EP3664935A1 - Eisengeträgerter katalysator mit einem ca-defizienten hydroxyapatit zur abgasbehandlung - Google Patents

Eisengeträgerter katalysator mit einem ca-defizienten hydroxyapatit zur abgasbehandlung

Info

Publication number
EP3664935A1
EP3664935A1 EP18752485.5A EP18752485A EP3664935A1 EP 3664935 A1 EP3664935 A1 EP 3664935A1 EP 18752485 A EP18752485 A EP 18752485A EP 3664935 A1 EP3664935 A1 EP 3664935A1
Authority
EP
European Patent Office
Prior art keywords
catalyst
iron
calcium
gas stream
porous support
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.)
Withdrawn
Application number
EP18752485.5A
Other languages
English (en)
French (fr)
Inventor
Thierry Delplanche
Antonella Gervasini
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Solvay SA
Original Assignee
Solvay SA
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Solvay SA filed Critical Solvay SA
Publication of EP3664935A1 publication Critical patent/EP3664935A1/de
Withdrawn legal-status Critical Current

Links

Classifications

    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/30—Ion-exchange
    • 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
    • B01D53/81—Solid phase processes
    • 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
    • B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9404—Removing only nitrogen compounds
    • B01D53/9409—Nitrogen oxides
    • B01D53/9413—Processes characterised by a specific catalyst
    • B01D53/9418—Processes characterised by a specific catalyst for removing nitrogen oxides by selective catalytic reduction [SCR] using a reducing agent in a lean exhaust gas
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/02—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the alkali- or alkaline earth metals or beryllium
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00—Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/14—Phosphorus; Compounds thereof
    • B01J27/185—Phosphorus; Compounds thereof with iron group metals or platinum group metals
    • B01J27/1853—Phosphorus; Compounds thereof with iron group metals or platinum group metals with iron, cobalt or nickel
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00—Catalysts, in general, characterised by their form or physical properties
    • B01J35/60—Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61—Surface area
    • B01J35/615—100-500 m2/g
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00—Catalysts, in general, characterised by their form or physical properties
    • B01J35/60—Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/63—Pore volume
    • B01J35/633—Pore volume less than 0.5 ml/g
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00—Catalysts, in general, characterised by their form or physical properties
    • B01J35/60—Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/63—Pore volume
    • B01J35/635—0.5-1.0 ml/g
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00—Catalysts, in general, characterised by their form or physical properties
    • B01J35/60—Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/64—Pore diameter
    • B01J35/643—Pore diameter less than 2 nm
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00—Catalysts, in general, characterised by their form or physical properties
    • B01J35/60—Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/64—Pore diameter
    • B01J35/647—2-50 nm
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00—Catalysts, in general, characterised by their form or physical properties
    • B01J35/60—Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/66—Pore distribution
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2251/00—Reactants
    • B01D2251/20—Reductants
    • B01D2251/206—Ammonium compounds
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2251/00—Reactants
    • B01D2251/30—Alkali metal compounds
    • B01D2251/304—Alkali metal compounds of sodium
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2251/00—Reactants
    • B01D2251/40—Alkaline earth metal or magnesium compounds
    • B01D2251/404—Alkaline earth metal or magnesium compounds of calcium
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2251/00—Reactants
    • B01D2251/60—Inorganic bases or salts
    • B01D2251/606—Carbonates
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2255/00—Catalysts
    • B01D2255/20—Metals or compounds thereof
    • B01D2255/204—Alkaline earth metals
    • B01D2255/2045—Calcium
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2255/00—Catalysts
    • B01D2255/20—Metals or compounds thereof
    • B01D2255/207—Transition metals
    • B01D2255/20738—Iron
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2255/00—Catalysts
    • B01D2255/90—Physical characteristics of catalysts
    • B01D2255/92—Dimensions
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2255/00—Catalysts
    • B01D2255/90—Physical characteristics of catalysts
    • B01D2255/92—Dimensions
    • B01D2255/9207—Specific surface
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2257/00—Components to be removed
    • B01D2257/20—Halogens or halogen compounds
    • B01D2257/204—Inorganic halogen compounds
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2257/00—Components to be removed
    • B01D2257/30—Sulfur compounds
    • B01D2257/302—Sulfur oxides
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2257/00—Components to be removed
    • B01D2257/60—Heavy metals or heavy metal compounds

