WO2014031269A1 - Divalent cation removal from rich monoethylene glycol (meg) feed streams by ion exchange - Google Patents
Divalent cation removal from rich monoethylene glycol (meg) feed streams by ion exchange Download PDFInfo
- Publication number
- WO2014031269A1 WO2014031269A1 PCT/US2013/051495 US2013051495W WO2014031269A1 WO 2014031269 A1 WO2014031269 A1 WO 2014031269A1 US 2013051495 W US2013051495 W US 2013051495W WO 2014031269 A1 WO2014031269 A1 WO 2014031269A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- meg
- feed stream
- ion exchange
- brine
- rich
- Prior art date
Links
- 150000001768 cations Chemical class 0.000 title claims abstract description 48
- 238000005342 ion exchange Methods 0.000 title claims abstract description 46
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 title description 80
- 238000000034 method Methods 0.000 claims abstract description 53
- 230000008929 regeneration Effects 0.000 claims abstract description 52
- 238000011069 regeneration method Methods 0.000 claims abstract description 52
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 claims abstract description 51
- 239000012267 brine Substances 0.000 claims abstract description 49
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 37
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 claims abstract description 36
- 238000004821 distillation Methods 0.000 claims abstract description 19
- 239000003729 cation exchange resin Substances 0.000 claims abstract description 18
- 239000011780 sodium chloride Substances 0.000 claims abstract description 18
- NWUYHJFMYQTDRP-UHFFFAOYSA-N 1,2-bis(ethenyl)benzene;1-ethenyl-2-ethylbenzene;styrene Chemical compound C=CC1=CC=CC=C1.CCC1=CC=CC=C1C=C.C=CC1=CC=CC=C1C=C NWUYHJFMYQTDRP-UHFFFAOYSA-N 0.000 claims abstract description 17
- 239000012153 distilled water Substances 0.000 claims description 8
- 230000001172 regenerating effect Effects 0.000 claims 2
- 239000002699 waste material Substances 0.000 abstract description 22
- 150000002500 ions Chemical class 0.000 abstract description 3
- 150000003839 salts Chemical class 0.000 description 10
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 6
- 239000001110 calcium chloride Substances 0.000 description 6
- 229910001628 calcium chloride Inorganic materials 0.000 description 6
- 239000011347 resin Substances 0.000 description 6
- 229920005989 resin Polymers 0.000 description 6
- AEDZKIACDBYJLQ-UHFFFAOYSA-N ethane-1,2-diol;hydrate Chemical compound O.OCCO AEDZKIACDBYJLQ-UHFFFAOYSA-N 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- -1 salt ions Chemical class 0.000 description 4
- 238000001179 sorption measurement Methods 0.000 description 4
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 3
- 239000003456 ion exchange resin Substances 0.000 description 3
- 229920003303 ion-exchange polymer Polymers 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 229910052708 sodium Inorganic materials 0.000 description 3
- 239000011734 sodium Substances 0.000 description 3
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical class [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 229910052791 calcium Inorganic materials 0.000 description 2
- 239000011575 calcium Chemical class 0.000 description 2
- 230000009977 dual effect Effects 0.000 description 2
- 150000004677 hydrates Chemical class 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000012607 strong cation exchange resin Substances 0.000 description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical class [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 229910052788 barium Chemical class 0.000 description 1
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical class [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 1
- 150000005323 carbonate salts Chemical class 0.000 description 1
- 229940023913 cation exchange resins Drugs 0.000 description 1
- 239000003518 caustics Substances 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 229910052712 strontium Inorganic materials 0.000 description 1
- CIOAGBVUUVVLOB-UHFFFAOYSA-N strontium atom Chemical class [Sr] CIOAGBVUUVVLOB-UHFFFAOYSA-N 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C29/00—Preparation of compounds having hydroxy or O-metal groups bound to a carbon atom not belonging to a six-membered aromatic ring
- C07C29/74—Separation; Purification; Use of additives, e.g. for stabilisation
- C07C29/76—Separation; Purification; Use of additives, e.g. for stabilisation by physical treatment
- C07C29/80—Separation; Purification; Use of additives, e.g. for stabilisation by physical treatment by distillation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/26—Selective adsorption, e.g. chromatography characterised by the separation mechanism
- B01D15/36—Selective adsorption, e.g. chromatography characterised by the separation mechanism involving ionic interaction
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/26—Selective adsorption, e.g. chromatography characterised by the separation mechanism
- B01D15/36—Selective adsorption, e.g. chromatography characterised by the separation mechanism involving ionic interaction
- B01D15/361—Ion-exchange
- B01D15/362—Cation-exchange
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D3/00—Distillation or related exchange processes in which liquids are contacted with gaseous media, e.g. stripping
