WO1994014703A1 - Method for desulfurizing a gas - Google Patents

Method for desulfurizing a gas Download PDF

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Publication number
WO1994014703A1
WO1994014703A1 PCT/NL1993/000281 NL9300281W WO9414703A1 WO 1994014703 A1 WO1994014703 A1 WO 1994014703A1 NL 9300281 W NL9300281 W NL 9300281W WO 9414703 A1 WO9414703 A1 WO 9414703A1
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Prior art keywords
oxide
iron
solid substance
molybdenum
aluminum
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PCT/NL1993/000281
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French (fr)
Inventor
John Wilhelm Geus
Renee Van Yperen
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Kiwa Gastec Holding NV
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Gastec NV
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Priority to AU58439/94A priority Critical patent/AU5843994A/en
Priority to EP94904346A priority patent/EP0684931B1/en
Priority to DE69319625T priority patent/DE69319625T2/en
Publication of WO1994014703A1 publication Critical patent/WO1994014703A1/en
Anticipated expiration legal-status Critical
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    • 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
    • B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/46—Removing components of defined structure
    • B01D53/48—Sulfur compounds
    • B01D53/52—Hydrogen sulfide
    • 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
    • B01D53/86—Catalytic processes
    • B01D53/8603—Removing sulfur compounds
    • B01D53/8612—Hydrogen sulfide
    • 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
    • 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
    • B01J27/186—Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J27/188—Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium with chromium, molybdenum, tungsten or polonium
    • B01J27/19—Molybdenum
    • C—CHEMISTRY; METALLURGY
    • C01—INORGANIC CHEMISTRY
    • C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00—Sulfur; Compounds thereof
    • C01B17/02—Preparation of sulfur; Purification
    • C01B17/04—Preparation of sulfur; Purification from gaseous sulfur compounds including gaseous sulfides
    • C—CHEMISTRY; METALLURGY
    • C01—INORGANIC CHEMISTRY
    • C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00—Sulfur; Compounds thereof
    • C01B17/48—Sulfur dioxide; Sulfurous acid
    • C01B17/50—Preparation of sulfur dioxide
    • C01B17/508—Preparation of sulfur dioxide by oxidation of sulfur compounds

