WO2003059922A1 - Concentrated aqueous iron chelate composition - Google Patents

Concentrated aqueous iron chelate composition Download PDF

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Publication number
WO2003059922A1
WO2003059922A1 PCT/EP2003/000273 EP0300273W WO03059922A1 WO 2003059922 A1 WO2003059922 A1 WO 2003059922A1 EP 0300273 W EP0300273 W EP 0300273W WO 03059922 A1 WO03059922 A1 WO 03059922A1
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Prior art keywords
iron
line
document
chelate
column
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PCT/EP2003/000273
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French (fr)
Inventor
Peter Jan Nieuwenhuizen
Axel Carstens
Rainer May
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Akzo Nobel N.V.
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Priority to AU2003235717A priority Critical patent/AU2003235717A1/en
Publication of WO2003059922A1 publication Critical patent/WO2003059922A1/en

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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/54Nitrogen compounds
    • B01D53/56Nitrogen oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1493Selection of liquid materials for use as absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/60Simultaneously removing sulfur oxides and nitrogen oxides
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C229/00Compounds containing amino and carboxyl groups bound to the same carbon skeleton
    • C07C229/76Metal complexes of amino carboxylic acids
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/10Capture or disposal of greenhouse gases of nitrous oxide (N2O)

Definitions

  • the present invention relates to a concentrated aqueous iron chelate composition.
  • Iron chelates such as ferric ion ethylenediaminetetraacetic acid (NaFeEDTA) are used in many applications. In particular, they can be used for the removal of NO ⁇ compounds from a gas stream, e.g. flue gas.
  • a gas stream e.g. flue gas.
  • NO x nitrogen oxides
  • SO ⁇ sulfur oxides
  • a scrub liquid in the form of an aqueous slurry comprising biomass, a transition metal chelate, such as NaFeEDTA, and a calcium compound suitable for binding sulfur oxides, such as lime or limestone, which rains down from spray bars in the scrubber.
  • the complex formed from NO and transition metal chelate and/or any spent transition metal chelate is regenerated biologically, NO and N0 2 being reduced to molecular nitrogen (N 2 ).
  • the sulfur oxides are removed by reacting with the calcium compound to form calcium sulfite, which is oxidized further, inside or outside the scrubber, to calcium sulfate, which is separated and land filled or used in construction.
  • the aqueous NaFeEDTA solution preferably is prepared using clarified process water.
  • iron chelates in different forms can be used, i.e. NaFeEDTA, which is commercially available as a solid material in a purified form, or KFeEDTA, which is commercially available in a concentrated liquid form (i.e. approx. 6 wt% Fe).
  • US 3,933,993 discloses a chelated iron solution of high concentration that is stable at a pH of 7-10.
  • the formulation is used for removing H 2 S and/or mercaptans as pollutants in a gas stream. It is mentioned that in order to provide the requisite sequestering action whereby iron is kept in solution, an excess of EDTA must be used, i.e. the molar ratio of EDTA to Fe must be greater than 1 :1 , i.e. 1.25:1 in Examples 2, 5, and 6.
  • the preferred ratio of EDTA to Fe is about 1.5:1 (see Examples 3 and 4).
  • Example 7 of this document a preferred chelated iron formulation having an Fe content of 2.8 wt% and a molar ratio of EDTA to Fe of 1.5:1 is disclosed.
  • SU 1287346 discloses an absorbent for the purification of gases from hydrogen sulphide comprising an aqueous solution of chelated iron, an organic amine, an alkali metal hydroxide or carbonate, and a sodium, potassium or ammonium phosphate.
  • an aqueous FeEDTA solution having a content of about 0.8 wt% Fe is described.
  • the molar ratio of EDTA to Fe is 1.65:1.
  • an excess of EDTA is undesirable, because in various applications the excess EDTA will be degraded, which adds to the cost of the formulation.
  • the excess EDTA can coordinate with (transition) metals, which may deactivate these metals.
  • an excess of EDTA is known to limit the oxidation of calcium sulfite to calcium sulfate, which is ascribed to the chelation of (trace amounts of) transition metals known to catalyze this oxidation reaction.
  • DE 4130132 relates to hydrogen sulphide absorption from gas with a high carbon dioxide content using a ferric amino-carboxylate solution stabilized with alkali hydrogen carbonate to avoid oxidative decomposition of the amino- carboxylate.
  • the alkali bicarbonate is added in an amount of 20-80 g/l, preferably 40-60 g/l.
  • the Fe content is 2-5 g/l, i.e. 0.2-0.5 wt%.
  • the molar ratio of alkali bicarbonate to iron varies between 2.6:1 and 26.5:1.
  • Example 2 of this document an aqueous FeEDTA solution having an iron content of 0.28 wt% is described.
  • the iron content of the formulations described in this document is too low, and this adds to the costs for transporting, e.g., shipping, such formulations over long distances and for storing during prolonged periods of time in a cost effective way.
