WO2000053284A1 - Process for removing hydrocarbons from a liquid mixture with a regenerable filter - Google Patents

Process for removing hydrocarbons from a liquid mixture with a regenerable filter Download PDF

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Publication number
WO2000053284A1
WO2000053284A1 PCT/US2000/006543 US0006543W WO0053284A1 WO 2000053284 A1 WO2000053284 A1 WO 2000053284A1 US 0006543 W US0006543 W US 0006543W WO 0053284 A1 WO0053284 A1 WO 0053284A1
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WO
WIPO (PCT)
Prior art keywords
resm
hydrocarbon
liquid
process according
ion exchange
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
Application number
PCT/US2000/006543
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English (en)
French (fr)
Inventor
Arthur L. Cummings
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
MPR Services Inc
Original Assignee
MPR Services Inc
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by MPR Services Inc filed Critical MPR Services Inc
Priority to AU35270/00A priority Critical patent/AU3527000A/en
Priority to EP00913910A priority patent/EP1161291B1/en
Priority to AT00913910T priority patent/ATE285281T1/de
Priority to DE60016899T priority patent/DE60016899T2/de
Priority to CA002362691A priority patent/CA2362691C/en
Priority to JP2000603772A priority patent/JP2002537986A/ja
Publication of WO2000053284A1 publication Critical patent/WO2000053284A1/en
Priority to NO20014403A priority patent/NO322664B1/no
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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Classifications

    • 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
    • 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
    • B01D53/14—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 by absorption
    • B01D53/1425—Regeneration of liquid absorbents
    • 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
    • B01J39/00—Cation exchange; Use of material as cation exchangers; Treatment of material for improving the cation exchange properties
    • B01J39/04—Processes using organic exchangers
    • 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
    • B01J41/00—Anion exchange; Use of material as anion exchangers; Treatment of material for improving the anion exchange properties
    • B01J41/04—Processes using organic exchangers
    • 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
    • B01J49/00—Regeneration or reactivation of ion-exchangers; Apparatus therefor
    • B01J49/50—Regeneration or reactivation of ion-exchangers; Apparatus therefor characterised by the regeneration reagents
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/28—Treatment of water, waste water, or sewage by sorption
    • C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • 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, e.g. ion-exchange, ion-pair, ion-suppression or ion-exclusion
    • B01D15/361—Ion-exchange
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2252/00—Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/20—Organic absorbents
    • B01D2252/204—Amines
    • B01D2252/20478—Alkanolamines
    • B01D2252/20484—Alkanolamines with one hydroxyl group
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2252/00—Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/20—Organic absorbents
    • B01D2252/204—Amines
    • B01D2252/20478—Alkanolamines
    • B01D2252/20489—Alkanolamines with two or more hydroxyl groups
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2257/00—Components to be removed
    • B01D2257/30—Sulfur compounds
    • B01D2257/304—Hydrogen sulfide
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2257/00—Components to be removed
    • B01D2257/50—Carbon oxides
    • B01D2257/504—Carbon dioxide
    • 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
    • B01D53/14—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 by absorption
    • B01D53/1456—Removing acid components
    • B01D53/1462—Removing mixtures of hydrogen sulfide and carbon dioxide
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00—Nature of the contaminant
    • C02F2101/30—Organic compounds
    • C02F2101/32—Hydrocarbons, e.g. oil
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/36—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
    • C02F2103/365—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds from petrochemical industry (e.g. refineries)
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00—Specific treatment goals
    • C02F2303/16—Regeneration of sorbents, filters
    • Y—GENERAL 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
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00—Capture or disposal of greenhouse gases
    • Y02C20/40—Capture or disposal of greenhouse gases of CO2

