WO2009113445A1 - Adsorbent desulfurizer for liquid phases - Google Patents

Adsorbent desulfurizer for liquid phases Download PDF

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WO2009113445A1
WO2009113445A1 PCT/JP2009/054189 JP2009054189W WO2009113445A1 WO 2009113445 A1 WO2009113445 A1 WO 2009113445A1 JP 2009054189 W JP2009054189 W JP 2009054189W WO 2009113445 A1 WO2009113445 A1 WO 2009113445A1
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desulfurization
sulfur
adsorption
desulfurizing agent
agent
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PCT/JP2009/054189
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French (fr)
Japanese (ja)
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宏昭 櫻井
木内 正人
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独立行政法人産業技術総合研究所
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Priority to JP2010502787A priority Critical patent/JP5170591B2/en
Publication of WO2009113445A1 publication Critical patent/WO2009113445A1/en

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    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G25/00Refining of hydrocarbon oils in the absence of hydrogen, with solid sorbents
    • C10G25/12Recovery of used adsorbent
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0233Compounds of Cu, Ag, Au
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28002Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
    • B01J20/28004Sorbent size or size distribution, e.g. particle size
    • B01J20/28007Sorbent size or size distribution, e.g. particle size with size in the range 1-100 nanometers, e.g. nanosized particles, nanofibers, nanotubes, nanowires or the like
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28054Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J20/28057Surface area, e.g. B.E.T specific surface area
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/32Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3202Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the carrier, support or substrate used for impregnation or coating
    • B01J20/3204Inorganic carriers, supports or substrates
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/32Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3231Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
    • B01J20/3234Inorganic material layers
    • B01J20/3236Inorganic material layers containing metal, other than zeolites, e.g. oxides, hydroxides, sulphides or salts
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/3433Regenerating or reactivating of sorbents or filter aids other than those covered by B01J20/3408 - B01J20/3425
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/3483Regenerating or reactivating by thermal treatment not covered by groups B01J20/3441 - B01J20/3475, e.g. by heating or cooling
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B82NANOTECHNOLOGY
    • B82YSPECIFIC USES OR APPLICATIONS OF NANOSTRUCTURES; MEASUREMENT OR ANALYSIS OF NANOSTRUCTURES; MANUFACTURE OR TREATMENT OF NANOSTRUCTURES
    • B82Y30/00Nanotechnology for materials or surface science, e.g. nanocomposites
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G25/00Refining of hydrocarbon oils in the absence of hydrogen, with solid sorbents
    • C10G25/003Specific sorbent material, not covered by C10G25/02 or C10G25/03
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G2300/00Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
    • C10G2300/20Characteristics of the feedstock or the products
    • C10G2300/201Impurities
    • C10G2300/202Heteroatoms content, i.e. S, N, O, P

Definitions

  • the present invention relates to a liquid phase adsorption desulfurization agent and a desulfurization method using the desulfurization agent.
  • the so-called sulfur-free fuel with a sulfur concentration of about 10 ppm has already started to be supplied as a commercial product, but at present, there is a need for technology to further reduce the sulfur concentration.
  • a fuel for fuel cells needs to have a sulfur concentration of 0.1 ppm or less.
  • the sulfur concentration is expressed in ppm by weight, and 1 ppm when 1 ⁇ g of sulfur is contained as an element in 1 g of liquid fuel oil.
  • a hydrodesulfurization method using a cobalt-molybdenum-based catalyst is exclusively used in the production process of the liquid fuel.
  • dibenzothiophene has a relatively low hydrogenation reactivity, and therefore has a problem that it tends to remain in the liquid fuel after hydrodesulfurization treatment.
  • 4,6-dimethyldibenzothiophene having an alkyl group substituted around the sulfur atom of dibenzothiophene has low reactivity on the catalyst surface due to steric hindrance, and is a difficult-to-removable compound. Therefore, improvement of hydrodesulfurization catalysts has been promoted, and other methods such as oxidative desulfurization and adsorptive desulfurization have been recently studied.
  • the liquid phase adsorptive desulfurization method is a method of adsorbing and removing sulfur compounds by bringing liquid fuel into contact with a desulfurizing agent, and has a feature that can be implemented with a simple apparatus.
  • the desulfurization agent reaches the adsorption saturation, no further desulfurization can be performed, and the adsorbent after replacement cannot be reused, resulting in a problem that a large amount of industrial waste is generated. For this reason, it is desirable to regenerate and reuse the desulfurization agent after use, but no thiophene adsorptive desulfurization agent satisfying such properties is known.
  • activated carbon is widely used as a general adsorbent, and its specific surface area is as large as 1000 m 2 / g or more, and it has excellent adsorption ability for organic substances in general, but it is a choice that removes only sulfur-containing organic substances. It is not possible to expect a specific adsorption.
  • the activated carbon is generally heated and regenerated, but there is a drawback that the activated carbon itself is partially decomposed during the regeneration. If activated carbon is not properly controlled, the activated carbon may ignite or carbon monoxide may be decomposed when the adsorbed material is decomposed. Can cause poisoning accidents.
  • oxide-based desulfurization agents materials such as iron oxide and zinc oxide have been put to practical use because they adsorb hydrogen sulfide, but those having sufficient performance as adsorbents for thiophene-based sulfur compounds have been reported so far. Absent.
  • Zeolite-based desulfurization agents have a large specific surface area of 500 m 2 / g or more, have heat resistance, and have been studied as adsorptive desulfurization agents because their properties can be greatly changed by modification by ion exchange or the like.
  • Y-type zeolite (Cu-Y, Ce-Y) ion-exchanged with Cu or Ce is suitable as an adsorbent for thiophene compounds (see Patent Documents 2 and 3 below).
  • Patent Documents 2 and 3 there has been no report on the regeneration method after desulfurization so far, and experiments by the inventors of the present application have confirmed that it is difficult to use the regeneration by a normal heating operation.
  • Ni-based desulfurization agents exhibit excellent performance with respect to thiophene compounds.
  • the Ni-based desulfurization agent needs to be adsorbed under heating at about 200 ° C. after undergoing hydrogen reduction at a high temperature and a special stabilization treatment, and the desulfurization operation is very complicated.
  • Ni forms a stable sulfide regeneration is very difficult (see Patent Document 1 below).
  • alkanethiols in particular, are known to regularly adsorb on the gold surface to form a self-assembled monolayer (SAM).
  • SAM self-assembled monolayer
  • thiophene since the SAM formation of polyalkylthiophene by Gao et al. In 1995 (see Non-Patent Document 5 below), SAM formation has also been experimentally confirmed by several researchers. Since it can be applied to an electronic device as a conductive polymer, research in this field is becoming active.