  • using an excess of alkali bicarbonate is undesirable, because it further adds to the cost of the formulation.
  • the present invention provides a composition having an increased, high concentration of soluble chelated iron, which can be shipped and stored for prolonged periods of time.
  • the concentrated aqueous iron chelate composition of the present invention contains more than 0.7 wt% of iron, in a molar ratio of iron to chelate of about 1 :1 , and contains an additive selected from the group consisting of alkali metal, protonated alkali metal, and ammonium salts of carbonate (C0 3 2" ), phosphate (P0 4 3" ), diphosphate (P 2 0 7 4" ), triphosphate (P 3 O 10 5" ), phosphite (HPO3 2" ), hypophosphite (H 2 P0 2 " ), tetraborate (B 4 0 7 2” ), disulfite (S 2 0 5 2" ), thiosulfate (S 2 0 3 2” ), and iminodiacetate (HN(CH 2 CO 2 )2 2 ⁇ ) > in a molar ratio of additive to iron of from 0.1 :1 to 2.5:1.
  • the iron chelate to be used in accordance with the present invention may be any single iron chelate or a mixture of two or more iron chelates.
  • Suitable iron chelates for use in accordance with the present invention include iron ethylenediaminetetraacetic acid (FeEDTA), iron nitrilotriacetic acid (FeNTA), iron hydroxyethylenediaminetriacetic acid (FeHEDTA), and iron (propylene- diamino)tetraacetic acid (FePDTA).
  • Preferred iron chelates are FeEDTA, FeNTA, and FePDTA. The most preferred iron chelate is FeEDTA.
  • the amount of iron present in the composition in accordance with the present invention is at least 0.7 wt%, based on the total weight of the composition.
  • the iron content is in the range of 0.7 to 6 wt%.
  • the iron content is at least 1.5, more preferably at least 1.7, most preferably at least 2 wt%.
  • the iron content is at most 4, more preferably at most 3, most preferably at most 2.5 wt%.
  • the molar ratio of iron to chelate in the composition of the invention is about 1 :1 , i.e. about equimolar. In the context of the present invention, this means that the molar ratio of iron to chelate is in the range of 0.95:1 to 1.05:1.
  • the additive to be used in accordance with the present invention is an alkali metal or protonated alkali metal salt, more preferably a sodium or protonated sodium salt.
  • the additive is selected from the group consisting of alkali metal, protonated alkali metal, and ammonium salts of carbonate, phosphate, diphosphate, triphosphate, phosphite, tetraborate, thiosulfate, and iminodiacetate, more preferably the sodium and protonated sodium salts thereof. More preferably, the additive is selected from the group consisting of sodium carbonate, trisodium phosphate, disodium hydrogen phosphate, sodium dihydrogen phosphate, and disodium iminodiacetate.
  • the additive to be used in accordance with the present invention is sodium carbonate.
  • the amount of additive to be used in accordance with the present invention is defined by a molar ratio of additive to iron of from 0.1 :1 to 2.5:1.
  • the additive is added in a molar ratio of at least 0.5:1.
  • the additive is added in a molar ratio of at most 2:1 , more preferably at most 1.5:1.
  • the pH of the composition of the present invention is in the range of 7 to 10.
  • the pH is at least 7.5.
  • the pH is at most 9.5, more preferably at most 9, most preferably at most 8.5.
  • sodium hydroxide may be added.
  • the higher the pH the higher the solubility of the iron chelate will be.
  • compositions in accordance with the present invention can be prepared using means and equipment known to a person of ordinary skill in the art.
  • conventional stainless steel equipment may be used.
  • compositions of the present invention can be prepared, for example, by first contacting an iron salt with a chelate sodium salt in water in a molar ratio of iron to chelate of about 1 :1 , resulting in a precipitation of the iron chelate salt, and subsequently adding the additive, in the amount which is defined above. It is also possible to dissolve solid sodium iron chelate in water and then add the additive in the amount which is described above.
  • the pH is adjusted to a pH of 7 to 10 as described above.
  • the iron salt is Fe 2 (S0 4 ) 3 and the chelate sodium salt is Na 4 EDTA.
  • an aqueous homogeneous iron chelate solution of a low concentration i.e. in the range of 0.1 to 0.5 wt% of iron, is prepared by first contacting an aqueous iron salt solution with an aqueous sodium chelate solution, then adding the additive in a molar ratio as defined above, after which iron salt, sodium chelate, and additive in the proper molar ratios (as described above) are added as solids or in an aqueous solution to reach the more preferred concentrations of iron and additive.
  • the aqueous homogeneous iron chelate solution of a low iron concentration is prepared by dissolving the pure, solid iron chelate or diluting commercially available (aqueous) solutions of the iron chelate with water, and then adding the additive in a molar ratio to iron as defined above, after which the preparation can continue as described in the previous sentence.
  • process water obtained from an installation which is used for the removal of NO x and/or SO x from a gas stream is used for preparing the composition in accordance with the present invention.