- B01D3/06—Flash distillation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D3/00—Distillation or related exchange processes in which liquids are contacted with gaseous media, e.g. stripping
- B01D3/14—Fractional distillation or use of a fractionation or rectification column
- B01D3/143—Fractional distillation or use of a fractionation or rectification column by two or more of a fractionation, separation or rectification step
-
- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C29/00—Preparation of compounds having hydroxy or O-metal groups bound to a carbon atom not belonging to a six-membered aromatic ring
- C07C29/74—Separation; Purification; Use of additives, e.g. for stabilisation
- C07C29/76—Separation; Purification; Use of additives, e.g. for stabilisation by physical treatment
-
- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C29/00—Preparation of compounds having hydroxy or O-metal groups bound to a carbon atom not belonging to a six-membered aromatic ring
- C07C29/74—Separation; Purification; Use of additives, e.g. for stabilisation
-
- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C31/00—Saturated compounds having hydroxy or O-metal groups bound to acyclic carbon atoms
- C07C31/18—Polyhydroxylic acyclic alcohols
- C07C31/20—Dihydroxylic alcohols
- C07C31/202—Ethylene glycol
Definitions
- This invention relates to systems and processes designed to treat monoethylene glycol (MEG) used in the oil and gas industry, especially in offshore locations, to control the formation of hydrates. More particularly, the invention relates to MEG reclamation or regeneration processes that are designed to remove divalent cations from a rich MEG feed stream.
- MEG monoethylene glycol
- lean (dry) MEG is mixed with the water in a produced stream to control the formation of hydrates within the stream.
- the now rich (wet) MEG is, in turn, dried by way of a MEG reclamation or MEG regeneration process so that the MEG can be re-used in hydrate control.
- the lean MEG cannot be recovered by simply distilling the rich MEG and water in conditions of high salt concentration because the rich MEG is loaded with dissolved salt ions from the produced water.
- Sodium chloride is commonly the most concentrated salt in the produced water, but it may also contain dissolved divalent salts of magnesium, calcium, strontium, and barium. If these divalent cations are not removed or controlled at a low concentration, their high solubility in MEG will alter the physical properties of the MEG, eventually leading to failure of the reclamation or regeneration process.
- the ions react with carbonate or hydroxide anions to form insoluble salt crystals, which are then removed from the feed stream.
- This process generally requires the addition of caustic and acid to completely remove the divalent cations and to neutralize the feed stream before it enters the MEG reclamation or MEG regeneration process.
- the time and temperature of the current separation process must be strictly controlled.
- the process requires large and expensive equipment, as well as additional chemicals that are not inherently available as part of the MEG reclamation or MEG regeneration process. These chemicals must be obtained from outside sources which can be very expensive, particularly when delivered to offshore platforms in remote parts of the world.
- the chemicals may also be a safety concern, require specialized handling and storage, and increase training, reporting, and recordkeeping requirements.
- the current separation process also produces a carbonate salt in the form of a solid or slurry material that is generally insoluble and requires disposal as a waste. Proper disposal of this material can be expensive, time-consuming, and labor-intensive. Disposal is even more difficult in offshore applications where temporary storage space and transportation to an approved disposal site are not readily available.
- a system for removing divalent cations from a rich MEG feed stream includes an ion exchange bed containing a cation exchange resin that adsorbs the divalent cations in the rich MEG feed stream as it flows through the bed.
- the feed stream flows through a flash separator and a distillation column to reclaim MEG.
- the feed stream flows through a distillation column to regenerate MEG.
- the spent cation exchange resin may be regenerated, without removing it from the ion exchange bed, using a regeneration brine.
- the regeneration brine may be comprised of distilled water that is produced during the MEG reclamation or MEG regeneration process.
- the regeneration brine may also be comprised of sodium chloride that is produced during the MEG reclamation process.
- the regeneration brine may be disposed of as waste or recycled to the brine storage tank and re-used to regenerate the cation exchange resin.
- a process for removing divalent cations from a rich MEG feed stream includes the steps of providing an ion exchange bed containing a cation exchange resin and passing the rich MEG feed stream through the bed so that the divalent cations are adsorbed to the resin.
- the process may also include the step of MEG reclamation or MEG regeneration.
- a regeneration brine may be used to regenerate the spent cation exchange resin without removing it from the ion exchange bed.