Definitions

  • This invention relates to a method for desulfurizing gases by absorption of H 2 S on absorbents based on metal oxides provided on a support.
  • sulfur compounds supplied by buyers or are released into the atmosphere, be purified of sulfur compounds, in particular hydrogen sulfide.
  • a problem associated with the gasification of coal or heavy petroleum fractions is that hydrogen sulfide is formed. Hydrogen sulfide should be removed because of its corrosive character and its poisonousness to catalysts which are used to convert such gases into useful compounds. In the case where the sulfur-containing gas is used as fuel gas, for instance in power stations, the hydrogen sulfide content, for
  • the aim is to keep the H 2 S content below 25 ppm, preferably below 10 ppm.
  • Examples include compounds of iron, magnesium, calcium, boron, copper, cerium, molybdenum, yttrium, lanthanum, cobalt and zinc. Substantially all of these compounds were tested as oxides, hydroxides or carbonates, in the form of granules sintered with fly ash. The best results were obtained with sintered granules comprising 75% fly ash with 25% iron oxide. At approx. 800°C, these yielded an absorption capacity of approximately 40 g sulfur per 100 g absorbent.
  • absorbents exhibit the same drawback as described hereinabove with respect to bulk metal oxides, viz. disintegration during absorption and during regeneration.
  • the object of the invention is to provide a method for removing hydrogen sulfide from gas streams, in which the problems outlined do not occur or do so to a much lesser extent.
  • the invention relates to a method for removing H 2 S from gases, comprising contacting the gases with an absorbent based on at least one metal oxide on support, with aluminum
  • the absorbent When used as absorbent, no problems with regard to metal sulfate formation occur, not even if a major proportion of aluminum relative to the phosphate is present in the support. Accordingly, the absorbent is particularly easy to regenerate. In this connection, it is not necessary to make use of a multi-stage regeneration process.
  • Another advantage of the present invention resides in the fact that the support, at the temperatures used in high- temperature desulfurization, is particularly stable and will retain its original structure completely or substantially completely, even in the case of prolonged use and frequent regeneration.
  • the structure of the amorphous aluminum phosphate support can be adjusted particularly well by varying the conditions of preparation, such as pH, temperature and the aluminum to phosphate ratio. In this connectiom, it is for instance possible to work with a minor proportion of aluminum or with a major proportion of aluminum relative to the stoichiometric amount that is required. It is also possible to work with substantially stoichiometric amounts of aluminum and
  • the aluminum phosphate support material can be prepared in various manners. In general, the preparation will start from separate aqueous solutions of a soluble phosphate and a soluble aluminum compound. From the viewpoint of solubility, aluminum nitrate and ammonium phosphate are preferred. The solutions are put together, whereby aluminum phosphate
  • This can be effected by simultaneously injecting both solutions at preferably constant pH into a reactor in which, if desired, water or an aqueous solution may already be present. It is also possible to initially provide either solution in the reactor and inject the other solution. In general, this will not be done at constant pH .
  • the solid substance functions as regenerable absorbent
  • metal component on the aluminum phosphate support one or more metal compounds are used which act as absorbent for H 2 S.
  • the metal component is selected from the suitable metals for absorption, such as calcium,
  • these metals will be used in the form of their oxides, although hydroxides or carbonates are also possible.
  • the distribution of the metal component over the support is of importance since a poor distribution detracts from the absorbing power.
  • the active component is preferably present on the support as homogeneously as possible. This can be realized through accurate selection of the method of application and/or through the choice of the loading degree.
  • the specific surface preferably amounts to 5 to 500 m 2 /g, whilst the average pore diameter, based on cylindrical pores, is between 1 and 100 nm.
  • specific surface is understood to mean the BET surface as defined by S. Brunauer et al. in J.A.C.S. 60, 309 (1938). Use was made of a nitrogen adsorption at 77 K according to the so-called three-point measurement. For the purpose of the calculation, the surface of a nitrogen molecule was assumed to be 16.2 A 2 .
  • the average pore radius is determined starting from a cylindrical pore model using the following formula:
  • the pore volume used herein is gravimetrically determined by impregnation with water under vacuum.
  • the specific pore volume can further be determined using mercury porosimetry up to a pressure of 2000 bar. The values obtained with the two methods show a good correspondence.
  • the hydrogen sulfide content should naturally be significantly lower.
  • the aim is for a content of 25 ppm at most, more particularly 10 ppm at most.
