WO1998027008A1 - Process for recovering sulfur hexafluoride - Google Patents

Process for recovering sulfur hexafluoride Download PDF

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Publication number
WO1998027008A1
WO1998027008A1 PCT/US1997/022588 US9722588W WO9827008A1 WO 1998027008 A1 WO1998027008 A1 WO 1998027008A1 US 9722588 W US9722588 W US 9722588W WO 9827008 A1 WO9827008 A1 WO 9827008A1
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WIPO (PCT)
Prior art keywords
sulfur hexafluoride
gas stream
pressure
contacting
adsorbent
Prior art date
Application number
PCT/US1997/022588
Other languages
French (fr)
Inventor
Stephen Frederic Yates
Romulus Gaita
Amar Ramachandra
Robert Morrell
Original Assignee
Alliedsignal Inc.
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Publication date
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Application filed by Alliedsignal Inc. filed Critical Alliedsignal Inc.
Priority to DE69720772T priority Critical patent/DE69720772T2/en
Priority to AU53790/98A priority patent/AU5379098A/en
Priority to EP97950910A priority patent/EP0946410B1/en
Priority to JP52779498A priority patent/JP2001508390A/en
Priority to CA002274570A priority patent/CA2274570A1/en
Publication of WO1998027008A1 publication Critical patent/WO1998027008A1/en

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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00Sulfur; Compounds thereof
    • C01B17/45Compounds containing sulfur and halogen, with or without oxygen
    • C01B17/4507Compounds containing sulfur and halogen, with or without oxygen containing sulfur and halogen only
    • C01B17/4515Compounds containing sulfur and halogen, with or without oxygen containing sulfur and halogen only containing sulfur and fluorine only
    • C01B17/453Sulfur hexafluoride
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00Sulfur; Compounds thereof
    • C01B17/45Compounds containing sulfur and halogen, with or without oxygen
    • 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
    • B01D53/02Separation 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 adsorption, e.g. preparative gas chromatography
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/102Carbon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/106Silica or silicates
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/106Silica or silicates
    • B01D2253/108Zeolites
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/30Physical properties of adsorbents
    • B01D2253/302Dimensions
    • B01D2253/308Pore size
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2256/00Main component in the product gas stream after treatment
    • B01D2256/10Nitrogen
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2256/00Main component in the product gas stream after treatment
    • B01D2256/12Oxygen
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2256/00Main component in the product gas stream after treatment
    • B01D2256/16Hydrogen
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2256/00Main component in the product gas stream after treatment
    • B01D2256/18Noble gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/20Halogens or halogen compounds
    • B01D2257/202Single element halogens
    • B01D2257/2027Fluorine
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/50Carbon oxides
    • B01D2257/502Carbon monoxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/50Carbon oxides
    • B01D2257/504Carbon dioxide
    • 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
    • B01D53/02Separation 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 adsorption, e.g. preparative gas chromatography
    • B01D53/04Separation 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 adsorption, e.g. preparative gas chromatography with stationary adsorbents
    • B01D53/047Pressure swing adsorption
    • 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
    • Y02C20/30Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]
    • 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
    • Y02C20/40Capture or disposal of greenhouse gases of CO2
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/151Reduction of greenhouse gas [GHG] emissions, e.g. CO2

Definitions

  • the present invention relates to a process for recovering sulfur hexafluoride ("SF ⁇ "). More specifically, the invention provides a pressure swing adsorption - deso ⁇ tion process for recovering SF 6 from a gas stream.
  • SF ⁇ a non-flammable gas used in industry in a variety of applications
  • the product SF 6 typically must be treated to remove impurities.
  • some SF ⁇ may be lost as one component of a gaseous stream of the impurities removed from the product SF ⁇ .
  • the gas stream containing the impurities and some SF 6 may be vented to the atmosphere. Not only does this result in loss of some of the SF ⁇ produced, but it is environmentally undesirable because SF ⁇ is suspected of being a "green-house", global warming gas.
  • United States Patent No. 3,675,392 discloses the use of molecular sieves to separate water and carbon dioxide from SF S .