Definitions

  • the invention pertains to the field of selective catalytic reduction catalysts.
  • embodiments of the invention relate to an iron-containing supported catalyst on a support material comprising hydroxyapatite having high BET surface area and pore volume and to methods to using such catalyst in a process for waste gas purification treatment.
  • embodiments of the invention relate to a DeNOx catalyst for the removal of nitrogen oxides (NOx) from a waste gas effluent generated by a combustion process, for example from a flue gas stream originating from a stationary combustion source.
  • NOx nitrogen oxides
  • NOx nitrogen oxides
  • SOx sulfur oxides
  • SCR Selective catalytic reduction
  • SCR process is widely used for example in the U.S., Japan, and Europe to reduce emissions of large utility boilers and other commercial applications.
  • SCR processes are being used to reduce emissions in mobile applications such as in large diesel engines like those found on ships, diesel locomotives, automobiles and the like.
  • the SCR process generally provides the reduction of NOx, (NO, N 2 0 and NO 2 ) species using the reducing agent (e.g., ammonia) in the presence of oxygen and a catalyst to produce molecular nitrogen and water.
  • a reducing agent such as ammonia
  • SCR Selective catalytic reduction
  • the SCR process is a competitive reaction scheme constituted by series of parallel reactions, the kinetics of each reaction and its dependence on
  • Catalysts including various metals, transition metal oxides, and mixed metal oxides have been employed for NO reduction.
  • Initial catalysts which employed platinum or platinum group metals, were found unsatisfactory because of the need to operate in a temperature range in which explosive ammonium nitrate forms.
  • the first vanadium/titanium SCR catalyst was developed, which has proven to be highly successful. Further development has resulted in the development of vanadium catalyst deposited on titanium oxide/tungsten oxide support material.
  • Metal-promoted zeolite catalysts including, among others, iron-promoted and iron-promoted zeolite catalysts, for the selective catalytic reduction of nitrogen oxides with ammonia are known.
  • Zeolites are aluminosilicate crystalline materials having rather uniform pore sizes which, depending upon the type of zeolite and the type and amount of cations included in the zeolite lattice, range from about 3 to 10 Angstroms in diameter.
  • Iron-promoted zeolite beta (US 4961917) has been an effective commercial catalyst for the selective reduction of nitrogen oxides with ammonia.
  • the catalysts employed in the SCR process ideally should be able to retain good catalytic activity over the wide range of temperature conditions of use, for example, from 200 °C to 600 °C or higher, preferably under hydrothermal conditions since water is generated during NOx reduction (see reactions (I) and (II) above). Hydrothermal conditions are also encountered in practice, such as during the regeneration of a soot filter, a component of the exhaust gas treatment system used for the removal of particles.
  • An embodiment of the present invention relates to a catalyst composition for catalytic reduction of NO x compounds, comprising an active catalyst component deposited on a porous support;
  • said active catalyst component comprises iron
  • porous support comprises at least 60 wt % of a calcium- deficient hydroxyapatite having a calcium to phosphate molar ratio (Ca/P) of less than 1.67, preferably more than 1.5 and less than 1.67;
  • porous support having a specific BET surface area of at least 110 m 2 /g and a pore volume of at least 0.5 cm 3 /g both measured after heat treatment at 200°C.
  • the porous support in the catalyst composition may further comprise calcium carbonate in an amount of less than 20 wt%, preferably from 1 wt% to 19 wt%, more preferably from 2 wt% to 18 wt%, even more preferably from 5 wt% to 15 wt%, yet even more preferably from 7 wt% to 13 wt%, most preferably from 8 wt% to 12 wt%.
  • the porous support in the catalyst composition may further comprise less than 1 wt% of calcium
  • dihydroxide Ca(OH) 2 preferably less than 0.5 wt% calcium dihydroxide Ca(OH) 2 , more preferably less than 0.3 wt% calcium dihydroxide Ca(OH) 2 , even more preferably less than 0.2 wt% calcium dihydroxide Ca(OH) 2 , most preferably being substantially free of calcium dihydroxide Ca(OH) 2 .
  • the porous support in the catalyst composition before deposition of the active catalyst component on its surface may further comprise water in an amount of less than 20 wt%, preferably from 1 wt% to 18 wt%, more preferably from 2 wt% to 15 wt%, even more preferably from 4 wt% to 12 wt%, yet even more preferably from 5 wt% to 11 wt% most preferably from 6 wt% to 11 wt%.
  • the porous support in the catalyst composition is substantially free of carbon, i.e., less than 0.5 wt% of carbon.
  • the porous support in the catalyst composition may comprise carbon for example in an amount of at least 0.5 wt% carbon but in an amount of less than 7 wt% carbon, preferably less than 6 wt% carbon, more preferably less than 5 wt% carbon or less than 4 wt% carbon.
  • the porous support in the catalyst composition is substantially free of bone char.
  • “Bone char” also called “bone charcoal” refers to a porous, black, granular material produced by charring animal bones. Its composition varies depending on how it is made. Bones (especially cow bones) are heated in a sealed vessel at up to 700 °C (1,292 °F); a low concentration of oxygen is maintained during heating, as oxygen content affects the quality of the bone char product, particularly its adsorption capacity. Most of the organic material in the bones is driven off by heat. Bone char generally contains 7-10% carbon.
  • the porous support in the catalyst composition may comprise a Ca/P molar ratio of 1.60 or more, preferably of 1.65 or more, preferably of 1.67 or more, more preferably of 1.68 or more.
  • the porous support in the catalyst composition may comprise a Ca/P molar ratio greater than the Ca/P molar ratio of the calcium-deficient hydroxyapatite.
  • the porous support in the catalyst composition may comprise at least 65 wt%, preferably at least 70 wt%, more preferably at least 75 wt%, yet more preferably at least 80 wt%, yet most preferably at least 85 wt%, of the calcium- deficient hydroxyapatite,
  • the porous support in the catalyst composition may have a BET specific surface area measured after heat treatment at 200°C of at least 120 m 2 /g and/or at most 160 m 2 /g. In some preferred embodiments, the porous support in the catalyst composition contains less than 1 wt% of magnesium.
  • the porous support in the catalyst composition may have a BET specific surface area measured after heat treatment at 400°C of at least 60 m 2 /g and/or at most 100 m 2 /g.
  • the porous support in the catalyst composition may have a pore volume measured after heat treatment at 200°C of at least 0.55 cm 3 /g, preferably of at least 0.55 cm 3 /g and/or at most 1.0 cm 3 /g, preferably of at most 0.95 cm 3 /g.
  • the porous support in the catalyst composition may have a pore volume measured after heat treatment at 400°C of at least 0.50 cm 3 /g, preferably of at least 0.60 cm 3 /g and/or of at most 1 cm 3 /g.
  • the active catalyst component may comprise
  • the active catalyst component may be deposited on the porous support by ion exchange or impregnation, preferably by ion exchange.
  • the active catalyst component may be deposited on the porous support using an iron precursor selected from the group consisting of iron nitrate, iron chloride, iron perchlorate, iron sulfate, iron fluorosilicate, any hydrated form thereof, and any mixture thereof.
  • the iron precursor may include Fe 3+ or Fe 2+ , preferably Fe 3+ .
  • the iron precursor is preferably selected from the group consisting of iron (III) nitrate, iron (III) chloride, iron (III) sulfate, iron (III) perchlorate, any hydrated form thereof, and any mixture thereof.
  • the solution preferably uses a solvent such as water.
  • the iron precursor is preferably selected to be soluble in that solvent.
  • the solution pH may be adjusted in order to increase the solubility of the iron precursor.
  • the catalyst may be subjected to a heat treatment using a temperature from 105°C up to 500°C, prior to being used as a catalyst.
  • the catalyst composition may have a BET specific surface area measured after being calcined at 400°C of at least 65 m 2 /g and/or at most 100 m 2 /g.
  • the catalyst composition may have a pore volume measured after being calcined at 400°C of: - at least 0.3 cm 3 /g, preferably of at least 0.41 cm 3 /g, and/or
  • Another aspect of the present invention relates to a process for treating a waste gas stream containing nitrogen oxides (NOx), said gas stream originating from a combustion process, in which an ammonia source is injected into the waste gas stream; and in which the catalyst composition according to any embodiments of the present invention is brought into contact with the waste gas stream containing ammonia at a temperature of at least 100°C and preferably at most 600°C to carry out, in the presence of 0 2 , a reduction by NH 3 of at least a portion of the NOx to N 2 and water.
  • NOx nitrogen oxides
  • the waste gas stream temperature is at least 105 °C, or at least 120 °C, or at least 150 °C, or at least 180 °C, or at least 200 °C, or at least 250 °C, or at least 300 °C; and/or at most 550 °C, or at most 500 °C, or at most 450 °C, or at most 400 °C.
  • the catalyst composition may be injected into the waste gas stream in the form of a dry powder injection or a semi-dry injection of a slurry of the catalyst to provide contact of the catalyst with the waste gas.
  • the catalyst composition may be packed into a fixed bed in order for the waste gas stream passes through the bed of the catalyst to provide contact of the catalyst with the waste gas.
  • the catalyst composition may be fluidized in a fluidized bed to provide contact of the catalyst with the waste gas.
  • the fluidization gas to maintain the catalyst particles suspended in the fluidized bed may comprise or consist of the waste gas stream to be treated.
  • Another aspect of the present invention relates to a multi-pollutant treatment process for treating a waste gas stream containing nitrogen oxides (NOx) and contaminants selected from the group consisting of heavy metals, acid gases (such as S0 2 , S0 3 , H 3 P0 4 , HC1, HI, HBr, and/or HF) HI, H 3 P0 4 , and/or heavy metals like an element selected from the group consisting of : Al, Ag, As, Ba, Be, Bi, Ce, Co, Cd, Cu, Cr, Fe, Hf, Hg, La, Li, Mg, Mn, Mo, Ni, Pb, Pd, Rb, Sb, Se, Sn, Sr, Th, Ti, U, V, Y, Zn, and Zr, and combinations thereof, said waste gas stream originating from a combustion process.
  • Such multi-pollutant treatment process may comprise:
  • alkali sorbent comprising a compound selected from the group consisting of sodium
  • bicarbonate sodium carbonate, sodium sesquicarbonate (trona), quick lime, hydrated lime, limestone, and combinations thereof, preferably selected from the group consisting of sodium bicarbonate, sodium carbonate, sodium sesquicarbonate (trona), quick lime, hydrated lime, limestone, and combinations thereof, preferably selected from the group consisting of sodium bicarbonate, sodium carbonate, sodium sesquicarbonate (trona), quick lime, hydrated lime, limestone, and combinations thereof, preferably selected from the group consisting of sodium bicarbonate, sodium carbonate, sodium
  • the catalyst comprises an active catalyst component deposited on the porous support (as described in any of the embodiments herein);
  • said active catalyst component comprises iron
  • porous support comprises at least 60 wt % of a calcium- deficient hydroxyapatite having a calcium to phosphate molar ratio (Ca/P) of less than 1.67, preferably more than 1.5 and less than 1.67.
  • Ca/P calcium to phosphate molar ratio
  • Another embodiment of the present invention relates to a blend comprising the catalyst and an alkali sorbent, wherein the alkali sorbent comprises a compound selected from the group consisting of sodium bicarbonate, sodium carbonate, sodium sesquicarbonate (trona), quick lime, hydrated lime, limestone, and combinations thereof, preferably selected from the group consisting of sodium bicarbonate, sodium carbonate, sodium sesquicarbonate (trona), and combinations thereof; more preferably selected from the group consisting of sodium bicarbonate, sodium sesquicarbonate (trona), and combinations thereof.
  • the alkali sorbent comprises a compound selected from the group consisting of sodium bicarbonate, sodium carbonate, sodium sesquicarbonate (trona), quick lime, hydrated lime, limestone, and combinations thereof, preferably selected from the group consisting of sodium bicarbonate, sodium carbonate, sodium sesquicarbonate (trona), and combinations thereof; more preferably selected from the group consisting of sodium bicarbonate, sodium sesquicarbonate (trona), and combinations thereof.
  • the blend may comprise
  • Another aspect of the present invention relates to the use of the blend in a process for treating a waste gas stream containing nitrogen oxides (NOx) and optionally other contaminants selected from the group consisting of heavy metals, acid gases (such as S0 2 , S0 3 , H 3 PO 4 , HC1, HI, HBr, and/or HF), and combinations thereof, said waste gas stream originating from a combustion process.
  • NOx nitrogen oxides
  • acid gases such as S0 2 , S0 3 , H 3 PO 4 , HC1, HI, HBr, and/or HF
  • Such treating process may comprise:
  • the alkali sorbent preferably comprises a sodium- based sorbent selected from the group consisting of sodium bicarbonate, sodium carbonate, sodium sesquicarbonate (trona), and
  • a sodium- based sorbent selected from the group consisting of sodium bicarbonate, sodium
  • sesquicarbonate sesquicarbonate
  • Sodium- based sorbents are generally more efficient at removing sulfur oxides (SOx) from a waste gas than calcium-based sorbents (such as quick lime, hydrated lime, limestone, or combinations thereof). Since sulfur oxides can interfere with the efficiency for denitrification (deNOx) activity of the catalyst, using a sodium-based .sorbent (particularly sodium bicarbonate and. or trona) with the present catalyst prov ides an advantage over the calcium-based sorbents.
  • the temperature of the waste gas stream to be treated may be:
  • the catalyst used in any embodiments referring to the treatment processes or to blend or to the use of blend in a treatment process according to the invention may have a BET specific surface area measured after being calcined at 400°C of at least 65 m 2 /g and/or at most 100 m 2 /g.
  • the catalyst used in the process or in the blend according to the invention may have a pore volume measured after being calcined at 400°C of:
  • porous support disclosed herein comprises a Ca-deficient
  • hydroxyapatite useful for the deposition of the active metallic component(s) of the catalytic composition.
  • the porous support generally comprises or at least 60 percent by weight (wt%), or at least 65 wt%, or at least 70 wt%, or at least 75 wt% percent by weight of the calcium-deficient hydroxyapatite.
  • the porous support may consist of or consist essentially of at least one calcium-deficient hydroxyapatite, as described herein.
  • the calcium-deficient hydroxyapatite is generally in the present invention in crystalline form or in vitreous form.
  • the porous support may further include one or more additional components different from the calcium-deficient hydroxyapatite.
  • the porous support is obtained or may be obtainable by the process of any items 1 to 16 of this patent application described herein below.
  • the porous support may be a material according to any items 17 to 30 of this patent application described herein below.
  • the porous support is advantageously a material according to any items 31 to 44 of this patent application described herein below.
  • the catalyst containing the active metallic component on the porous support is advantageously a material according to any items 45 to 53 of this patent application described herein below.
  • the catalyst according to any of the embodiments presented herein comprising iron is brought into contact with a waste gas stream containing nitrogen oxides (NOx) according to any items 54 to 115 of this patent application described herein below.
  • NOx nitrogen oxides
  • the porous support may be used in the form of a wet solid (D'), or a pulverulent solid (D"), preferably a pulverulent solid (D"), when the support particles are loaded with iron.
  • An advantage of the present invention is that the support used in the catalyst according to the invention, presents when in dried powder (as pulverulent solid) an improved flowability and dispersion ability in gas streams compared to previous calcium phosphate material of prior art (in particular the ones described in WO 2008/095921 from SOL V AY, using a gel step during the manufacture of the support).
  • FIG. 1 illustrates the conversion of NO and ⁇ 3 ⁇ 4 over a hydroxyapatite- based support over the range of temperature 120-450°C in a NH 3 -SCR reaction test.
  • FIG. 2 illustrates the conversion of NO and NH 3 and the percent of production of N 2 over the range of temperature in a NH 3 -SCR reaction test 120- 400°C for a hydroxyapatite-based Fe-exchanged catalyst with about 2 wt% Fe.
  • FIG. 3 illustrates the conversion of NO and NH 3 and the percent of production of N 2 over the range of temperature 120-400°C in a NH 3 -SCR reaction test for a hydroxyapatite-based Fe-exchanged catalyst with about 6 wt% Fe.
  • FIG. 4 is a schematic of a treatment process according to an embodiment of the present invention, wherein an ammonia source, an alkaline compound 2 and a particulate reactant containing apatite 3 are injected separately into a flue gas stream.
  • FIG. 5 is a schematic of a treatment process according to an embodiment of the present invention, wherein an ammonia source and a particulate catalyst 3 containing hydroxyapatite are injected together and an alkaline compound 2 is injected separately into a flue gas stream.
  • FIG. 6 is a schematic of a treatment process according to an embodiment of the present invention, wherein an ammonia source and an alkaline compound 2 are injected together and a particulate catalyst 3 containing hydroxyapatite is injected separately into a flue gas stream.
  • FIG. 7 is a schematic of a treatment process according to an embodiment of the present invention, wherein an ammonia source, an alkaline compound 2 and a particulate catalyst 3 containing hydroxyapatite are injected together into a flue gas stream.
  • FIG. 8 is a schematic of a treatment process according to an embodiment of the present invention, wherein an alkaline compound 2 and a particulate catalyst 3 containing hydroxyapatite are injected together and an ammonia source is injected separately into a flue gas stream.
  • active metal catalyst or active component refer to the active component deposited on support material that catalyzes the reduction of NOx compounds.
  • catalyst (or “catalyst composition”) is intended to have its standard meaning in the art and refers to the combination of the active metal catalyst supported on the catalyst support particles
  • “Fresh” catalyst denotes a material which has not been in contact with NOx
  • “spent” catalyst denotes a material which has already been in contact with NOx
  • trona is intended to mean a mineral containing at least 60 %, preferably at least 80 %, more preferably at least 90 %, even more preferably at least 95 % by weight of sodium sesquicarbonate (NaHCO 3 .Na 2 CO 3 .2H 2 O).
  • the remainder of the mineral generally consists of clays, or carbonate of calcium or magnesium.
