolar electrode, acid with higher concentrations can be used in the process for scrubbing without increasing the electrical resistance excessively.
- Example 1 Engineering data were developed for a scrubber to treat the stack gases from a 500 megawatt power plant burning coal with a 2% sulfur content.
- the scrubber was based on the design disclosed in U.S. Patent 4,830,718, such that the column packing served also as the anode, and the cathode was placed in a separate compartment. Assuming a generating efficiency of 30% and a scrubbing efficiency of 95%, the size of the scrubbing column was determined to be 103 ft. high and 52 ft. in diameter. The necessary electrical current was 7.37 x 10 6 amps. Assuming in the extreme case that the column was flooded, the current density in the column was 7.94 x 10 3 amps, per cm 2 . Using 40% sulfuric acid with an electrical resistance of 1.47 ohm cm., the voltage drop equalled 1.17 x 10 4 volts per cm. This result showed the impracticality of this scrubber design for large power plants.
- Example 2 A scrubber was designed for the same power plant as in Example 1 but using the bipolar process of the present invention. In this case, 1 inch graphite saddles were used. This packing has a surface area of 79 ft 2 per ft 3 . The total surface of the packing in the column equalled 1.58 x 10 10 cm 2 . Thus, the current density was equal to the 0.47 milliamps per cm 2 of packing. Assuming that only 10% of the surface contained positively charged sites, the current density at these sites was 4.7 milliamps per cm 2 . This value compared favorably with experimental data which show a cell potential of close to 0.6 volts at this current density.
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Electrochemistry (AREA)
- Inorganic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Treating Waste Gases (AREA)
Abstract
Description
Claims
Priority Applications (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7501730A JPH09500569A (en) | 1993-06-15 | 1994-03-01 | Method for removing sulfur dioxide from exhaust gas by bipolar electrolysis |
AU65869/94A AU6586994A (en) | 1993-06-15 | 1994-03-01 | Bipolar process for removal of sulfur dioxide from waste gases |
EP94913886A EP0703995A4 (en) | 1993-06-15 | 1994-03-01 | Bipolar process for removal of sulfur dioxide from waste gases |
PL94311703A PL311703A1 (en) | 1993-06-15 | 1994-03-01 | Bipolar method of removing sulphur dioxide from flue gases |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US08/076,982 | 1993-06-15 | ||
US08/076,982 US5344529A (en) | 1991-06-17 | 1993-06-15 | Bipolar process for removal of sulfur dioxide from waste gases |
Publications (1)
Publication Number | Publication Date |
---|---|
WO1994029497A1 true WO1994029497A1 (en) | 1994-12-22 |
Family
ID=22135418
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/US1994/002224 WO1994029497A1 (en) | 1993-06-15 | 1994-03-01 | Bipolar process for removal of sulfur dioxide from waste gases |
Country Status (8)
Country | Link |
---|---|
US (1) | US5344529A (en) |
EP (1) | EP0703995A4 (en) |
JP (1) | JPH09500569A (en) |
CN (1) | CN1125469A (en) |
AU (1) | AU6586994A (en) |
CA (1) | CA2163771A1 (en) |
PL (1) | PL311703A1 (en) |
WO (1) | WO1994029497A1 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103551027A (en) * | 2013-08-31 | 2014-02-05 | 中盐金坛盐化有限责任公司 | Sulfur dioxide absorbent prepared from lime-flue gas secondary salt slurry |
CN104524942A (en) * | 2014-12-18 | 2015-04-22 | 昆明理工大学 | Method and device for liquid-phase purification of industrial sulphur dioxide waste gas in synergetic effect of electrodialysis |
Families Citing this family (19)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5512144A (en) * | 1995-03-28 | 1996-04-30 | John E. Stauffer | Pulse method for sulfur dioxide electrolysis |
US6010604A (en) * | 1998-02-04 | 2000-01-04 | Stauffer; John E. | Neural network packing |
JP2002017838A (en) * | 2000-07-12 | 2002-01-22 | Takahiko Sato | Deodorizing device and method for deodorizing treated gas including odor substance |
US6689263B1 (en) * | 2003-04-28 | 2004-02-10 | John E. Stauffer | Dimensionally stable electrodes |
US20050153203A1 (en) * | 2004-01-13 | 2005-07-14 | Stauffer John E. | Lead-zinc battery |
US20100047697A1 (en) * | 2004-01-13 | 2010-02-25 | Stauffer John E | Lead-zinc battery |
WO2007033082A2 (en) | 2005-09-12 | 2007-03-22 | Abela Pharmaceuticals, Inc. | Compositions comprising dimethyl sulfoxide (dmso) |