  • the process disclosed in this patent is a batch process and suitable only for gas streams in which SF ⁇ is the major component.
  • Japanese Patent Application No. 60-054723 discloses the removal of water and carbon dioxide from SF ⁇ using calcium hydride. This process is disadvantageous because calcium hydride is a dangerous material and has a relatively low capacity for removal of water and carbon dioxide.
  • None of the foregoing methods provide an industrial useful method for recovering SF6 from a gas stream in which SF 6 is a minor component. Therefore, a need exists for a cost-effective, efficient, industrial useful method for recovering SF 6 .
  • the invention provides a simple, economical method for recovering SF 6 from a gas stream.
  • the process of the invention comprises contacting a gas stream comprising a minor amount of SF ⁇ with an adsorbent capable of selectively adsorbing SF ⁇ under conditions suitable for the selective adso ⁇ tion of SF 6 from the gas stream.
  • the process additionally comprises regenerating SF 6 from the adsorbent.
  • the gas streams useful in the invention contain a minor amount of SF ⁇ along with at least one other component.
  • minor amount is meant less than about 50 volume percent, preferably less than about 20 volume percent, more preferably about 1 volume percent SF 6 based on the total volume of the gas stream.
  • the other component of the gas stream may be one or more non- condensible gases.
  • the component typically will be one or more of air, helium, argon, carbon monoxide, carbon dioxide, nitrogen, oxygen, neon, hydrogen, or carbon tetrafluoride. The process may find its greatest utility for gas streams in which carbon tetrafluoride is the other component or one of the other components.
  • Adsorbents useful in this invention are any adsorbents capable of selectively adsorbing SF ⁇ .
  • selective adsorbing is meant that the adsorbent has an affinity for SF 6 that is greater than its affinity for the other component or components in the gas stream.
  • the adsorbent has an affinity for SF ⁇ such that SF ⁇ is substantially entirely adsorbed from the gas stream while little or none of the other component or components is adsorbed.
  • Suitable adsorbents useful in the invention are commercially available. Examples of useful adsorbents include, without limitation, zeolites, activated carbons, and silicalite. Preferably, zeolites or activated carbons are used. More preferably, activated carbons are used as the adsorbent.
  • Zeolites that may be used in the process of the invention are natural or synthetic zeolites with mean pore sizes of greater than about 5, preferably from about 5 to about 20 A.
  • the zeolite used is X or Y Faujasite zeolite. More preferably, sodium X (13X) zeolite is used.
  • Activated carbons useful in the invention are any of the granular, activated carbons with a mesh of from about 4 to about 300, preferably from about 20 to about 50.
  • the activated carbon has a surface area of at least about 200 m 2 /g , preferably from about 1000 to about 1500 m 2 /g.
  • the activated carbon is PCBTM or ASCTM carbon available from Calgon Co ⁇ .
  • the amount of adsorbent used is an amount effective to allow the adso ⁇ tion cycle to run for the period desired before regeneration of the adsorbent is necessary. The precise amount of adsorbent used will be readily determinable by one ordinarily skilled in the art by considering the chosen adsorbent's capacity, the desired time period between adsorbent regenerations, and the flow rate of the SF 6 gas stream.
  • Contacting of the gas stream and adsorbents may take place in any manner known in the art. Preferably, contacting takes place by passing the gas stream through a fixed, packed bed of adsorbent. Passage of the gas stream takes place at a gas hourly space velocity of less than about 240, preferably less than about 100, h- 1 .
  • the contacting is performed under any conditions such that the selective adso ⁇ tion of SF 6 from the gas stream is facilitated. Accordingly, the temperature and pressure for contacting will be such that the temperature is greater, preferably about 10° C greater, than the boiling point of SF 6 for the contacting pressure. Preferably, contacting is performed at a temperature of from about 10 to about 40° C, preferably from about 25 to about 40° C. Most preferably, contacting is performed at room temperature.
  • the pressure at which contacting is carried out is at least about 5,170 torr (100 psia), preferably at least about 10,340 torr (200 psia).