  • a chelate sodium salt is used for preparing the composition of the present invention.
  • Suitable chelates for use in accordance with the present invention include EDTA, nitrilotriacetic acid (NTA), and (propylenediamino)tetra- acetic acid (PDTA).
  • NTA nitrilotriacetic acid
  • PDTA propylenediamino tetra- acetic acid
  • the chelate is EDTA.
  • a suitable chelate sodium salt is Na 4 EDTA.
  • Suitable iron salts include Fe 2 (SO ) 3 , FeS0 4 , FeCI 3 , and Fe(N0 3 ) 3 .
  • Fe 2 (S0 4 ) 3 is used.
  • compositions in accordance with the present invention generally do not contain any further components other than the iron chelate and the additive, as claimed, with the exception of the by-product salt - i.e. Na2S0 in Examples 1 and 2 below - formed from the in situ preparation of the iron chelate, as described above, or by-products present in a commercially available iron chelate, and/or a pH adjusting agent.
  • by-product salt i.e. Na2S0 in Examples 1 and 2 below
  • compositions of the present invention can be sufficiently concentrated in iron to be highly useful.
  • the compositions of the present invention were storage stable for prolonged periods of time, e.g., the composition of Example 1 was stable for more than four months of storage at room temperature, meaning that during this time period no solid material was observed by visual inspection.
  • the compositions of the present invention are particularly useful for the removal of NO x from a gas stream, more in particular for the removal of NO x in combination with SO x .
  • the use of the invention composition has the additional advantage that it aids in neutralizing acidic components in the flue gases.
  • the present invention is illustrated by the following Examples.
  • An aqueous solution of NaFeEDTA (20 mmoles) was prepared from 20 mmoles of an aqueous Na 4 EDTA solution (Dissolvine E-39, 19.0 g, 39.4 wt%), 10 mmoles of an aqueous Fe 2 (S0 ) 3 solution (9.0 g, 44.4 wt%), and 18.2 g of extra water.
  • This solution - which further contained 30 mmoles of Na 2 SO - were added 14.1 mmoles of an aqueous Na 2 C0 3 solution (13.6 g, 11.0 wt%) at room temperature with stirring.
  • the resulting aqueous solution having a pH of 7.9 and an Fe content of 2.4 wt%, was stable at room temperature for at least four months.
  • An aqueous solution of NaFeEDTA (100 mmoles) was prepared from 100 mmoles of an aqueous Na 4 EDTA solution (Dissolvine E-39, 93.5 g, 40.1 wt%), 50 mmoles of an aqueous Fe 2 (S0 4 ) 3 solution (45.0 g, 44.4 wt%), and 35.0 g of process water having the typical composition of clarified process water from a Flue Gas Desulfurization unit (-1 ,600 ppm Ca, -1 ,200 ppm sulfate, -2,600 ppm chloride, and pH ⁇ 5).
  • Example 4 To an aqueous solution of 20 mmoles of pure NaFeEDTA (Dissolvine E-Fe-13, 8.43 g) in 44.3 g of water were added 10 mmoles of Na 3 P0 4 (1.64 g) at room temperature with stirring. The resulting aqueous solution, having a pH of 7.2 and an Fe content of 2.1 wt%, was stable at room temperature for at least two months.
  • An aqueous solution of NaFeEDTA (20 mmoles) was prepared from 20 mmoles of an aqueous Na 4 EDTA solution (Dissolvine E-39, 19.0 g, 39.4 wt%), 10 mmoles of an aqueous Fe 2 (S0 4 ) 3 solution (9.0 g, 44.4 wt%), and 147.8 g of extra water - this solution further contained 30 mmoles of Na 2 S0 4 .
  • the resulting aqueous solution had a pH of 5.3 and an Fe content of 0.7 wt%.

Abstract

The invention relates to a concentrated aqueous iron chelate composition containing at least 0.7 wt % of iron, in a molar ratio of iron to chelate of about 1:1, and containing an additive selected from the group consisting of alkali metal, protonated alkali metal, and ammonium salts of carbonate (CO32-), phosphate (P043-), diphosphate (P2O74-), triphosphate (P3O105-), phosphite (HPO32-), hypophosphite (H2PO2-), tetraborate (B4O72-), disulfite (S2O52-), thiosulfate (S2O32-), and iminodiacetate (HN(CH2CO2)22-), in a molar ratio of additive to iron of from 0.1:1 to 2.5:1. Most preferably, the additive is sodium carbonate. The invention further relates to a process for preparing said composition and to the use of said composition for the removal of NOx from a gas stream. Typically, the invention compositions have an increased, high content of iron and are stable for prolonged periods of time.

Description

CONCENTRATED AQUEOUS IRON CHELATE COMPOSITION
The present invention relates to a concentrated aqueous iron chelate composition.