- the regeneration brine may be comprised of distilled water produced during the MEG reclamation or MEG regeneration process.
- the regeneration brine may also be comprised of sodium chloride that is produced during the MEG reclamation process.
- the regeneration brine may be disposed of as waste or recycled to the brine storage tank and re-used to regenerate the cation exchange resin.
- the objects of this invention are to (1) provide a more efficient process to remove divalent cations contained in a rich MEG feed stream before the stream enters a MEG reclamation or MEG regeneration process; (2) simplify the removal process by eliminating required conditions for time and temperature; (3) reduce the volume, footprint, and cost of the processing equipment typically required to remove divalent cations from the rich MEG feed stream; (4) provide a renewable or reusable bed for divalent cation removal; (5) provide a process for physical separation of the divalent cations from the rich MEG feed stream, thus eliminating the need for additional chemicals; and (6) facilitate the disposal of waste streams.
- FIG. 1 presents an embodiment of a process for removing divalent cations from a rich MEG feed stream as part of a MEG reclamation process, practiced according to this invention.
- FIG. 2 presents an embodiment of a process for removing divalent cations from a rich MEG feed stream as part of a MEG regeneration process, practiced according to this invention.
- An ion exchange process may be used to remove divalent cations from the rich MEG feed stream before the feed stream enters the MEG reclamation process, as shown in FIG. 1, or the MEG regeneration process, as shown in FIG. 2.
- This ion exchange process is different than conventional water treatment because the rich MEG feed stream is more viscous than water and interacts differently with the ion exchange resins.
- the ion exchange resins of the present invention are subject to higher concentrations of sodium and calcium than would generally be found in water treatment systems.
- a preferred embodiment of a divalent cation removal process 10A practiced according to this invention begins with the rich MEG feed stream 15, which is a mixture of produced water and MEG.
- the rich MEG feed stream 15 is routed to a divalent cation removal step comprised of dual ion exchange beds 20 which contain a strong cation exchange resin in the sodium form and alternate between adsorption and regeneration phases.
- the resin removes divalent cations from the rich MEG feed stream 15 by adsorbing the divalent cations from the produced water and displacing the sodium cations.
- two ion exchange beds 20 are shown in FIG. 1, the ion exchange process may use more than two beds or a single bed.
- the rich MEG stream with the majority of divalent cations removed 25 then exits the ion exchange beds 20 and flows to the MEG reclamation process.
- the MEG reclamation process begins in a flash separator 30, where the pressure is reduced in order to separate salts from the rich MEG and water.
- a sodium chloride waste stream 35 exits the bottom end of the flash separator 30, while the vaporized water and MEG stream 40 exits the top end and flows to the distillation column 45.
- the distillation column 45 uses partial condensation to separate the water and MEG components of the vaporized water and MEG stream 40.
- Lean MEG 50 exits the bottom end of the distillation column 45 and distilled water 55 is discharged from the top end of the distillation column 45. After meeting necessary quality requirements, the distilled water 55 may be discharged as waste or recycled to the brine storage tank 60.
- Regeneration of the ion exchange beds 20 may be accomplished with water containing large amounts of a salt.
- the sodium chloride waste stream 35 from the flash separator 30 is combined with distilled water 55 from the distillation column 45 in the brine storage tank 60 to form regeneration brine 65.
- one of the ion exchange beds 20 is taken off-line by diverting the flow of the rich MEG feed stream 15 from that bed 20 to the alternate bed 20.
- a stream of regeneration brine 65 from the brine storage tank 60 is then routed through the off-line ion exchange bed 20 in a direction opposite that of the flow of the rich MEG feed stream 15.
- the waste stream of sodium chloride and calcium chloride brine 70 can be disposed of as waste or re-used to regenerate the ion exchange beds 20.
- an ion exchange process may also be used to regenerate MEG by removing divalent cations from the rich MEG feed stream.
- This process may be used in applications where the produced water is relatively free of salts and the purity standards for MEG are less stringent.
- the MEG may contain divalent cations at a concentration that would cause equipment and scaling issues. Removing these ions protects downstream equipment and extends the useful life of the MEG.
- a preferred embodiment of a divalent cation removal process 10B practiced according to this invention begins with a rich MEG feed stream 85, which is routed to a divalent cation removal step.
- the divalent cation removal step is comprised of dual ion exchange beds 20 which contain a strong cation exchange resin in the sodium form and alternate between adsorption and regeneration phases. In the adsorption phase, the resin removes divalent cations from the feed stream 85 by adsorbing the divalent cations from the produced water and displacing the sodium cations.