WO2007033180A1 (en) | 2005-09-12 | 2007-03-22 | Abela Pharmaceuticals, Inc. | Materials for facilitating administration of dimethyl sulfoxide (dmso) and related compounds |
JP5399072B2 (en) | 2005-09-12 | 2014-01-29 | アベラ ファーマスーティカルズ インコーポレイテッド | System for removing dimethyl sulfoxide (DMSO) or related compounds or odors associated therewith |
US8480797B2 (en) | 2005-09-12 | 2013-07-09 | Abela Pharmaceuticals, Inc. | Activated carbon systems for facilitating use of dimethyl sulfoxide (DMSO) by removal of same, related compounds, or associated odors |
US7550231B2 (en) * | 2006-10-12 | 2009-06-23 | Stauffer John E | Tin-zinc secondary battery |
US7604724B2 (en) * | 2007-07-03 | 2009-10-20 | Aristos Energy Inc. | Method for sour gas treatment |
BRPI0921494A2 (en) | 2008-11-03 | 2018-10-30 | Prad Reasearch And Development Ltd | method of planning a underground forming sampling operation, method of controlling a underground forming sampling operation, method of controlling a drilling operation for an underground formation, and method of sampling during the drilling operation. |
FI122606B (en) * | 2009-05-25 | 2012-04-13 | Outotec Oyj | Method for Concentration of Diluted Sulfuric Acid and Concentration Equipment for Concentration of Diluted Sulfuric Acid |
EP2493314B1 (en) | 2009-10-30 | 2020-04-08 | Abela Pharmaceuticals, Inc. | Dimethyl sulfoxide (dmso) and methylsulfonylmethane (msm) formulations to treat osteoarthritis |
US20110186441A1 (en) * | 2010-01-29 | 2011-08-04 | Conocophillips Company | Electrolytic recovery of retained carbon dioxide |
US8945368B2 (en) | 2012-01-23 | 2015-02-03 | Battelle Memorial Institute | Separation and/or sequestration apparatus and methods |
CN104722184B (en) * | 2013-12-18 | 2020-03-10 | 苏州鼎德电环保科技有限公司 | Washing tower, waste gas purification system comprising same and air purification method |
WO2016189031A1 (en) * | 2015-05-25 | 2016-12-01 | Gas2Green | Scrubber wash water electrolytic treatment |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4004994A (en) * | 1972-07-12 | 1977-01-25 | Stauffer Chemical Company | Electrochemical removal of contaminants |
US4830718A (en) * | 1985-10-21 | 1989-05-16 | John Stauffer | Removal of sulfur dioxide (SO2) from waste gases and recovery as sulfuric acid |
Family Cites Families (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
NL8601467A (en) * | 1986-06-06 | 1988-01-04 | Elten Nederland | TRANSPORT DEVICE. |
AU2226692A (en) * | 1991-06-17 | 1993-01-12 | John E. Stauffer | Improved process for removal of sulfur dioxide from waste gases |
-
1993
- 1993-06-15 US US08/076,982 patent/US5344529A/en not_active Expired - Lifetime
-
1994
- 1994-03-01 PL PL94311703A patent/PL311703A1/en unknown
- 1994-03-01 JP JP7501730A patent/JPH09500569A/en active Pending
- 1994-03-01 CN CN94192448A patent/CN1125469A/en active Pending
- 1994-03-01 CA CA002163771A patent/CA2163771A1/en not_active Abandoned
- 1994-03-01 EP EP94913886A patent/EP0703995A4/en not_active Withdrawn
- 1994-03-01 WO PCT/US1994/002224 patent/WO1994029497A1/en not_active Application Discontinuation
- 1994-03-01 AU AU65869/94A patent/AU6586994A/en not_active Abandoned
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4004994A (en) * | 1972-07-12 | 1977-01-25 | Stauffer Chemical Company | Electrochemical removal of contaminants |
US4830718A (en) * | 1985-10-21 | 1989-05-16 | John Stauffer | Removal of sulfur dioxide (SO2) from waste gases and recovery as sulfuric acid |
Non-Patent Citations (1)
Title |
---|
See also references of EP0703995A4 * |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103551027A (en) * | 2013-08-31 | 2014-02-05 | 中盐金坛盐化有限责任公司 | Sulfur dioxide absorbent prepared from lime-flue gas secondary salt slurry |
CN103551027B (en) * | 2013-08-31 | 2015-10-28 | 中盐金坛盐化有限责任公司 | With the sulphur dioxide absorbent that lime-flue gas method secondary salt slurry is raw material |
CN104524942A (en) * | 2014-12-18 | 2015-04-22 | 昆明理工大学 | Method and device for liquid-phase purification of industrial sulphur dioxide waste gas in synergetic effect of electrodialysis |
Also Published As
Publication number | Publication date |
---|---|
US5344529A (en) | 1994-09-06 |
EP0703995A4 (en) | 1996-10-23 |
AU6586994A (en) | 1995-01-03 |
CN1125469A (en) | 1996-06-26 |
CA2163771A1 (en) | 1994-12-22 |
EP0703995A1 (en) | 1996-04-03 |
PL311703A1 (en) | 1996-03-04 |
JPH09500569A (en) | 1997-01-21 |
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