EP0779834A1 - Reaktive komposition und verfahren zur reinigung eines stickoxid-enthaltenden gases - Google Patents
Reaktive komposition und verfahren zur reinigung eines stickoxid-enthaltenden gasesInfo
- Publication number
- EP0779834A1 EP0779834A1 EP95931957A EP95931957A EP0779834A1 EP 0779834 A1 EP0779834 A1 EP 0779834A1 EP 95931957 A EP95931957 A EP 95931957A EP 95931957 A EP95931957 A EP 95931957A EP 0779834 A1 EP0779834 A1 EP 0779834A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- alkali metal
- smoke
- composition according
- nitric oxide
- composition
- 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
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B15/00—Peroxides; Peroxyhydrates; Peroxyacids or salts thereof; Superoxides; Ozonides
- C01B15/055—Peroxyhydrates; Peroxyacids or salts thereof
- C01B15/10—Peroxyhydrates; Peroxyacids or salts thereof containing carbon
- C01B15/106—Stabilisation of the solid compounds, subsequent to the preparation or to the crystallisation, by additives or by coating
-
- 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
- B01D53/54—Nitrogen compounds
- B01D53/56—Nitrogen oxides
Definitions
- the invention relates to the purification of gases contaminated with nitric oxide, in particular the purification of the fumes generated by the combustion of a fuel in the presence of air.
- the fumes generated by the combustion of gaseous, liquid or solid combustible materials are usually contaminated with nitrogen oxides from the nitrogen in atmospheric air and, where appropriate, nitrogen compounds present in the fuel.
- the major part of the nitrogen oxides is nitric oxide (NO), the balance being mainly constituted by nitrogen peroxide (NO2).
- NO2 nitrogen peroxide
- the great toxicity of nitric oxide and nitrogen peroxide and their contribution to the formation of acid rain means eliminating them from the fumes before discharging them into the atmosphere.
- a two-step process is proposed for purifying a gas containing nitric oxide.
- a gaseous mixture of oxygen and a perhydroxyl radical initiator is introduced into the gas to be purified, maintained at high temperature, so as to oxidize the nitric oxide to nitrogen peroxide;
- the gas collected from the first step is treated with lime, sodium carbonate, sodium bicarbonate or sodium sesquicarbonate, to decompose the nitrogen peroxide.
- the gaseous compound which initiates perhydroxyl radicals can be a vaporized hydrocarbon or gaseous hydrogen peroxide.
- This known method implies that two different reagents are introduced separately and successively into the gas to be treated, which complicates its implementation and requires an expensive installation. The use of a gaseous reagent further complicates the execution of the process.
- the invention aims to provide a reactive, solid composition which allows good purification of a gas contaminated with nitric oxide, while avoiding the drawbacks of the known methods described above. Consequently, the invention relates to a reactive, solid, pulverulent composition for purifying a gas containing nitric oxide from nitric oxide, said composition comprising a mixture consisting of at least one solid peroxide compound and at least one salt of alkali metal selected from alkali metal carbonates, alkali metal bicarbonates and solid solutions of alkali metal carbonate and alkali metal bicarbonate.
- the term “solid peroxide compound” means a peroxide compound which is solid and stable at room temperature.
- the peroxide compound should be solid and stable at temperatures of at least 15 ° C, preferably at least 25 ° C.
- the function of the peroxide compound is to release active oxygen into the gas.
- the peroxide compound of the composition according to the invention must therefore have a decomposition temperature which is at most equal and, preferably, lower than the normal temperature of the gas purification treatment.
- the peroxide compound is selected from those whose normal decomposition temperature is below 200 ° C, preferably below 100 ° C, peroxide compounds whose decomposition temperature is less than or equal at 60 ° C being especially advantageous.
- the peroxide compound can be an inorganic compound or an organic compound. It can for example be selected from metal peroxides and persalts derived from inorganic or organic acids. It is advantageously selected from among the alkali metal compounds.
- the alkali metal percarbonates are preferred. Sodium percarbonate is especially recommended.
- the composition according to the invention may comprise a single peroxide compound or several different peroxide compounds.
- the alkali metal salt of the composition according to the invention is selected from carbonates of alkali metals, bicarbonates of alkali metals and solid solutions of alkali metal carbonate and alkali metal bicarbonate.
- the alkali metal salt is preferably selected from the sodium salts, more specifically sodium carbonate, sodium bicarbonate, sodium sesquicarbonate and Wegscheider salt. Sodium bicarbonate and sodium sesquicarbonate are especially advantageous. Sodium bicarbonate is preferred.