  • the adjustment of the H 2 S content in the treated gas can be effected by varying the time of contact between the gas and the absorbent. On the one hand, this can be effected by varying the gas rate and, on the other, by varying the amount and the height of the bed in which the absorbent is provided. Suitable contact times lie between 0.01 and 10 seconds.
  • the greater part of the hydrogen sulfide will react with the metal oxide to form metal sulfide.
  • the regeneration of the absorbent thus loaded with sulfur is accordingly effected through conversion of the metal sulfide with oxygen to form metal oxide.
  • the sulfur can be obtained in the form of elemental sulfur, SO 2 , 2r mixtures thereof.
  • substantially elemental sulfur is obtained in the gas. Since sulfur can easily cause stoppages .in the further equipment, it is preferred to condense this sulfur directly after the regeneration.
  • the contact takes place at a temperature of 150 to 400°C in the case of absorbent based on molybdenum (VI) oxide; and at a temperature of 150 to 625°C, preferably 400 to 625°C, if the absorbent is based on iron (II) molybdate or a combination of iron and molybdenum oxide.
  • substantially iron oxide working at temperatures of at least 600°C is
  • the absorbents are preferably made by homogeneous
  • the starting-point is an absorbent based on molybdenum, tungsten and/or iron oxides as absorbent component. More particularly molybdenum oxides, iron oxide or combinations thereof are preferred.
  • the molybdenum oxide may be any suitable molybdenum oxide or mixture containing molybdenum oxide.
  • the absorbent preferably comprises an active component selected from the group consisting of iron (II) oxide,
  • iron (III) oxide mixed oxides of iron (II) oxide and
  • iron (III) oxide molybdenum (VI) oxide, iron molybdate, mixtures of iron (II) oxide and/or iron (III) oxide with
  • the amount of metal component provided on the support is not critical. This amount can vary within wide limits.
  • the suitable amounts are related to the specific surface of the support and will lie between 1 and 75 wt.%, more particularly between 1 and 50 wt.%.
  • the aim is to have a highest possible content of metal component, finely distributed, present on the support since this enables a highest possible loading thereof.
  • It is preferred to utilize a particle size of 0.1 ⁇ m at a maximum, more particularly 0.05 ⁇ m at a maximum.
  • the lower limit of the particle size is not very critical and is preferably at least 1 nm.
  • the method according to the invention is especially suitable for treating large amounts of hot gases which may, for instance, originate from the gasification of coal or oil Such gases are typically used as fuel gas in power stations and other gas-fueled installations. It is also possible to convert such gases catalytically to other compounds, such a ⁇ ammonia, methanol or higher hydrocarbons, for instance via a Fischer Tropsch synthesis.
  • absorbents were prepared by homogeneous deposition precipitation, as described in J.W. Geus, Prep, of Cat. Ill, ed. G. Poncelet et al. (1983) pp. 1-25.
  • the absorbents based on molybdenum or silicon dioxide were prepared by injection of an aqueous solution of molybdenum (III) chloride under the surface of a vigorously stirred suspension of silicon dioxide (Aerosil 200, Degussa) at a constant pH of 5.
  • molybdenum (III) chloride was prepared through electrochemical reduction of an aqueous solution of ammonium-hepta-molybdate (Merck p. a.) at pH 1.
  • Iron molybdate on silicon dioxide was prepared by
  • absorbents were filtered and dried overnight at 120°C. The absorbents were tabletted and broken again. A sieve fraction between 150 and 500 ⁇ m was separated and calcined in the air at 500°C at a heating rate of 5°C/minute. After reaching 500°C it was maintained at that temperature for one hour.
  • the test procedure which was followed in testing the divers absorbents was carried out with an appliance as described in Fig 1.
  • This appliance comprised a gas stream control system with a mass-controlled feed of various gases, magnetic valves, and saturator and reactor oven and analyzing equipment.
  • the gas was analyzed using a thermal conductivity detector (TCD) and a UV-VI spectrophotometer, Varian Cary 1.
  • TCD thermal conductivity detector
  • UV-VI spectrophotometer Varian Cary 1.
  • the hydrogen sulfide concentration was measured at 232 nm and the sulfur dioxide concentration at 262 nm.
  • the experiments consisted of a number of absorption and regeneration cycli, temperature-programmed reductions and oxidations, during which the hydrogen sulfide and sulfur dioxide concentrations were monitored.
  • the absorption step was generally preceded by a reduction step i which any iron sulfates formed were reduced in 10% hydrogen at the same temperature as the absorption step.
  • the absorbent was regenerated with a reaction mixture of 2 vol.% oxygen in argon under otherwise equal conditions.
  • Figure 2 shows a hydrogen sulfide absorption curve of 12 wt.% iron oxide and 10 wt.% molybdenum oxide on aluminum phosphate absorbent PFe 12 Mo 10 .
  • a similar characteristic curve is obtained as with absorbents based on silicon dioxide.
  • the capacity is somewhat smaller because of interaction of a part of the active compounds with the phosphate groups. The fact is the metal phosphates are not active in the absorption of hydrogen sulfide.