Definitions

  • This invention relates to a process for removing hydrocarbons from a solution. More particularly, this invention relates to a process for absorbing hydrocarbons from a solution onto a medium and to the in si tu regeneration of the absorbing medium.
  • the solutions are composed of polar solvents, such as alkanolamines, glycols, sulfolane, and their aqueous mixtures .
  • alkanolamine sweetening units The removal of acid gases (such as H 2 S and C0 2 ) from natural gases, enhanced oil recovery gases, petroleum gases and liquids, tail gases, ammonia plant gases, coke oven gases, and the like, is commonly accomplished by alkanolamine sweetening units.
  • acid gases such as H 2 S and C0 2
  • hydrocarbons may also be absorbed or entrained in the alkanolamine solution.
  • aqueous solutions of alkanolamines are contacted with streams containing H 2 S and CO;, the H 2 S and C0 2 dissolve into the alkanolamine solution to form solvated alkanolamine salts (e.g., protonated alkanolamine cation with HS " ar.a HC0 3 " anions; .
  • solvated alkanolamine salts e.g., protonated alkanolamine cation with HS " ar.a HC0 3 " anions; .
  • the solution of water, unreacted alkanolamine, and alkanolamine salts is subjected to steam stripping to decompose the alkanolamine salts and remove K;S and CO 2 from the alkanolamine.
  • Thiocyanate anion forms from the reaction of HCN with H 2 S or sulfides in the gases from crude units or catalytic reformers.
  • Other typical alkanolamine salt anions include S; ⁇ ' '- , S0 3 " ⁇ , SO, ? 2" , HC0 2 ⁇ , CH 3 C0; ⁇ , and the like.
  • These alkanolamine salts cannot be removed by steam stripping. Thus, they are called heat stable salts and remain in the system where they accumulate in the alkanolamine solution, gradually depleting the e fectiveness of alkanolamine treatment.
  • the heat stable salt anions are removed by exchange with hydroxide from an anion exchange resin and cations, such as sodium and potassium, are removed by exchange with hydrogen ion from a cation exchange resin.
  • Ion exchange to remove heat stable salts from alkanolamine solutions has been a subject in the patent literature for many years, see for example, Taylor, U.S. Patent No. 2,797,188; Pearce, U.S. Patent No. 4,477,419; Keller, U.S. Patent No. 4,970,344; Yan, U.S. Patent No. 4,795,565; Veatch, U.S. Patent No. 5,006,258; and Cummings, U.S. Patent No. 5,162,C34.
  • U.S. Patent 2,762,852 is directed to an adsorption process in which a hy ⁇ rocaroon is contacted with activated carbon. When saturated, the activated caroon must be separately regenerated or exchangee for new carbon. Thus activated carbon adsorption is expensive ana labor intensive.
  • .S. Patent 2,963,519 uses a zeolitic molecular sieve as the adsorbent to remove small diameter nydrocarbons from petroleum refinery hydrocarbon streams.
  • the molecular sieves are regenerated by heating and passing hot adsorbate through the bed.
  • aromatics are remove ⁇ from non-aqueous hydrocarbon mixtures by adsorption onto a cation ion- exchange resin that has been charged with silver ions.
  • Adsorbed aromatics are desorbed by flowing water through the resin, then the adsorbed water is removed from the resin by evaporation or by flashing with a volatile solvent .
  • This patent has for its purpose a method of activating fresh or regenerate ⁇ ion-exchange resin by contacting with one or a mixture cf lower molecular weight mononydric alconols prior to cleansing a hydrocarbcr fluid. The activaticr is said to improve the effectiveness of the resm at removing mercaptans from nydrocarbon liquids.
  • the genera-, object of the present invention to provide a process for absorbing hydrocarbons from an alkanolamine-, glycol-, or other polar solvent- containing solution onto an ion exchange resm and to the in si tu regeneration of the ion exchange resm.
  • Anotner object of this invention is to provide a process for regenerating a filter oed of ion exchange resm having a hydrocarbon adsorbe ⁇ thereon.
  • a process for removing r ⁇ drocarbons from liquid streams s ⁇ ci as an amme-contammg solution or a glycol- contain g solution by passing t r e solution through an ion exchar ⁇ e resm m a filtratic bed, whereby the hydrocaroc-s are retained o tne ced.
  • the resm is either cation or anion exchange resm.
  • the liquid stream passes through the ion excnange resm and leaves the filtration bed substantially reduced in hydrocarbon content .
  • the ion exchange resm may be regenerated m situ by removing the hydrocarbons from the resm bed oy flowing water therethrough, such that the nydrocarbon is carried away in tnat liquid.
  • the ion excnange resm may be reused to remove hydrocarbons from a liquid stream.
  • Figure 1 is a schematic flow diagram which illustrates a preferred embodiment of the present invention.
  • the process of the present invention is used to remove hydrocaroons from liquid streams such as an amine- containmg section or a glyccl-containing solution by passing the solution through an ion exchange resm, whereby the hydrocarbons are retained by the resm bed.
  • the ion exchange resm is then regenerated in si tu by removing tne hydrocarbons from the ion exchange resm by flowing water therethrough, such tnat the hydrocarbon is carried away in that liquid.
  • FIG. 1 An example of one system in which the process of the present invention may be used is shown m Figure 1, wherein hydrocarbons are removed from a first liquid stream 12, such as an alkanolamme-contammg solution and/or glycol-contammg solution, as they separate from the liquid stream as it passes through filtration bed 10, composed of resm beads.