  • upstream refers to a position situated in the opposite direction from that in which the gas stream to be treated flows.
  • downstream refers to a position situated in the same direction from that in which the gas stream to be treated flows.
  • % by weight As used herein, the terms “% by weight”, “wt%”, “wt. %”, “weight percentage”, or “percentage by weight” are used interchangeably.
  • a range of values for a variable defined by a bottom limit, or a top limit, or by a bottom limit and a top limit, also comprises the embodiments in which the variable is chosen, respectively, within the value range : excluding the bottom limit, or excluding the top limit, or excluding the bottom limit and the top limit.
  • the description of several successive ranges of values for the same variable also comprises the description of embodiments where the variable is chosen in any other intermediate range included in the successive ranges.
  • the present description also describes the embodiment where : “the magnitude X is at least 11", or also the embodiment where : “the magnitude X is at least 13.74", etc.; 11 or 13.74 being values included between 10 and 15.
  • a mineral denotes one mineral or more than one mineral.
  • porous support may be referred to as the "calcium phosphate porous support”; these terms can be used
  • the porous support used in the catalyst of the present invention preferably consists of particles.
  • the mean diameter D50 of the porous support is greater than 10 ⁇ , in general greater than 20 ⁇ , or even greater than 50 ⁇ .
  • this mean diameter of the porous support is in general preferably less than 200 ⁇ , or even less than 150 ⁇ . This makes it possible to limit the stirring powers to prevent the particles of the porous support from needing high velocities of waste gases to be treated at the injection points of the catalyst for the treatment of the waste gases.
  • the mean diameter of the porous support may be at least 150 ⁇ , or at least 200 ⁇ , or at least 250 ⁇ , and/or up to 1,500 ⁇ , or up to 1,000 ⁇ , or up to 750 ⁇ , or up to 600 ⁇ , or up to 500 ⁇ .
  • This mean diameter would allow for the resulting particles supported on the porous support to be used in a flow-through system, for example where the waste gas to be treated is passed through a bed of catalyst particles.
  • the porous support may have a particularly high BET specific surface area (at least 110 mVg) measured after treatment of the porous support at 120°C.
  • the porous support may have a particularly high pore volume (at least 0.41 cm 3 /g) measured after heat treatment of the porous support at 120°C.
  • the porous support may have a high adsorption capacity of metals, in particular of iron.
  • the porous support has a BET specific surface area measured after heat treatment at 200°C of at least 120 m 2 /g and/or at most 160 m 2 /g.
  • the porous support has a BET specific surface area measured after heat treatment at 600°C of at least 20 m 2 /g and/or at most 40 m 2 /g.
  • the porous support has a pore volume measured after heat treatment at 200°C of at least 0.55 cm 3 /g, preferably of at least 0.55 cm 3 /g and/or at most 1.0 cm 3 /g, preferably of at most 0.95 cm 3 /g.
  • the porous support has a pore volume measured after heat treatment at 600°C of at least 0.42 cm 3 /g, preferably of at least 0.44 cm 3 /g and/or at most 0.8 cm 3 /g, preferably of at most 0.75 cm 3 /g.
  • a synthetic hydroxyapatite made using an aqueous medium had a BET about 35 m 2 /g and a pore volume of 0.4 cm 3 /g, while another synthetic hydroxyapatite made using an ethanol- water medium had a BET about 72 m 2 /g and a pore volume of 0.34 cm 3 /g.
  • the porous support should comprise at least 60 wt % of a calcium- deficient hydroxyapatite having a calcium to phosphate molar ratio (Ca/P) of less than 1.67.
  • the calcium-deficient hydroxyapatite has a calcium to phosphate molar ratio (Ca/P) of more than 1.5 and less than 1.67.
  • the porous support comprises at least 65 wt%, preferably at least 70 wt%, more preferably at least 75 wt%, yet more preferably at least 80 wt%, yet most preferably at least 85 wt%, of the calcium-deficient hydroxyapatite.
  • the porous support comprises at most 99 wt%, preferably at most 98 wt%, more preferably at most 97 wt%, yet more preferably at most 95 wt%, even more preferably at most 93 wt%, most preferably at most 91 wt% of the calcium-deficient hydroxyapatite.
  • the porous support may comprise a Ca/P molar ratio of 1.60 or more, preferably more than 1.62, more preferably more than 1.65.
  • the porous support may comprise a Ca/P molar ratio of 1.60 or more, preferably of 1.62 or more, more preferably of 1.65 or more, even more preferably of 1.67 or more, most preferably of 1.68 or more.
  • the porous support particles are preferably composed of calcium phosphate, the structure of which is intermediate between tricalcium phosphate and calcium phosphate hydroxyapatite. These particles then evolve very rapidly towards an apatite structure.
  • the porous support particles preferably contain a calcium-deficient hydroxyapatite structure having a calcium to phosphate molar ratio (Ca/P) of less than 1.67. It is preferred that the calcium-deficient hydroxyapatite has a calcium to phosphate molar ratio (Ca/P) of more than 1.5 and less than 1.67.
  • Such porous support particles are composed on their surface of plate-like crystallites, of thickness of a few nano-meters (nm).
  • Particles of calcium phosphate porous support may be covered with platelike crystallites, having a thickness of at most 25 nm, preferably of at most 20 nm, more preferably of at most 10 nm.
  • the thickness of plate-like crystallites may be at least 1 nm, preferably at least 2 nm, more preferably at least 4 nm.
  • the porous support used in the present invention may further have a remarkably low solubility of the phosphates contained in the porous support particles.
  • the particles of the calcium phosphate porous support used in the catalyst of the present invention in general comprise at least 60 wt% calcium phosphate and advantageously still at least 65 wt% calcium phosphate.
  • the particles of the calcium phosphate porous support may further comprise : water, of the order of from 0 to 20 wt%, advantageously from 3 % to 20 wt%, more advantageously from 5 wt% to 20 wt%; calcium carbonate from 0 to 20 wt%, advantageously from 1 wt% to 25 wt% , more advantageously from
  • the particles of the calcium phosphate porous support may further comprises calcium carbonate in an amount of less than 20 wt%, preferably from 1 wt% to 19 wt%, more preferably from 2 wt% to 18 wt%, even preferably from 5 wt% to 15 wt%, yet even more preferably from 7 wt% to
  • the particles of the calcium phosphate porous support may further comprise : water, of the order of from 0 to 20 wt%, advantageously from 3 % to 20 wt%, more advantageously from 5 wt% to 20 wt%; calcium carbonate from 0 to 20 wt%, advantageously from 1 wt% to 25 wt% , more advantageously from
  • the particles of the calcium phosphate porous support may further comprise calcium dihydroxide from 0 to 20 %, advantageously from 0 % to 4 %, or more advantageously from 0 to 1 wt%.
  • the porous support may comprise less than 1 wt% of calcium dihydroxide Ca(OH) 2 , preferably less than 0.5 wt% calcium dihydroxide, more preferably less than 0.3 wt% calcium dihydroxide, even more preferably less than 0.2 wt% calcium dihydroxide.
  • the porous support is substantially free of calcium dihydroxide (i.e., less tha 0.1 wt% Ca(OH) 2 ).
  • the porous support may comprise at least 2 wt%, preferably at least 2.5 wt% or at least 3 wt%, more preferably at least 5 wt%, and yet more preferably at least 6 wt% of hydroxide ions.
  • the porous support may comprise from 2 wt% to 6 wt% of hydroxide ions, preferably from 2.5 wt% to 5 wt% of hydroxide ions.
  • the particles of calcium phosphate porous support may additionally contain residual compounds originating from the use of the raw materials in the method of making it, such as : CaCl 2 , Ca(N03) 2 , sands or clays; these constituents are in general less than 5 wt%, advantageously less than 2 wt%.
  • the calcium phosphate porous support may contain iron in its structure
  • the calcium phosphate porous support on which iron is deposited is preferably substantially free of iron, that is to say, the iron content of the calcium phosphate porous support should be less than 0.5 wt%, preferably less than 0.3 wt%, more preferably less than 0.1 wt%.
  • Any iron present in the calcium phosphate porous support structure generally originates from one or more raw materials from which the support is made.
  • apatite denotes a family of mineral compounds, the chemical formula of which can be written in the following general form :
  • Me generally represents a divalent cation (Me 2+ ), X0 4 a trivalent anionic group (X0 4 3 ⁇ ) and Y a monovalent anion (Y ).
  • Calcium phosphate hydroxyapatite Caio (P0 4 )6(OH) 2 crystallizes in the space group of the hexagonal system.
  • This structure consists of a close-packed quasi- hexagonal stack of X0 4 groups, forming two types of parallel tunnels.
  • Hydroxyapatite should not be confused with tricalcium phosphate (TCP), which has a similar weight composition : Ca 3 (P0 4 ) 2 .
  • the Ca/P molar ratio of TCP is 1.5 whereas the Ca/P molar ratio is 1.67 for hydroxyapatite.
  • Industrial apatites sold as food additives or mineral fillers are, as a general rule, variable mixtures of TCP and hydroxyapatite.
  • the present hydroxyapatite in the porous support is deficient in calcium compared to a hydroxyapatite with a Ca/P molar ratio of 1.67.
  • the Ca/P molar ratio of the calcium-deficient hydroxyapatite is preferably more than 1.5 and less than 1.67.
  • Calcium may be and is preferably present in another form (other than the calcium-deficient hydroxyapatite) in the porous support.
  • Calcium carbonate is generally present in the porous support.
  • the weight ratio of the calcium-deficient hydroxyapatite to calcium carbonate is generally equal to or greater than 3, preferably equal to or greater than 4, more preferably equal to or greater than 5, yet more preferably greater than 7, most preferably equal to or greater than 9.
  • the porous support generally has a higher Ca/P molar ratio than the calcium-deficient hydroxyapatite present in the porous support. For that reason, even though the calcium-deficient hydroxyapatite in the porous support may have a Ca/P molar ratio less than 1.67, the entire porous support may have a Ca/P molar ratio equal to or more than 1.67. In preferred embodiments, the calcium-deficient hydroxyapatite in the porous support may have a Ca/P molar ratio of about 1.55- 1.59, while the porous support may have a Ca/P molar ratio of about 1.60-1.67.
  • hydroxyapatite do not have the same properties as hydroxyapatite or a hydroxyapatite like structure.
  • the calcium phosphate porous support is substantially free of carbon, i.e., less than 0.5 wt% of carbon.
  • the calcium phosphate porous support may comprise carbon for example in an amount of at least 0.5 wt% carbon but in an amount of less than 7 wt% carbon, preferably less than 6 wt% carbon, more preferably less than 5 wt% carbon or less than 4 wt% carbon.
  • the calcium phosphate porous support is substantially free of bone char.
  • the calcium phosphate porous support excludes bone char.
  • the process for producing the calcium phosphate porous support may comprise :
  • a source of calcium and a source of phosphate ions in water, in a molar ratio that is adjusted so as to obtain a Ca/P molar ratio of between 0.5 and 1.6, and the source of calcium is reacted with the phosphate ions at a pH of between 2 and 8, in order to obtain a suspension (A) of calcium phosphate, and
  • a suspension (A) added to the suspension (A) are an alkaline compound comprising hydroxide ions in order to set a pH of more than 8, preferably of at least 8.5, and an additional source of calcium in order to obtain a suspension (B) of calcium phosphate porous support having a Ca/P molar ratio of more than 1.6.
  • the source of calcium to make the support advantageously comprises calcium carbonate, or calcium oxide, or calcium hydroxide, or calcium chloride, or calcium nitrate, or calcium acetate.
  • the source of calcium is more advantageously a limestone, or a mixture of limestone and calcium oxide or hydroxide. More advantageously, the source of calcium is in the form of powder or aqueous suspension of powder and the powder is selected from the group consisting of: calcium carbonate, calcium oxide, calcium hydroxide, and a mixture thereof, and the powder for the source of calcium has a mean particle size of less than 300 ⁇ .
  • the source of calcium selected from the group consisting of: calcium carbonate, calcium oxide, calcium hydroxide, and mixtures thereof to be in the form of a powder or aqueous suspension of powder, and to have a small particle size.
  • the mean diameter of the particles of the powder for the calcium source is less than 300 ⁇ , advantageously less than 200 ⁇ and preferably less than 100 ⁇ .
  • the mean diameter in question is the D50, that is to say the diameter such that 50 % by weight of the particles have a diameter less than said value.
  • a dihydrogen phosphate salt such as a sodium, potassium or
  • ammonium dihydrogen phosphate salt preferably a sodium dihydrogen phosphate salt
  • phosphoric acid is preferred due to its greater availability and lower cost compared to dihydrogen and monohydrogen phosphate salts.
  • the Ca/P molar ratio is in particular :
  • the compounds formed in the suspension (A) are a mixture of monocalcium phosphate (MCP) having the weight formula Ca(H 2 P0 4 )2, of dicalcium phosphate (DCP) having the weight formula CaHP0 4 , or the hydrate thereof, brushite, having the weight formula CaHP0 4 .2H 2 0, and of octacalcium having the weight formula Ca 8 H 2 (P0 4 )6.6.5H 2 0.
  • MCP monocalcium phosphate
  • DCP dicalcium phosphate
  • brushite having the weight formula CaHP0 4 .2H 2
  • octacalcium having the weight formula Ca 8 H 2 (P0 4 )6.6.5H 2 0.
  • the Ca/P molar ratios are respectively for these compounds : 0.5 (MCP), 1.0 (DCP and brushite), 1.33 (octacalcium).
  • a Ca/P ratio of between 0.50 and 1.35, preferably between 0.7 and 1.30, is favored.
  • This Ca/P molar ratio is particularly advantageous when the source of calcium from the first step comprises calcium carbonate, and the source of phosphate is phosphoric acid (H 3 P0 4 ) or is a dihydrogen phosphate salt such as a sodium or potassium or ammonium salt. Specifically, this makes it possible to obtain a rapid attack of the calcium carbonate and a rapid degassing of the C0 2 .
  • the source of calcium may comprise calcium oxide, or calcium hydroxide, or calcium chloride, or calcium nitrate, or calcium acetate.
  • octacalcium a Ca/P ratio of between 1.4 and 1.6, preferably between 1.4 and 1.5, is favored. This molar ratio is advantageous when use is made of a source of calcium having less than 30 % by weight of carbonate, such as preferably :
  • the source of calcium and the phosphate ions are in general reacted for at least 0.1 hour, preferably at least 0.5 hour. It is not useful to react them over excessively long periods of time.
  • the source of calcium and the phosphate ions are reacted for at most 4 hours, more advantageously at most 2 hours, or even at most 1 hour.
  • the suspension (B) of calcium phosphate porous support in general has a Ca/P molar ratio of at most 5, preferably of at most 3, more preferably still of at most 2.
  • the alkaline compound used that comprises hydroxide ions, to be sodium hydroxide and/or calcium hydroxide.
  • the additional source of calcium is selected from the group consisting of calcium chloride, calcium nitrate, and calcium acetate, preferably calcium chloride, and for this additional source of calcium to be added to the alkaline compound, in order to finely adjust the Ca/P molar ratio and in order to limit the concentration of phosphorus element in the aqueous solution (C) of the suspension (B) to at most 5 mmol, advantageously to at most 0.5 mmol, more advantageously to at most 0.05 mmol of phosphorus element per liter of the aqueous solution (C).
  • this makes it possible, coupled with the use of hydroxide ions for setting the pH of the second step, to limit the losses of phosphates in the process water.
  • the viscosity of the porous support suspension (B) in the second step of the process of the present invention is typically about 10 cps (mPa.s).
  • the production of a gel results in making porous support particles of small particle size, with weight-mean D50 values of less than 10 ⁇ , which may be a disadvantage for certain applications.
  • the suspended solids density of the suspension (A) in the first step is in general at most 20 wt%.
  • the suspended solids density of the suspension (B) in the second step is in general at most 15 wt%.
  • the suspended solids density of the suspension (A) and/or of the suspension (B) is advantageously at least 5 wt%, more advantageously at least 7 wt%, most advantageously at least 10 wt%. It has been indeed observed that a too low density of the suspension decreases the efficacy of the produced porous support particles in metal adsorption (in particular on Fe). Moreover a too low density of the suspension induces longer time of water separation when decantation or filtration is used in the method of making the support.
  • the stirring speed of the suspension during the first and second steps corresponds generally to a stirring dissipated energy in the reactors volume of at least 0.2 kW/m 3 and at most 1.5 kW/m 3 , preferably at least 0.5 kW/m 3 and at most 1.0 kW/m 3 .
  • the first step is carried out at a temperature of less than 50°C, preferably at most 45°C, or at most 40°C.
  • This low-temperature first step makes it possible to obtain a calcium phosphate porous support at the end of the second step in the form of particles of large to medium particle size and having a high specific surface area.
  • the method may manufacture in particular particles of porous support by this first embodiment, comprising at least 60 % by weight of hydroxyapatite or hydroxyapatite-like structure, and having a mean size of at least 30 ⁇ , preferably of at least 50 ⁇ and having a specific BET surface area and/or pore volume as described above.
  • the specific BET surface area measured after heat treatment at 200°C is at least 110 mVg.
  • the porous support may comprise at least 2 wt%, preferably at least 2.5 wt% or at least 3 wt%, more preferably at least 5 wt%, and yet more preferably at least 6 wt% of hydroxide ions.
  • the porous support may comprise from 2 wt% to 6 wt% of hydroxide ions, preferably from 2.5 wt% to 5 wt% of hydroxide ions.
  • the first step is carried out at a temperature of at least 50°C, preferably of at least 55°C, or of at least 60°C.
  • a porous support in the second step in the form of particles of small particle size and having a lower specific surface area.
  • the process may manufacture in particular particles of porous support obtained by the method according to this second embodiment, comprising at least 60 % by weight of hydroxyapatite, and having a mean size of at most 30 ⁇ , preferably of at most 20 ⁇ .
  • particles of porous support have a specific BET surface area of at least 15 m 2 /g, preferably of at least 50 mVg, and having a content of hydroxide ions of greater than 2 % by weight, preferably greater than 3.5 % by weight, and more preferably greater than 4 % by weight.
  • the second step is advantageous for the second step to be carried out at a temperature of at least 45°C, preferably of at least 55°C, or of at least 60°C, or of at least 80°C.