  • the present invention has been made in view of the above-mentioned problems of the prior art, and its main purpose is to provide a desulfurization agent by liquid phase adsorption effective for sulfur compounds contained in liquid fuel, in particular, It is possible to remove thiophene-based sulfur compounds that were difficult to remove sufficiently by this method until a sulfur concentration of less than 10 ppm is reached, and a new desulfurization that can be reused with a simple treatment method after desulfurization. Is to provide an agent.
  • the present inventor has intensively studied to achieve the above-mentioned purpose.
  • metal oxides supporting gold nanoparticles known as various chemical reaction catalysts act as adsorbents with good selectivity for sulfur-containing organic compounds in liquid fuels.
  • the thiophene sulfur compound which was difficult to remove to a sufficiently low concentration by this method, could be adsorbed and removed to a sufficiently low concentration.
  • the adsorbed sulfur compound can be efficiently removed by a simple heat treatment and can be reused as an adsorbent, and the present invention has been completed here.
  • the present invention provides the following liquid phase adsorption desulfurization agent and a desulfurization method using the desulfurization agent.
  • a liquid phase adsorptive desulfurization agent obtained by supporting gold nanoparticles having an average particle size of 50 nm or less on a metal oxide.
  • a liquid phase adsorptive desulfurization agent, wherein the gold nanoparticle-supported metal oxide according to Item 1 is immobilized on a support. 4).
  • a desulfurization method comprising contacting the desulfurizing agent according to item 1 with a liquid containing a sulfur-containing organic compound. 6).
  • Item 7. The desulfurization method according to Item 6, wherein the liquid fuel to be treated contains an organic compound having a thiophene ring. 8).
  • Item 8 The desulfurization method according to Item 7, wherein the organic compound having a thiophene ring is at least one compound selected from the group consisting of dibenzothiophene and alkyldibenzothiophenes. 9.
  • a method for regenerating a desulfurization agent comprising performing a desulfurization treatment by the method of Item 5 above, and then heat-treating the desulfurization agent to remove the sulfur-containing organic compound adsorbed on the desulfurization agent. 10.
  • a desulfurization method wherein the desulfurization agent regenerated by the method of item 9 is contacted with a liquid containing a sulfur-containing organic compound by the method of claim 5.
  • Desulfurizing agent of the present invention has a structure in which gold nanoparticles having an average particle size of 50 nm or less are supported on a metal oxide.
  • Metal oxides carrying such gold nanoparticles are the oxidation removal of carbon monoxide and formaldehyde, the reduction of NOx in exhaust gas by hydrocarbons, the methanol synthesis reaction by hydrogenation of carbon monoxide and carbon dioxide, carbon monoxide It is known to exhibit high activity as a catalyst for various chemical reactions such as water gas shift reaction for producing carbon dioxide and hydrogen from water and water, and propylene oxide synthesis reaction by selective oxidation of propylene. However, until now, it has not been known at all to have a selective adsorption action for sulfur compounds in the liquid phase.
  • the substance having a structure in which the above-described nanosized gold fine particles are supported on a metal oxide has a selective adsorption action on various organic compounds containing sulfur in the liquid phase, It was newly found to be effective as a desulfurization agent.
  • the desulfurizing agent of the present invention preferably has a structure in which nano-sized gold particles are uniformly supported on the surface of the metal oxide support. Since the gold fine particles supported on the metal oxide are in a very fine state of nano-size, the gold surface area necessary for adsorption is very large and can exhibit excellent adsorption performance. In addition, it is considered that the combustion active point necessary for regeneration of the adsorbent after desulfurization is formed at the bonding interface between gold and metal oxide, so that the particle size should be as small as possible in order to increase this bonding portion. preferable.
  • the average particle diameter of the gold particles may be not less than the size of the gold atom and not more than about 50 nm, preferably about 1 to 10 nm.
  • the average particle diameter of the gold particles is the average value of the values measured by transmission electron microscopy, or the value of the crystallite diameter of gold calculated from the powder X-ray diffraction measurement data by the Sherrer equation. In the case of gold nanoparticle catalyst, it is confirmed that both values are almost the same.
  • metal oxides supporting gold particles include beryllium, magnesium, aluminum, silicon, calcium, scandium, titanium, vanadium, chromium, manganese, iron, cobalt, nickel, copper, zinc, gallium, germanium, strontium, yttrium.
  • An oxide containing a metal element such as zirconium, cadmium, indium, tin, barium, or a lanthanoid element can be used.
  • These metal oxides may be single metal oxides containing only one of the above metal elements, or complex oxides containing two or more metal elements.
  • metal oxides containing one or more metal elements such as titanium, manganese, iron, cobalt, nickel, zinc, zirconium, lanthanum, and cerium are particularly preferable.
  • the above-mentioned single metal metal oxide and composite oxide can be mixed and used as necessary.
  • beryllium, magnesium, calcium, strontium, and barium of the periodic group 2 elements may include hydroxides, basic carbonates, and the like in addition to the corresponding oxides depending on the manufacturing method.
  • the “oxide” supporting gold in the form of nanoparticles may contain these hydroxides, basic carbonates and the like.
  • the gold content is not particularly limited as long as it can be prepared so that gold can be maintained in a nanoparticle state.
  • a desulfurization agent having a gold content of about 0.1 to 60% by weight can be prepared based on the total amount of gold nanoparticles and metal oxide.
  • the form of the desulfurization agent of the present invention that is, the metal oxide supporting the gold nanoparticles can be appropriately selected depending on the purpose of use.
  • it can be used in a powder form, or can be used after being formed into a granular form, a pellet form, or the like.
  • a metal oxide supporting gold nanoparticles on a support can be fixed and used as a shape of the support.
  • the shape of the support is not particularly limited as long as the metal oxide carrying gold nanoparticles on the surface can be fixed, and is flat, block, fiber, net, bead, honeycomb, etc. anything is fine.
  • a desulfurization agent prepared in a powder form can be used by adhering to the surface of the honeycomb, or an oxide is supported on the surface of the honeycomb in advance, and a precipitation method described later is applied.
  • Gold nanoparticles can be directly supported on the surface of the lever.
  • the material of the support is not particularly limited as long as it is stable under conditions for supporting gold nanoparticles or under desulfurization conditions.
  • various ceramics can be used.
  • the specific surface area of the metal oxide in a state where gold nanoparticles are supported is preferably about 1 to 2000 m 2 / g, more preferably about 5 to 1000 m 2 / g as measured by the BET method. .
  • a metal oxide supporting gold nanoparticles having a specific surface area in the above range may be used.