  • SF ⁇ adsorbed in the contacting step may be regenerated from the adsorbent by any convenient manner.
  • the regeneration is performed by lowering the pressure to about 760 torr (14.7 psia), more preferably to about 100 torr (1.93 psia), most preferably to about 40 torr (0.77 psia) over the adsorbent bed releasing the SF 6 so that it may be collected.
  • the regeneration so performed may take place at temperatures of at least about 10° C, preferably at least about 25° C.
  • the time necessary to regenerate the SF 6 will depend on the amount of SF 6 adsorbed on the adsorbent as well as the amount of adsorbent used. Generally, regeneration will take place in from about 5 to about 40 hours.
  • the process of the invention may be used to recover SF ⁇ from any gas stream, but may find its greatest utility in recovering SF ⁇ from gas streams in which the SF ⁇ is present in a minor amount.
  • the SF ⁇ produced is typically distilled and purified SF ⁇ is removed as the column bottoms stream.
  • the column overhead stream will contain a minor amount of SF ⁇ as well as other components.
  • SF6 may be recovered from the overhead stream by using the process of the invention.
  • the process of the invention may be carried out using any suitable vessel.
  • a chromatography column with pipe fittings on either end Preferably, more than one vessel is used so that regeneration of the adsorbent in one column may be carried out without interruption of the SF ⁇ recovery.
  • Example 1 A 500 mL (14 in x 1.814 in i.d.) column was filled with 275 g dry 13X zeolite available from UOP Inc. A feed stream, prepared by mixing a stream of air flowing at 400 mL/min and a stream of SF 6 contaminated with 0.091 % carbon tetrafluoride flowing at 100 mL/min, was allowed to pass through the column at 25° C. The pressure in the column was adjusted to approximately 248 - 265 psia. Samples of the gas stream exiting the column were taken periodically and analyzed by gas chromatography. The concentration of SF 6 and CF 4 obtained by the analysis are shown on Table 1 The capacity of the adsorbent for SF ⁇ was calculated from the time required for the SF ⁇ concentration to reach 50 % of the feed concentration.
  • brackets denote concentrauon of CF 4 in weight percent.
  • the brackets denote concentrauon of SF 6 in weight percent.
  • Example 2 The procedure of Example 1 was used except that 215 g of CPG activated carbon, available from Calgon Co ⁇ ., were used as the adsorbent. The results are shown on Table 2. Table 2
  • Example 3 The procedure of Example 1 was used except that 332 g silicalite were used as the adsorbent. The results are shown on Table 3.
  • Example 4 The procedure of Example 1 was used except that 226 g F-400 activated carbon, available from the Calgon Co ⁇ ., were used as the adsorbent. The results are shown on Table 4.
  • Example 5 The procedure of Example 1 was used except that 225 g PCB activated carbon, available from Calgon Co ⁇ ., were used as the adsorbent. The results are shown on Table 5. Table 5
  • Example 6 The procedure of Example 1 was used except that 346.8g 5A zeolite, available from UOP Inc., were used as the adsorbent. The results are shown on Table 6. Table 6
  • Example 7 The procedure of Example 1 was used except that 287 g ASC activated carbon, available from Calgon Co ⁇ ., were used as the adsorbent. The results are shown on Table 7.
  • Example 8 The column of Example 1 was used and filled with 225 g dry PCB activated carbon, available from Calgon Co ⁇ .
  • the feed gas stream prepared by mixing a stream of air flowing at 400 mL/min and a stream of SF ⁇ contaminated with 2.25 % CF 4 flowing at 100 mL/min, was allowed to pass through the column at a temperature of 25° C.
  • the pressure in the column was adjusted to 248 - 265 psia. Samples of the gas stream exiting the column were taken periodically and analyzed by GC. The results are shown on Table 8.
  • the capacity for the adsorbent for SF 6 was calculated from the time required for the SF ⁇ concentration to reach 50 % of its feed concentration.