  • the second step of the manufacture method is carried out at a temperature of at least 45°C, preferably of at least 55°C, or of at least 60°C, or of at least 80°C, for a time period of at least 0.1 to 0.5 hour.
  • the addition of the alkaline compound comprising hydroxide ions in order to set the pH of the second step, and of the additional source of calcium in order to obtain a suspension (B) of calcium phosphate porous support having a Ca/P molar ratio of greater than 1.6 last no more than 4 hours, advantageously no more than 2.5 hours : at higher temperature such as at 50°C or at 60°C generally one hour is sufficient, as at 40°C the alkaline compound addition to set the pH of the second step is generally longer : and about 2.5 hours are needed.
  • the alkaline compound addition is stopped when the pH remains at the set value for at least 15 minutes.
  • the suspension (B) is left to cool for 1 to 24 hours, preferably at least 10 hours, down to ambient temperature. This makes it possible to mature the calcium phosphate porous support and to reduce the residues of MCP/DCP or brushite, or of octacalcium (precipitated during the first step), into a hydroxyapatite structure and into calcium phosphate and calcium hydroxide complexes, within the suspension (B).
  • the suspension (B) comprises an aqueous solution (C) and calcium phosphate porous support particles, and
  • a portion of the aqueous solution (C) is separated from the suspension (B) in order to obtain an aqueous suspension (D) comprising at least 18 % and at most 50 % of calcium phosphate porous support particles, or in order to obtain a wet solid (D') comprising at least 50 % and at most 80 % of calcium phosphate porous support particles, or a pulverulent solid (D") comprising at least 80 % and at most 95 % of calcium phosphate porous support particles and at least 5 % and at most 20 % of water.
  • the porous support material is not isolated from the aqueous solution in which it is suspended prior to deposition of the active catalyst component.
  • the porous support material may be isolated prior to deposition of the active catalyst component. Preferably in this instance, greater than 90% or 95% by weight of the solvent or dispersion medium is removed.
  • the isolation may comprise any type of solid/liquid separation; filtration is a preferred isolation technique.
  • the porous support material may not be subjected to drying prior to deposition of the active catalyst component.
  • the porous support material may be dried prior to deposition of the active catalyst component. Drying is preferably carried out after the porous support material has been isolated.
  • a suitable drying temperature is about 80° C to about 120° C.
  • drying temperatures may be used. For example, drying temperatures of less than 80° C may be used if the drying time is increased or the drying pressure is decreased. A preferred drying temperature is from about 100° C to about 120° C.
  • the calcium phosphate porous support obtained by the manufacture method described herein may be effective for use as a support for a catalyst for treating a waste gas contaminated by nitrogen oxides, in particular a flue gas contaminated by NOx and originating from a combustion process.
  • One or more embodiments of the present invention pertain to a catalyst supported on the calcium phosphate porous support as described previously.
  • a particular embodiment of the present invention pertains to a catalyst composition for catalytic reduction of NO x compounds, comprising an active catalyst component deposited on the porous support; wherein the active catalyst component comprises iron.
  • the calcium phosphate porous support may contain iron in its structure
  • the calcium phosphate porous support on which iron is deposited is preferably substantially free of iron, that is to say, the iron content of the calcium phosphate porous support should be less than 0.5 wt%, preferably less than 0.3 wt%, more preferably less than 0.1 wt%.
  • the active catalyst component may comprise at least 0.5 wt%, preferably at least 0.7 wt%, more preferably at least 1.0 wt%, most preferably at least 1.5 wt%, of iron; and/or may comprise at most 15 wt%, preferably at most 13 wt%, more preferably at most 12 wt%, most preferably at most 11 wt%, of iron.
  • a range of from 1.5 wt% to 12 wt% of Fe is particularly suitable.
  • a range of from 2 wt% to 8 wt% of Fe is also particularly suitable.
  • the catalyst composition has a BET specific surface area measured after being calcined at 400 °C of at least 65 m 2 /g and/or at most 100 m 2 /g.
  • the catalyst composition has a pore volume measured after being calcined at 400 °C of at least 0.3 cm 3 /g, preferably of at least 0.41 cm 3 /g, and/or at most 1.1 cm 3 /g, preferably of at most 1.0 cm 3 /g, more preferably of at most 0.9 cm 3 /g. most preferably of at most 0.8 cm 3 /g.
  • the catalyst composition has an average pore radius measured after being calcined at 400°C of at least 5 nm, preferably at least 7 nm, and/or at most 30 nm, preferably at most 25 nm.
  • the catalyst composition has a microporous and mesoporous morphology.
  • the catalyst composition contains not more than
  • the catalyst composition is in the form of particles.
  • the mean diameter D50 of the catalyst composition is greater than 10 ⁇ , in general greater than 20 ⁇ , or even greater than 50 ⁇ .
  • this mean diameter of the catalyst composition is in general preferably less than 200 ⁇ , or even less than 150 ⁇ . This makes it possible to limit the stirring powers to prevent the particles from needing high velocities of waste gases to be treated at the injection points of the catalyst for the treatment of the waste gases.
  • the mean diameter of the catalyst composition may be at least 150 ⁇ , or at least 200 ⁇ , or at least 250 ⁇ , and/or up to 1500 ⁇ , or up to 1000 ⁇ , or up to 750 ⁇ , or up to 600 ⁇ , or up to 500 ⁇ . This mean diameter would allow for the resulting catalyst particles to be used in a flow-through system where the waste gas to be treated is passed through a bed of catalyst particles.
  • the active catalyst component may be deposited on the porous support using a solution of an iron precursor.
  • the iron precursor may include Fe 3+ or Fe 2+ , preferably Fe 3+ .
  • a preferred iron precursor may be selected from the group consisting of iron nitrate, iron chloride, iron perchlorate (Fe(C10 4 ) 2 ), iron sulfate (Fe 2 (S04)3), iron fluorosilicate (FeSiF 6 ), any hydrated form thereof, and any mixture thereof.
  • the iron nitrate may be selected from Fe(N03) 2 .6H 2 0 or Fe(N03) 3 .9H 2 0.
  • the iron chloride may be selected from FeCl 2 or FeCi3.
  • the iron precursor is more preferably selected from the group consisting of iron (III) nitrate, iron (III) chloride, iron (III) sulfate, iron (III) perchlorate, any hydrated form thereof, and any mixture thereof.
  • the active catalyst component may be deposited on the porous support by wet impregnation or ion-exchange, preferably by ion-exchange.
  • wet impregnation (with small amount of excess water solution) is a catalyst preparation technique that does not require an iron precursor with ionic character. Therefore, an iron precursor which is not water soluble may be used for the catalyst preparation via impregnation.
  • Impregnation is a technique in which a new phase is added on the external surface and in the pores of the porous support (if the pore dimensions allow the entrance of the used Fe precursor).
  • Fe besides Ca will be present in the final catalyst composition.
  • Ionic exchange is a technique for modifying the surface composition of materials that have metal cations bound to the framework with electrostatic bonds. This preparation technique necessitates a Fe precursor with ionic character. Therefore, iron sulfate, iron chloride, iron perchlorate, and iron nitrate can be selected as iron precursor to provide iron cations. Iron (III) chloride, iron (III) sulfate, and iron (III) nitrate are particularly suitable as iron precursor with the ion exchange method.
  • the new iron cations are introduced in the sample composition and they substitute the original cations of the sample (in this case iron cations substitute Ca 2+ cations of the hydroxyapatite which enter into solution).
  • Ionic exchange is a method that exploits the electrostatic interaction between the added cations and the negative framework of the starting material (hydroxyapatite).
  • washing medium may comprise water (such as deionized water) or a solvent similar to the one used to dissolve or disperse the iron precursor(s).
  • the particles may be isolated by any suitable means, such as filtration, to remove the medium/solvent into which the iron precursor is dissolved or suspended or to remove the washing medium at the end of the washing step.
  • filtration to remove the medium/solvent into which the iron precursor is dissolved or suspended or to remove the washing medium at the end of the washing step.
  • greater than 90% or 95% of the medium is removed. More preferably, greater than 98% of the medium is removed.
  • the (isolated) catalyst particles may be subjected to a heat treatment.
  • the heat treatment may use a temperature from 105°C to 500°C, preferably from 200°C to 400°C.
  • the resulting (isolated) catalyst particles may be subjected to a heat treatment (drying).
  • the temperature at which the particles are dried is dependent on the solvent medium and the pressure which is used to dry the particles.
  • Drying typically uses a temperature of 180 °C or less. Drying is typically carried out in air or in an 0 2 -containing atmosphere which may comprise another gaseous component such as nitrogen gas (N 2 ), helium or combination thereof. Drying may be carried out in a vacuum or not.
  • N 2 nitrogen gas
  • the same drying temperatures and times described above for drying the porous support will be useful for drying the supported catalyst after the active metal component has been deposited.
  • the moisture level of the dried supported catalyst can be measured by standard methods known in the art to determine if the material has been dried for a sufficient amount of time at the particular temperature.
  • a suitable drying temperature is about 80° C to about 120° C.
  • drying temperatures of less than 80° C may be used if the drying time is increased or the drying pressure is decreased.
  • a preferred drying temperature is from about 100 °C to about 120 °C.
  • the catalyst is dried for at least 10 hours at 100-120 °C to ensure that the solvent is adequately removed. More typically, the catalyst may be dried for at least 12, 14 or 16 hours at 100-120 °C to ensure that the solvent is removed to a sufficient level.
  • the catalyst is subjected to a heat treatment (calcining) using a temperature more than 180 °C and up to 500 °C.
  • calcining is performed after a drying step, but not necessarily.
  • the catalyst is not subjected to a heat treatment using a temperature greater than 180 °C (no calcination), prior to being used as a catalyst.
  • the alkali sorbent may comprise a sodium-containing compound or a calcium-containing compound.
  • a preferred alkali sorbent may comprise sodium bicarbonate, sodium carbonate, sodium sesquicarbonate (trona), quick lime, hydrated lime, limestone or any mixture thereof.
  • the more preferred alkali sorbent may comprise sodium bicarbonate, sodium carbonate, sodium bicarbonate, sodium carbonate, sodium bicarbonate, sodium carbonate, sodium bicarbonate, sodium carbonate, sodium
  • the yet more preferred alkali sorbent may comprise sodium bicarbonate, sodium sesquicarbonate (trona), or any mixture thereof.
  • the most preferred alkali sorbent may comprise or consist of sodium bicarbonate.
  • the alkali sorbent may comprise a sodium-containing compound and in addition an ammonia source.
  • the alkali sorbent may contain between 60 % and 98 %, preferably between 80 and 98 %, by weight of sodium bicarbonate, but may additionally contain up to 2 wt%, preferably between 0.02 % and 2.0 % by weight of ammonia, expressed in the form of ammonium ions NH 4 + .
  • WO2015/118166 both from SOLVAY SA are suitable to be used in this process.
  • a suitable alkali sorbent in this process may include or consist of the reactive composition disclosed in WO2015/118165.
  • This reactive composition comprises between 60 % and 98 %, preferably between 80 and 98 %, by weight of sodium bicarbonate, between 1 % and 40 %, preferably between 1 % and
  • composition 12 % by weight of sodium carbonate and between 0.02 % and 2.0 % by weight of ammonia, expressed in the form of ammonium ions NH 4 + , characterized in that the composition comprises less than 1.0 %, preferably less than 0.9 %, more preferably less than 0.8 % by weight of water.
  • Another suitable alkali sorbent in this process may include or consist of the reactive composition disclosed in WO2015/118166.
  • This reactive composition comprises between 60 % and 98 %, preferably between 80 and 98 %, by weight of sodium bicarbonate, between 1 % and 40 %, preferably between 1 % and 12 % by weight of sodium carbonate and between 0.02 % and 2.0 % by weight of ammonia, expressed in the form of ammonium ions NH 4 + , and comprising from 0.01 to 5 % by weight of a compound selected from hydrocarbons, fatty alcohols, fatty acids, or fatty acid salts , preferably fatty acids having 12 to 20 carbon atoms per molecule or a salt thereof.
  • the alkali sorbent is preferably in the form of particles having a diameter D90 of less than 50 ⁇ and a diameter D50 of less than 35 ⁇ , preferably a diameter D90 of less than 35 ⁇ and a diameter D50 of less than 20 ⁇ , more preferably a diameter D90 of less than 30 ⁇ and a diameter D50 of less than 15 ⁇ , measured by laser diffractometry.
  • the ammonia source may include urea, N3 ⁇ 4, and/or an ammonium containing salt or solution (such as ammonium bicarbonate).
  • the ammonia source may be in the form of a gas (a gas comprising or consisting of NH 3 ), a liquid (e.g., solution of ammonium salt such as ammonium bicarbonate, solution of urea, solution of N3 ⁇ 4, or any mixtures thereof), or a solid (powder comprising an ammonium salt and/or urea).
  • the ammonia source may be included in the alkali sorbent and/or in the catalyst.
  • the present invention also relates to a blend comprising the supported deNOx catalyst and an alkali sorbent.
  • This blend may be used for the multi-pollutant purification of a waste gas.
  • this blend may be used for the removal of NOx and acid gases like SOx, HC1, and/or HF through an injection of this blend into a waste gas stream contaminated by these pollutants.
  • the blend may comprise:
  • the weight ratio of the deNOx catalyst to the alkaline sorbent in the blend may be at least 0.001, or at least 0.005, or at least 0.010, or at least 0.020, or at least 0.030, or at least 0.045.
  • the weight ratio of the deNOx catalyst to the alkaline sorbent in the blend may be at most 1.00, or at most 0.50, or at most 0.40, or at most 0.30.
  • the blend may further comprise an ammonia source.
  • the ammonia source may include urea, an ammo ium, salt, and, or Nl
  • the alkali sorbent in the blend may further contain an ammonia source.
  • the ammonia source may include urea, an ammonium salt, and. or NH 3 .
  • the preferred alkali sorbent in the blend may comprise a compound selected from the group consisting of sodium scsquicarbonate (trona), sodium bicarbonate, and mixture thereof.
  • the alkali sorbent in the blend may comprise sodium bicarbonate and an ammonia source.
  • the alkali sorbent in the blend may comprise at least
  • the alkali sorbent in the blend may comprise between 60 % and 98 %, preferably between 80 and 98 %, by weight of sodium bicarbonate, between 1 % and 40 %, preferably between 1 % and 12 % by weight of sodium carbonate and between 0.02 % and 2.0 % by weight of ammonia, expressed in the form of ammonium ions NH 4 , characterized in that the alkali sorbent comprises less than 1 .0 %, preferably less than 0.9 %, more preferably less than 0.8 % by weight of water.
  • the alkali sorbent in the blend may comprise between 60 % and 98 %, preferably between 80 and 98 %, by weight of sodium bicarbonate, between 1 % and 40 %, preferably between 1 % and 12 % by weight of sodium carbonate and between 0.02 % and 2.0 % by weight of ammonia, expressed in the form of ammonium ions NH 4 + , and comprising from 0.01 to 5 % by weight of a compound selected from hydrocarbons, fatty alcohols, fatty acids, or fatty acid salts , preferably fatty acids having 12 to 20 carbon atoms per molecule or a salt thereof.
  • the alkali sorbent in the blend is in the form of particles having a diameter D90 of less than 50 ⁇ and a diameter D50 of less than 35 ⁇ , preferably a diameter D90 of less than 35 ⁇ and a diameter D50 of less than 20 ⁇ , more preferably a diameter D90 of less than 30 ⁇ and a diameter D50 of less than 15 ⁇ , measured by laser diffractometry.
  • the catalyst in the blend is in the form of particles having a diameter D90 of less than 50 ⁇ and a diameter D50 of less than 35 ⁇ , preferably a diameter D90 of less than 35 ⁇ and a diameter D50 of less than 20 ⁇ , more preferably a diameter D90 of less than 30 ⁇ and a diameter D50 of less than 15 ⁇ , measured by laser diffractometry.
  • another aspect of the present invention also relates to the use of the supported catalyst for the purification of a waste gas.
  • the supported catalyst may be used for the removal of NOx by contacting the supported catalyst with a waste gas stream contaminated by the NOx pollutants. Since the catalyst is active for the removal of NOx and hence has deNOx activity, the catalyst may be referred to as a "deNOx catalyst".
  • An embodiment of the present invention also relates to the use of the supported catalyst and the alkali sorbent for the purification of a waste gas.
  • the supported deNOx catalyst and the alkali sorbent may be used for the removal of pollutants: NOx and acid gases like SOx, HF, HCl, HBr, HI, and/or H 3 PO 4 by contacting the supported deNOx catalyst and the alkali sorbent with a waste gas stream contaminated by these NOx and acid gas (e.g., SOx) pollutants.
  • NOx and acid gases like SOx, HF, HCl, HBr, HI, and/or H 3 PO 4
  • a particular embodiment of the present invention relates to a deNOx process according to which an ammonia source is injected into a combustion waste gas stream containing NOx; and according to which the catalyst composition is brought into contact with the waste gas stream at a temperature of at least 100°C and preferably at most 600°C to carry out, in the presence of 0 2 , a reduction by N3 ⁇ 4 of at least a portion of the NOx.
  • the catalyst particles are contacted with the waste gas stream for a sufficient time so that the catalyst converts by reduction by N3 ⁇ 4 at least a portion of the NOx.
  • the particulate catalyst is used with the waste gas stream in a contact reactor such as packed in a fixed bed or fluidized in a fiuidized bed, or is injected in a duct/pipe/conduit through which the waste gas stream flows.
  • the fiuidization gas to maintain the catalyst particles suspended in the fluidized bed may comprise or consist of the waste gas stream to be treated.
  • the catalyst may be injected into the waste gas stream in the form of a dry powder injection or a semi-dry injection of a slurry of the catalyst.
  • the catalyst is dispersed into the waste gas to be treated, the resulting mixture is subjected to a separation in order to produce a treated gas which is partially purified of NOx and a spent catalyst that is removed from the treated gas.
  • the waste gas stream may be a flue gas stream containing at least NOx.
  • the catalyst supported on the porous support particles may be contacted with the flue gas stream, the flue gas stream being at a temperature of at least 100°C, or of at least 150°C, or of at least 180°C, or of at least 200°C, the resulting mixture then being subjected to a separation in order to obtain a resulting solid and a flue gas stream partially purified of NOx.