Iron chelates such as ferric ion ethylenediaminetetraacetic acid (NaFeEDTA) are used in many applications. In particular, they can be used for the removal of NOχ compounds from a gas stream, e.g. flue gas.
It is known to scrub nitrogen oxides (NOx) in combination with sulfur oxides (SOχ) as gaseous components from a gas by causing the gas to rise in a scrubber, the gas being brought into contact with a scrub liquid in the form of an aqueous slurry comprising biomass, a transition metal chelate, such as NaFeEDTA, and a calcium compound suitable for binding sulfur oxides, such as lime or limestone, which rains down from spray bars in the scrubber. The complex formed from NO and transition metal chelate and/or any spent transition metal chelate is regenerated biologically, NO and N02 being reduced to molecular nitrogen (N2). In addition, the sulfur oxides are removed by reacting with the calcium compound to form calcium sulfite, which is oxidized further, inside or outside the scrubber, to calcium sulfate, which is separated and land filled or used in construction.
The water balance of this scrubbing process is important, and it is preferred to only have a limited purge of water used in this process. Hence, the intake of additional water is to be limited. For this reason, the aqueous NaFeEDTA solution should be as concentrated as possible. In order to further decrease the intake of additional water, the aqueous NaFeEDTA solution preferably is prepared using clarified process water.
For the removal of NOx compounds from a gas stream, iron chelates in different forms can be used, i.e. NaFeEDTA, which is commercially available as a solid material in a purified form, or KFeEDTA, which is commercially available in a concentrated liquid form (i.e. approx. 6 wt% Fe).
Unfortunately, these commercial sources of iron chelates are relatively expensive. In addition, it is a known problem that handling solid iron chelate materials causes dusting. These drawbacks preclude their use for the removal of NOx compounds from a gas stream.
US 3,933,993 discloses a chelated iron solution of high concentration that is stable at a pH of 7-10. The formulation is used for removing H2S and/or mercaptans as pollutants in a gas stream. It is mentioned that in order to provide the requisite sequestering action whereby iron is kept in solution, an excess of EDTA must be used, i.e. the molar ratio of EDTA to Fe must be greater than 1 :1 , i.e. 1.25:1 in Examples 2, 5, and 6. The preferred ratio of EDTA to Fe is about 1.5:1 (see Examples 3 and 4). In Example 7 of this document a preferred chelated iron formulation having an Fe content of 2.8 wt% and a molar ratio of EDTA to Fe of 1.5:1 is disclosed.
SU 1287346 discloses an absorbent for the purification of gases from hydrogen sulphide comprising an aqueous solution of chelated iron, an organic amine, an alkali metal hydroxide or carbonate, and a sodium, potassium or ammonium phosphate. In the Example, an aqueous FeEDTA solution having a content of about 0.8 wt% Fe is described. The molar ratio of EDTA to Fe is 1.65:1.
Using an excess of EDTA is undesirable, because in various applications the excess EDTA will be degraded, which adds to the cost of the formulation. Furthermore, the excess EDTA can coordinate with (transition) metals, which may deactivate these metals. For example, in the application where NOx is removed simultaneously with SOx (see above), an excess of EDTA is known to limit the oxidation of calcium sulfite to calcium sulfate, which is ascribed to the chelation of (trace amounts of) transition metals known to catalyze this oxidation reaction. DE 4130132 relates to hydrogen sulphide absorption from gas with a high carbon dioxide content using a ferric amino-carboxylate solution stabilized with alkali hydrogen carbonate to avoid oxidative decomposition of the amino- carboxylate. The alkali bicarbonate is added in an amount of 20-80 g/l, preferably 40-60 g/l. The Fe content is 2-5 g/l, i.e. 0.2-0.5 wt%. Hence, the molar ratio of alkali bicarbonate to iron varies between 2.6:1 and 26.5:1. In Example 2 of this document an aqueous FeEDTA solution having an iron content of 0.28 wt% is described.
The iron content of the formulations described in this document is too low, and this adds to the costs for transporting, e.g., shipping, such formulations over long distances and for storing during prolonged periods of time in a cost effective way. Hence, it is desired that the iron content of aqueous iron chelate solutions be increased. Also, using an excess of alkali bicarbonate is undesirable, because it further adds to the cost of the formulation.
Hence, there is a need in the art for an aqueous composition which does not have the aforementioned problems. The present invention provides a composition having an increased, high concentration of soluble chelated iron, which can be shipped and stored for prolonged periods of time.