  • the CF broke through the column before the SF ⁇ and its concentration exceeds its feed concentration at the time of breakthrough. It is theorized that this indicates that the adsorbent had ' a stronger affinity for SF 6 than for CF 4 .
  • Example 9 The column of Example 1 was filled with 275 g dry, 13X zeolite.
  • a feed gas stream prepared by mixing a stream of air flowing at 400 mL/min and a stream of SF ⁇ contaminated with 0 091 % CF flowing at 100 mL/min, was allowed to pass through the column at a temperature of 25° C.
  • the column pressure was adjusted to 248 - 265 psia. Samples of the exiting gas stream were taken periodically and analyzed by GC. The results are shown in Table 9 on which the SF ⁇ concentrations are listed
  • the column was allowed to vent to an internal pressure of 760 torr (14.7 psia) for one hour.
  • the column was again used to purify the same SF ⁇ /air stream and monitored in the same way, the results of which are also found on Table 9.
  • the column then was again vented, this time for 20 hours, and again used to purify the same stream.
  • the column was reduced in internal pressure to 27 torr (0.52 psia) using a vacuum pump for one hour.
  • the column was again used to purify the same stream during which the SF ⁇ concentration initially was much lower and the time required for breakthrough longer.
  • regeneration experiments were run at 1.25 and 3.5 hours. This example demonstrates that better regeneration of the adsorbent is obtained with the use of lower pressures.
  • Example 10 The column of Example 1 was filled with 222 g dry PCB activated carbon.
  • a feed gas stream prepared by mixing a stream of air flowing at 400 mL/min and a stream of SF ⁇ contaminated with 0.091 % CF flowing at 100 mL/min, was allowed to pass through the column at a temperature of 25° C .
  • the pressure in the column was adjusted to 248 - 265 psia.
  • Samples of the exit gas were taken periodically and analyzed by GC.
  • the adsorbent capacity for SF ⁇ was calculated from the time required for the SF ⁇ concentration to reach 50 % of its feed concentration.
  • the pre-breakthrough concentration of SF ⁇ was calculated by averaging the concentrations of SF ⁇ for all samples taken before breakthrough.
  • the column was then regenerated by reducing it in pressure to 43 torr (0.83 psia) using a vacuum pump at room temperature for 16 hours.
  • the column was then re-used in the same way as above.
  • the column was alternately used for adso ⁇ tion and regenerated for a total of twelve cycles.
  • the capacities and pre- breakthrough concentrations of SF ⁇ are shown on Table 10. No significant deterioration in performance was observed.
  • Example 11 A 500 mL (14 in x 1.814 in i.d.) column is filled with activated carbon.
  • a feed gas stream is prepared by mixing a stream of air flowing at 400 mL/min and a stream of sulfur hexafluoride, contaminated with 0.091 % carbon tetrafluoride, flowing at 100 mL/min, is allowed to pass through this column at 40° C.
  • the pressure in the column is adjusted to approximately 248 - 265 psia. Samples of the gas stream exiting this column are taken periodically and analyzed by GC. Results are observed comparable to those of Example 1.
  • Example 12 A 500 mL (14 in x 1.814 in i.d.) column is filled with activated carbon.
  • a feed gas stream is prepared by mixing a stream of air flowing at 400 mL/min and a stream of sulfur hexafluoride, contaminated with 0.091 % carbon tetrafluoride, flowing at 100 mL/min, is allowed to pass through this column at 25° C. The pressure in the column is adjusted to approximately 100 - 200 psia. Samples of the gas stream exiting this column are taken periodically and analyzed by GC. Results are observed comparable to those of Example 1.

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Abstract

The present invention relates to a process for recovering sulfur hexafluoride ('SF6'). More specifically, the invention provides a pressure swing adsorption - desorption process for recovering SF6 from a gas stream using zeolites, activated carbons, or silicalites to adsorb the SF6.

Description

PROCESS FOR RECOVERING SULFUR HEXAFLUORIDE
Field of the Invention
The present invention relates to a process for recovering sulfur hexafluoride ("SFβ"). More specifically, the invention provides a pressure swing adsorption - desoφtion process for recovering SF6 from a gas stream.