  • the flue gas stream may be at a temperature of at most 800°C, or of at most 600°C, of at most 550°C, or of at most 500°C.
  • the catalyst composition may be packed into a fixed bed in order for the waste gas stream passes through the bed of the catalyst to provide contact of the catalyst with the waste gas.
  • the catalyst composition may be fluidized in a fluidized bed to provide contact of the catalyst with the waste gas.
  • the fluidization gas to maintain the catalyst particles suspended in the fluidized bed may comprise or consist of the waste gas stream to be treated.
  • the contact time between the particulate catalyst and the flue gas stream to be treated may be very short in the order of millisecond(s) to seconds, such as at least one millisecond (ms), advantageously at least 5 ms, more advantageously at least 10 ms and/or at most 5 seconds, even more
  • the catalyst When the catalyst is packed or fluidized in a contact reactor, its use may be more long term - that is to say, the catalyst bed, whether fixed or fluidized, is used for a period of time greater than one week or even several months.
  • the contact time between the particulate catalyst and the waste gas effluent to be treated may be in the order of millisecond(s) to seconds, such as at least one millisecond (ms), advantageously at least 5 ms, more advantageously at least 10 ms and/or at most 3 seconds, even more advantageously at most 2 seconds, yet even more advantageously at most 1 second.
  • the effectiveness of the treatment of NOx may be monitored by comparing the concentrations of NOx upstream (in the waste gas stream) and downstream of the treatment (in the partially treated gas stream), for example by an automatic analyser or by sampling and analysis.
  • the supported catalyst charge of a SCR contact reactor may be in general regularly renewed in portions, for example, by partial purging of the spent catalyst which has been in contact with NOx, and by adding fresh supported catalyst to the contact reactor.
  • "Fresh" catalyst denotes a material which has not been in contact with NOx, whereas
  • “spent” catalyst denotes a material which has already been in contact with NOx. Such a process thus may ensure a replenishment of the catalyst activity when the catalyst may suffer from some catalytic deactivation after contact with the waste gas stream and reaction with NOx. Purification process for the removal of several pollutants from waste gas
  • the present invention also relates to the use of the supported catalyst and the alkali sorbent for the purification of a waste gas.
  • the supported deNOx catalyst and the alkali sorbent may be used for the removal of several pollutants including NOx and acid gases like SOx, HF, HCl, HBr, HI, and/or H 3 PO 4 by their injection into a waste gas stream contaminated by these NOx and acid gas (e.g., SOx) pollutants.
  • NOx and acid gases like SOx, HF, HCl, HBr, HI, and/or H 3 PO 4
  • the supported deNOx catalyst and the alkali sorbent may be injected together by first forming a blend and then injecting the blend, or by injecting the two materials at the same time and same location into the gas stream for effectively mixing them in situ.
  • a particular embodiment of the present invention relates to a purification process for the removal of pollutants, such as NOx, acid gas such as SOx (S0 2 & SO 3 ), HF, HCl, HBr, HI, H 3 PO 4 , and/or heavy metals like an element selected from the group consisting of : Al, Ag, As, Ba, Be, Bi, Ce, Co, Cd, Cu, Cr, Fe, Hf, Hg, La, Li, Mg, Mn, Mo, Ni, Pb, Pd, Rb, Sb, Se, Sn, Sr, Th, Ti, U, V, Y, Zn, and Zr, from a combustion waste gas stream.
  • pollutants such as NOx, acid gas such as SOx (S0 2 & SO 3 ), HF, HCl, HBr, HI, H 3 PO 4 , and/or heavy metals like an element selected from the group consisting of : Al, Ag, As, Ba, Be, Bi, Ce, Co, Cd, Cu,
  • the process comprises the steps:
  • an ammonia source is injected into the combustion waste gas stream; - the deNOx catalyst as described herein is brought into contact with the waste gas stream at a temperature of at least 100°C and preferably at most 600°C to carry out, in the presence of 0 2 , a reduction by NH 3 of at least a portion of the NOx, and
  • the alkali sorbent is brought into contact with the same waste gas stream at a temperature of at least 100°C and preferably at most 600°C to remove at least a portion of the acid gas(es) like SOx, HF, HCl, HBr, HI, and/or H 3 PO 4 and/or at least a portion of the heavy metals.
  • the catalyst particles are contacted with the waste gas stream for a sufficient time so that the catalyst converts by reduction by N3 ⁇ 4 at least a portion of the NOx.
  • the alkali sorbent is contacted with the waste gas stream for a sufficient time so that the alkali sorbent adsorbs/reacts with at least a portion of the acid gas (SOx, HF, HCl, HBr, HI, and/or H 3 PO 4 ) and/or heavy metals.
  • the acid gas SOx, HF, HCl, HBr, HI, and/or H 3 PO 4
  • the deNOx catalyst, the alkali sorbent, and the ammonium source used in the process has been described previously.
  • the deNOx catalyst and/or the alkali sorbent is preferably in the form of particles having a diameter D90 of less than 50 ⁇ and a diameter D50 of less than 35 ⁇ , preferably a diameter D90 of less than 35 ⁇ and a diameter D50 of less than 20 ⁇ , more preferably a diameter D90 of less than 30 ⁇ and a diameter D50 of less than 15 ⁇ , measured by laser diffractometry.
  • the weight ratio of the DeNOx catalyst to said alkaline sorbent brought into contact with the waste gas stream to be treated may be at least 0.001, or at least 0.005, or at least 0.010, or at least 0.020, or at least 0.030, or at least 0.045.
  • the weight ratio of the deNOx catalyst to said alkaline sorbent brought into contact with the waste gas stream to be treated may be at most 1.00, or at most 0.50, or at most 0.40, or at most 0.30.
  • the particulate catalyst (solid), the sorbent (solid) and the ammonia source are injected in a duct/pipe/conduit through which the waste gas stream flows.
  • the catalyst When the catalyst is dispersed into the waste gas to be treated, the catalyst may be injected into the waste gas stream in the form of a dry powder injection or a semi-dry injection of a slurry of the catalyst.
  • the sorbent When the sorbent is dispersed into the waste gas to be treated, the sorbent may be injected into the waste gas stream in the form of a dry powder injection or a semi-dry injection of a slurry of the catalyst.
  • the ammonia source When the ammonia source is dispersed into the waste gas to be treated, the ammonia source may be injected into the waste gas stream in the form of a gas (NH 3 gas), in the form of a liquid (solution of ammonium bicarbonate and/or solution of urea, solution of ammonia, or combinations thereof), in the form of a powder (urea).
  • a gas NH 3 gas
  • a liquid solution of ammonium bicarbonate and/or solution of urea, solution of ammonia, or combinations thereof
  • urea urea
  • the ammonia source may be present in the catalyst composition or in the alkali sorbent.
  • the waste gas stream may be a flue gas stream containing at least NOx and SOx.
  • the injection in the treatment process may proceed as follows:
  • an ammonia source is injected in the flue gas stream downstream of the point of injection where the alkaline sorbent is injected;
  • a particulate deNOx catalyst (as described herein) containing a Ca- deficient hydroxyapatite is injected into the flue gas stream downstream of the point of injection where the alkaline sorbent and the ammonia source is injected.
  • the injection in the treatment process may proceed as follows:
  • an ammonia source and a particulate deNOx catalyst are injected simultaneously in the flue gas stream downstream of the point of injection where the alkaline sorbent is injected.
  • the injection in the treatment process may proceed as follows:
  • an alkaline sorbent and the ammonia source are injected simultaneously injected in the flue gas stream
  • the particulate deNOx catalyst is injected separately in the flue gas stream downstream of the point of injection where the alkaline sorbent and the ammonia source are injected.
  • the injection in the treatment process may proceed as follows:
  • the alkali sorbent, the ammonia source , and the deNOx catalyst are injected simultaneously into the flue gas stream.
  • the injection in the treatment process may proceed as follows:
  • the ammonia source is injected into the flue gas stream
  • the alkali sorbent and the particulate deNOx catalyst are injected simultaneously in the flue gas stream downstream of the point of injection where the ammonia source is injected.
  • the catalyst and the sorbent both in solid form (powder) are dispersed into the waste gas stream to be treated, the resulting mixture is subjected to a gas/solid separation in order to produce a treated gas which is partially purified of NOx and SOx and solids comprising spent catalyst and sorbent in order for the solids to be removed from the treated gas.
  • the separation preferably comprises a bag filter or an electrostatic precipitator (ESP), preferably a bag filter.
  • the supported catalyst and the sorbent may be dispersed in the flue gas stream, the flue gas stream being at a temperature of at least 100°C, or of at least 150°C, or of at least 180°C, or of at least 200°C.
  • the supported catalyst and the sorbent may be dispersed in the flue gas stream, the flue gas stream being at a temperature of at most 800°C, or of at most 600°C, of at most 550°C, or of at most 500°C, of at most 450°C, of at most 400°C.
  • the catalyst and sorbent are injected as powder into a flue gas stream flowing through a flue duct, their use may be once-through - that is to say, the catalyst and the sorbent are not used again.
  • the contact time between the solid particles (catalyst and sorbent) and the waste gas stream to be treated may be very short in the order of millisecond(s) to seconds, such as at least one millisecond (ms), advantageously at least 5 ms, more advantageously at least 10 ms and/or at most 5 seconds, even more advantageously at most 4 seconds, yet even more advantageously at most 3 seconds.
  • ms millisecond
  • the effectiveness of the treatment of NOx and SOx may be monitored by comparing the concentrations of NOx and SOx upstream (in the waste gas stream) and downstream of the treatment (in the partially treated gas stream), for example by an automatic analyser or by sampling and analysis.
  • FIG. 4 is a schematic of a treatment process according to an embodiment of the present invention, in which a flue gas stream (dashed line in the figure) containing NOx and SOx and optionally heavy metals, is treated, and in which an alkali sorbent, an ammonia source, and the deNOx catalyst are injected separately into the flue gas.
  • a flue gas stream dashed line in the figure
  • an alkali sorbent, an ammonia source, and the deNOx catalyst are injected separately into the flue gas.
  • FIG. 5 is a schematic of a treatment process according to another embodiment of the present invention, in which a flue gas stream (dashed line in the figure) containing NOx and SOx and optionally heavy metals, is treated and an alkali sorbent is injected into the flue gas stream and separately the ammonia source and the deNOx catalyst are injected simultaneously downstream into the flue gas stream.
  • a flue gas stream dashed line in the figure
  • SOx and optionally heavy metals an alkali sorbent is injected into the flue gas stream and separately the ammonia source and the deNOx catalyst are injected simultaneously downstream into the flue gas stream.
  • an ammonia source 1 and the particulate deNOx catalyst 3 (as described herein) containing a Ca-deficient hydroxyapatite are injected simultaneously in the flue gas stream downstream of the point of injection where the alkaline sorbent 2 is injected;
  • the ammonia source may be injected at the same time and at the same location as the catalyst 3 is, but the N3 ⁇ 4 source and catalyst are not blended before they are injected.
  • FIG. 6 is a schematic of a treatment process according to yet another embodiment of the present invention, in which a flue gas stream (dashed line in the figure) containing NOx and SOx and optionally heavy metals, is treated and an alkali sorbent and the ammonia source are injected simultaneously into the flue gas stream and separately the deNOx catalyst is injected downstream into the flue gas stream.
  • a flue gas stream dashed line in the figure
  • an alkali sorbent and the ammonia source are injected simultaneously into the flue gas stream and separately the deNOx catalyst is injected downstream into the flue gas stream.
  • the particulate deNOx catalyst 3 (as described herein) containing a Ca- deficient hydroxyapatite is injected separately in the flue gas stream downstream of the point of injection where the alkaline sorbent 2 and the ammonia source 1 are injected;
  • the ammonia source may be injected at the same time and at the same location as the alkali sorbent is, but the NH 3 source and catalyst are not blended before they are injected.
  • the NH 3 source and the alkali sorbent are blended before they are injected together into the flue gas.
  • the alkali sorbent is manufactured so that its composition includes a suitable NH 3 source.
  • FIG. 7 is a schematic of a treatment process according to a preferred embodiment of the present invention, in which a flue gas stream (dashed line in the figure) containing NOx and SOx and optionally heavy metals, is treated, and the alkali sorbent 2, the ammonia source 1, and the deNOx catalyst 3 are injected simultaneously into the flue gas stream and the rest of the process downstream of this injection is the same as described for FIG. 4.
  • a flue gas stream dashex and SOx and optionally heavy metals
  • the ammonia source and the catalyst may be injected at the same time and at the same location as the alkali sorbent is, but the NH 3 source, the alkali sorbent and the catalyst are not blended together before they are injected at the same time and at the same location in a flue gas duct.
  • the NH 3 source and the alkali sorbent are blended before they are injected together into the flue gas, and the deNOx catalyst is injected at the same time and at the same location where the blend is injected.
  • the alkali sorbent is manufactured so that its composition includes a suitable NH 3 source, and the deNOx catalyst is injected at the same time and at the same location where the NH 3 source- containing sorbent is injected.
  • the NH 3 source, the alkali sorbent and the catalyst are comprised in a blend, and this blend is injected into the flue gas stream.
  • FIG. 8 is a schematic of a treatment process according to yet another preferred embodiment of the present invention, in which a flue gas stream (dashed line in the figure) containing NOx and SOx and optionally heavy metals, is treated and the alkali sorbent and the deNOx catalyst are injected
  • an alkaline sorbent 2 and the particulate deNOx catalyst 3 (as described herein) containing a Ca-deficient hydroxyapatite are injected simultaneously in the flue gas stream downstream of the point of injection where the ammonia source 1 is injected;
  • the deNOx catalyst may be injected at the same time and at the same location as the alkali sorbent is, but the alkali sorbent and deNOx catalyst are not blended before they are injected.
  • the deNOx catalyst and the alkali sorbent are blended before they are injected together into the flue gas.
  • Item 1 Process for producing a calcium phosphate porous support, according to which :
  • a source of calcium and a source of phosphate ions in water, in a molar ratio that is adjusted so as to obtain a Ca/P molar ratio of between 0.5 and 1.6, and the source of calcium is reacted with the phosphate ions at a pH of between 2 and 8, in order to obtain a suspension (A) of calcium phosphate, and
  • an alkaline compound comprising hydroxide ions in order to set a pH of more than 8, preferably of more than 8.5, preferably of at least 9, or of at least 10, and an additional source of calcium in order to obtain a suspension (B) of calcium phosphate porous support having a Ca/P molar ratio of more than 1.6.
  • Item 3 Process according to any one of the preceding items, in which the source of calcium comprises calcium carbonate, or calcium oxide, or calcium hydroxide, or calcium chloride, or calcium nitrate, or calcium acetate.
  • Item 4 Process according to any one of the preceding items, in which the source of phosphate ions is phosphoric acid.
  • Item 5 Process according to any one of items 1 to 3, in which the source of phosphate ions is a dihydrogen phosphate salt such as a sodium, potassium or ammonium dihydrogen phosphate salt, preferably a sodium dihydrogen phosphate salt.
  • a dihydrogen phosphate salt such as a sodium, potassium or ammonium dihydrogen phosphate salt, preferably a sodium dihydrogen phosphate salt.
  • Item 6 Process according to any one of items 1 to 3, in which the source of phosphate ions is a monohydrogen phosphate salt such as a sodium, potassium or ammonium monohydrogen phosphate salt, preferably a sodium
  • Item 7 Process according to any one of the preceding items, wherein in the second step, the suspension (B) of calcium phosphate porous support has a Ca/P molar ratio of at most 5, preferably of at most 3, more preferably still of at most 2.
  • Item 8 Process according to any one of the preceding items, in which, in the first step, the Ca/P molar ratio is :
  • Item 9 Process according to any one of the preceding items, wherein the source of calcium is in the form of powder or aqueous suspension of powder and the powder is selected from : calcium carbonate, calcium oxide, calcium hydroxide, or a mixture thereof, and the powder has a mean particle size of less than 300 ⁇ .
  • Item 10 Process according to any one of the preceding items, in which the stirring speed and the density of suspension, in the second step and
  • the additional source of calcium is selected from calcium chloride, calcium nitrate, or calcium acetate, preferably calcium chloride, and is added in addition to the alkaline compound, in order to finely adjust the Ca/P molar ratio and limit the concentration of phosphorus element in the aqueous solution (C) of the suspension (B) to at most 5 mmol, advantageously to at most 0.5 mmol, more advantageously to at most 0.05 mmol of phosphorus element per litre of aqueous solution (C).
  • Item 13 Process according to any one of the preceding items, in which the first step is carried out at a temperature of less than 50°C, preferably of at most 45°C, more preferably of at most 40°C.
  • Item 14 Process according to any one of items 1 to 12, in which the first step is carried out at a temperature of at least 50°C, preferably of at least 55°C, more preferably of at least 60°C.
  • Item 15 Process according to any one of the preceding items, in which the second step is carried out at a temperature of at least 40°C, preferably of at least 45°C, more preferably of at least 55°C, even more preferably of at least 60°C, or of at least 80°C.
  • the suspension (B) comprises an aqueous solution (C) and calcium phosphate porous support particles, and
  • a portion of the aqueous solution (C) is separated from the suspension (B) in order to obtain an aqueous suspension (D) comprising at least 18 % and at most 50 % of calcium phosphate porous support particles, or to obtain a wet solid (D') comprising at least 50 % and at most 80 % of calcium phosphate porous support particles, or to obtain a pulverulent solid (D") comprising at least 80 % and at most
  • hydroxyapatite and having a mean size of at least 30 ⁇ .