The concentrated aqueous iron chelate composition of the present invention contains more than 0.7 wt% of iron, in a molar ratio of iron to chelate of about 1 :1 , and contains an additive selected from the group consisting of alkali metal, protonated alkali metal, and ammonium salts of carbonate (C03 2"), phosphate (P04 3"), diphosphate (P207 4"), triphosphate (P3O10 5"), phosphite (HPO32"), hypophosphite (H2P02 "), tetraborate (B407 2"), disulfite (S205 2"), thiosulfate (S203 2"), and iminodiacetate (HN(CH2CO2)22~)> in a molar ratio of additive to iron of from 0.1 :1 to 2.5:1. The iron chelate to be used in accordance with the present invention may be any single iron chelate or a mixture of two or more iron chelates. Suitable iron chelates for use in accordance with the present invention include iron ethylenediaminetetraacetic acid (FeEDTA), iron nitrilotriacetic acid (FeNTA), iron hydroxyethylenediaminetriacetic acid (FeHEDTA), and iron (propylene- diamino)tetraacetic acid (FePDTA). Preferred iron chelates are FeEDTA, FeNTA, and FePDTA. The most preferred iron chelate is FeEDTA.
The amount of iron present in the composition in accordance with the present invention is at least 0.7 wt%, based on the total weight of the composition. Typically, the iron content is in the range of 0.7 to 6 wt%. Preferably, the iron content is at least 1.5, more preferably at least 1.7, most preferably at least 2 wt%. Preferably, the iron content is at most 4, more preferably at most 3, most preferably at most 2.5 wt%.
The molar ratio of iron to chelate in the composition of the invention is about 1 :1 , i.e. about equimolar. In the context of the present invention, this means that the molar ratio of iron to chelate is in the range of 0.95:1 to 1.05:1.
Preferably, the additive to be used in accordance with the present invention is an alkali metal or protonated alkali metal salt, more preferably a sodium or protonated sodium salt. Preferably, the additive is selected from the group consisting of alkali metal, protonated alkali metal, and ammonium salts of carbonate, phosphate, diphosphate, triphosphate, phosphite, tetraborate, thiosulfate, and iminodiacetate, more preferably the sodium and protonated sodium salts thereof. More preferably, the additive is selected from the group consisting of sodium carbonate, trisodium phosphate, disodium hydrogen phosphate, sodium dihydrogen phosphate, and disodium iminodiacetate. Most preferably, the additive to be used in accordance with the present invention is sodium carbonate. The amount of additive to be used in accordance with the present invention is defined by a molar ratio of additive to iron of from 0.1 :1 to 2.5:1. Preferably, the additive is added in a molar ratio of at least 0.5:1. Preferably, the additive is added in a molar ratio of at most 2:1 , more preferably at most 1.5:1.
Typically, the pH of the composition of the present invention is in the range of 7 to 10. Preferably, the pH is at least 7.5. Preferably, the pH is at most 9.5, more preferably at most 9, most preferably at most 8.5. In order to adjust the pH, for example sodium hydroxide may be added. In general, the higher the pH, the higher the solubility of the iron chelate will be.
The compositions in accordance with the present invention can be prepared using means and equipment known to a person of ordinary skill in the art. For example, conventional stainless steel equipment may be used.
The compositions of the present invention can be prepared, for example, by first contacting an iron salt with a chelate sodium salt in water in a molar ratio of iron to chelate of about 1 :1 , resulting in a precipitation of the iron chelate salt, and subsequently adding the additive, in the amount which is defined above. It is also possible to dissolve solid sodium iron chelate in water and then add the additive in the amount which is described above. Preferably, if necessary, the pH is adjusted to a pH of 7 to 10 as described above. Preferably, the iron salt is Fe2(S04)3 and the chelate sodium salt is Na4EDTA.
In a preferred embodiment, an aqueous homogeneous iron chelate solution of a low concentration, i.e. in the range of 0.1 to 0.5 wt% of iron, is prepared by first contacting an aqueous iron salt solution with an aqueous sodium chelate solution, then adding the additive in a molar ratio as defined above, after which iron salt, sodium chelate, and additive in the proper molar ratios (as described above) are added as solids or in an aqueous solution to reach the more preferred concentrations of iron and additive. Alternatively, the aqueous homogeneous iron chelate solution of a low iron concentration is prepared by dissolving the pure, solid iron chelate or diluting commercially available (aqueous) solutions of the iron chelate with water, and then adding the additive in a molar ratio to iron as defined above, after which the preparation can continue as described in the previous sentence. Preferably, process water obtained from an installation which is used for the removal of NOx and/or SOx from a gas stream is used for preparing the composition in accordance with the present invention.
Preferably, a chelate sodium salt is used for preparing the composition of the present invention. Suitable chelates for use in accordance with the present invention include EDTA, nitrilotriacetic acid (NTA), and (propylenediamino)tetra- acetic acid (PDTA). Most preferably, the chelate is EDTA. A suitable chelate sodium salt is Na4EDTA.
Suitable iron salts include Fe2(SO )3, FeS04, FeCI3, and Fe(N03)3. Preferably, Fe2(S04)3 is used.
The compositions in accordance with the present invention generally do not contain any further components other than the iron chelate and the additive, as claimed, with the exception of the by-product salt - i.e. Na2S0 in Examples 1 and 2 below - formed from the in situ preparation of the iron chelate, as described above, or by-products present in a commercially available iron chelate, and/or a pH adjusting agent.