Background of the Invention
SFβ, a non-flammable gas used in industry in a variety of applications, is manufactured by any of a number of known processes. In its manufacture, the product SF6 typically must be treated to remove impurities. In so treating the product SFβ , some SFβ may be lost as one component of a gaseous stream of the impurities removed from the product SFβ. The gas stream containing the impurities and some SF6 may be vented to the atmosphere. Not only does this result in loss of some of the SFβ produced, but it is environmentally undesirable because SFβ is suspected of being a "green-house", global warming gas.
A number of processes for separating SF6 from other gases are known. J. J.
Perona and J.S. Watson in "Sulfur Hexafluoride Purification From Mixtures With Air: A Process Feasibility Study" disclose the adsoφtion of SF6 from an air-SF6 mixture using activated carbon and temperatures below -50° F. This process is disadvantageous because it is an energy-intensive process.
In C. Brassard, Proceedings of the Symposium of Northeast Accelerator Personnel (S.N.E.A.P. . 60 (1976), a process for recovering SF6 using activated charcoal adsoφtion is disclosed. In this process, short bursts of gas are admitted to a column and the impurities, traveling at a faster rate than the SFβ, exit before the SFβ. This method is disadvantageous because it is impractical for use in industry.
Further, United States Patent No. 3,675,392 discloses the use of molecular sieves to separate water and carbon dioxide from SFS. However, the process disclosed in this patent is a batch process and suitable only for gas streams in which SFβ is the major component. Finally, Japanese Patent Application No. 60-054723 discloses the removal of water and carbon dioxide from SFβ using calcium hydride. This process is disadvantageous because calcium hydride is a dangerous material and has a relatively low capacity for removal of water and carbon dioxide.
None of the foregoing methods provide an industrial useful method for recovering SF6 from a gas stream in which SF6 is a minor component. Therefore, a need exists for a cost-effective, efficient, industrial useful method for recovering SF6.
Description of the Invention and Its Preferred Embodiments The invention provides a simple, economical method for recovering SF6 from a gas stream. The process of the invention comprises contacting a gas stream comprising a minor amount of SFβ with an adsorbent capable of selectively adsorbing SFβ under conditions suitable for the selective adsoφtion of SF6 from the gas stream. Optionally, the process additionally comprises regenerating SF6 from the adsorbent.
The gas streams useful in the invention contain a minor amount of SFβ along with at least one other component. By "minor amount" is meant less than about 50 volume percent, preferably less than about 20 volume percent, more preferably about 1 volume percent SF6 based on the total volume of the gas stream. The other component of the gas stream may be one or more non- condensible gases. The component typically will be one or more of air, helium, argon, carbon monoxide, carbon dioxide, nitrogen, oxygen, neon, hydrogen, or carbon tetrafluoride. The process may find its greatest utility for gas streams in which carbon tetrafluoride is the other component or one of the other components.
Adsorbents useful in this invention are any adsorbents capable of selectively adsorbing SFβ. By "selectively adsorbing" is meant that the adsorbent has an affinity for SF6 that is greater than its affinity for the other component or components in the gas stream. Preferably, the adsorbent has an affinity for SFβ such that SFβ is substantially entirely adsorbed from the gas stream while little or none of the other component or components is adsorbed. Suitable adsorbents useful in the invention are commercially available. Examples of useful adsorbents include, without limitation, zeolites, activated carbons, and silicalite. Preferably, zeolites or activated carbons are used. More preferably, activated carbons are used as the adsorbent.
Zeolites that may be used in the process of the invention are natural or synthetic zeolites with mean pore sizes of greater than about 5, preferably from about 5 to about 20 A. Preferably, the zeolite used is X or Y Faujasite zeolite. More preferably, sodium X (13X) zeolite is used.