  • Item 18 Particles of calcium phosphate porous support according to the preceding item comprising at least 70 %, preferably at least 75 %, more preferably at least 80 % by weight of hydroxyapatite.
  • Item 19 Particles of calcium phosphate porous support according to Items 17 or 18 having a mean size of at least 50 ⁇ .
  • Item 20 Particles of calcium phosphate porous support according to items 17 to 19 having a specific surface area of at least 50 m 2 /g, more preferably of at least 110 m 2 /g, even more preferably of at least 120 m 2 /g, or of at least 140 m 2 /g, or at least 160 m 2 /g.
  • Item 21 Particles of calcium phosphate porous support according to Items
  • 17 or 19 having a mean size of at most 200 ⁇ , preferably of at most 100 ⁇ , more preferably of at most 70 ⁇ .
  • Item 22 Particles of calcium phosphate porous support according to items 17 to 21 comprising at least 2 %, preferably at least 2.5 wt% or at least 3 wt%, more preferably at least 5 %, and yet more preferably at least 6 % by weight of hydroxide ions, or comprising from 2 wt% to 6 wt% of hydroxide ions, preferably from 2.5 wt% to 5 wt% of hydroxide ions.
  • Item 23 Particles of calcium phosphate porous support according to items 17 to 22 covered with plate-like crystallites, and wherein the plate-like crystallites have a thickness of at most 25 nm, preferably of at most 20 nm, more preferably of at most 10 nm.
  • Item 24 Particles of calcium phosphate porous support according to item 23 wherein the thickness of plate-like crystallites is at least 1 nm, preferably at least 2 nm, more preferably at least 4 nm.
  • Item 25 Particles of calcium phosphate porous support according to Items
  • Item 26 Particles of calcium phosphate porous support according to Items 17 to 25 wherein the solubilized phosphate of 10 g of such particles stirred in 90 mL of water during 24 hours with a lab magnetic barrel, then filtrated on a 0.45 ⁇ nitrocellulose membrane, is less than 10 mg P0 4 / L of water.
  • Aqueous suspension (D) comprising at least 25 % and at most 50 % by weight of calcium phosphate porous support particles according to item 17 to 26, preferably obtainable from the process of item 16.
  • a pulverulent solid (D) comprising at least 80 wt% and at most 95 wt% of the calcium phosphate porous support particles according to item 17 to 26 and comprising at least 5 wt%, preferably at least 6 wt%, more preferably at least 10 wt%, even more preferably at least 15 wt% of water, advantageously obtainable from the process of item 16.
  • Item 29 A pulverulent solid (D) according to item 28 comprising at most 20 wt% of water.
  • Item 30 Particles of calcium phosphate porous support obtainable by the process according to item 14, comprising at least 60 % by weight of
  • hydroxyapatite and having a mean size of at most 30 ⁇ , preferably of at most 20 ⁇ and having a specific surface area of at least 15 m 2 /g, preferably of at least 50 m 2 /g, and having a content of hydroxide ions of greater than 2 % by weight, preferably greater than 3.5 % by weight, and more preferably greater than 4 % by weight.
  • a porous support comprises at least 60 wt % of a calcium- deficient hydroxyapatite having a calcium to phosphate molar ratio (Ca/P) of less than 1.67, preferably more than 1.5 and less than 1.67; the porous support having a specific BET surface area measured after heat treatment at 200°C of at least 110 m2/g and a pore volume measured after heat treatment at 200°C of at least 0.5 cm3/g.
  • Ca/P calcium to phosphate molar ratio
  • Item 32 The porous support according to Item 31 further comprising calcium carbonate in an amount of less than 20 wt%, preferably from 1 wt% to 19 wt%, more preferably from 2 wt% to 18 wt%, even more preferably from 5 wt% to 15 wt%, yet even more preferably from 7 wt% to 13 wt%, most preferably from 8 wt% to 12 wt%.
  • Item 33 The porous support according to Item 31 or 32, comprising less than 1 wt% of calcium dihydroxide Ca(OH) 2 , preferably less than 0.5 wt% calcium dihydroxide Ca(OH) 2 , more preferably less than 0.3 wt% calcium dihydroxide Ca(OH) 2 , even more preferably less than 0.2 wt% calcium dihydroxide Ca(OH) 2 , most preferably being substantially free of calcium dihydroxide Ca(OH) 2 .
  • Item 34 The porous support according to any of the items 31 to 33, further comprising water in an amount of less than 20 wt%, preferably from 1 wt% to 18 wt%, more preferably from 2 wt% to 15 wt%, even more preferably from 4 wt% to 12 wt%, yet even more preferably from 5 wt% to 11 wt% most preferably from 6 wt% to 11 wt%.
  • Item 35 The porous support according to any of the Items 31 to 34, comprising a Ca/P molar ratio of 1.60 or more, preferably of 1.65 or more, preferably of 1.67 or more, more preferably of 1.68 or more.
  • Item 36 The porous support according to any of the Items 31 to 35, comprising a Ca/P molar ratio greater than the Ca/P molar ratio of the calcium- deficient hydroxyapatite.
  • Item 37 The porous support according to any of the Items 31 to 36, comprising at least 65 wt%, preferably at least 70 wt%, more preferably at least 75 wt%, yet more preferably at least 80 wt%, yet most preferably at least 85 wt%, of the calcium-deficient hydroxyapatite.
  • Item 38 The porous support according to any of the Items 31 to 37, comprising at most 99 wt%, preferably at most 98 wt%, more preferably at most 97 wt%, yet more preferably at most 95 wt%, even more preferably at most 93 wt%, most preferably at most 91 wt% of the calcium-deficient hydroxyapatite.
  • Item 39 The porous support according to any of the Items 31 to 38, having a BET specific surface area measured after heat treatment at 200°C of at least 120 m 2 /g and/or at most 160 m 2 /g.
  • Item 40 The porous support according to any of the Items 31 to 39, having a BET specific surface area measured after heat treatment at 400°C of at least 60 m 2 /g and/or at most 100 m 2 /g.
  • Item 41 - The porous support according to any of the Items 31 to 40, having a BET specific surface area measured after heat treatment at 600°C of at least 20 m 2 /g and/or at most 40 m 2 /g.
  • Item 42 The porous support according to any of the Items 31 to 41 , having a pore volume measured after heat treatment at 200°C of at least 0.55 cm 3 /g, preferably of at least 0.55 cm 3 /g and/or at most 1.0 cm 3 /g, preferably of at most 0.95 cm 3 /g.
  • Item 43 The porous support according to any of the Items 31 to 42, having a pore volume measured after heat treatment at 400°C of at least 0.50 cm 3 /g, preferably of at least 0.60 cm 3 /g and/or at most 1 cm 3 /g.
  • Item 44 The porous support according to any of the Items 31 to 43, having a pore volume measured after heat treatment at 600°C of at least 0.42 cm 3 /g, preferably of at least 0.44 cm 3 /g and/or at most 0.8 cm 3 /g, preferably of at most 0.75 cm 3 /g.
  • Item 45- A catalyst composition for catalytic reduction of NO x compounds, comprising an active catalyst component deposited on the porous support of any of the Items 31 to 44, wherein said active catalyst component comprises iron.
  • Item 46- The catalyst composition for catalytic reduction of NO x compounds according to any of the preceding Item 45, according to which the active catalyst component comprises
  • Item 47- The catalyst composition for catalytic reduction of NO x compounds according to any of the Items 45-46, according to which the active catalyst component is deposited on the porous support by ion exchange.
  • Item 48- The catalyst composition for catalytic reduction of NO x compounds according to any of the Items 45-47, according to which the active catalyst component is deposited on the porous support using an iron precursor selected from the group consisting of iron nitrate, iron chloride, iron perchlorate, iron sulfate, iron fluorosilicate, any hydrated form thereof, and any mixture thereof; preferably using an iron precursor selected from the group consisting of iron (III) nitrate, iron (III) chloride, iron (III) sulfate, iron (III) perchlorate, any hydrated form thereof, and any mixture thereof.
  • an iron precursor selected from the group consisting of iron (III) nitrate, iron (III) chloride, iron (III) sulfate, iron (III) perchlorate, any hydrated form thereof, and any mixture thereof.
  • Item 49- The catalyst composition for catalytic reduction of NO x compounds according to any of the Items 45-48, which is subjected to a heat treatment using a temperature from 105°C up to 500°C, preferably from 200°C to 400°C, prior to being used as a catalyst.
  • Item 50- The catalyst composition for catalytic reduction of NO x compounds according to any of the Items 45-49, which is not subjected to a heat treatment using a temperature greater than 200°C, prior to being used as a catalyst for catalytic reduction of NO x compounds.
  • Item 51 The catalyst composition for catalytic reduction of NO x compounds according to any of the Items 45-50, in which the catalyst composition has a BET specific surface area measured after being calcined at 400°C of at least 65 m 2 /g and/or at most 100 m 2 /g, and /or in which the catalyst composition has a pore volume measured after being calcined at 400°C of :
  • Item 53- A catalyst composition for catalytic reduction of NO x compounds, comprising an active catalyst component deposited on the particles of the calcium phosphate porous support according to any of the Items 17 to 26 or Item 30, or of the pulverulent solid (D") according to Item 28 or 29, wherein the active catalyst component comprises iron.
  • Item 54 Process for treating a waste gas stream containing nitrogen oxides (NOx), said gas stream originating from a combustion process, in which an ammonia source is injected into the waste gas stream; and in which the catalyst composition according to any of the Items 45-53 is brought into contact with the waste gas stream containing ammonia at a temperature of at least 100°C and preferably at most 600°C to carry out, in the presence of 0 2 , a reduction by NH 3 of at least a portion of the NOx to N 2 and water.
  • NOx nitrogen oxides
  • Item 56 Process according to Item 54 or 55 in which the catalyst composition is injected into the waste gas stream in the form of a dry powder injection or a semi-dry injection of a slurry of the catalyst.
  • alkali sorbent comprising a compound selected from the group consisting of sodium bicarbonate, sodium carbonate, sodium sesquicarbonate (trona), quick lime, hydrated lime, limestone, and combinations thereof;
  • the catalyst comprises an active catalyst component deposited on a porous support
  • said active catalyst component comprises iron
  • porous support comprises at least 60 wt % of a calcium- deficient hydroxyapatite having a calcium to phosphate molar ratio (Ca/P) of less than 1.67, preferably more than 1.5 and less than 1.67.
  • Ca/P calcium to phosphate molar ratio
  • Item 58 Provides according to Item 57 wherein the porous support of the catalyst further comprises calcium carbonate in an amount of less than 20 wt%, preferably from 1 wt% to 19 wt%, more preferably from 2 wt% to 18 wt%, even more preferably from 5 wt% to 15 wt%, yet even more preferably from 7 wt% to 13 wt%, most preferably from 8 wt% to 12 wt%.
  • the porous support of the catalyst comprises less than 1 wt% of calcium dihydroxide Ca(OH) 2 , preferably less than 0.5 wt% calcium dihydroxide Ca(OH) 2 , more preferably less than 0.3 wt% calcium, dihydroxide Ca(OH) 2 , even more preferably less than 0.2 wt% calcium dihydroxide Ca(OH) 2 , most preferably being substantially free of calcium dihydroxide Ca(OH) 2 .
  • the porous support of the catalyst further comprises water in an amount of less than 20 wt%, preferably from 1 wt% to 18 wt%, more preferably from 2 wt% to 15 wt%, even more preferably from 4 wt% to 12 wt%, yet even more preferably from 5 wt% to 11 wt% most preferably from 6 wt% to 1 1 wt%.
  • Item 64 Provides according to any of Items 57-63, wherei the porous support has a specific BET surface area of at least 1 10 nr/g and a pore v olume of at least 0.5 cm 3 /g after a heat treatment at 200°C
  • Item 65 Provides according to any of Items 57-64, wherein the catalyst has a BET specific surface area measured after being calcined at 400°C of at least 65 m 2 /g and/or at most 100 nr/g.
  • alkali sorbent comprises or consists of a compound selected from the group consisting of trona, sodium bicarbonate, and mixture thereof.
  • Item 70 Provides according to any of Items 57-69, wherein the alkali sorbent contains an ammonia source.
  • Item 72 Provides according to any of Items 57-71 , wherein the alkali sorbent and the catalyst are mixed to form a blend to be injected together into the waste gas stream.
  • Item 74 Process according to any of Items 57-73, wherein the alkali sorbent and the catalyst are injected sequentially into the waste gas stream flowing through a duct, and wherein the alkali sorbent is injected in a duct at a location upstream of where the catalyst is injected.
  • Item 75 Provides according to any of Items 57-74, wherein the ammonia source and the catalyst are injected simultaneously into the waste gas stream.
  • Item 76 Process according to any of Items 57-75, wherein the temperature is at least 105 °C, or at least 120 °C, or at least 150 °C, or at least 180 °C, or at least 200 °C, or at least 250 °C, or at least 300 °C; and/or at most 550 °C, or at most 500 °C, or at most 450 °C, or at most 400 °C.
  • Item 77 Process according to any of Items 57-76, wherein the alkali sorbent is selected from the group consisting of trona, sodium bicarbonate, and mixture thereof.
  • Item 78 Process according to any of Items 57-77, wherein the alkali sorbent contains an ammonia source.
  • Item 80 Process according to any of Items 57-79, wherein the catalyst further comprises an ammonia source.
  • Item 81 Process according to any of Items 57-80, wherein the alkali sorbent further comprises an ammonia source.
  • Item 82 Process according to Item 81 , wherein the alkali sorbent comprises sodium bicarbonate and an ammonia source.
  • Item 83 Process according to any of Items 57-82, wherein the ammonia source is urea, an ammonium salt, and/or NH3.
  • Item 84 Process according to Item 82, wherein the alkali sorbent comprises at least 60 wt% sodium bicarbonate and from 0.02 wt% to 2 wt% of ammonia expressed in the form of ammonium ions NH .
  • Item 85 Process according to Item 84, wherein the alkali sorbent comprises between 60 % and 98 %, preferably between 80 and 98 %, by weight of sodium bicarbonate, between 1 % and 40 %, preferably between 1 % and 12 % by weight of sodium carbonate and between 0.02 % and 2.0 % by weight of ammonia, expressed in the form of ammonium ions NH 4 + , characterized in that the alkali sorbent comprises less than 1 .0 %, preferably less than 0.9 %, more preferably less than 0.8 % by weight of water.
  • the alkali sorbent comprises comprises between 60 % and 98 %, preferably between 80 and 98 %, by weight of sodium bicarbonate, between 1 % and 40 %, preferably between 1 % and 12 % by weight of sodium carbonate and between 0.02 % and 2.0 % by weight of ammonia, expressed in the form of ammonium ions NH 4 + , and comprising from 0.01 to 5 % by weight of a compound selected from
  • hydrocarbons preferably fatty acids having 12 to 20 carbon atoms per molecule or a salt thereof.
  • Item 87 Process according to any of Items 57-86, wherein the alkali sorbent is in the form of particles having a diameter D90 of less than 50 ⁇ and a diameter D50 of less than 35 ⁇ , preferably a diameter D90 of less than 35 ⁇ and a diameter D50 of less than 20 ⁇ , more preferably a diameter D90 of less than 30 ⁇ and a diameter D50 of less than 15 ⁇ , measured by laser
  • Item 88 Process according to any of Items 57-87, wherein the catalyst is in the form of particles having a diameter D90 of less than 50 ⁇ and a diameter D50 of less than 35 ⁇ , preferably a diameter D90 of less than 35 ⁇ and a diameter D50 of less than 20 ⁇ , more preferably a diameter D90 of less than 30 ⁇ and a diameter D50 of less than 15 ⁇ , measured by laser diffractometry.
  • Item 89 - A blend comprising or consisting of an alkali sorbent and a catalyst
  • said alkali sorbent being selected from the group consisting of limestone, lime, trona, sodium bicarbonate, and combinations thereof,
  • said catalyst comprising an active catalyst component deposited on a porous support; wherein said active catalyst component comprises iron;
  • porous support comprises at least 60 wt % of a calcium- deficient hydroxy apatite having a calcium to phosphate molar ratio (Ca/P) of less than 1.67, preferably more than 1 .5 and less than 1.67.
  • Ca/P calcium to phosphate molar ratio
  • Item 91 - Blend according to Item 89 or 90 wherein the porous support of the catalyst further comprises calcium carbonate in an amount of less tha 20 wt%, preferably from 1 wt% to 19 wt%, more preferably from 2 wt% to 18 wt%, even more preferably from 5 wt% to 15 wt%, yet even more preferably from 7 wt% to 13 wt%, most preferably from 8 wt% to 12 wt%.
  • the porous support of the catalyst comprises less than I wt% of calcium dihydroxide Ca(OH) 2 , preferably less than 0.5 wt% calcium dihydroxide Ca(OH) 2 , more preferably less than 0.3 wt% calcium dihydroxide Ca(OH) 2 , ev en more preferably less than 0.2 wt% calcium dihydroxide Ca(OH) 2 , most preferably being substantially free of calcium dihydroxide Ca(OH) 2 .
  • Item 96 - Blend according to any of Items 89-95, wherein the porous support has a specific BET surface area of at least 1 10 m 2 /g and a pore volume of at least 0.5 env /g after a heat treatment at 200°C
  • Item 97 - Blend according to any of Items 89-96, wherein the catalyst has a BET specific surface area measured after being calcined at 400°C of at least 65 m 2 /g and/or at most 1 00 m 2 /g.
  • Item 100 Blend according to any of Items 89-99, wherein the active catalyst component is deposited on the porous support by ion exchange or impregnation using an iron precursor selected from the group consist ing of iron nitrate, iron chloride, iron perchlorate.
  • iron sulfate iron fluorosilicate, any hydrated form thereof, and any mixture thereof; preferably using an iron precursor selected from the group consisting of iron (III) nitrate, iron (III) chloride, iron (III) sulfate, iron (III) perchlorate, any hydrated form thereof, and any mixture thereof.
  • the alkali sorbent comprises between 60 % and 98 %, preferably between 80 and 98 %, by weight of sodium bicarbonate, between 1 % and 40 %, preferably between 1 % and 12 % by weight of sodium carbonate and between 0.02 % and 2.0 % by weight of ammonia, expressed in the form of ammonium ions NH 4 + , characterized in that the alkali sorbent comprises less than 1 .0 %, preferably less than 0.9 %, more preferably less than 0.8 % by weight of water.
  • the alkali sorbent comprises comprises between 60 % and 98 %, preferably between 80 and 98 %, by weight of sodium bicarbonate, between 1 % and 40 %, preferably between 1 % and 12 % by weight of sodium carbonate and between 0.02 % and 2.0 % by weight of ammonia, expressed in the form of ammonium ions N3 ⁇ 4 + , and comprising from 0.01 to 5 % by weight of a compound selected from hydrocarbons, fatty alcohols, fatty acids, or fatty acid salts , preferably fatty acids having 12 to 20 carbon atoms per molecule or a salt thereof.
  • Item 1 12 The process according to Item 1 1 1 , wherein the temperature is at least 105°C and at most 500°C; preferably at least 105°C, or at least 120°C, or at least 150°C, or at least 180°C, or at least 200°C, or at least 250°C, or at least 300°C; and/or at most 550°C, or at most 500°C, or at most 450°C, or at most 400°C.