As described above, the compositions of the present invention can be sufficiently concentrated in iron to be highly useful. We have found that the compositions of the present invention were storage stable for prolonged periods of time, e.g., the composition of Example 1 was stable for more than four months of storage at room temperature, meaning that during this time period no solid material was observed by visual inspection. The compositions of the present invention are particularly useful for the removal of NOx from a gas stream, more in particular for the removal of NOx in combination with SOx. Apart from providing the ability to limit the intake of additional water as much as possible, the use of the invention composition has the additional advantage that it aids in neutralizing acidic components in the flue gases.
The present invention is illustrated by the following Examples.
EXAMPLES
Example 1
An aqueous solution of NaFeEDTA (20 mmoles) was prepared from 20 mmoles of an aqueous Na4EDTA solution (Dissolvine E-39, 19.0 g, 39.4 wt%), 10 mmoles of an aqueous Fe2(S0 )3 solution (9.0 g, 44.4 wt%), and 18.2 g of extra water. To this solution - which further contained 30 mmoles of Na2SO - were added 14.1 mmoles of an aqueous Na2C03 solution (13.6 g, 11.0 wt%) at room temperature with stirring. The resulting aqueous solution, having a pH of 7.9 and an Fe content of 2.4 wt%, was stable at room temperature for at least four months.
Example 2
An aqueous solution of NaFeEDTA (100 mmoles) was prepared from 100 mmoles of an aqueous Na4EDTA solution (Dissolvine E-39, 93.5 g, 40.1 wt%), 50 mmoles of an aqueous Fe2(S04)3 solution (45.0 g, 44.4 wt%), and 35.0 g of process water having the typical composition of clarified process water from a Flue Gas Desulfurization unit (-1 ,600 ppm Ca, -1 ,200 ppm sulfate, -2,600 ppm chloride, and pH < 5). To this solution - which further contained 150 mmoles of Na2S04 - were added 70 mmoles of an aqueous Na2CO3 solution (67.9 g, 11.0 wt% in process water) at room temperature with stirring. The resulting aqueous solution, having a pH of 7.8 and an Fe content of 2.4 wt%, was stable at room temperature for at least three months. Example 3
To an aqueous solution of 20 mmoles of pure NaFeEDTA (Dissolvine E-Fe-13, 8.43 g) in 38.3 g of water were added 10 mmoles of Na2C03 (1.06 g) at room temperature with stirring. The resulting aqueous solution, having a pH of 7.2 and an Fe content of 2.4 wt%, was stable at room temperature for at least two months.
Example 4 To an aqueous solution of 20 mmoles of pure NaFeEDTA (Dissolvine E-Fe-13, 8.43 g) in 44.3 g of water were added 10 mmoles of Na3P04 (1.64 g) at room temperature with stirring. The resulting aqueous solution, having a pH of 7.2 and an Fe content of 2.1 wt%, was stable at room temperature for at least two months.
Example 5
To an aqueous solution of 20 mmoles of pure NaFeEDTA (Dissolvine E-Fe-13, 8.43 g) in 50.25 g of water were added 20 mmoles of disodium iminodiacetate (3.54 g) at room temperature with stirring. The resulting aqueous solution, having a pH of 7.2 and an Fe content of 1.8 wt%, was stable at room temperature for at least two months.
Example 6
To an aqueous solution of 20 mmoles of pure NaFeEDTA (Dissolvine E-Fe-13, 8.43 g) in 9.8 g of water were added 10 mmoles of Na2C03 (1.06 g) and 8.9 mmoles (8.9 ml) of an aqueous 1 N NaOH solution at room temperature with stirring. The resulting aqueous solution, having a pH of 7.9 and an Fe content of 4.0 wt%, was stable at room temperature for at least two months.
Comparative Example A
An aqueous solution of NaFeEDTA (20 mmoles) was prepared from 20 mmoles of an aqueous Na4EDTA solution (Dissolvine E-39, 19.0 g, 39.4 wt%), 10 mmoles of an aqueous Fe2(S04)3 solution (9.0 g, 44.4 wt%), and 147.8 g of extra water - this solution further contained 30 mmoles of Na2S04. The resulting aqueous solution had a pH of 5.3 and an Fe content of 0.7 wt%.

Claims

1. A concentrated aqueous iron chelate composition containing at least 0.7 wt% of iron, in a molar ratio of iron to chelate of about 1 :1 , and containing an additive selected from the group consisting of alkali metal, protonated alkali metal, and ammonium salts of carbonate (CO3 2"), phosphate (PO4 3"), diphosphate (P2O7 4") triphosphate (P3O10 5"), phosphite (HPO3 2"), hypo- phosphite (H2PO2 "), tetraborate (B4O7 2"), disulfite (S205 2"), thiosulfate (S203 2"), and iminodiacetate (HN(CH2C02)22~)> in a molar ratio of additive to iron of from 0.1 :1 to 2.5:1.