  • the method for supporting gold as nano-sized particles on the metal oxide is not particularly limited, and for example, the following known preparation methods can be employed.
  • (d) Gas phase grafting method JP-A-9-122478
  • e Liquid phase grafting method (Okumura M. et al., Chem. Lett., (2000) 396)
  • a gold precursor for precipitating gold fine particles depending on the method employed, for example, heating of a water-soluble gold compound (for example, chloroauric acid), gold acetylacetonate complex, etc.
  • a water-soluble gold compound for example, chloroauric acid
  • gold acetylacetonate complex etc.
  • a compound that vaporizes due to the above can be used.
  • metal oxide raw material various metal nitrates, sulfates, acetates, chlorides, and the like can be used depending on the loading method employed. Specifically, nitrates such as cerium nitrate and zirconium nitrate, sulfates such as titanium sulfate, chlorides such as cerium chloride, titanium trichloride, and titanium tetrachloride can be used.
  • the coprecipitation method (a) first, a precursor of these oxides and a gold precursor are simultaneously precipitated under alkaline conditions. Subsequently, the precipitate of the mixture of the obtained gold hydroxide and the oxide precursor hydroxide is filtered, washed with water, and dried, and then heat treatment described later is performed to obtain an oxide carrying gold nanoparticles.
  • the oxide precursor is preliminarily formed into an oxide or hydroxide before carrying gold. It is also possible to use what is marketed as an oxide or hydroxide from the beginning. These may be in any form, and may be in the form of powder, beads, pellets, honeycombs, etc. Even if they are not of a single composition, for example, a ceramic honeycomb coated with titanium oxide is also used. it can.
  • a gold precursor is supported on the surface of the oxide or hydroxide as described above by the methods (b) to (e), and if necessary, filtered, washed with water, dried, and then subjected to a heat treatment to be described later. An oxide carrying particles can be obtained.
  • heat treatment may be performed in various atmospheres such as an oxygen-containing atmosphere, a reducing gas atmosphere, and an inert gas atmosphere.
  • an oxygen-containing atmosphere an air atmosphere or a mixed gas atmosphere in which oxygen is diluted with nitrogen, helium, argon, or the like can be used.
  • the reducing gas for example, about 1 to 10 vol% hydrogen gas or carbon monoxide gas diluted with nitrogen gas can be used.
  • nitrogen, helium, argon, or the like can be used as the inert gas.
  • the heat treatment temperature may be appropriately selected from the range of known metal gold production conditions, and is usually preferably about room temperature to 600 ° C. In order to obtain stable and fine gold particles, about 200 to 400 ° C. is more preferable.
  • the heat treatment time may be about 1 to 12 hours, for example.
  • the desulfurization agent of the present invention can be applied to a method of adsorbing and removing various organic compounds containing sulfur in the liquid phase.
  • sulfur-containing organic compounds include thiol (R-SH), sulfide (RSR), disulfide (RSSR), tetrahydrothiophene, and thiophene compounds.
  • the thiophene compound means a compound group having a thiophene ring, and examples thereof include thiophene, alkylthiophene, benzothiophene, alkylbenzothiophene, dibenzothiophene, alkyldibenzothiophene, and dialkyldibenzothiophene. .
  • the desulfurizing agent of the present invention is effectively used for adsorptive desulfurization of sulfur-containing organic compounds remaining in liquid fuel, particularly thiophene compounds.
  • the desulfurizing agent of the present invention it has been difficult to reduce the sulfur concentration below 10 ppm by a conventional method until a sulfur concentration below 10 ppm is reached for a thiophene compound such as 4,6-dimethylbenzothiophene. It can be removed by adsorption.
  • the type of liquid fuel to be treated is not particularly limited, and any of gasoline, kerosene, kerosene, light oil, heavy oil, etc. may be used.
  • the sulfur concentration contained in the liquid fuel before treatment is not particularly limited, but hydrodesulfurization and other methods are taken into consideration that the amount of desulfurization agent required is increased when directly treating high-sulfur fuel oil.
  • the sulfur concentration is preferably 50 ppm or less in advance, and more preferably 10 ppm or less.
  • Desulfurization method In the desulfurization method using the desulfurization agent of the present invention, a sulfur-containing organic compound in the liquid can be adsorbed and desulfurized by bringing the liquid to be desulfurized, for example, liquid fuel into contact with the desulfurization agent.
  • a sulfur-containing organic compound in the liquid can be adsorbed and desulfurized by bringing the liquid to be desulfurized, for example, liquid fuel into contact with the desulfurization agent.
  • a general method there are two methods, a batch method and a flow method.
  • a method of introducing a desulfurizing agent into a container containing liquid fuel and stirring can be employed.
  • the appropriate amount of the desulfurizing agent varies depending on the type of desulfurizing agent actually used. For example, it is preferably used in the range of 1 to 500 g of desulfurizing agent for 1 liter of liquid fuel, and 10 to 10 desulfurizing agent for 1 liter of liquid fuel. More preferably, it is used in the range of 100 g.
  • the processing temperature is not particularly limited as long as the fuel to be processed can maintain a liquid state, and may be performed at room temperature, for example.
  • the pressure is not particularly limited, and it may be in a pressurized state. Usually, the treatment may be performed under atmospheric pressure.
  • a desulfurizing agent is added, and a liquid and a desulfurizing agent with a reduced amount of sulfur-containing organic compound can be obtained by separating the liquid and the desulfurizing agent after a predetermined time has elapsed.
  • the treatment time varies depending on the concentration of the sulfur compound and the amount of the desulfurization agent used, so it cannot be specified unconditionally. For example, the treatment is performed within the range of 1 hour to several days until the desired desulfurization effect is obtained. Just do it.
  • the separated desulfurizing agent can be regenerated and reused by, for example, a method described later, which is dried and then heated in air.
  • a desulfurizing agent is filled in a layered manner in a tubular container, and the liquid to be treated is circulated at a constant flow rate.
  • the liquid hourly space velocity (LHSV) can be set, for example, within a range of about 0.01 to 100 h ⁇ 1 , preferably about 0.01 to 1 h ⁇ 1 .
  • the temperature conditions, pressure conditions, and the like at the time of desulfurization are not particularly limited as long as the fuel is in a liquid range as in the case of the batch method. If there is no external heating source, it may be performed at room temperature. When the liquid fuel is supplied in a preheated state, adsorptive desulfurization can be performed at the same temperature.
  • the sulfur-containing organic compound adsorbed on the desulfurizing agent is removed by heating the desulfurizing agent, and the desulfurizing agent is regenerated and reused. Can do.