- two ion exchange beds 20 are shown in FIG. 2, the ion exchange process may use more than two beds or a single bed.
- the rich MEG stream with the majority of divalent cations removed 90 then exits the ion exchange beds 20 and flows to a distillation column 45, which separates the water from the lean MEG.
- Lean MEG 50 exits the bottom end of the distillation column 45, while the vaporized water 95 exits the top end. After the vaporized water 95 cools, it may be discharged as waste or recycled to the brine storage tank 60.
- Regeneration of the ion exchange beds 20 may be accomplished with water containing large amounts of a salt.
- sodium chloride 80 from an external source is combined with the water 95 from the distillation column 45 in the brine storage tank 60 to form regeneration brine 65.
- one of the ion exchange beds 20 is taken off-line by diverting the flow of the rich MEG feed stream 85 from that bed 20 to the alternate bed 20.
- a stream of regeneration brine 65 from the brine storage tank 60 is then routed through the off-line ion exchange bed 20 in a direction opposite that of the flow of the feed stream 85.
- the waste stream of sodium chloride and calcium chloride brine 70 can be disposed of as waste or re-used to regenerate the ion exchange beds 20.
- the present invention allows the MEG to remain in service for a longer period of time before the concentration of divalent cations increases to a level that could cause scaling or corrosion of the equipment.
- Another advantage of the present invention is that distilled water, which is produced during MEG reclamation and MEG regeneration and conventionally managed as a waste material, is recycled to form regeneration brine.
- Sodium chloride produced during MEG reclamation can also be recycled to form regeneration brine.
- Another advantage is that the waste stream of sodium chloride and calcium chloride brine from regeneration of the ion exchange beds contains only the salts that were originally present in the produced water. As a result, this waste stream can be discharged, if the appropriate water quality standards are met, to the marine environment or an injection well.
- This waste stream may also be recycled through the regeneration process for the cation exchange resin in the ion exchange beds until the concentration of divalent cations increases to a level that impairs regeneration of the resin. While preferred embodiments of a system and process for removing divalent cations from a rich MEG feed stream have been described in detail, a person of ordinary skill in the art understands that certain changes can be made in the arrangement of process steps and type of components used in the system and process without departing from the scope of the following claims.
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Analytical Chemistry (AREA)
- Treatment Of Water By Ion Exchange (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
Abstract
Description
Claims
Priority Applications (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
MX2015002094A MX2015002094A (en) | 2012-08-24 | 2013-07-22 | Divalent cation removal from rich monoethylene glycol (meg) feed streams by ion exchange. |
EP13747546.3A EP2888021A1 (en) | 2012-08-24 | 2013-07-22 | Divalent cation removal from rich monoethylene glycol (meg) feed streams by ion exchange |
CA2880889A CA2880889A1 (en) | 2012-08-24 | 2013-07-22 | Divalent cation removal from rich monoethylene glycol (meg) feed streams by ion exchange |
BR112015003860A BR112015003860A2 (en) | 2012-08-24 | 2013-07-22 | divalent cation removal from rich monoethylene glycol (meg) feed streams by ion exchange |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US13/593,734 US9433875B2 (en) | 2012-08-24 | 2012-08-24 | Divalent cation removal from rich monoethylene glycol (MEG) feed streams by ion exchange |
US13/593,734 | 2012-08-24 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2014031269A1 true WO2014031269A1 (en) | 2014-02-27 |
Family
ID=48949214
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/US2013/051495 WO2014031269A1 (en) | 2012-08-24 | 2013-07-22 | Divalent cation removal from rich monoethylene glycol (meg) feed streams by ion exchange |
Country Status (7)
Country | Link |
---|---|
US (4) | US9433875B2 (en) |
EP (1) | EP2888021A1 (en) |
BR (1) | BR112015003860A2 (en) |
CA (1) | CA2880889A1 (en) |
MX (1) | MX2015002094A (en) |
MY (1) | MY166800A (en) |