2. A composition according to claim 1 , characterized in that the additive is an alkali metal or protonated alkali metal salt.
3. A composition according to claim 1 or 2, characterized in that the iron chelate is selected from the group consisting of iron ethylene diamine tetraacetic acid, iron nitrilotriacetic acid, and iron (propylenedi- amino)tetraacetic acid.
4. A composition according to any one of claims 1-3, characterized in that the pH of the composition is 7 to 10.
5. A process for preparing the composition according to any one of the preceding claims containing at least 0.7 wt% of iron comprising first contacting an iron salt with a chelate sodium salt in water in a molar ratio of iron to chelate of about 1 :1 , and subsequently adding the additive in an amount of a molar ratio of additive to iron of from 0.1 :1 to 2.5:1.
6. A process according to claim 5, characterized in that the pH of the composition is adjusted to a pH of 7 to 10.
7. A process according to claim 6, characterized in that the pH of the composition is adjusted using sodium hydroxide.
8. A process according to any one of claims 5-7, characterized in that the water is process water obtained from an installation which is used for the removal of NOx from a gas stream.
9. A process according to any one of claims 5-8, characterized in that the iron salt is Fe2(S0 )3 and the chelate sodium salt is Na4EDTA.
10. Use of the composition according to any one of claims 1-4 for the removal of NOx, optionally in combination with SOx, from a gas stream.
Figure imgf000013_0001
w/14
According to International Patent Classification (IPC) or to both national classification and IPC
B. FIELDS SEARCHED
Minimum documentation searched (classification system followed by classification symbols)
IPC 7 C07F B01D C07C
Documentation searched other than minimum documentation to the extent that such documents are included in the fields searched
Electronic data base consulted during the international search (name of data base and, where practical, search terms used)
WPI Data, EPO-Internal , PAJ
C. DOCUMENTS CONSIDERED TO BE RELEVANT
Category " | Citation of document, with indication, where appropriate, of the relevant passages Relevant to claim No.
X US 4055623 A (SAITOH SHIGERU ET AL) 1-10 25 October 1977 (1977-10-25) examples 4-6
X US 4186176 A (KITAMURA TAKETSUGU ET AL) 1-10
29 January 1980 (1980-01-29) . col umn 2, l ine 18 - l ine. 65; examples 1,2
EP 0257124 A (ARI TECHNOLOGIES INC) 1-9
2 March 1988 (1988-03-02) page 2, l i ne 27 - l ine 31 page 5, l ine 47 -page 6, l ine 40 page 7, l i ne 42 - l ine 46; table 4
-/-
Further documents are listed in the continuation of box C. x_ Patent family members are listed in annex.
° Special categories of cited documents :
T" later document published after the international filing date or priority date and not in conflict with the application but
"A" document defining the general state of the art hich is not cited to understand the principle or theory underlying the considered to be of particular relevance invention
"E" earlier document but published on or after the international "X" document of particular relevance; the claimed invention filing date cannot be considered novel or cannot be considered to
"L" documentwhich may throw doubts on priority claim(s) or involve an inventive step when the document is taken alone which is cited to establish the publication date of another "Y" document of particular relevance; the claimed invention citation or other special reason (as specified) cannot be considered to involve an inventive step when the
"O" document referring to an oral disclosure, use, exhibition or document is combined with one or more other such docuother means ments, such combination being obvious to a person skilled
"P" document published prior to the international filing date but in the art. later than the priority date claimed "&" document member of the same patent family
Date of the actual completion of the international search Date of mailing of the international search report
13 Oune 20Θ3 ,^ ii π -a
Name and mailing address of the ISA Authorized officer
European Patent Office, P.B. 5818 Patentlaan 2 NL- 2280 HV Rijswijk Tel. (+31-70) 340-2040, Tx.31 651 epo n), Fax: (+31-70) 340-3016 Eij kenboom, A
Form PCT/ISA 210 (second sheet) (July 1992) page 1 of 2 C(Continuation) DOCUMENTS CONSIDERED TO BE RELEVANT
Category" | Citation of document, with indication, where appropriate, of the relevant passages Relevant to claim No.