- the alkali metal salt of the composition according to the invention simultaneously comprises alkali metal carbonate and alkali metal bicarbonate
- compositions according to the invention are those in which the alkali metal peroxide compound comprises a sodium peroxide compound and the alkali metal salt is selected from sodium carbonate, sodium bicarbonate and solid solutions sodium carbonate and sodium bicarbonate.
- the respective contents of peroxide compound and of alkali metal salt will depend on various parameters, in particular of the selected peroxide compound, of the selected alkali metal salt and of the composition of the gas to be purified, in particular of its relative content of nitric oxide and the possible presence of other nitrogen compounds, sulfur oxides, hydrogen chloride and oxygen. These contents must therefore be determined in each particular case by routine laboratory work.
- the composition according to the invention can thus comprise the peroxide compound in an amount by weight of 5% (preferably 20%) to 95% (preferably 80%) of the weight of the mixture consisting of the peroxide compound and the alkali metal salt. .
- the composition according to the invention contains the peroxide compound in an amount by weight of 10 to 50% (preferably 10 to 25%) of the weight of the above-mentioned mixture.
- additives in addition to the mixture of the peroxide compound and the alkali metal salt, for example stabilizers of the peroxide compound or an additive facilitating fluidization of the composition for bringing it into contact with a gas to be purified.
- the composition according to the invention is in the form of a powder.
- the peroxide compound and the alkali metal salt have similar particle size distributions, although this is not an essential condition.
- the optimum particle size of the composition according to the invention will depend on its destination, in particular on the gas to be purified, on its flow rate and on the process used to treat the gas with the composition.
- the particle size distribution of the reactive composition must respect a compromise, knowing that a fine particle size will promote the reaction with the nitrogen oxides of the gas to be purified, while a coarse particle size will promote the subsequent separation of the solid products. of the reaction. It must therefore be defined in each particular case by means of routine laboratory tests, depending on the destination of the composition.
- n ⁇ denotes the frequency (by weight) of the particles of diameter D and DQQ (respectively D $ Q and DJQ represents the diameter for which 90% (respectively 50% and 10%) of the particles of the reactive composition (expressed by weight ) have a diameter less than D ⁇ Q (respectively Dgn and DI).
- D and DQQ denotes the frequency (by weight) of the particles of diameter D and DQQ (respectively D $ Q and DJQ represents the diameter for which 90% (respectively 50% and 10%) of the particles of the reactive composition (expressed by weight ) have a diameter less than D ⁇ Q (respectively Dgn and DI).
- the reactive composition according to the invention is also suitable to purify gases contaminated with other nitrogen oxides, such as nitrous oxide (N2O), nitrogen trioxide (N2O3), nitrogen pentoxide (N2O5) and nitrogen peroxide (NO2) . Thereafter, all of the nitrogen oxides in the gas will be designated NO ⁇ .
- the composition according to the invention may also be suitable for purifying a gas contaminated with hydrogen chloride or sulfur oxides, in particular carbon dioxide. sulfur.
- the composition according to the invention thus has the advantageous property of allowing simultaneous purification of a gas in nitrogen oxides NO ⁇ , in hydrogen chloride and in sulfur oxides.
- the composition according to the invention therefore finds an advantageous application for the purification of the smoke generated by the combustion of sulfur-containing fossil fuels (such as fuel oil or coal) and for the purification of residual smoke from incineration.
- waste such as, for example, household waste, hospital care residues and plant waste.
- the reactive composition comprises carbon in the form of particles.
- the reactive composition according to this embodiment of the invention is specially adapted for the purification of smoke contaminated with mercury, dioxins or furans.
- the carbon is advantageously activated carbon and its particle size conforms to the conditions imposed above for the peroxide compound and the alkali metal salt.
- the carbon content by weight of the reactive composition is generally at least 0.5% (preferably at least 1%) of the weight of the mixture consisting of the peroxide compound and the alkali metal salt; it is generally less than 20% (preferably 15%) of the weight of this mixture.
- Specially recommended compositions comprise from 1 to 10% by weight of carbon relative to the weight of said mixture.
- the invention also relates to a process for the purification of a smoke into nitric oxide, according to which a reactive composition according to the invention is introduced into the smoke, and the smoke is then subjected to a dedusting.
- the reactive composition is introduced in the solid state into the smoke.
- the reactive composition is introduced into a stream of smoke, circulating inside a reaction chamber.