  • the heat treatment of the desulfurizing agent it is desirable to heat the desulfurizing agent after washing with a solvent or the like, if necessary.
  • the heat treatment can be performed in various atmospheres such as inert gas, diluted oxygen, air, water vapor, diluted hydrogen and the like.
  • the metal oxide supporting the gold nanoparticles constituting the desulfurizing agent of the present invention is a reaction of hydrocarbons such as methane and propane with O 2 (combustion reaction), a reaction of carbon compounds such as CO and H 2 O (shift reaction). It is known that it has catalytic activity for any of the reaction (hydrogenation reaction) of carbon compounds such as CO, CO 2 and aldehyde with H 2 (hydrogenation reaction). For this reason, by performing a heat treatment in an atmosphere containing any of O 2 , H 2 O, and H 2 , a catalytic reaction between these molecules and the sulfur-containing organic compound adsorbed on the surface of the desulfurizing agent or a sulfur-containing organic compound Thus, the adsorbed sulfur-containing organic compound can be efficiently removed.
  • the concentration range of O 2 , H 2 O, H 2, etc. in the atmosphere is not particularly limited, but especially when H 2 is included, it is necessary to avoid the explosion composition.
  • the pressure condition normal pressure may be used in the case of a combustion reaction, but in the case of performing a hydrogenation reaction or the like, the reaction may be accelerated by pressurizing at about 10 MPa or less.
  • the heating temperature can be selected in the range of about 50 to 500 ° C, preferably about 100 to 400 ° C, more preferably about 150 to 400 ° C. An excessively high heating temperature is not preferable because gold nanoparticles tend to aggregate and the adsorption performance after regeneration deteriorates.
  • the desulfurizing agent of the present invention has a selective adsorption action for sulfur-containing organic compounds in the liquid phase.
  • the sulfur compound concentration in the liquid fuel can be lowered to a level that is difficult with the prior art.
  • the desulfurizing agent of the present invention can be used for various applications by utilizing such excellent adsorption removal performance for sulfur-containing organic compounds.
  • the sulfur-containing organic compound is adsorbed and removed using an adsorption tower filled with the desulfurizing agent of the present invention, thereby allowing sulfur in the liquid fuel.
  • the concentration can be made 10 ppm or less, and in particular, the sulfur concentration desired for fuel for fuel cells can be lowered to 0.1 ppm or less.
  • a column filled with the desulfurization agent of the present invention is installed between a tank of a gas station and a fueling machine, and desulfurization is performed when fueling an automobile. It can also be used.
  • FIG. 3 is a graph showing a change over time in a dibenzothiophene concentration in a solution in Test Example 1.
  • FIG. 4 is a graph showing the sulfur concentration remaining in the solution after conversion to equilibrium (converted from the analysis value of dibenzothiophene concentration) and the amount of dibenzothiophene adsorbed on the desulfurizing agent when the amount of desulfurizing agent used is changed in Test Example 2.
  • DBT dibenzothiophene
  • DMDBT 4,6-dimethyldibenzothiophene
  • NA naphthalene
  • 6 is a graph showing the amount of saturated adsorption of dibenzothiophene (DBT) in each adsorption operation when adsorption-regeneration is repeated in Test Example 4.
  • 6 is a graph showing the relationship between the heating temperature of regeneration treatment in Test Example 5 and the saturated adsorption amount of dibenzothiophene (DBT) of a sample after regeneration.
  • 6 is a graph in which the amount of CO 2 generated during temperature rise is plotted against temperature when heat regeneration treatment at 350 ° C. is performed in Test Example 5.
  • Test Example 6 a graph showing the saturated adsorption amount of 4,6-dimethyldibenzothiophene (DMDBT) in test solution E obtained for each sample in comparison with the adsorption amounts of DBT, DMDBT, and NA in test solutions A and C It is.
  • DMDBT 4,6-dimethyldibenzothiophene
  • Example 1 (1) Preparation of desulfurization agent Desulfurization agent 1: gold / cerium oxide (Au / CeO 2 ) 1000 mL of an aqueous solution of chloroauric acid [HAuCl 4 ⁇ 4H 2 O] (5 mmol / L) was heated to 70 ° C., and KOH was added dropwise to adjust the pH to 7. 7.7 g of cerium oxide powder was added, and then 370 mL of a 10 mmol / L solution of magnesium citrate was added. After stirring for 1 hour, filtration, washing and drying, the resulting powder is calcined in air at 400 ° C.
  • the average particle diameter of the gold nanoparticles in the examples is the value of the crystallite diameter of gold calculated from the powder X-ray diffraction measurement data according to the Sherrer equation.
  • Desulfurization agent 2 Gold / cerium oxide (Au / CeO 2 )
  • the gold nanoparticles with an average particle size of 4.9 nm are supported on the cerium oxide surface in the same manner as the preparation of the desulfurizing agent 1 except that the amount of chloroauric acid used is reduced and magnesium citrate is not added.
  • Desulfurization agent 3 Gold / Zinc oxide (Au / ZnO) An aqueous solution in which 8 g of sodium carbonate Na 2 CO 3 was dissolved in 200 mL of water was heated to 70 ° C. An aqueous solution prepared by dissolving 14.2 g of zinc nitrate and 1.1 g of chloroauric acid in 200 mL of water was added thereto at 70 ° C. to form a precipitate. After stirring for 1 hour, filtration, washing and drying, the resulting powder is calcined in air at 400 ° C. for 4 hours to desulfurize the structure in which gold nanoparticles with an average particle size of 5.8 nm are supported on the surface of zinc oxide Agent 3 (Au / ZnO) (Au supported amount 10.0 wt%) was prepared.
  • Desulfurization agent 4 Gold / titanium oxide (Au / TiO 2 ) 1000 mL of an aqueous solution of chloroauric acid (5 mmol / L) was heated to 70 ° C., and KOH was added dropwise to adjust the pH to 7. 3.6 g of titanium oxide powder was added, and then 400 mL of a 10 mmol / L solution of magnesium citrate was added. After stirring for 1 hour, filtration, washing with water and drying, the resulting powder is baked in air at 400 ° C. for 4 hours to desulfurize the structure in which gold nanoparticles with an average particle size of 4.0 nm are supported on the surface of titanium oxide. Agent 4 (Au / TiO 2 ) (Au gold supported amount 21.5 wt%) was prepared.
  • Comparative desulfurization agent 1 Cerium oxide (CeO 2 ) The cerium oxide powder used for the preparation of the desulfurizing agents 1 and 2 was used as it was.
