WO1994014703A1 - Method for desulfurizing a gas - Google Patents
Method for desulfurizing a gas Download PDFInfo
- 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
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- oxide
- iron
- solid substance
- molybdenum
- aluminum
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Ceased
Links
Classifications
-
- 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)
- Chemical Kinetics & Catalysis (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Materials Engineering (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Treating Waste Gases (AREA)
Abstract
Description
Claims
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 |
|---|---|
| WO1994014703A1 true WO1994014703A1 (en) | 1994-07-07 |
Family
ID=19861700
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/NL1993/000281 Ceased WO1994014703A1 (en) | 1992-12-29 | 1993-12-29 | Method for desulfurizing a gas |
Country Status (7)
| Country | Link |
|---|---|
| EP (1) | EP0684931B1 (en) |
| 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)
| 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)
| 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 |
-
1992
- 1992-12-29 NL NL9202283A patent/NL9202283A/en not_active Application Discontinuation
-
1993
- 1993-12-29 EP EP94904346A patent/EP0684931B1/en not_active Expired - Lifetime
- 1993-12-29 AU AU58439/94A patent/AU5843994A/en not_active Abandoned
- 1993-12-29 WO PCT/NL1993/000281 patent/WO1994014703A1/en not_active Ceased
- 1993-12-29 ES ES94904346T patent/ES2120007T3/en not_active Expired - Lifetime
- 1993-12-29 ZA ZA939766A patent/ZA939766B/en unknown
- 1993-12-29 DE DE69319625T patent/DE69319625T2/en not_active Expired - Fee Related
Patent Citations (4)
| 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)
| 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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