- the nitrogen oxides are destroyed by the reactive composition, forming nitrite and alkali metal nitrate.
- these compounds are broken down to form chloride or sulfate of alkali metal.
- a reactive composition which advantageously comprises carbon particles is selected. In this way, the smoke is purified into mercury, dioxins or furans, by adsorbing these contaminants on the carbon particles.
- the purpose of dust extraction is to extract the particles of nitrite and nitrate of the alkali metal and, where appropriate, the particles of chloride or sulphate of alkali metal formed and the particles of carbon impregnated with mercury and dioxins. or furans.
- the dedusting can be carried out by any suitable known means, for example by mechanical separation in a cyclone, by filtration through a filter cloth or by electrostatic separation. Filtration through a filter cloth (for example a bag filter) is the preferred mode of dust removal.
- the treatment of the smoke with the reactive composition must be carried out at an adequate temperature to allow an effective reaction of the composition with the nitric oxide of the smoke.
- the temperature must be greater than 350 K, preferably at least equal to 375 K, temperatures greater than or equal to 400 K being especially advantageous.
- the maximum admissible limit for the temperature corresponds to the melting temperatures of the compounds of the reactive composition and of the compounds of the reaction with the constituents of the smoke. In practice, it is imposed by the mechanical maintenance of industrial installations, in particular of the device for dust removal. In the case where the dedusting includes filtration through a filter cloth, it is recommended that the temperature of the smoke does not exceed about 550 K on the filter cloth.
- the reactive composition must therefore be used in an amount sufficient to convert a substantial fraction of the nitrogen oxides NO ⁇ to nitrite and alkali metal nitrate, said fraction corresponding for example to a national or international standard, imposed for the composition of industrial or domestic fumes, released into the atmosphere.
- the optimum amount of reactive composition to be used must therefore be determined in each particular case, by tests or routine calculations, according to the purification standards imposed.
- the symbols D relate to the composition smoke entering the reaction chamber and the + symbols relate to the composition of the smoke leaving the reaction chamber.
- a sodium percarbonate powder was prepared (active oxygen content: 135.7 g / kg), a sodium bicarbonate powder and a powder obtained by mixing the sodium percarbonate powder (15 % by weight) and sodium bicarbonate powder (85% by weight).
- the powders had an average diameter of 15 to 25 ⁇ m and a particle size slope of 2 to 3, as defined above.
- Example 1 (reference)
- the smoke was treated with 5 kg of sodium percarbonate powder per hour. The results of the test are shown on the diagrams of FIGS. 1 to 4. It is observed that the purification of the smoke into nitric oxide (Fig. 1) and into nitrogen oxides NO ⁇ (Fig. 2) has been little efficient and very irregular.
- Example 2 reference
- Example 1 The test of Example 1 was repeated, using, as reactive composition, 5 kg of the sodium bicarbonate powder per hour. The results of the test are shown on the diagrams of FIGS. 5 to 8. It is observed that the sodium bicarbonate had no appreciable effect on the purification of the smoke into nitric oxide (FIG. 5) , in nitrogen oxides NO ⁇ (Fig. 6) and in sulfur dioxide (Fig. 8).
- Example 3 (according to the invention)
- Example 1 The test of Example 1 was repeated, using the reactive composition according to the invention, consisting of the mixture of sodium percarbonate and sodium bicarbonate. 10 kg of the reactive composition was injected into the smoke per hour. The results of the test are shown on the diagrams of FIGS. 9 to 12. It is observed that the smoke has undergone a very efficient purification, not only in nitric oxide (FIG. 9), but also in all of the oxides of nitrogen NO ⁇ (Fig. 10). Furthermore, the purification in hydrogen chloride (Fig. 11) and in sulfur dioxide (Fig. 12) was higher than that obtained in the tests of Examples 1 and 2.