  • Comparative desulfurization agent 2 Platinum / Cerium oxide (Pt / CeO 2 ) 500 mL of an aqueous solution of chloroplatinic acid [H 2 PtC 6 ⁇ 6H 2 O] (2 mmol / L) was heated, and KOH was added dropwise to adjust the pH to 7. 6.5 g of cerium oxide powder was added. After stirring for 1 hour, filtration, washing with water and drying, the powder obtained was calcined in air at 400 ° C for 4 hours, and further raised to 350 ° C under the flow of H 2 (3%) + He (balance) mixed gas. Pt was reduced by heating to prepare a comparative desulfurization agent 2 (Pt / CeO 2 ) (Pt loading 3.0 wt%) in which platinum having an average particle size of 2.0 nm or less was supported on the surface of cerium oxide.
  • Pt / CeO 2 platinum / Cerium oxide
  • Comparative desulfurization agent 3 Cerium ion exchange Y-type zeolite (Ce-Y) 0.75 g of Y-type zeolite powder was added to 30 mL of an aqueous solution of cerium nitrate [Ce (NO 3 ) 3 ⁇ 6H 2 O] (0.2 mol / L), and the mixture was shaken and stirred for 3 days.
  • the comparative desulfurization agent 3 made of cerium ion-exchanged Y-type zeolite (Ce-Y) was prepared by filtering, washing and drying, and calcining the obtained powder at 400 ° C. in air for 2 hours.
  • Comparative desulfurization agent 4 Copper / Zinc oxide (Cu / ZnO) An aqueous solution in which 7.6 g of sodium carbonate Na 2 CO 3 was dissolved in 200 mL of water was heated to 70 ° C. An aqueous solution in which 12.5 g of zinc nitrate and 4.3 g of copper nitrate were dissolved in 300 mL of water was added thereto at 70 ° C. to form a precipitate. After stirring for 1 hour, it was filtered, washed with water and dried. The obtained powder was calcined in air at 400 ° C. for 4 hours, and further heated to 400 ° C.
  • Comparative desulfurizing agent 4 (Cu / ZnO) (Cu supported amount 25.1 wt%) in which copper of nm was supported on the surface of zinc oxide was prepared.
  • Test solution A n-decane (manufactured by Kishida Chemical, special grade) as a solvent, dibenzothiophene (manufactured by Kanto Chemical Co., special grade) as an organic sulfur compound, 39.9 mg / L, n-tetradecane (manufactured by Kishida Chemical, special grade) as an internal standard for solution analysis ) was prepared to contain 39.5 mg / L. The sulfur concentration of this solution corresponds to 9.5 ppm.
  • Test solution B Similarly to test solution A, a solution containing 51.2 mg / L of dibenzothiophene as an organic sulfur compound was prepared using n-decane as a solvent. The sulfur concentration of this solution corresponds to 12.2 ppm.
  • Test solution C n-decane (manufactured by Kishida Chemical, special grade) as a solvent, dibenzothiophene (manufactured by Kanto Chemical Co., special grade) as an organic sulfur compound, 22.7 mg / L, 4,6-dimethyldibenzothiophene (manufactured by Wako Pure Chemical, special grade), 23.1 mg / L, 22.1 mg / L of naphthalene (made by Wako Pure Chemicals, special grade) as an aromatic organic compound not containing sulfur, and 26.5 mg / L of n-tetradecane (made by Kishida Chemical, special grade) as an internal standard for solution analysis
  • a solution containing L was prepared. The sulfur concentration of this solution is 5.4 ppm as dibenzothiophene and 4.8 ppm as 4,6-dimethyldibenzothiophene, for a total of 10.2 ppm.
  • Test solution D Similarly to the test solution A, a solution containing n-decane as a solvent, 43.2 mg / L of dibenzothiophene as an organic sulfur compound, and 69.3 mg / L of n-tetradecane as an internal standard for solution analysis was prepared. The sulfur concentration of this solution corresponds to 10.3 ppm.
  • Test solution E n-decane (manufactured by Kishida Chemical, special grade) is used as a solvent, 4,6-dimethyldibenzothiophene (manufactured by Wako Pure Chemical Industries, special grade) is 46.7 mg / L, and n-tetradecane (manufactured by Kishida Chemical Co., Ltd.) is used as an internal standard for solution analysis. , Special grade) 45.3 mg / L. The sulfur concentration of this solution corresponds to 9.7 ppm.
  • Adsorption and regeneration test method test example 1 Each sample powder of desulfurizing agents 1 and 2 and comparative desulfurizing agent 1 prepared by the above method was heated in air at 300 ° C. for 30 minutes to remove adsorbed water, and then cooled to room temperature in a desiccator containing silica gel. . 100 mg of this sample was weighed into a screw tube bottle, 5 mL of test solution A was added, the cap was capped, and this time was taken as the adsorption start time. The solution was stirred using a shaker at room temperature.
  • the temperature of the desulfurizing agent 1 is raised to 60 ° C for 8.5 to 24 hours, and the desulfurizing agent 2 and the comparative desulfurizing agent 1 are raised to 60 ° C for 27 to 47 hours. It has been confirmed in a separate experiment that there is almost no effect on adsorption. Every few hours after the start of adsorption, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC. The time change of the dibenzothiophene concentration in the solution is shown in FIG.
  • the desulfurization agents 1 and 2 in which gold nanoparticles are supported on cerium oxide have a larger adsorption amount of dibenzothiophene than the comparative desulfurization agent 1 made only of cerium oxide. It can be seen that with a large amount (11.3 wt%) of the desulfurizing agent 1, the amount of adsorption of dibenzothiophene is very large. In addition, as for desulfurizing agents 1 and 2, the adsorption amount was stabilized after 24 hours or more, whereas in comparative desulfurizing agent 1 consisting only of cerium oxide, it was confirmed that the adsorption amount decreased after 5 hours. .
  • dibenzothiophene having a sulfur concentration of 10 ppm in the decane solution can be effectively adsorbed and desulfurized by using desulfurization agents 1 and 2 in which gold nanoparticles are supported on cerium oxide.
  • Test example 2 One sample powder of the desulfurizing agent prepared by the above method was heated in air at 300 ° C. for 30 minutes to remove adsorbed water, and then cooled to room temperature in a desiccator containing silica gel. Weighed 26, 51, 101, 200, and 300 mg of this sample in 5 screw tube bottles, added 5 mL of test solution B to each screw tube bottle, capped, and this time was taken as the adsorption start time. . The solution was stirred using a shaker at room temperature. The solution was extracted and analyzed with a dropper 74 hours after the start of adsorption (confirming that the adsorption equilibrium was reached). A known amount of 2,8-dimethyldibenzothiophene (manufactured by Tokyo Chemical Industry Co., Ltd.) was added to each analysis solution as an internal standard substance, and composition analysis was performed by FPD-GC.