WO (1) | WO2014031269A1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2016012500A1 (en) * | 2014-07-25 | 2016-01-28 | Novasep Process | Method for purifying glycol used as a hydrate inhibitor |
Families Citing this family (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US9433875B2 (en) * | 2012-08-24 | 2016-09-06 | Cameron International Corporation | Divalent cation removal from rich monoethylene glycol (MEG) feed streams by ion exchange |
KR102647868B1 (en) * | 2016-12-01 | 2024-03-15 | 한화오션 주식회사 | MEG recovery apparatus using hybrid process based on hollow fiber membrane filter |
CN108794302A (en) * | 2018-08-23 | 2018-11-13 | 西南石油大学 | A kind of desalination regeneration technology of saliferous ethylene glycol rich solution |
US10954179B1 (en) * | 2019-08-28 | 2021-03-23 | Cameron International Corporation | Method and apparatus for filtering heat transfer fluid from a monoethylene glycol stream |
US11325878B2 (en) | 2019-09-13 | 2022-05-10 | Cameron International Corporation | Removing organic acids in monoethylene glycol recovery |
US11976770B2 (en) * | 2020-09-29 | 2024-05-07 | Saudi Arabian Oil Company | Solid removal in glycol reclamation |
US20240318514A1 (en) * | 2023-03-21 | 2024-09-26 | Saudi Arabian Oil Company | Systems and methods for operating candle filters to recover glycols from drilling operations |
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CN101773749A (en) * | 2010-03-01 | 2010-07-14 | 新疆石油学院 | Method for purifying polyol for preventing natural gas from freezing and dehydrating natural gas and equipment |
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IL32812A (en) * | 1968-08-17 | 1974-05-16 | Asahi Chemical Ind | Process for producing fresh water and concentrated brine from brine |
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GB0813484D0 (en) * | 2008-07-24 | 2008-08-27 | Rolls Royce Plc | Gas turbine engine nacelle |
US9089790B2 (en) * | 2012-08-24 | 2015-07-28 | Cameron International Corporation | Hydrocarbon and divalent cation removal from rich mono ethylene glycol (MEG) feed streams by regenerable filters |
US9433875B2 (en) * | 2012-08-24 | 2016-09-06 | Cameron International Corporation | Divalent cation removal from rich monoethylene glycol (MEG) feed streams by ion exchange |
US8808546B2 (en) * | 2012-08-24 | 2014-08-19 | Cameron International Corporation | Hydrocarbon removal from gas process feed streams by regenerable filters |
-
2012
- 2012-08-24 US US13/593,734 patent/US9433875B2/en not_active Expired - Fee Related
-
2013
- 2013-07-22 CA CA2880889A patent/CA2880889A1/en not_active Abandoned
- 2013-07-22 MX MX2015002094A patent/MX2015002094A/en unknown
- 2013-07-22 WO PCT/US2013/051495 patent/WO2014031269A1/en active Application Filing
- 2013-07-22 MY MYPI2015000194A patent/MY166800A/en unknown
- 2013-07-22 BR BR112015003860A patent/BR112015003860A2/en not_active IP Right Cessation
- 2013-07-22 EP EP13747546.3A patent/EP2888021A1/en not_active Withdrawn
-
2016
- 2016-09-01 US US15/254,125 patent/US20170050908A1/en not_active Abandoned
-
2019
- 2019-04-17 US US16/386,906 patent/US20190241493A1/en not_active Abandoned
- 2019-10-23 US US16/661,599 patent/US20200071250A1/en not_active Abandoned
Patent Citations (8)
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GB1219018A (en) * | 1967-12-07 | 1971-01-13 | Frbwerke Hoechst Ag | Process for the purification of glycols |
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Cited By (5)
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WO2016012500A1 (en) * | 2014-07-25 | 2016-01-28 | Novasep Process | Method for purifying glycol used as a hydrate inhibitor |
FR3024142A1 (en) * | 2014-07-25 | 2016-01-29 | Novasep Process | METHOD OF PURIFYING GLYCOL AS ANTI-HYDRATE AGENT |
CN106536465A (en) * | 2014-07-25 | 2017-03-22 | 诺瓦塞普工艺公司 | Method for purifying glycol used as a hydrate inhibitor |
CN106536465B (en) * | 2014-07-25 | 2020-11-10 | 诺瓦塞普工艺公司 | Method for purifying ethylene glycol used as water repellent agent |
US10953347B2 (en) | 2014-07-25 | 2021-03-23 | Novasep Process | Method for purifying glycol used as a hydrate inhibitor |
Also Published As
Publication number | Publication date |
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US9433875B2 (en) | 2016-09-06 |
US20140054160A1 (en) | 2014-02-27 |
US20190241493A1 (en) | 2019-08-08 |
MX2015002094A (en) | 2015-05-11 |
BR112015003860A2 (en) | 2017-07-04 |
EP2888021A1 (en) | 2015-07-01 |
US20170050908A1 (en) | 2017-02-23 |
MY166800A (en) | 2018-07-23 |
CA2880889A1 (en) | 2014-02-27 |
US20200071250A1 (en) | 2020-03-05 |
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