  • the resm is a polymeric material, such as cation or anion exchange resm.
  • the first liquid stream is from an alkanolamine system it generally enters the filtration bed at a temperature of between about 0°F. and about 130°F. and a pressure of about 15 to 600 p.s.i.
  • the liquid stream 14 passes from the resm bed substantially reduced in hydrocarbon content. In the case of an amme stream it is returned to the system.
  • a second liqui ⁇ stream 16 such as water
  • the second liquid backwash water
  • the flow rate is aoout 1 to 10 gallons/min/ft' .
  • the resin may be used again to remove undesirable hydrocarbons from a liquid stream.
  • the hydrocarbons in question include a variety of aliphatic and aromatic hydrocarbons such as those common to petroleum production, syngas production, steel production and chemical processing.
  • hydrocarbons are aliphatic and aromatic hydrocarbons, petroleum hydrocarbons, gasoline, kerosene, gas oil, waxes, and the like. These hydrocarbons are often present as mixtures of hydrocarbons.
  • Ion exchange resins exhibit the desired property for removing hydrocarbons from alkanolamine solutions and glycol solutions. Cation and anion exchange resins are similarly effective. Thus, one can assume it is not the ionic exchange capability that is important, rather it is the polymer structure, or perhaps a physical surface phenomenon that is responsible for effecting the desired separation .
  • resins include anion exchange resins of the strong base, weak base, strong cation and weak cation varieties.
  • strong base anion exchange resins include styrene-divinylbenzene resins with quaternary alkanolamine groups attached to the polymer framework, such as ResintechTM SBG-2, Sybron lonacTM ASB-2 , Rohm and Haas Amberlite ⁇ IRA-410; styrene-divinylbenzene resins having quaternary amine functional groups, such as Dow SBR, Dow MSA-1, Rohm and Haas IRA-900 and IRA-400, ResinTech S3G1, SBMP1, and the like.
  • strong acid cation resins include suifonated stryrene- divinylbenzene resins, such as Dow HCR, ResinTech CG8 and CG10, Sybron C250, and Rohm and Haas IR-120.
  • weak base anion exchange resins include stryrene- divmylbenzene resins with tertiary amine functional groups, such as Rohm and Haas IRA93/94, ResinTech WBMP, Sybron AFP-329, and Dow MWA-1.
  • weak acid cation exchange resins ciude acrylic resins such as
  • Alkanolamine-containing solutions from petroleum production refining, gas production, syn-gas production and the like typically contain 30 to 85% water by weight.
  • the alkanolamine solutions commonly used include, for example, monoethanolamme, methylethanolamme, dietnanoiamme, methyldiethanolamme, diisopropanolamme, t ⁇ ethanolamme, diglycolamme, proprietary hindered ammes, proprietary mixtures of ammes, and mixtures with physical solvents, like sulfolane, and various other mixtures .
  • Glycol-contammg solutions typically contain from about 2% to about 80% water.
  • Typical glycols used in dehy ⁇ ratcr service and hydrate inhibition include monoetny_ene glycol, diethylene glycol, t ⁇ ethylene glycol and tetraethylene glycol. The following examples are presented as illustrations of the invention.
  • kerosene was ad ⁇ ed to a 50% /50% mef-vldiethanolamine/water solution such that the kerosene concentration in the solution was about 100 ppm.
  • the solution was passed through 100 ml. of strong base ion exchange resin.
  • the effluent from the filtration bed was collected and the amount of unabsorbed kerosene was determined.
  • the kerosene concentrations were:
  • a monoethanolamine solution from a petroleum refinery amine system was run through a bed of strong base anion exchange resin.
  • the hydrocarbon concentrations in the amine were analyzed by gas chromatography as follows:
  • An anion exchange resin bed was used for 3 weeks removing heat stable salts from a refinery amine system.
  • the amine solution also contained varying amounts of petroleum hydrocarbons.
  • a heavy goo of hydrocarbon developed at and near the top of the resin bed that eventually severely reduced the ion exchange function of the resin.
  • the resin was slurried with water and removed from the service vessel. The resin that came from most near the top of the vessel was most heavily coated with waxy goo and could not participate in the ion exchange.
  • the goo and resm separated. The recovered resm was tested and found to have acceptable ion exchange capacity.
  • the hydrocarbon could also oe separated from the resm with the aid of a detergent in water.
  • Example 4 A cation exchange resm was used for several weeks removing cations from a refinery amine system. Upon opening the vessel, a greasy substance was observed on the top of the resm. Subsequently the resm was slurried with water and flushed from the vessel into an open container. A hydrocarbon layer appeared on top of the water as it separated from the resm below.
  • a five-foot diameter vessel was filled with anion exchange resm.
  • Flow was taken from a circulating refinery amine system known to contain paraffins, including waxes, and passed througn the resm bed at 60 to 90 gallons per minute for several days.
  • Amine flow was stopped, the amine rinsed from the resm bed with ambient temperature water, and the resm bed was back- flushed with water at 150°F. to 160°F. at about 30 gpm, and the flushed material was collected in a settling tank. The cycle was repeated twice more.
  • the flushed material was found to have a layer of wax on it, indicating transfer of wax from amme to tne resm bed and from the resm bed to the settling tank.