  • FIG. 2 is a graph showing the relationship between the weight of the desulfurizing agent used, the sulfur concentration remaining in the test example solution after adsorption, and the amount of dibenzothiophene (DBT) adsorbed by the desulfurizing agent.
  • the sulfur concentration in the test solution in FIG. 2 is obtained by converting the DBT concentration into the sulfur concentration.
  • FIG. 2 clearly shows that the total amount of adsorbed dibenzothiophene (DBT) increases and the amount of DBT remaining in the solution decreases as the amount of the desulfurizing agent increases.
  • DBT dibenzothiophene
  • Test example 3 Using the desulfurizing agents 1, 3, and 4 and comparative desulfurizing agents 2 to 4 prepared by the above method, adsorption and regeneration experiments were performed by the following procedures (1) to (3).
  • DBT + DMDBT dibenzothiophenes
  • the comparative desulfurizing agent 2 made of cerium ion Y-type exchanged zeolite (Ce-Y) has a larger total adsorption amount than the desulfurizing agents 1, 3, and 4, but DBT, DMDBT, NA are almost equimolar The selective adsorption to sulfur-containing organic compounds was not observed.
  • desulfurizing agents 1, 3 and 4 can adsorb 70% or more of dibenzothiophenes (DBT + DMDBT) in the first adsorption test, and the adsorption rate after regeneration is comparative desulfurizing agent 2 It is clear that it is much higher than 3 and 3.
  • Cu / ZnO (Comparative desulfurization agent 4), which is effective as an adsorbent for hydrogen sulfide, has a small amount of dibenzothiophenes adsorbed despite the fact that Cu, which is the same group IB element as Au, is supported in large quantities. It can be seen that the performance as an adsorbent for sulfur-containing organic compounds is poor.
  • Test example 4 Repeated tests of adsorption of dibenzothiophene (DBT) and regeneration of desulfurization agent were performed by the following methods (1) to (3). This test was conducted by devising a treatment method during regeneration in order to prevent a decrease in the recovered amount of the desulfurizing agent after regeneration.
  • DBT dibenzothiophene
  • test solution D 5 mL of test solution D was added and a Teflon (registered trademark) stopper was added, and this time was taken as the adsorption start time.
  • the solution was stirred using a shaker at room temperature. When the adsorption equilibrium was reached after 24 hours or more, the shaking was stopped and the flask was allowed to stand to allow the desulfurizing agent powder to settle. The supernatant was extracted with a dropper and the solution composition was analyzed with FID-GC.
  • the mixture was cooled to room temperature in a desiccator containing silica gel, the flask was taken out of the desiccator, immediately plugged with Teflon (registered trademark), and weighed to determine the weight of the desulfurizing agent after regeneration.
  • Teflon registered trademark
  • test solution D was added at a rate of 5 mL to 100 mg of the desulfurizing agent powder in the flask, and the Teflon (registered trademark) stopper was attached. (Second adsorption start). The solution was stirred using a shaker at room temperature. When the adsorption equilibrium was reached after 24 hours or more, the shaking was stopped and the flask was allowed to stand to allow the desulfurizing agent powder to settle. The supernatant was extracted with a dropper and the solution composition was analyzed with GC. Thereafter, the regeneration and adsorption operations were repeated in the same manner.
  • the adsorbent powder stuck to the vessel wall at the top of the flask and contact with the solution worsened. Therefore, in the fourth and subsequent adsorptions, the adsorbent solution was added at the start of adsorption, and the Teflon (registered trademark) plug was inserted. Then, the flask was immersed in the water of an ultrasonic cleaner and operated for 10 seconds to several minutes to improve the dispersion of the adsorbent powder and to recover the contact with the solution.
  • the amount of dibenzothiophene (DBT) adsorbed per gram of desulfurizing agent powder was calculated from the analysis result of the solution composition at the end of each adsorption. The results are shown in FIG.
  • FIG. 4 clearly shows that there is no significant decrease in the amount of adsorption even if adsorption-regeneration is repeated.
  • the adsorption amount is slightly reduced in the second and third times, but in the first to third adsorptions, the operation of improving the dispersibility of the adsorbent is not performed at the start of adsorption using an ultrasonic cleaner. This is probably due to the fact that the state of contact with the sample was slightly worse.
  • the adsorption amount was stable in the fourth and fifth adsorption, and the adsorption amount of 95% or more during the first adsorption could be maintained.
  • the desulfurization agent of the present invention in which gold nanoparticles are supported on a metal oxide is excellent in selective adsorption performance for sulfur-containing organic compounds, particularly dibenzothiophenes, and is also regenerated by heating. After the treatment, it is clear that sufficient adsorption performance can be exhibited and reused as a desulfurization agent.
  • Test Example 5 The desulfurization agent 1 prepared by the above method was used for adsorption and regeneration in the following procedures (1) to (3), and the influence of the heating temperature during regeneration was examined.
  • test solution A 5 mL was added to each screw tube bottle and the lid was covered, and this time was taken as the adsorption start time.
  • the solution was stirred using a shaker at room temperature. When the adsorption equilibrium was reached after 24 hours or more had passed, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC.
  • the desulfurization agent After the heat treatment of the desulfurization agent at 25, 100, 150, 200, 250, 300 or 350 ° C in this way, it was cooled to room temperature in a desiccator containing silica gel and the relative humidity was adjusted to 85% with a saturated potassium chloride solution. It was left overnight to absorb moisture.
  • test solution A was added at a ratio of 5 mL with respect to 100 mg of the desulfurization agent powder, and the cap was capped.
  • the adsorption equilibrium was reached after 24 hours or more had passed, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC.
  • the amount of dibenzothiophene (DBT) adsorbed per gram of desulfurizing agent powder was calculated from the analysis results of the solution composition.
  • the DBT adsorption amount of 3.3 ⁇ 0.1 ⁇ mol / g-catalyst for each of the seven screw tube bottles adsorbed under the same conditions.
  • FIG. 5 shows the relationship between the heat treatment temperature and the DBT adsorption amount for the second DBT adsorption amount after the heat treatment regeneration at each temperature. From FIG. 5, it can be seen that for the desulfurization agent 1 (Au / CeO 2 ), at the heat treatment temperature of 100 ° C.
  • the second adsorption amount is greatly reduced compared to the first treatment, and the heat treatment is not sufficient. Further, at a heat treatment temperature of 200 ° C. or higher, the amount of adsorption at the second time becomes almost the same as that at the first time, and it can be confirmed that the regeneration is completely completed.