Activated carbons useful in the invention are any of the granular, activated carbons with a mesh of from about 4 to about 300, preferably from about 20 to about 50. In terms of surface area, the activated carbon has a surface area of at least about 200 m2/g , preferably from about 1000 to about 1500 m2/g. Preferably, the activated carbon is PCB™ or ASC™ carbon available from Calgon Coφ. The amount of adsorbent used is an amount effective to allow the adsoφtion cycle to run for the period desired before regeneration of the adsorbent is necessary. The precise amount of adsorbent used will be readily determinable by one ordinarily skilled in the art by considering the chosen adsorbent's capacity, the desired time period between adsorbent regenerations, and the flow rate of the SF6 gas stream.
Contacting of the gas stream and adsorbents may take place in any manner known in the art. Preferably, contacting takes place by passing the gas stream through a fixed, packed bed of adsorbent. Passage of the gas stream takes place at a gas hourly space velocity of less than about 240, preferably less than about 100, h-1.
The contacting is performed under any conditions such that the selective adsoφtion of SF6 from the gas stream is facilitated. Accordingly, the temperature and pressure for contacting will be such that the temperature is greater, preferably about 10° C greater, than the boiling point of SF6 for the contacting pressure. Preferably, contacting is performed at a temperature of from about 10 to about 40° C, preferably from about 25 to about 40° C. Most preferably, contacting is performed at room temperature. The pressure at which contacting is carried out is at least about 5,170 torr (100 psia), preferably at least about 10,340 torr (200 psia).
SFβ adsorbed in the contacting step may be regenerated from the adsorbent by any convenient manner. Preferably; the regeneration is performed by lowering the pressure to about 760 torr (14.7 psia), more preferably to about 100 torr (1.93 psia), most preferably to about 40 torr (0.77 psia) over the adsorbent bed releasing the SF6 so that it may be collected. The regeneration so performed may take place at temperatures of at least about 10° C, preferably at least about 25° C. The time necessary to regenerate the SF6 will depend on the amount of SF6 adsorbed on the adsorbent as well as the amount of adsorbent used. Generally, regeneration will take place in from about 5 to about 40 hours.
The process of the invention may be used to recover SFβ from any gas stream, but may find its greatest utility in recovering SFβ from gas streams in which the SFβ is present in a minor amount. For example, in the manufacture of SF6, the SFβ produced is typically distilled and purified SFβ is removed as the column bottoms stream. The column overhead stream will contain a minor amount of SFβ as well as other components. SF6 may be recovered from the overhead stream by using the process of the invention.
The process of the invention may be carried out using any suitable vessel. For example, a chromatography column with pipe fittings on either end. Preferably, more than one vessel is used so that regeneration of the adsorbent in one column may be carried out without interruption of the SFβ recovery.
The invention will be clarified further by the following, non-limiting examples.
Examples Example 1 A 500 mL (14 in x 1.814 in i.d.) column was filled with 275 g dry 13X zeolite available from UOP Inc. A feed stream, prepared by mixing a stream of air flowing at 400 mL/min and a stream of SF6 contaminated with 0.091 % carbon tetrafluoride flowing at 100 mL/min, was allowed to pass through the column at 25° C. The pressure in the column was adjusted to approximately 248 - 265 psia. Samples of the gas stream exiting the column were taken periodically and analyzed by gas chromatography. The concentration of SF6 and CF4 obtained by the analysis are shown on Table 1 The capacity of the adsorbent for SFβ was calculated from the time required for the SFβ concentration to reach 50 % of the feed concentration.
Table 1
Figure imgf000008_0001
1. The brackets denote concentrauon of CF4 in weight percent.
2. The brackets denote concentrauon of SF6 in weight percent.
Example 2 The procedure of Example 1 was used except that 215 g of CPG activated carbon, available from Calgon Coφ., were used as the adsorbent. The results are shown on Table 2. Table 2
Figure imgf000009_0001
Example 3 The procedure of Example 1 was used except that 332 g silicalite were used as the adsorbent. The results are shown on Table 3.
Table 3
Figure imgf000010_0001
Example 4 The procedure of Example 1 was used except that 226 g F-400 activated carbon, available from the Calgon Coφ., were used as the adsorbent. The results are shown on Table 4.