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
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  • Environmental & Geological Engineering (AREA)
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  • Inorganic Chemistry (AREA)
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Abstract

The invention relates inter alia to a new method for removing H2S from all sorts of gases, comprising contacting the gases with at least one solid substance comprising at least one solid metal component, preferably a solid metal oxide, on a support, with aluminum phosphate being used as support.

Description

Title: Method for desulfurizing a gas.
This invention relates to a method for desulfurizing gases by absorption of H2S on absorbents based on metal oxides provided on a support.
It is generally known that it is necessary that gases which are further processed in chemical processes, are
supplied by buyers or are released into the atmosphere, be purified of sulfur compounds, in particular hydrogen sulfide.
A problem associated with the gasification of coal or heavy petroleum fractions is that hydrogen sulfide is formed. Hydrogen sulfide should be removed because of its corrosive character and its poisonousness to catalysts which are used to convert such gases into useful compounds. In the case where the sulfur-containing gas is used as fuel gas, for instance in power stations, the hydrogen sulfide content, for
environmental reasons and because of its corrosive action, should preferably be below 100 ppm. In the case where the gas is used as feed for catalytic conversions, the aim is to keep the H2S content below 25 ppm, preferably below 10 ppm.
Accordingly, a number of methods are known which are directed to the removal of hydrogen sulfide from gas.
There are a large number of methods known for the removal of hydrogen sulfide from gas streams by adsorption or
absorption on solid substances. In the purification of gas streams coming from the gasification of coal or oil, for instance, involving particularly large amounts having a high temperature, often metal oxides are used for that purpose. Very typical are so-called bulk metal oxides, but the
disintegration thereof during the absorption and regeneration results in dust formation, which renders these materials little attractive. The problem of disintegration can at least partly be overcome by the use of highly dispersed metal oxide on a stable support. For such purposes, it is known to use silicon dioxide as a support for iron oxide. In the literature (EP-A-71, 983 ) an iron oxide absorbent on silicon dioxide is described, which exhibits a good conversion degree and stability.
The publication by Abel, Shultz and Langdon, Bur. Mines RI 7947 (1974) describes the results of an investigation into the usefulness of a large number of solid absorbents for the removal of hydrogen sulfide from hot gases. It appears from this publication that a large number of compounds, mainly metal compounds, exhibit an absorption of hydrogen sulfide.
Examples include compounds of iron, magnesium, calcium, boron, copper, cerium, molybdenum, yttrium, lanthanum, cobalt and zinc. Substantially all of these compounds were tested as oxides, hydroxides or carbonates, in the form of granules sintered with fly ash. The best results were obtained with sintered granules comprising 75% fly ash with 25% iron oxide. At approx. 800°C, these yielded an absorption capacity of approximately 40 g sulfur per 100 g absorbent. These
absorbents exhibit the same drawback as described hereinabove with respect to bulk metal oxides, viz. disintegration during absorption and during regeneration.
The article by Furimsky at al, Solid adsorbents for removal of hydrogen sulfide from hot gases, Wissenschaft & Technik, Bd. 39, Heft 4, April 1986, pp. 163-172, gives an overview of absorbents described in the literature for the absorption of hydrogen sulfide from hot gases. Examples of absorbents described therein include compounds of calcium, magnesium, iron, manganese, zinc, molybdenum, tungsten, nickel, cobalt, barium, vanadium and copper. According to the authors, deactivated cracking catalysts based on molybdenum, cobalt and nickel on aluminum oxide, after the cokes are burnt off, are suitable as absorbent.
The absorbents described in this article, too, exhibit the above-indicated drawbacks of disintegration and the associated dust formation. In the deactivated cracking catalysts referred to, this is caused by the reaction of the aluminum oxide to form sulfate. Further, a large number of the materials described have the disadvantage of a slight
temperature resistance, which, after some time, leads to sintering and accordingly to loss of activity. A number of materials moreover exhibit the property of volatilizing at higher temperatures, which is undesired in view of the
environment and the loading degree.
Finally, a number of prior art materials present a problem in that they are very difficult to regenerate, if at all.
The object of the invention is to provide a method for removing hydrogen sulfide from gas streams, in which the problems outlined do not occur or do so to a much lesser extent.
The invention relates to a method for removing H2S from gases, comprising contacting the gases with an absorbent based on at least one metal oxide on support, with aluminum
phosphate being used as support.
Surprisingly, it has been found that when such support materials based on amorphous, non-crystalline aluminum
phosphate are used in the removal of hydrogen sulfide from gas streams, the disadvantages referred to do not occur or do so to a much lesser extent, while moreover a number of unexpected advantages are present.
When used as absorbent, no problems with regard to metal sulfate formation occur, not even if a major proportion of aluminum relative to the phosphate is present in the support. Accordingly, the absorbent is particularly easy to regenerate. In this connection, it is not necessary to make use of a multi-stage regeneration process.
Another advantage of the present invention resides in the fact that the support, at the temperatures used in high- temperature desulfurization, is particularly stable and will retain its original structure completely or substantially completely, even in the case of prolonged use and frequent regeneration. The structure of the amorphous aluminum phosphate support can be adjusted particularly well by varying the conditions of preparation, such as pH, temperature and the aluminum to phosphate ratio. In this connectiom, it is for instance possible to work with a minor proportion of aluminum or with a major proportion of aluminum relative to the stoichiometric amount that is required. It is also possible to work with substantially stoichiometric amounts of aluminum and