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Treating Waste Gases (AREA)
- Detergent Compositions (AREA)
- Catalysts (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
FR9410944A FR2724328B1 (fr) | 1994-09-09 | 1994-09-09 | Composition reactive et procede pour l'epuration d'un gaz contenant de l'oxyde nitrique |
FR9410944 | 1994-09-09 | ||
PCT/EP1995/003430 WO1996007468A1 (fr) | 1994-09-09 | 1995-08-31 | Composition reactive et procede pour l'epuration d'un gaz contenant de l'oxyde nitrique |
Publications (1)
Publication Number | Publication Date |
---|---|
EP0779834A1 true EP0779834A1 (de) | 1997-06-25 |
Family
ID=9466918
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP95931957A Ceased EP0779834A1 (de) | 1994-09-09 | 1995-08-31 | Reaktive komposition und verfahren zur reinigung eines stickoxid-enthaltenden gases |
Country Status (18)
Country | Link |
---|---|
US (1) | US5935539A (de) |
EP (1) | EP0779834A1 (de) |
JP (1) | JPH10508789A (de) |
KR (1) | KR970705428A (de) |
CN (1) | CN1164831A (de) |
AU (1) | AU3519895A (de) |
BR (1) | BR9509162A (de) |
CA (1) | CA2199421A1 (de) |
CZ (1) | CZ71097A3 (de) |
FI (1) | FI970937A (de) |
FR (1) | FR2724328B1 (de) |
HU (1) | HUP9800150A2 (de) |
IL (1) | IL115127A0 (de) |
NO (1) | NO971071L (de) |
NZ (1) | NZ292894A (de) |
PL (1) | PL319015A1 (de) |
SK (1) | SK29097A3 (de) |
WO (1) | WO1996007468A1 (de) |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
ZA959926B (en) * | 1995-11-03 | 1997-02-20 | Dynamotive Corp | Reduction of acid rain and ozone depletion precursors. |
BE1011344A3 (fr) | 1997-08-27 | 1999-07-06 | Solvay | Procede pour epurer une fumee et fabriquer une solution aqueuse de chlorure, de sodium. |
US7531154B2 (en) | 2005-08-18 | 2009-05-12 | Solvay Chemicals | Method of removing sulfur dioxide from a flue gas stream |
Family Cites Families (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS516884A (en) * | 1974-06-28 | 1976-01-20 | Osaka Soda Co Ltd | Nisankachitsusono kyushujokyohoho |
US4301652A (en) * | 1977-07-28 | 1981-11-24 | Kathuharu Sohda | Exhaust gas purification apparatus for motor vehicles |
JPS5718974A (en) * | 1980-07-11 | 1982-01-30 | Kowa Co | Tobacco filter |
US4783325A (en) * | 1985-05-14 | 1988-11-08 | Jones Dale G | Process and apparatus for removing oxides of nitrogen and sulfur from combustion gases |
DE3644102A1 (de) * | 1986-12-23 | 1988-07-07 | Metallgesellschaft Ag | Abgasreinigungsverfahren |
EP0301272A3 (de) * | 1987-07-29 | 1990-12-05 | Waagner-Biro Aktiengesellschaft | Verfahren und Vorrichtung zur Abgas- oder Abluftreinigung |
DE3908052B4 (de) * | 1989-03-13 | 2004-12-09 | Ftu Gmbh | Verfahren zur Behandlung von Abgasen unter Oxidation von Schadstoffen |
US5118480A (en) * | 1990-06-25 | 1992-06-02 | General Electric Environmental Services, Incorporated | Method for removing hcl and hf from coal derived fuel gas |
JP2605179B2 (ja) * | 1990-11-26 | 1997-04-30 | 社会福祉法人 北海道リハビリー | 活性炭によるSO▲下2▼,NOxの除去方法及び除去装置 |
FR2681795B1 (fr) * | 1991-09-30 | 1993-11-19 | Solvay | Procede pour epurer un gaz contenant de l'oxyde nitrique et du dioxyde de soufre. |
-
1994
- 1994-09-09 FR FR9410944A patent/FR2724328B1/fr not_active Expired - Fee Related
-
1995
- 1995-08-31 PL PL95319015A patent/PL319015A1/xx unknown
- 1995-08-31 WO PCT/EP1995/003430 patent/WO1996007468A1/fr not_active Application Discontinuation
- 1995-08-31 US US08/809,271 patent/US5935539A/en not_active Expired - Fee Related
- 1995-08-31 HU HU9800150A patent/HUP9800150A2/hu unknown
- 1995-08-31 BR BR9509162A patent/BR9509162A/pt not_active Application Discontinuation
- 1995-08-31 JP JP8509181A patent/JPH10508789A/ja active Pending
- 1995-08-31 AU AU35198/95A patent/AU3519895A/en not_active Abandoned
- 1995-08-31 CZ CZ97710A patent/CZ71097A3/cs unknown