Table 4
Figure imgf000011_0001
Example 5 The procedure of Example 1 was used except that 225 g PCB activated carbon, available from Calgon Coφ., were used as the adsorbent. The results are shown on Table 5. Table 5
Figure imgf000012_0001
Example 6 The procedure of Example 1 was used except that 346.8g 5A zeolite, available from UOP Inc., were used as the adsorbent. The results are shown on Table 6. Table 6
Figure imgf000013_0001
Example 7 The procedure of Example 1 was used except that 287 g ASC activated carbon, available from Calgon Coφ., were used as the adsorbent. The results are shown on Table 7.
Table 7
Figure imgf000013_0002
Example 8 The column of Example 1 was used and filled with 225 g dry PCB activated carbon, available from Calgon Coφ. The feed gas stream, prepared by mixing a stream of air flowing at 400 mL/min and a stream of SFβ contaminated with 2.25 % CF4 flowing at 100 mL/min, was allowed to pass through the column at a temperature of 25° C. The pressure in the column was adjusted to 248 - 265 psia. Samples of the gas stream exiting the column were taken periodically and analyzed by GC. The results are shown on Table 8. The capacity for the adsorbent for SF6 was calculated from the time required for the SFβ concentration to reach 50 % of its feed concentration.
As can be seen, the CF broke through the column before the SFβ and its concentration exceeds its feed concentration at the time of breakthrough. It is theorized that this indicates that the adsorbent had' a stronger affinity for SF6 than for CF4. By choosing the appropriate time for which to operate the column in the adsoφtion mode before regeneration of the SFβ, it is possible to displace essentially all of the CF leaving the column loaded with only SFβ. This allows CF - free SFβ to be harvested from the column during regeneration.
Table 8
Figure imgf000015_0001
Example 9 The column of Example 1 was filled with 275 g dry, 13X zeolite. A feed gas stream, prepared by mixing a stream of air flowing at 400 mL/min and a stream of SFβ contaminated with 0 091 % CF flowing at 100 mL/min, was allowed to pass through the column at a temperature of 25° C. The column pressure was adjusted to 248 - 265 psia. Samples of the exiting gas stream were taken periodically and analyzed by GC. The results are shown in Table 9 on which the SFβ concentrations are listed
Once the SF6 had broken through, the column was allowed to vent to an internal pressure of 760 torr (14.7 psia) for one hour. The column was again used to purify the same SFβ/air stream and monitored in the same way, the results of which are also found on Table 9. The column then was again vented, this time for 20 hours, and again used to purify the same stream. After breakthrough was again observed, the column was reduced in internal pressure to 27 torr (0.52 psia) using a vacuum pump for one hour. The column was again used to purify the same stream during which the SFβ concentration initially was much lower and the time required for breakthrough longer. In the same way, regeneration experiments were run at 1.25 and 3.5 hours. This example demonstrates that better regeneration of the adsorbent is obtained with the use of lower pressures.
Table 9
Figure imgf000016_0001
Figure imgf000017_0001
Table 9 (cont.)
Figure imgf000018_0001
Example 10 The column of Example 1 was filled with 222 g dry PCB activated carbon. A feed gas stream, prepared by mixing a stream of air flowing at 400 mL/min and a stream of SFβ contaminated with 0.091 % CF flowing at 100 mL/min, was allowed to pass through the column at a temperature of 25° C . The pressure in the column was adjusted to 248 - 265 psia. Samples of the exit gas were taken periodically and analyzed by GC. The adsorbent capacity for SFβ was calculated from the time required for the SFβ concentration to reach 50 % of its feed concentration. The pre-breakthrough concentration of SFβ was calculated by averaging the concentrations of SFβ for all samples taken before breakthrough.
The column was then regenerated by reducing it in pressure to 43 torr (0.83 psia) using a vacuum pump at room temperature for 16 hours. The column was then re-used in the same way as above. The column was alternately used for adsoφtion and regenerated for a total of twelve cycles. The capacities and pre- breakthrough concentrations of SFβ are shown on Table 10. No significant deterioration in performance was observed.