  • Item 113 The process according to any Items 1-16, or the particles according to any Items 17-26 or 30, or the aqueous suspension according to Item 27, or the pulverulent solid (D") of Item 28 or 29, or the support according to any Items 31-44, or the catalyst according to any Items 45-53, or the process according to any Items 54-88, or the blend according to any Items 89-110, or the process according to Item 111 or 112, wherein the support is substantially free of carbon, i.e., less than 0.5 wt% of carbon.
  • Item 114 The process according to any Items 1-16, or the particles according to any Items 17-26 or 30, or the aqueous suspension according to Item 27, or the pulverulent solid (D") of Item 28 or 29, or the support according to any Items 31-44, or the catalyst according to any Items 45-53, or the process according to any Items 54-88, or the blend according to any Items 89-110, or the process according to Item 111 or 112, wherein the support comprises at least 0.5 wt% but less than 7 wt%, preferably less than 6 wt%, more preferably less than 5 wt% or less than 4 wt% carbon.
  • Item 115 The process according to any Items 1-16, or the particles according to any Items 17-26 or 30, or the aqueous suspension according to Item 27, or the pulverulent solid (D") of Item 28 or 29, or the support according to any Items 31-44, or the catalyst according to any Items 45-53, or the process according to any Items 54-88, or the blend according to any Items 89-110, or the process according to Item 111 or 112, wherein the support is substantially free of bone char.
  • the calcium phosphate (Ca/P) support S12 was prepared in similar conditions as the ones of example lb of WO2015/173437. Limestone was dispersed in water at 20-25°C in a baffled 200-liter reactor. For the first step, H 3 PO 4 (75%) was then added to this suspension and the mixture was stirred at 390 rpm using a double 4-blade impeller. At the end of the addition of acid, the mixture was heated up to about 50°C, and a 25 wt% suspension of Ca(OH) 2 was added to maintain the pH of the suspension at 8-8.8 for the second step. The reaction time was 140 minutes.
  • the suspension is continually stirred at half the stirring speed than was used in the first step to allow it to cool down to 20-25°C.
  • the final density of solid suspension in aqueous suspension (B) was 18% by weight (solid weight reported to total weight of the aqueous suspension).
  • the calcium phosphate (Ca/P) support S14 was prepared in similar conditions as the ones of example lc of WO2015/173437. Limestone was dispersed in water at 20-25°C in a 5-liter reactor (without baffle). For the first step, H 3 PO 4 (75%)) was then added to this suspension and the mixture was stirred at 700 rpm using a 4-blade impeller. At the end of the addition of acid, the mixture was heated up to about 50°C, and a 25 wt% suspension of Ca(OH) 2 was added to maintain the pH of the suspension at 8.2-8.7 for the second step. The reaction time was 145 minutes.
  • the suspension is continually stirred at half the stirring speed than was used in the first step to allow it to cool down to 20-25°C.
  • the final density of solid suspension in aqueous suspension (B) was 5% by weight (solid weight reported to total weight of the aqueous suspension).
  • the calcium phosphate (Ca/P) support S16 was prepared in similar conditions as the ones of example lb of WO2015/173437. Limestone was dispersed in water at 20-25°C in a 5-liter reactor (without baffle). For the first step, H 3 PO 4 (75%)) was then added to this suspension and the mixture was stirred at 320 rpm using a double 4-blade impeller. At the end of the addition of acid, the mixture was heated up to about 50°C, and a 25 wt% suspension of Ca(OH) 2 was added to maintain the pH of the suspension at 8.1-8.9 for the second step. The reaction time was 175 minutes.
  • the suspension is continually stirred at half the stirring speed than was used in the first step to allow it to cool down to 20-25°C.
  • the final density of solid suspension in aqueous suspension (B) was 18% by weight (solid weight reported to total weight of the aqueous suspension).
  • the porosity characteristics were determined after a heat treatment at 110 °C under vacuum overnight (about 16 hours).
  • the BET specific surface area was determined by gas adsorption on a Micro meritics ASAP2020 machine. Before the analysis, the samples (0.7 to 1 g) are pretreated under vacuum at 110°C until a stable vacuum of 4-5 ⁇ bar has been achieved. The measurements were carried out using nitrogen as adsorbent gas at 77°K via the volumetric method, according to the ISO 9277 : 2010 standard (Determination of the specific surface area of solids by gas adsorption - BET method). The BET specific surface area was calculated in a relative pressure (P/P0) range varying from around 0.05 to 0.20.
  • the mean particles size D50 was also measured.
  • the mean diameter D50 is the diameter such that 50 % by weight of the particles have a diameter less than said value.
  • the particle size measurement was carried out on a Beckman Coulter LS 230 laser diffraction particle size analyser (laser of wavelength 750 nm) on particles suspended in water and using a size distribution calculation based on Fraunhofer diffraction theory (particles greater than 10 ⁇ ) and on Mie scattering theory (particles less than 10 ⁇ ), the particles being considered to be spherical.
  • the specific surface area (computed by the linear BET equation) and porosity (pore volume, pore size and pore size distribution) have been determined by N2 adsorption/desorption isotherms collected at -196 °C using an automatic analyzer of surface area on a Sorptomatic 1900 instrument, Italy. From the Slope and Intercept of the obtained line, the volume of N2 adsorbed on the surface in a monolayer (VM) and CBET constant have been calculated.
  • Pore size distribution was computed by Barrett- Joyner-Halenda (BJH) model equation from the desorption branch of the collected isotherms and average pore size (rav,p, pore radius in nm or in A) was calculated by the classical Gurvitch's rule:
  • Vp is the pore volume in cm 3 /g
  • SBET is the BET surface area in m 2 /g
  • the wet hydroxyapatite samples and the thermally treated samples Prior to the analysis, the wet hydroxyapatite samples and the thermally treated samples (from 0.15 to 0.30 g) have been outgassed at 150°C for 4 hours under vacuum.
  • Sintering causes loss of surface, decrease of pore volume and of pore size.
  • the small pores disappear and large porosity appeared.
  • the new porosity can be also associated with inter-particle voids. This is due to the decrease of the pore volume that results in the formation of larger volume (void) among the solid particles.
  • the wet support samples (S12, S14, and S16) have been weighed in ceramic crucibles (ca. 10 g with precision on an analytical scale).
  • the crucibles were put into an oven (Heraeus Instruments, Germany, vacutherm.) overnight (ca. 16 h) at 120°C in static dry air atmosphere. After cooling to room
  • thermobalance ca. 15 mg
  • the following three-step program on a TGA 7 PerkinElmer thermal analyzer was applied entirely done under N2 flowing: i) isothermal step at 35°C for 2 min; ii) heating from 35°C to 800°C, at controlled rate (10°C/min); Hi) cooling from 800°C to 50°C.
  • a calibration of the temperature was performed by measuring the Curie transitions (TC) of high- purity reference materials (alumel, nickel, perkalloy, and iron: TC of 163°, 354°, 596°, and 780°C, respectively) at the same heating rate (b) employed for this analysis. For each sample, three analyses were carried out to check the reproducibility of the obtained results.
  • a calcium phosphate (Ca/P) support labelled S97 was made under similar conditions as those described in example 1 of WO2015/173437 patent application. The sample was dried for 48 h at 105 °C in a drying oven. All analyses below have been carried on the dried sample.
  • composition of the support was determined.
  • the calcium carbonate (CaC0 3 ) concentration was calculated from the following technique.
  • An Orsat gas analyzer is an apparatus in which various gases, in this case C0 2 , can be selectively absorbed by passing them through a series of preselected chemical solutions.
  • the apparatus mainly consists of a calibrated water-jacketed gas burette, containing slightly acidified NaCl brine with a trace of a colour indicator (methyl orange).
  • the burette is connected by glass capillary tubing to an absorption bottle containing a 4 M sodium hydroxide solution, which absorbs the C0 2 gas.
  • the volume of gas in the burette is read before and after absorption in the NaOH solution. The difference in volume
  • the quantity of carbonate is calculated from the volume of C0 2 , taking the temperature of the water in the water-jacket of the burette into account as well as the atmospheric pressure.
  • the total calcium concentration was determined by potentiometric titration with EDTA solution using an indicative calcium electrode (ion selective electrode Ca 2+ electrode Metrohm 6.0508.110) and an Ag/AgCl reference electrode (Metrohm 6.0726.100).
  • an electronic voltmeter can be used to detect the change in potential between the two electrodes.
  • the equivalence point of the titration corresponds to the jump in voltage observed when all the Ca is complexed by EDTA.
  • the indicative calcium electrode detects the disappearance of free (uncomplexed) calcium.
  • the titrator was Metrohm 799 GPT Titrino.
  • ICP-OES Inductively coupled plasma optical emission spectrometry
  • the water content was determined by colometric Karl-Fisher titration after thermal desorption at 300 °C.
  • the sample was heated in a dedicated tubular furnace for KF analysis and the desorbed water was swept by means of a dry argon gas flow into the colometric titration cell, containing the colometric Karl Fischer reagent (methanol, diethanolamine, sulfur dioxide, imidazole and imidazolium iodide).
  • the hydroxyapatite concentration was calculated from the Ca and P concentrations in the following way:
  • the molar Ca concentration to be assigned to hydroyxylapatite was calculated from the total % Ca concentration (determined by
  • the molar P concentration assigned to hydroxyapatite was calculated from the total % P concentration (measured by ICP-OES): 5.19 mol/kg
  • TABLE 4 summarizes the estimated composition in wt% of the support sample S97. The sum of the compounds in this table is slightly below 100 % due to the experimental uncertainty associated with each of the analytical methods applied. The support contains no carbon.
  • the support did not contain calcium dihydroxide (Ca(OH) 2 ).
  • the pH of the sample solution was 6.3. Since there is no alkalinity, there was no calcium dihydroxide in the sample.
  • the pH of the sample spiked with 0.1 % of calcium dihydroxide was 7.5. It was concluded that the support material did not contain calcium dihydroxide.
  • the preparation method used was ion exchange, and the Fe-precursor used was iron nitrate.
  • H 2 0 from Sigma Aldrich was dissolved in water to reach a molar concentration of 10 "2 M.
  • Fe-nitrate water solution was put at pH of about 5 to increase Fe stabilization and avoid aggregation.
  • the first 3 steps were carried out two times in order to obtain a total Fe loading of 6 w% on HAP support.
  • two final steps were carried out:
  • 5° step calcination, l°C/min up to 450°C, maintained for 4 hours.
  • Catalyst sample obtained 5.48 wt% Fe on HAP
  • One more catalyst was prepared by ion exchange in a similar manner as the one prepared with 6 wt% using Fe(N0 3 ) 3 as Fe precursor except that only one ion exchange was carried out (steps 1-3 were performed only once), and identified as Fe2/HAP (with an actual loading of 2 wt% Fe).
  • Structural properties of the samples were performed by X-ray powder diffractometer equipped with a PW 1830 generator, monochromator in graphite, copper pipe, Cu Ka radiation at 40 kV x 40 mA.
  • start angle 10° 2 ⁇
  • end angle 60° 2 ⁇
  • step size 0.05° 2 ⁇
  • time for step 5 sec
  • scan speed 0.010 29/sec
  • number of step 1000
  • total time lh 23 min.
  • Hydroxyapatite is a crystalline material with a typical XRD pattern that can be found in JCPDS: 00-009- 0432 (see relevant TABLE 5).
  • the dried support sample S16 (dried at 120°C, labelled "SI 6- 120") and calcined support sample S16 samples treated at higher temperatures: 400°C and 600°C for 8 hours (labelled "SI 6-400-8” and "SI 6-600-8") had all the same structure that corresponds to the hydroxyapatite XRD pattern JCPDS: 00-009- 0432.
  • the crystallinity degree became higher with the temperature increasing of S16 treatment (see relevant XRD patterns in TABLES 6 A, 6B, 6C).
  • Fe6/HAP catalyst has been analyzed by the same XRD method.
  • This catalyst sample presents the typical crystalline structure of hydroxyapatite (09- 0432) without any line for the presence of some structures of iron oxide (as hematite, F 2 O 3 , pattern 40-1139) - see XRD pattern in TABLE 7. This finding suggests the absence of structured Fe-oxide aggregates in the catalyst and indicates a good dispersion of Fe in and on the hydroxyapatite support structure.
  • a continuous flow reactor was part of the Selective Catalytic Reaction system.
  • the catalyst sample has to be put inside as grains of given size; placing solids in powder form would result in high pressure loss, with consequences of having non-correct fluid dynamics when feeding gaseous mixture.
  • the dimension of the grains has to be selected so as to guarantee the absence of diffusional limits (external and internal diffusion) and a suitable fluid dynamics of the gaseous mixture.
  • the catalyst samples to be tested were pressed, crushed, and sieved as particles of 45-60 mesh (0.354 mm - 0.250 mm, respectively) in size.
  • the procedure to realize such particles was not straightforward as the correct pressure had to be found experimentally in order to obtain catalyst grain sizes stable to mechanical shocks; the grains should not lose powder with time during the reaction.
  • the grains were obtained by pressing each powder sample put between two steel disks under 3 tons for 30 seconds. The resulting sample in form of compacted disk (of few mm thickness) was then crushed and sieved between two sieves of 45 and 60 mesh (0.354 mm - 0.250 mm, respectively) of size.
  • Tests of the SCR reaction were performed in a continuous reaction line equipped with a set of mass flow controllers (Bronkhorst, Hi-Tec and Brooks Instruments), a tubular vertical electric oven (maximum temperature of 1000°C), a glass tubular catalytic micro reactor (with 5 mm i.d.), and an on-line FTIR spectrophotometer (Bio-Rad with DTGS detector) for the qualitative and quantitative determination of the fed and vented gaseous species.
  • mass flow controllers Bronkhorst, Hi-Tec and Brooks Instruments
  • a tubular vertical electric oven maximum temperature of 1000°C
  • a glass tubular catalytic micro reactor with 5 mm i.d.
  • an on-line FTIR spectrophotometer Bio-Rad with DTGS detector
  • a catalyst sample (ca. 0.20 g), sieved as particles of 0.35-0.25 mm of size and dried at 120°C in an oven overnight, was pre-treated in situ under an 0 2 /He flow (20% v/v) at 120 °C for 30 min.
  • the concentration of the feeding gas mixture and total flow rate were maintained constant via a Eurotherm Controller- Programmer type 818, and the temperature at which the reaction was being studied was maintained at least for 60 minutes in order to allow reaching steady- state conditions.
  • the fed gas mixture was prepared mixing ca. 500 ppm of NO, 500 ppm of NH3, and 10,000 ppm of 0 2 .
  • the effective gas mixture being fed to the catalyst bed also contained N0 2 (because N0 2 is formed from the reaction in gas phase between NO and 0 2 ): ca. 450 ppm of NO, 50 ppm of N02, 500 ppm of NH 3 , and ca. 10,000 ppm of 0 2 .
  • the total flow of the gaseous mixture was kept constant at 6 NL/h (corresponding to 0.12 s of contact time).
  • the mixture exiting from the reactor was monitored each 180 seconds by FT-IR equipped with a multiple reflection gas cell with 2.4 m path length;
  • the NH 3 - SCR reaction on the hydroxyapatite-based support (SI 6/400/8, calcined at 400°C for 8 h) was studied over the range of temperature 120-450°C while the concentration of the feeding mixture and flow rate were maintained the same (that is to say the contact time remained the same).
  • the sample was prepared as explained in the Section 4. a. The sample was pre-treated under a flow of 0 2 in He (20 %) at 3 NL/h for 30 min at 120°C.
  • the feeding mixture contained NO, NH 3 , 0 2 , as well as N0 2 formed in gas phase from NO+0 2 .
  • FIG. 1 illustrates the conversion of NO and NH 3 over the hydroxyapatite-based support SI 6/400/8 over the range of temperature 120-450°C. Conversion of NO was around 15-20% and that of N0 2 was much higher (ca. 60-70%); the reactivity of N0 2 is much higher than that of NO. Ammonia, after being adsorbed at low temperature (120°C), had conversion around 20-30%) in the temperature range 200-450°C. These observations showed that SI 6/400/8 support sample was inert in the NH 3 -SCR reaction. 5d. NH 3 -SCR catalytic tests: experimental results with two Fe catalysts over temperature range
  • the NH 3 -SCR reaction was studied on two catalysts prepared by ion- exchange on the same support S16 with iron nitrate as a precursor (Fe2/HAP and Fe6/HAP) over the range of temperature 120-400°C while the concentration of the feeding mixture and flow rate were maintained the same (that is to say the contact time remained the same).
  • the catalyst samples were made as explained in the Section 3; their actual Fe contents were 2 wt% Fe and 5.48 wt% Fe.
  • the catalyst samples were prepared and loaded in the SCR reactor as explained in the Section 5a.
  • the catalyst sample was pre-treated under a flow of 0 2 in He (20 % v/v) at 3 NL/h for 30 min at 120°C.
  • the conditions for reaction are provided in the TABLES 10a and 10b.
  • N 2 0 species were not detected among the formed products (this species can be formed from NH 3 oxidation by 0 2 ). It is worth noticing that the conversion of NO, N0 2 , and NOx starts to be observed at 250°C. At higher temperatures, NOx conversion increases attaining a value of about 70% (at 400°C). Ammonia conversion follows the trend of the NO species (maximum conversion observed at 400°C is around 60%>).
  • N 2 Formation of N 2 is computed by difference between the total NO x fed and the total NO x present at given temperature.
  • N 2 can be formed from NO x reduction and NH 3 oxidation. The (little) superior amount of N 2 formed in comparison with NO x converted is likely to an experimental error or a (little) oxidation of ammonia to N 2 .
  • Results indicate that a low Fe concentration to the HAP support was sufficient in order to observe SCR activity.
  • the activity on Fe2/HAP started at higher temperatures in comparison with the activity observed on Fe-catalyst at higher Fe-concentration (Fe6/HAP).
  • a lower NOx conversion was obtained on Fe2/HAP than on Fe6/HAP.
  • the Fe catalyst had poor deNOx activity at low temperature (150-250°C). However the Fe-based catalyst seems very promising for actual applications due to its high selectivity to the deNOx reaction. This catalyst was able to utilize ammonia to reduce NOx and this action was maintained at high temperatures.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Biomedical Technology (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • General Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Combustion & Propulsion (AREA)
  • Catalysts (AREA)
EP18752485.5A 2017-08-09 2018-08-08 Eisengeträgerter katalysator mit einem ca-defizienten hydroxyapatit zur abgasbehandlung Withdrawn EP3664935A1 (de)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US201762543099P 2017-08-09 2017-08-09
PCT/EP2018/071493 WO2019030278A1 (en) 2017-08-09 2018-08-08 IR SUPPORTED CATALYST COMPRISING A POOR AC HYDROXYAPATITE FOR THE TREATMENT OF WASTE GAS