x US 4518577 A (KLECKA MIRO E) 1-9 21 May 1985 (1985-05-21) column 1, line 22 - line 27 column 5, line 12 -column 6, line 5 column 9, line 24 - line 31
US 4518576 A (DIAZ ZAIDA) 1-9
21 May 1985 (1985-05-21) column 2, line 64 -column 3, line 30 column 5, line 5 - line 12; examples 1,2
X US 5223173 A (JEFFREY GAINES C) 1-9
29 June 1993 (1993-06-29) column 1, line 35 - line 38 column 10, line 1 -column 11, line 19; claims 1-4
WO 8906675 A (CHEVRON RES) 1-9
27 July 1989 (1989-07-27) page 25, line 18 - line 32; examples
Form PGT/ISA/210 (continuation of second sheet) (July 1992) page 2 of 2 j/
Figure imgf000015_0001
Patent document Publication Patent family Publication cited in search report ' date member(s) date
US 4055623 A 25-10-1977 P 50105593 A 20-08-1975
JP 50144694 A 20-11-1975
JP 51065078 A 05-06-1976
JP 1153912 C 30-06-1983
JP 51065098 A 05-06-1976
JP 57043527 B 16-09-1982
CA 1058829 Al 24-07-1979
CA 1058830 Al 24-07-1979
CA 1061519 A2 04-09-1979
DE 2502117 Al 24-07-1975
DE 2502118 Al 24-07-1975
FR 2258214 Al 18-08-1975
FR 2258215 Al 18-08-1975
GB 1501701 A 22-02-1978
GB 1501702 A 22-02-1978
NL 7500672 A 23-07-1975
NL 7500673 A 23-07-1975
NO 750153 A ,B, 18-08-1975
NO 750154 A ,B, 18-08-1975
NO 771759 A ,B, 22-07-1975
SE 407790 B 23-04-1979
SE 7500563 A 22-07-1975
SE 406190 B 29-01-1979
SE 7500564 A 22-Q7-1975
SE 410303 B 08-10-1979
SE 7610594 A 24-09-1976
US 3991161 A 09-11-1976
US 3992508 A 16-11-1976
US 4186176 A 29-01-1980 JP 54028274 A 02-03-1979
JP 54072799 A 11-06-1979
DE 2833440 Al 08-62-1979
EP 0257124 A 02-03-1988 EP 0257124 Al 02-03-1988
AT 88657 T 15-05-1993
DE 3688372 Dl 03-06-1993
DE 3688372 T2 12-08-1993
US 4622212 A 11-11-1986
US 4518577 A 21-05-1985 CA 1207513 Al 15-07-1986
US 4518576 A 21-05-1985 AU 569006 B2 14-01-1988
AU 3686684 A 04-07-1985
CA 1221673 Al 12-05-1987
DE 3465886 Dl 15-10-1987
EP 0152647 Al 28-08-1985
JP 1802322 C 26-11-1993 P 5012965 B 19-02-1993 P 60153921 A 13-08-1985
ZA 8409844 A 28-08-1985
US 5223173 A 29-06-1993 US 4816238 A 28-03-1989
US 4774071 A 27-09-1988
AU 605244 B2 10-01-1991
AU 1179688 A 25-08-1988
CA 1305464 Al 21-07-1992
CN 88100739 A , B 07-09-1988
DK 85388 A 20-08-1988
Form PGT/ISW210 (patent family annex) (July 1992) page 1 of 2
PCT/EP2003/000273 2002-01-16 2003-01-08 Concentrated aqueous iron chelate composition WO2003059922A1 (en)

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Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4055623A (en) * 1974-01-21 1977-10-25 Kureha Kagaku Kogyo Kabushiki Kaisha Method of removing nitrogen oxides from a gas as a salt of imidodisulfonic acid
US4186176A (en) * 1977-08-04 1980-01-29 Asahi Kasei Kogyo Kabushiki Kaisha Method of simultaneously removing sulfur dioxide and nitrogen oxides from exhaust gases
US4518577A (en) * 1982-12-20 1985-05-21 Shell Oil Company Sulfur separation process
US4518576A (en) * 1983-12-20 1985-05-21 Shell Oil Company H2 S Removal from gas streams
EP0257124A1 (en) * 1986-08-22 1988-03-02 ARI TECHNOLOGIES, INC. (a corporation of Illinois) Hydrogen sulfide removal
WO1989006675A1 (en) * 1988-01-15 1989-07-27 Chevron Research Company Composition, method and apparatus for removal of hydrogen sulfide
US5223173A (en) * 1986-05-01 1993-06-29 The Dow Chemical Company Method and composition for the removal of hydrogen sulfide from gaseous streams

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4055623A (en) * 1974-01-21 1977-10-25 Kureha Kagaku Kogyo Kabushiki Kaisha Method of removing nitrogen oxides from a gas as a salt of imidodisulfonic acid
US4186176A (en) * 1977-08-04 1980-01-29 Asahi Kasei Kogyo Kabushiki Kaisha Method of simultaneously removing sulfur dioxide and nitrogen oxides from exhaust gases
US4518577A (en) * 1982-12-20 1985-05-21 Shell Oil Company Sulfur separation process
US4518576A (en) * 1983-12-20 1985-05-21 Shell Oil Company H2 S Removal from gas streams
US5223173A (en) * 1986-05-01 1993-06-29 The Dow Chemical Company Method and composition for the removal of hydrogen sulfide from gaseous streams
EP0257124A1 (en) * 1986-08-22 1988-03-02 ARI TECHNOLOGIES, INC. (a corporation of Illinois) Hydrogen sulfide removal
WO1989006675A1 (en) * 1988-01-15 1989-07-27 Chevron Research Company Composition, method and apparatus for removal of hydrogen sulfide

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