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Analytical Chemistry (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
  • Treatment Of Liquids With Adsorbents In General (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
PCT/US2000/006543 1999-03-12 2000-03-13 Process for removing hydrocarbons from a liquid mixture with a regenerable filter Ceased WO2000053284A1 (en)

Priority Applications (7)

Application Number Priority Date Filing Date Title
AU35270/00A AU3527000A (en) 1999-03-12 2000-03-13 Process for removing hydrocarbons from a liquid mixture with a regenerable filter
EP00913910A EP1161291B1 (en) 1999-03-12 2000-03-13 Process for removing hydrocarbons from a liquid mixture with a regenerable filter
AT00913910T ATE285281T1 (de) 1999-03-12 2000-03-13 Verfahren zum entfernen von kohlenwasserstoffen aus einem flüssigkeitsgemisch mit einem regenerierbaren filter
DE60016899T DE60016899T2 (de) 1999-03-12 2000-03-13 Verfahren zum entfernen von kohlenwasserstoffen aus einem flüssigkeitsgemisch mit einem regenerierbaren filter
CA002362691A CA2362691C (en) 1999-03-12 2000-03-13 Process for removing hydrocarbons from a liquid mixture with a regenerable filter
JP2000603772A JP2002537986A (ja) 1999-03-12 2000-03-13 再生可能な炭化水素フィルター
NO20014403A NO322664B1 (no) 1999-03-12 2001-09-11 Fremgangsmate for a fjerne hydrokarboner fra en flytende blanding med et regenererbart filter

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US09/267,813 1999-03-12
US09/267,813 US6416670B1 (en) 1999-03-12 1999-03-12 Regenerable hydrocarbon filter

Publications (1)

Publication Number Publication Date
WO2000053284A1 true WO2000053284A1 (en) 2000-09-14

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Application Number Title Priority Date Filing Date
PCT/US2000/006543 Ceased WO2000053284A1 (en) 1999-03-12 2000-03-13 Process for removing hydrocarbons from a liquid mixture with a regenerable filter

Country Status (9)

Country Link
US (1) US6416670B1 (https=)
EP (1) EP1161291B1 (https=)
JP (1) JP2002537986A (https=)
AT (1) ATE285281T1 (https=)
AU (1) AU3527000A (https=)
CA (1) CA2362691C (https=)
DE (1) DE60016899T2 (https=)
NO (1) NO322664B1 (https=)
WO (1) WO2000053284A1 (https=)

Cited By (1)

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WO2020043862A1 (fr) * 2018-08-30 2020-03-05 Suez Groupe Procede de traitement d'un effluent aqueux contenant des composes organiques

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US7922913B2 (en) * 2008-02-21 2011-04-12 Rousseau Research, Inc. Removing oil from surface using dry amorphous silica product with inert carrier
US8696871B2 (en) * 2009-06-02 2014-04-15 Uop Llc Apparatus for removing a contaminant from a solvent separation process
US20100300939A1 (en) * 2009-06-02 2010-12-02 Uop Llc Process for Removing a Contaminant from an Aromatic Selective Solvent
US8808546B2 (en) * 2012-08-24 2014-08-19 Cameron International Corporation Hydrocarbon removal from gas process feed streams by regenerable filters
CN103961901B (zh) * 2013-01-30 2016-04-06 中国石油天然气股份有限公司 一种脱除醇胺溶液中长链羧酸盐和烃的方法
CN107530590B (zh) * 2015-03-17 2021-03-19 唐纳森公司 水包烃净化系统
US10604707B2 (en) * 2015-03-17 2020-03-31 Donaldson Company, Inc. Hydrocarbon-in-water purification anion-exchange system
US9944873B1 (en) * 2016-04-26 2018-04-17 Phil Belveal, Sr. Add-on system for removing paraffin from a natural gas dehydration system
EP3401001A1 (de) * 2017-05-12 2018-11-14 L'air Liquide, Société Anonyme Pour L'Étude Et L'exploitation Des Procédés Georges Claude Verfahren und anlage zur abtrennung von begleitgasen aus einem rohsynthesegas

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NO20014403L (no) 2001-10-18
CA2362691C (en) 2008-12-02
US6416670B1 (en) 2002-07-09
JP2002537986A (ja) 2002-11-12
NO322664B1 (no) 2006-11-13
EP1161291A1 (en) 2001-12-12
CA2362691A1 (en) 2000-09-14
DE60016899T2 (de) 2005-12-01
NO20014403D0 (no) 2001-09-11
EP1161291B1 (en) 2004-12-22
AU3527000A (en) 2000-09-28
DE60016899D1 (de) 2005-01-27

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