phosphate.
Surprisingly, it has been found that with the invention, it is no problem if an aluminum phosphate is used comprising amounts of aluminum and phosphate deviating from the
stoichiometric amount. Although it could be expected that in particular the use of a major proportion of aluminum would give rise to problems of sulfate and sulfide formation, it has been found that such is not the case at all.
The aluminum phosphate support material can be prepared in various manners. In general, the preparation will start from separate aqueous solutions of a soluble phosphate and a soluble aluminum compound. From the viewpoint of solubility, aluminum nitrate and ammonium phosphate are preferred. The solutions are put together, whereby aluminum phosphate
precipitates.
This can be effected by simultaneously injecting both solutions at preferably constant pH into a reactor in which, if desired, water or an aqueous solution may already be present. It is also possible to initially provide either solution in the reactor and inject the other solution. In general, this will not be done at constant pH .
According to the first embodiment of the method according to the invention, in which the solid substance functions as regenerable absorbent, as metal component on the aluminum phosphate support one or more metal compounds are used which act as absorbent for H2S. The metal component is selected from the suitable metals for absorption, such as calcium,
magnesium, iron, manganese, zinc, molybdenum, tungsten, nickel, cobalt, barium, vanadium and copper, or combinations of two or more of these metals. In general, these metals will be used in the form of their oxides, although hydroxides or carbonates are also possible.
The distribution of the metal component over the support is of importance since a poor distribution detracts from the absorbing power. The active component is preferably present on the support as homogeneously as possible. This can be realized through accurate selection of the method of application and/or through the choice of the loading degree.
The specific surface preferably amounts to 5 to 500 m2/g, whilst the average pore diameter, based on cylindrical pores, is between 1 and 100 nm.
Within the concept of the invention, specific surface is understood to mean the BET surface as defined by S. Brunauer et al. in J.A.C.S. 60, 309 (1938). Use was made of a nitrogen adsorption at 77 K according to the so-called three-point measurement. For the purpose of the calculation, the surface of a nitrogen molecule was assumed to be 16.2 A2.
The average pore radius is determined starting from a cylindrical pore model using the following formula:
Average pore radius (Å) = 20,000 x pore volume (cm3/g)
BET surface (m2/g)
The pore volume used herein is gravimetrically determined by impregnation with water under vacuum. The specific pore volume can further be determined using mercury porosimetry up to a pressure of 2000 bar. The values obtained with the two methods show a good correspondence.
The extent of removal of the hydrogen sulfide will be adjusted depending on the application contemplated. For the less critical applications, the typical aim is for the H2S content not to exceed 100 ppm. When 'using catalytic
conversions of the treated gas with sulfur-sensitive
catalysts, the hydrogen sulfide content should naturally be significantly lower. For such applications, the aim is for a content of 25 ppm at most, more particularly 10 ppm at most.
The adjustment of the H2S content in the treated gas can be effected by varying the time of contact between the gas and the absorbent. On the one hand, this can be effected by varying the gas rate and, on the other, by varying the amount and the height of the bed in which the absorbent is provided. Suitable contact times lie between 0.01 and 10 seconds.
During the absorption of hydrogen sulfide, the greater part of the hydrogen sulfide will react with the metal oxide to form metal sulfide. The regeneration of the absorbent thus loaded with sulfur is accordingly effected through conversion of the metal sulfide with oxygen to form metal oxide.
Depending on the amount of oxygen used, the sulfur can be obtained in the form of elemental sulfur, SO2, 2r mixtures thereof.
In the case where relatively little oxygen is used in the regeneration, substantially elemental sulfur is obtained in the gas. Since sulfur can easily cause stoppages .in the further equipment, it is preferred to condense this sulfur directly after the regeneration.
When a large excess of oxygen is used, all of the sulfur is released in the form of SO2. If desired, this can be separated and/or further processed in known manner.
The advantages of the present invention are especially evident in the desulfurization at very high temperatures.
These temperatures generally lie above 150°C and more
particularly between 400 and 625°C. At these temperatures, therefore, it is possible to regenerate the absorbent, the regeneration being preferably effected at a temperature substantially comparable with that of the absorption.
According to the invention, it is preferred that the contact takes place at a temperature of 150 to 400°C in the case of absorbent based on molybdenum (VI) oxide; and at a temperature of 150 to 625°C, preferably 400 to 625°C, if the absorbent is based on iron (II) molybdate or a combination of iron and molybdenum oxide. When substantially iron oxide is used, working at temperatures of at least 600°C is
advantageous, since at lower temperatures iron sulfate is stable and the absorbent can therefore not be simply
regenerated.
The absorbents are preferably made by homogeneous
deposition precipitation of the metal component or precursor therefor on the finished support. This method is described in J.W. Geus, Prep, of Cat. Ill, ed. G. Poncelet et al. (1983) pp. 1-25.
According to a preferred embodiment of the invention, the starting-point is an absorbent based on molybdenum, tungsten and/or iron oxides as absorbent component. More particularly molybdenum oxides, iron oxide or combinations thereof are preferred. In practice, the molybdenum oxide may be any suitable molybdenum oxide or mixture containing molybdenum oxide.