- 1995-08-31 SK SK290-97A patent/SK29097A3/sk unknown
- 1995-08-31 KR KR1019970701513A patent/KR970705428A/ko not_active Application Discontinuation
- 1995-08-31 CA CA002199421A patent/CA2199421A1/fr not_active Abandoned
- 1995-08-31 CN CN95195956A patent/CN1164831A/zh active Pending
- 1995-08-31 EP EP95931957A patent/EP0779834A1/de not_active Ceased
- 1995-08-31 NZ NZ292894A patent/NZ292894A/en unknown
- 1995-09-01 IL IL11512795A patent/IL115127A0/xx unknown
-
1997
- 1997-03-05 FI FI970937A patent/FI970937A/fi unknown
- 1997-03-07 NO NO971071A patent/NO971071L/no unknown
Non-Patent Citations (1)
Title |
---|
See references of WO9607468A1 * |
Also Published As
Publication number | Publication date |
---|---|
AU3519895A (en) | 1996-03-27 |
MX9701736A (es) | 1997-09-30 |
KR970705428A (ko) | 1997-10-09 |
FR2724328A1 (fr) | 1996-03-15 |
CA2199421A1 (fr) | 1996-03-14 |
CZ71097A3 (en) | 1997-09-17 |
SK29097A3 (en) | 1997-09-10 |
JPH10508789A (ja) | 1998-09-02 |
IL115127A0 (en) | 1995-12-31 |
PL319015A1 (en) | 1997-07-21 |
FI970937A (fi) | 1997-05-07 |
FR2724328B1 (fr) | 1997-01-10 |
WO1996007468A1 (fr) | 1996-03-14 |
NO971071L (no) | 1997-05-07 |
CN1164831A (zh) | 1997-11-12 |
FI970937A0 (fi) | 1997-03-05 |
NZ292894A (en) | 1998-09-24 |
HUP9800150A2 (en) | 2001-06-28 |
BR9509162A (pt) | 1997-11-25 |
NO971071D0 (no) | 1997-03-07 |
US5935539A (en) | 1999-08-10 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CA2233246C (fr) | Procede de traitement de fumees a base d'oxydes de soufre | |
EP0779834A1 (de) | Reaktive komposition und verfahren zur reinigung eines stickoxid-enthaltenden gases | |
CA2233249C (fr) | Composition comprenant au moins du bicarbonate de sodium, son procede d'obtention et ses utilisations | |
EP0606268B1 (de) | Verfahren zum Reinigen von einem Stickstoffoxid- und Schwefeldioxid-enthaltenden Gas. | |
FR2751560A1 (fr) | Procede pour epurer une fumee contenant du chlorure d'hydrogene, un oxyde d'azote ou du dioxyde de soufre | |
EP0899000B1 (de) | Verfahren zur Reinigung von Müllverbrennungsabgasen und zur Herstellung einer wässrigen Salzlösung | |
WO2020169928A1 (fr) | Procédé de traitement de fumées d'unités de combustion | |
WO1997016236A1 (fr) | Procede de traitement de fumees avec du carbonate et/ou du bicarbonate de sodium humidifies | |
EP0606271B1 (de) | Verfahren zum Reinigen von einem Stickstoffoxide enthaltenden Gas | |
JP4367280B2 (ja) | 除塵装置の運転方法 | |
EP0541155B1 (de) | Verfahren zum Reinigen von Stickstoffoxid enthaltendem Gas | |
EP0190116B1 (de) | Sorptionsmasse zur Entschwefelung von Gasen | |
EP0951339B1 (de) | Zusammensetzung zur behandlung von abgasen und ihre verwendungen | |
JPH1170315A (ja) | 高温ガスの処理方法 | |
WO2003090907A1 (fr) | Procede et installation d'epuration de fumees contenant du mercure | |
EP0946265A1 (de) | Zusammensetzung zur behandlung von abgasen und deren verwendungen | |
MXPA97001736A (en) | Reactive composition and procedure for the depuration of a gas containing oxide nitr |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PUAI | Public reference made under article 153(3) epc to a published international application that has entered the european phase |
Free format text: ORIGINAL CODE: 0009012 |
|
17P | Request for examination filed |
Effective date: 19970409 |
|
AK | Designated contracting states |
Kind code of ref document: A1 Designated state(s): AT BE CH DE DK ES FR GB GR IE IT LI LU MC NL PT SE |
|
17Q | First examination report despatched |
Effective date: 19980220 |
|
GRAG | Despatch of communication of intention to grant |
Free format text: ORIGINAL CODE: EPIDOS AGRA |
|
STAA | Information on the status of an ep patent application or granted ep patent |
Free format text: STATUS: THE APPLICATION HAS BEEN REFUSED |
|
18R | Application refused |
Effective date: 19990814 |