Publications (1)

Publication Number Publication Date
EP3664935A1 true EP3664935A1 (de) 2020-06-17

Family

ID=63145015

Family Applications (1)

Application Number Title Priority Date Filing Date
EP18752485.5A Withdrawn EP3664935A1 (de) 2017-08-09 2018-08-08 Eisengeträgerter katalysator mit einem ca-defizienten hydroxyapatit zur abgasbehandlung

Country Status (2)

Country Link
EP (1) EP3664935A1 (de)
WO (1) WO2019030278A1 (de)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110833839A (zh) * 2019-11-12 2020-02-25 上海纳米技术及应用国家工程研究中心有限公司 微纳化单分散磷化铜催化剂及其制备方法和应用
CN111569916B (zh) * 2020-05-11 2021-08-24 四川大学 一种改性羟基磷灰石脱硝催化剂及其制备方法
CN111921487A (zh) * 2020-08-13 2020-11-13 西南科技大学 一种铁/钇改性羟基磷灰石复合材料及其制备方法和应用
CN113318749B (zh) * 2021-06-23 2023-05-09 贵州大学 抗重金属中毒的高效中低温nh3-scr脱硝催化剂及其制备方法和应用
EP4122887A1 (de) * 2021-07-22 2023-01-25 B. Braun Surgical, S. A. Verfahren zur herstellung von ammoniak

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4961917A (en) 1989-04-20 1990-10-09 Engelhard Corporation Method for reduction of nitrogen oxides with ammonia using promoted zeolite catalysts
FR2912396B1 (fr) 2007-02-09 2011-08-26 Solvay Procede de production d'un reactif phosphocalcique, reactif obtenu et son utilisation
PE20170212A1 (es) 2014-02-10 2017-04-13 Solvay Composicion reactiva basada en bicarbonato de sodio y procedimiento para su produccion
ES2700121T3 (es) 2014-02-10 2019-02-14 Solvay Composición reactiva basada en bicarbonato de sodio y procedimiento para su producción
FR3021045B1 (fr) 2014-05-16 2020-02-21 Solvay Sa Procede de production d'un reactif phosphocalcique, reactif obtenu et son utilisation
EP3302763A1 (de) * 2015-06-03 2018-04-11 Solvay SA Verfahren zur behandlung eines mit metallen oder organischen verbindungen kontaminierten gases unter verwendung eines calciumphosphatreaktanden mit apatit
US10661225B2 (en) * 2016-12-07 2020-05-26 Solvay Sa Copper supported catalyst comprising a Ca-deficient hydroxyapatite for waste gas NOx removal

Also Published As

Publication number Publication date
WO2019030278A1 (en) 2019-02-14

Similar Documents

Publication Publication Date Title
US10661225B2 (en) Copper supported catalyst comprising a Ca-deficient hydroxyapatite for waste gas NOx removal
EP3664935A1 (de) Eisengeträgerter katalysator mit einem ca-defizienten hydroxyapatit zur abgasbehandlung
US7153345B2 (en) Sulfur oxide adsorbents and emissions control
EP2874741B1 (de) Regenerierbares sorptionsmittel zur entfernung von kohlendioxid
RU2673295C2 (ru) Композиция на основе оксидов циркония, церия, ниобия и олова, способы получения и применение для катализа
KR101570565B1 (ko) 세륨, 지르코늄 및 텅스텐 기재 조성물, 제조 방법 및 촉매작용에서의 용도
KR101990156B1 (ko) 세륨 산화물 및 니오븀 산화물을 포함하는 조성물을 촉매로 사용하는, 질소 산화물(NOx)-함유 가스를 처리하는 방법
KR20080066920A (ko) 산화 지르코늄 및 산화 프라세오디뮴 기재의 조성물을 질소산화물(ｎｏｘ) 트랩으로서 사용하는, 질소 산화물 함유가스의 처리 방법
US10913658B2 (en) Carbon dioxide removal using lithium borate
Jin et al. Salt-composition-controlled precipitation of triple-salt-promoted MgO with enhanced CO2 sorption rate and working capacity
WO2016061394A1 (en) CATALYSTS FOR ENHANCED REDUCTION OF NOx GASES AND PROCESSES FOR MAKING AND USING SAME
JP6503473B2 (ja) 安定化されたマイクロポーラス結晶性物質、それを作成する方法、およびＮＯｘの選択的触媒還元のためのその使用
CA3097911A1 (en) Low-silica chabazite zeolites with high acidity
Buelna et al. Characteristics and desulfurization-regeneration properties of sol–gel-derived copper oxide on alumina sorbents
KR102067668B1 (ko) 질소산화물 환원용 촉매 및 이를 이용한 질소산화물 환원 시스템
CN109589969A (zh) 铝锰共柱撑蒙脱石负载Eu-Ce复合催化剂的制备方法和应用
WO2014202149A1 (en) Composite oxide based on cerium oxide, silicon oxide and titanium oxide
Svoboda et al. Low-temperature flue gas desulfurization by alumina-CaO regenerable sorbents
JP2011148678A (ja) 新規メタロシリケート及び窒素酸化物浄化触媒
CN108698034B (zh) 废气净化用组合物
WO2010073350A1 (ja) ＮＯｘ吸収剤及びその製造方法並びにその除去方法
JP4841768B2 (ja) 含クロム酸化物からなる窒素酸化物吸着剤及びその製造方法
Zhao et al. Designing direct redox reaction chemically coupling NO and SO2 removal
CN115430433B (zh) 一种具有高效活性的催化剂及其制备方法
JPH0796175A (ja) 吸着剤

Legal Events

Date Code Title Description
STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: UNKNOWN

STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: THE INTERNATIONAL PUBLICATION HAS BEEN MADE

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

STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: REQUEST FOR EXAMINATION WAS MADE

17P Request for examination filed

Effective date: 20200309

AK Designated contracting states

Kind code of ref document: A1

Designated state(s): AL AT BE BG CH CY CZ DE DK EE ES FI FR GB GR HR HU IE IS IT LI LT LU LV MC MK MT NL NO PL PT RO RS SE SI SK SM TR

AX Request for extension of the european patent

Extension state: BA ME

DAV Request for validation of the european patent (deleted)
DAX Request for extension of the european patent (deleted)
STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: THE APPLICATION IS DEEMED TO BE WITHDRAWN

18D Application deemed to be withdrawn

Effective date: 20210302