Table 10
Figure imgf000020_0001
Example 11 A 500 mL (14 in x 1.814 in i.d.) column is filled with activated carbon. A feed gas stream is prepared by mixing a stream of air flowing at 400 mL/min and a stream of sulfur hexafluoride, contaminated with 0.091 % carbon tetrafluoride, flowing at 100 mL/min, is allowed to pass through this column at 40° C. The pressure in the column is adjusted to approximately 248 - 265 psia. Samples of the gas stream exiting this column are taken periodically and analyzed by GC. Results are observed comparable to those of Example 1.
Example 12 A 500 mL (14 in x 1.814 in i.d.) column is filled with activated carbon. A feed gas stream is prepared by mixing a stream of air flowing at 400 mL/min and a stream of sulfur hexafluoride, contaminated with 0.091 % carbon tetrafluoride, flowing at 100 mL/min, is allowed to pass through this column at 25° C. The pressure in the column is adjusted to approximately 100 - 200 psia. Samples of the gas stream exiting this column are taken periodically and analyzed by GC. Results are observed comparable to those of Example 1.

Claims

What is claimed is:
1. A process for recovering sulfur hexafluoride comprising the step of contacting a gas stream comprising a minor amount of sulfur hexafluoride with an adsorbent capable of selectively adsorbing sulfur hexafluoride under conditions suitable for the selective adsoφtion of the sulfur hexafluoride from the gas stream.
2. The process of claim 1 wherein the gas stream comprises the minor amount of sulfur hexafluoride and the at least one component is air and carbon tetrafluoride.
3. The process of claim 1 wherein the minor amount of sulfur hexafluoride is less than about 20 volume percent of the gas stream.
4. The process of claim 1 wherein the adsorbent is selected from the group consisting of zeolites, activated carbons, and silicalites.
5. The process of claim 1 wherein the zeolite is sodium X (13X) zeolite.
6. The process of claim 1 further comprising the step of regenerating the sulfur hexafluoride selectively adsorbed.
7. A process for recovering sulfur hexafluoride comprising the step of contacting a gas stream comprising a less than about 50 volume percent sulfur hexafluoride and at least one component selected from the group consisting of air, carbon tetrafluoride, argon, helium, carbon monoxide, carbon dioxide, nitrogen, oxygen , neon, and hydrogen with an adsorbent selected from the group consisting of zeolites, activated carbons, and silicalites, the contacting carried out at a temperature from about 10 to about 40 ° C and a pressure at least about 100 psia, the temperature and pressure such that the temperature is above the boiling point of the sulfur hexafluoride for the contacting pressure, and at a gas hourly space velocity of less than about 240 h"1.
8. The process of claim 7 wherein the sulfur hexafluoride is present in an amount of less than about 20 volume percent of the gas stream.
The process of claim 7 wherein the zeolite is sodium X (13X) zeolite.
10. A process for recovering sulfur hexafluoride comprising the steps of: contacting a gas stream comprising about less than 20 volume percent sulfur hexafluoride and at least one component selected from the group consisting of air, carbon tetrafluoride, argon, helium, carbon monoxide, carbon dioxide, nitrogen, oxygen , neon, and hydrogen with an adsorbent selected from the group consisting of zeolites, activated carbons, and silicalites, the contacting carried out at a temperature from about 25 to about 40° C and a pressure at least about 100 psia, the temperature and pressure such that the temperature is above the boiling point of the sulfur hexafluoride for the contacting pressure, and at a gas hourly space velocity of less than about 240 h"1; and regenerating the sulfur hexafluoride selectively adsorbed by lowering the pressure to about 14.7 psia and at a temperature of at least about 10° C.
PCT/US1997/022588 1996-12-18 1997-12-10 Process for recovering sulfur hexafluoride WO1998027008A1 (en)

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EP97950910A EP0946410B1 (en) 1996-12-18 1997-12-10 Process for recovering sulfur hexafluoride
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