The absorbent preferably comprises an active component selected from the group consisting of iron (II) oxide,
iron (III) oxide, mixed oxides of iron (II) oxide and
iron (III) oxide, molybdenum (VI) oxide, iron molybdate, mixtures of iron (II) oxide and/or iron (III) oxide with
molybdenum (VI) oxide and mixtures of iron molybdate with molybdenum (VI) oxide and/or iron (II) oxide and/or
iron (III) oxide.
In general, the amount of metal component provided on the support is not critical. This amount can vary within wide limits. The suitable amounts are related to the specific surface of the support and will lie between 1 and 75 wt.%, more particularly between 1 and 50 wt.%. Naturally, the aim is to have a highest possible content of metal component, finely distributed, present on the support since this enables a highest possible loading thereof. It, is preferred to utilize a particle size of 0.1 μm at a maximum, more particularly 0.05 μm at a maximum. The lower limit of the particle size is not very critical and is preferably at least 1 nm. The method according to the invention is especially suitable for treating large amounts of hot gases which may, for instance, originate from the gasification of coal or oil Such gases are typically used as fuel gas in power stations and other gas-fueled installations. It is also possible to convert such gases catalytically to other compounds, such aε ammonia, methanol or higher hydrocarbons, for instance via a Fischer Tropsch synthesis.
The invention will now be illustrated in and by some examples without being limited thereto.
EXAMPLES
1 Experimental procedures
1.1 Preparation of the absorbents
All absorbents were prepared by homogeneous deposition precipitation, as described in J.W. Geus, Prep, of Cat. Ill, ed. G. Poncelet et al. (1983) pp. 1-25. The absorbents based on molybdenum or silicon dioxide were prepared by injection of an aqueous solution of molybdenum (III) chloride under the surface of a vigorously stirred suspension of silicon dioxide (Aerosil 200, Degussa) at a constant pH of 5. The
molybdenum (III) chloride was prepared through electrochemical reduction of an aqueous solution of ammonium-hepta-molybdate (Merck p. a.) at pH 1.
Iron molybdate on silicon dioxide was prepared by
coprecipitation of an iron and molybdenum precursor on the support. The use of a solution of iron (III) chloride was not possible because of the redox reaction between Fe3+ and
Mo3+ ions. This resulted in reduction of the iron (III) ions and oxidation of the molybdenum (III) ions. Accordingly, a mixture of iron (II) chloride and molybdenum (III) chloride was used to prevent the formation of molybdenum with a higher valency. The aqueous solution of iron (II) was obtained by dissolving iron powder (Baker 99.99%) in concentrated hydrochloric acid (Merck p .a.).
Utilizing aluminum phosphate as support, we used only the coprecipitation method. In this method Fe3+ and Mo6- were used as precursor. The preparation of aluminum phosphate with an aluminum/phosphate ratio of 2 took place at pH 5.
After the homogeneous deposition precipitation, the
absorbents were filtered and dried overnight at 120°C. The absorbents were tabletted and broken again. A sieve fraction between 150 and 500 μm was separated and calcined in the air at 500°C at a heating rate of 5°C/minute. After reaching 500°C it was maintained at that temperature for one hour.
In the following table the various absorbents are included.
Figure imgf000011_0001
1) Coprecipitation of iron(II) and molybdenum ( III)
2) Coprecipitation of iron (III) and molybdenum (IV)
The test procedure which was followed in testing the divers absorbents was carried out with an appliance as described in Fig 1. This appliance comprised a gas stream control system with a mass-controlled feed of various gases, magnetic valves, and saturator and reactor oven and analyzing equipment. The gas was analyzed using a thermal conductivity detector (TCD) and a UV-VI spectrophotometer, Varian Cary 1. With the last, the hydrogen sulfide concentration was measured at 232 nm and the sulfur dioxide concentration at 262 nm. The experiments consisted of a number of absorption and regeneration cycli, temperature-programmed reductions and oxidations, during which the hydrogen sulfide and sulfur dioxide concentrations were monitored.
During the absorption procedure, use was made of a sample size of 1.5 ml, a reaction mixture of 1 vol.% hydrogen sulfide and 10 vol. % hydrogen in argon with a total amount of
100 ml/minute, a speed of 4000 hour-1 and a temperature of 400°C. The absorption step was generally preceded by a reduction step i which any iron sulfates formed were reduced in 10% hydrogen at the same temperature as the absorption step. After the absorptio procedure the absorbent was regenerated with a reaction mixture of 2 vol.% oxygen in argon under otherwise equal conditions.
During the temperature-programmed reduction 10 vol. % hydrogen in argon was used and the temperature was increased by 4°C/minute. For the temperature-programmed oxidation a gas mixture of 2 vol.% oxygen in argon was used. During two
experiments the reactor was flushed with argon for 10 minutes.
Since the preparation of iron molybdate on silicon dioxide is rather cumbersome, tests were performed with an absorbent on aluminum phosphate. Owing to the positive interaction of the metal precursors with the phosphate groups on the surface of the support, the use of iron(III) and molybdenum (VI) ions is
possible. Figure 2 shows a hydrogen sulfide absorption curve of 12 wt.% iron oxide and 10 wt.% molybdenum oxide on aluminum phosphate absorbent PFe12Mo10. A similar characteristic curve is obtained as with absorbents based on silicon dioxide. The capacity, however, is somewhat smaller because of interaction of a part of the active compounds with the phosphate groups. The fact is the metal phosphates are not active in the absorption of hydrogen sulfide.
The use of aluminum phosphate as support accordingly simplifies the preparation of iron molybdates considerably. The interaction of the metal precursors with the phosphate groups at the surface make it possible to use iron (III) and molybdenum (VI) as precursor during precipitation. As a result, a hig h deqree or dispersion and thermal stability is obtained.