  • FIG. 6 is a graph in which the amount of CO 2 generated during heating is plotted against temperature when heated to 350 ° C.
  • CO 2 peaks were observed at two temperatures, 115 ° C and 225 ° C. Of these, the peak on the low temperature side was also observed in the Au / CeO 2 sample that did not adsorb DBT, which is thought to have adsorbed CO 2 in the air. The peak on the high temperature side was observed only after DBT adsorption, and it is considered that the adsorbed DBT burned on the catalyst surface and became CO 2 .
  • the amount of CO 2 corresponding to the shaded portion in FIG.
  • Test Example 6 The desulfurization agents 1, 3 and 4 prepared by the above method were subjected to adsorption experiments according to the following procedure using the test solution E (a solution containing only 4,6-dimethyldibenzothiophene as dibenzothiophenes).
  • Each desulfurization agent was heated in air at 350 ° C. for 30 minutes to remove adsorbed water, and then cooled to room temperature in a desiccator containing silica gel.
  • 100 mg of each desulfurizing agent was weighed into a screw tube bottle, 5 mL of the test solution E was added and the lid was covered, and this time was taken as the adsorption start time.
  • the solution was stirred using a shaker at room temperature. When the adsorption equilibrium was reached after 24 hours or more had passed, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC.
  • FIG. 7 further shows the results of an adsorption test using test solution A (a solution containing only DBT) and test solution C (a mixed solution of DBT, DMDBT, and NA) calculated from the results of Test Example 1 and Test Example 3. Also shown.
  • test solution A a solution containing only DBT
  • test solution C a mixed solution of DBT, DMDBT, and NA
  • test solution E which is a solution of DMDBT alone
  • test solution C which is a mixed solution.
  • desulfurization agent 1 Au / CeO 2
  • the amount of DMDBT adsorbed from a solution of DMDBT alone (test solution E) compared to the amount of DBT adsorbed from a solution of DBT alone (test solution A) is approximately 97%. It can be confirmed that the adsorbent of the present invention has excellent adsorption performance for DMDBT.

Abstract

Provided are an adsorbent desulfurizer for liquid phases made by loading gold nanoparticles with a mean particle diameter of 50 nm or less on a metal oxide, a desulfurizing method characterized by the fact that said desulfurizer is brought into contact with a liquid that includes sulfur-containing organic compounds, and a desulfurizer regeneration method characterized by the fact that the desulfurizer is heat-treated to remove the sulfur-containing organic compounds adsorbed onto said desulfurizer. This invention can remove even thiophene sulfur compounds, for which satisfactory removal was difficult with prior methods, to sulfur concentrations of 10 ppm and below. Also provided is a novel desulfurizer that can be regenerated with a simple treatment method after the desulfurizing treatment.

Description

液相用吸着脱硫剤Adsorption desulfurization agent for liquid phase
 本発明は、液相用吸着脱硫剤、及び該脱硫剤を用いる脱硫方法に関する。 The present invention relates to a liquid phase adsorption desulfurization agent and a desulfurization method using the desulfurization agent.
 公害防止、エンジンの燃費向上、将来の自動車用燃料電池システムへの対応等の観点から、ガソリン、灯油、軽油等の液体燃料に含まれる硫黄濃度をより低減させることが要求されている。このため、液体燃料からの脱硫技術の確立が重要な課題となっている。 From the standpoints of pollution prevention, improvement of engine fuel consumption, and response to future automotive fuel cell systems, it is required to further reduce the concentration of sulfur contained in liquid fuels such as gasoline, kerosene and light oil. For this reason, establishment of desulfurization technology from liquid fuel has become an important issue.
 硫黄濃度が10ppm程度のいわゆるサルファーフリー燃料については、既に商品としての供給が開始されているが、現在、それ以上に硫黄濃度を低減させる技術が求められている。特に、燃料電池用の燃料については、硫黄濃度を0.1ppm以下にする必要があると言われている。尚、本願明細書において、硫黄濃度のppm表示は重量ppmであり、液体燃料油1g中に硫黄分が元素として1μg含まれる場合を1ppmとする。 The so-called sulfur-free fuel with a sulfur concentration of about 10 ppm has already started to be supplied as a commercial product, but at present, there is a need for technology to further reduce the sulfur concentration. In particular, it is said that a fuel for fuel cells needs to have a sulfur concentration of 0.1 ppm or less. In the present specification, the sulfur concentration is expressed in ppm by weight, and 1 ppm when 1 μg of sulfur is contained as an element in 1 g of liquid fuel oil.
 液体燃料中の硫黄濃度を減少させる方法としては、液体燃料の製造工程では、コバルト-モリブデン系触媒を用いた水素化脱硫法が専ら用いられている。しかしながら、液体燃料に含まれる各種硫黄化合物のうちでジベンゾチオフェンは相対的に水素化の反応性が低いために、水素化脱硫処理後にも液体燃料に残存しやすいという問題点がある。特に、ジベンゾチオフェンの硫黄原子の周辺にアルキル基が置換された4,6-ジメチルジベンゾチオフェン等は立体障害のため触媒表面での反応性が低く、難除去性化合物となっている。そこで、水素化脱硫触媒の改良が進められており、更に、酸化脱硫や吸着脱硫などの他法も最近検討されている。 As a method for reducing the sulfur concentration in the liquid fuel, a hydrodesulfurization method using a cobalt-molybdenum-based catalyst is exclusively used in the production process of the liquid fuel. However, among the various sulfur compounds contained in the liquid fuel, dibenzothiophene has a relatively low hydrogenation reactivity, and therefore has a problem that it tends to remain in the liquid fuel after hydrodesulfurization treatment. In particular, 4,6-dimethyldibenzothiophene having an alkyl group substituted around the sulfur atom of dibenzothiophene has low reactivity on the catalyst surface due to steric hindrance, and is a difficult-to-removable compound. Therefore, improvement of hydrodesulfurization catalysts has been promoted, and other methods such as oxidative desulfurization and adsorptive desulfurization have been recently studied.