Claims

1. A method for removing H2S from gases, comprising
contacting the gases with a solid substance comprising at least one metal component, preferably a metal oxide, on support, with aluminum phosphate being used as support.
2. A method according to claim 1, characterized in that a metal component is used which is selected from the group consisting of compounds of calcium, magnesium, iron,
manganese, zinc, molybdenum, tungsten, chromium, nickel, cobalt, barium, vanadium and copper, or combinations of two or more of these metals.
3. A method according to claim 2, characterized in that as metal component a compound is used which is selected from the group consisting of compounds of iron, molybdenum and
tungsten, compounds of two or more of these metals and mixtures of two or more of these compounds.
4. A method according to claim 3, characterized in that a metal component is used which is selected from the group consisting of iron (II) oxide, iron (III) oxide, mixed oxides of iron (II) oxide and iron (III) oxide, molybdenum (VI) oxide, iron molybdate, mixtures of iron (II) oxide and/or iron (III) oxide with molybdenum (VI) oxide and mixtures of iron molybdate with molybdenum (VI) oxide and/or iron (II) oxide and/or
iron (III) oxide.
5. A method according to claims 1-4, characterized in that the content of support material is between 25 and 99 wt.%.
6. A method according to claims 1-5, characterized in that in the aluminum phosphate support material a major proportion of aluminum with regard to phosphate groups is present.
7. A method according to claims 1-5, characterized in that in the aluminum phosphate a minor proportion of aluminum with regard to phosphate groups is present.
8. A method according to claims 1-5, characterized in that in the aluminum phosphate a substantially stoichiometric
amount of aluminum with regard to phosphate groups is present.
9. A method according to claims 1-8, characterized in that the gases are contacted with the solid substance for
absorption of the hydrogen sulfide, followed by regeneration of the loaded solid substance at a temperature of 150 to
800°C, preferably of 150 to 625°C.
10. A method according to claim 9, characterized in that the regeneration takes place
at a temperature of 150 to 400°C if the solid substance is based on molybdenum oxide or tungsten oxide;
at a temperature of 150 to 525°C, preferably 400 to 625°C, if the solid substance is based on a combination of molybdenum oxide and/or tungsten oxide with at least one iron oxide;
and
at a temperture of at least 600°C if the solid substance is based on an iron oxide.
11. A method according to claims 1-10, characterized in that the solid substance has a specific surface of 5 to 500 m2/g.
12. A method according to claims 1-11, characterized in that the solid substance has an average pore diameter of 1 to 100 nm.
13. A method according to claims 3-12, characterized in that the molar ratio Fe/Mo is 0 to 20.
14. A method according to claims 1-13, wherein the solid substance comprises 5 to 25 wt.% iron oxide.
15. A method according to claims 1-14, wherein the gas to be desulfurized is selected from the group consisting of gases originating from gasification of coal and of oil.
16. A method according to claims 1-15, wherein the treatment with the solid substance occurs under conditions such that the H2S content in the treated gas is 100 ppm at a maximum, more particularly 25 ppm at a maximum.
17. A method according to claims 1-16, wherein the contact time between gas and the solid substance is between 0.01 and 10 s.
PCT/NL1993/000281 1992-12-29 1993-12-29 Method for desulfurizing a gas Ceased WO1994014703A1 (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
AU58439/94A AU5843994A (en) 1992-12-29 1993-12-29 Method for desulfurizing a gas
EP94904346A EP0684931B1 (en) 1992-12-29 1993-12-29 Method for desulfurizing a gas
DE69319625T DE69319625T2 (en) 1992-12-29 1993-12-29 METHOD FOR THE DESOLUTIONATION OF A GAS

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
NL9202283 1992-12-29
NL9202283A NL9202283A (en) 1992-12-29 1992-12-29 Method for desulfurizing a gas.

Publications (1)

Publication Number Publication Date
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AU (1) AU5843994A (en)
DE (1) DE69319625T2 (en)
ES (1) ES2120007T3 (en)
NL (1) NL9202283A (en)
WO (1) WO1994014703A1 (en)
ZA (1) ZA939766B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2005056164A1 (en) * 2003-12-05 2005-06-23 Jayalekshmy Ayyer A catalyst useful for h2s removal from gas stream preparation thereof and use thereof
CN100488605C (en) * 2003-12-05 2009-05-20 贾亚来克西米·艾耶尔 Catalysts for removing H2S from gas streams, methods for their preparation and uses thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4311683A (en) * 1976-06-28 1982-01-19 Union Oil Company Of California Process for removal of hydrogen sulfide from gas streams
EP0242920A1 (en) * 1986-04-16 1987-10-28 Veg-Gasinstituut N.V. A catalyst for the selective oxidation of sulfur containing compounds, in particular hydrogen sulfide, to elemental sulfur; a process for the preparation of the catalyst; and a process for the selective oxidation of sulfur containing compounds in particular hydrogen sulfide, to elemental sulfur
US4743574A (en) * 1986-01-09 1988-05-10 Intevep, S.A. Catalyst for hydrotreatment of distillates of petroleum and method for the preparation of same
EP0409353A1 (en) * 1989-07-21 1991-01-23 Gastec N.V. Catalyst and process for the selective oxidation of hydrogen sulphide to elemental sulphur

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4311683A (en) * 1976-06-28 1982-01-19 Union Oil Company Of California Process for removal of hydrogen sulfide from gas streams
US4743574A (en) * 1986-01-09 1988-05-10 Intevep, S.A. Catalyst for hydrotreatment of distillates of petroleum and method for the preparation of same
EP0242920A1 (en) * 1986-04-16 1987-10-28 Veg-Gasinstituut N.V. A catalyst for the selective oxidation of sulfur containing compounds, in particular hydrogen sulfide, to elemental sulfur; a process for the preparation of the catalyst; and a process for the selective oxidation of sulfur containing compounds in particular hydrogen sulfide, to elemental sulfur
EP0409353A1 (en) * 1989-07-21 1991-01-23 Gastec N.V. Catalyst and process for the selective oxidation of hydrogen sulphide to elemental sulphur

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2005056164A1 (en) * 2003-12-05 2005-06-23 Jayalekshmy Ayyer A catalyst useful for h2s removal from gas stream preparation thereof and use thereof
CN100488605C (en) * 2003-12-05 2009-05-20 贾亚来克西米·艾耶尔 Catalysts for removing H2S from gas streams, methods for their preparation and uses thereof

Also Published As

Publication number Publication date
AU5843994A (en) 1994-07-19
NL9202283A (en) 1994-07-18
EP0684931B1 (en) 1998-07-08
EP0684931A1 (en) 1995-12-06
DE69319625T2 (en) 1998-11-05
ES2120007T3 (en) 1998-10-16
ZA939766B (en) 1994-08-15
DE69319625D1 (en) 1998-08-13

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