 液相吸着脱硫法は、液体燃料を脱硫剤と接触させて硫黄化合物を吸着除去する方法であり、簡単な装置で実施できる特徴がある。しかしながら、脱硫剤が吸着飽和に達するとそれ以上は脱硫できず、交換後の吸着剤は再使用できないため、産業廃棄物が多量に発生するという問題がある。このため、使用後の脱硫剤を再生して再使用することが望まれるが、チオフェン類の吸着脱硫剤において、このような性質を満たすものは知られていない。 The liquid phase adsorptive desulfurization method is a method of adsorbing and removing sulfur compounds by bringing liquid fuel into contact with a desulfurizing agent, and has a feature that can be implemented with a simple apparatus. However, when the desulfurization agent reaches the adsorption saturation, no further desulfurization can be performed, and the adsorbent after replacement cannot be reused, resulting in a problem that a large amount of industrial waste is generated. For this reason, it is desirable to regenerate and reuse the desulfurization agent after use, but no thiophene adsorptive desulfurization agent satisfying such properties is known.
 現在、液相吸着脱硫剤として検討されている材料は、活性炭系、金属酸化物系、ゼオライト系及び金属系の4つのカテゴリーに分類できる(下記非特許文献1参照)。これらの内で、活性炭は、一般的な吸着剤として広く使用されており、比表面積が1000m2/g以上と非常に大きく、有機物一般の吸着能力に優れるが、含硫黄有機物だけを除去する選択的吸着については期待できない。また活性炭の加熱再生は一般的に行われているが、再生時に活性炭自体が一部分解される欠点があり、安全管理を適切に行わないと活性炭が発火したり、吸着物の分解時に一酸化炭素が発生して中毒事故などが起こる可能性がある。 Currently, materials that are being studied as liquid phase adsorption desulfurization agents can be classified into four categories: activated carbon, metal oxide, zeolite, and metal (see Non-Patent Document 1 below). Among these, activated carbon is widely used as a general adsorbent, and its specific surface area is as large as 1000 m 2 / g or more, and it has excellent adsorption ability for organic substances in general, but it is a choice that removes only sulfur-containing organic substances. It is not possible to expect a specific adsorption. In addition, the activated carbon is generally heated and regenerated, but there is a drawback that the activated carbon itself is partially decomposed during the regeneration. If activated carbon is not properly controlled, the activated carbon may ignite or carbon monoxide may be decomposed when the adsorbed material is decomposed. Can cause poisoning accidents.
 酸化物系脱硫剤としては、酸化鉄、酸化亜鉛などの材料が硫化水素を吸着するため実用化されているが、チオフェン系硫黄化合物の吸着剤として十分な性能を持つものはこれまで報告されていない。 As oxide-based desulfurization agents, materials such as iron oxide and zinc oxide have been put to practical use because they adsorb hydrogen sulfide, but those having sufficient performance as adsorbents for thiophene-based sulfur compounds have been reported so far. Absent.
 ゼオライト系脱硫剤は、比表面積が500m2/g以上と大きく、耐熱性もあり、イオン交換等による修飾で特性を大きく変えられるため、吸着脱硫剤としても検討されている。例えば、CuやCeでイオン交換したY型ゼオライト(Cu-Y, Ce-Y)がチオフェン類化合物の吸着剤として適することが報告されている(下記特許文献2,3参照)。しかしながら、脱硫後の再生法についてはこれまでに報告がなく、本願発明者等の実験では、通常の加熱操作では再生使用が難しいことが確認されている。 Zeolite-based desulfurization agents have a large specific surface area of 500 m 2 / g or more, have heat resistance, and have been studied as adsorptive desulfurization agents because their properties can be greatly changed by modification by ion exchange or the like. For example, it has been reported that Y-type zeolite (Cu-Y, Ce-Y) ion-exchanged with Cu or Ce is suitable as an adsorbent for thiophene compounds (see Patent Documents 2 and 3 below). However, there has been no report on the regeneration method after desulfurization so far, and experiments by the inventors of the present application have confirmed that it is difficult to use the regeneration by a normal heating operation.
 金属系の脱硫剤については、金属種により有効に吸着除去できる硫黄化合物の種類が異なり、Ni系脱硫剤がチオフェン類化合物に関して優れた性能を示すことが知られている。しかしながら、Ni系脱硫剤は、高温での水素還元と特殊な安定化処理を経た後に200℃程度の加熱下で吸着を行わせることが必要であり、脱硫操作が非常に煩雑である。また、Niが一度安定な硫化物を形成すると再生は非常に困難である(下記特許文献1参照)。 Regarding metal-based desulfurization agents, the types of sulfur compounds that can be effectively adsorbed and removed vary depending on the metal species, and it is known that Ni-based desulfurization agents exhibit excellent performance with respect to thiophene compounds. However, the Ni-based desulfurization agent needs to be adsorbed under heating at about 200 ° C. after undergoing hydrogen reduction at a high temperature and a special stabilization treatment, and the desulfurization operation is very complicated. Moreover, once Ni forms a stable sulfide, regeneration is very difficult (see Patent Document 1 below).
 ところで、金属酸化物を担体として、その表面に貴金属ナノ粒子として担持した材料が、各種の化学反応に対して高い活性を有することが知られており、各種の化学反応用触媒として用いられている。この様な貴金属触媒では、一般に硫黄化合物は貴金属触媒の活性点に吸着して、触媒毒となることが知られている。このため、Pt, Pd等の貴金属触媒を脱硫の目的に検討した報告はコバルト-モリブデン系触媒と比べ少ないが、例えば、白金をゼオライトに担持した系が水素化脱硫に活性を示すことが最近報告されている(下記非特許文献4参照)。また、白金触媒に対し、金の添加により水素化脱硫性能の制御を試みた報告はあるが、貴金属として金のみを含む材料については脱硫触媒として報告された例はない。 By the way, it is known that a material having a metal oxide as a carrier and supported as noble metal nanoparticles on the surface thereof has high activity for various chemical reactions, and is used as a catalyst for various chemical reactions. . In such noble metal catalysts, it is generally known that sulfur compounds are adsorbed on the active sites of noble metal catalysts and become catalyst poisons. For this reason, there are few reports examining noble metal catalysts such as Pt, Pd, etc. for the purpose of desulfurization compared to cobalt-molybdenum-based catalysts, but recently, for example, a system in which platinum is supported on zeolite shows activity in hydrodesulfurization. (See Non-Patent Document 4 below). In addition, although there has been a report of trying to control hydrodesulfurization performance by adding gold to a platinum catalyst, there is no report of a material containing only gold as a noble metal as a desulfurization catalyst.
 硫黄化合物の内で、特にアルカンチオール類(RSH)は、金の表面に規則正しく吸着して自己組織化単分子膜(SAM:Self Assembled Monolayer)を形成することが知られている。また、チオフェンについても、1995年のGaoらによるポリアルキルチオフェンのSAM形成の報告(下記非特許文献5参照)以来、SAM形成についても複数の研究者により実験的に確認されており、チオフェンポリマーが導電性高分子として電子デバイスなどへの応用が可能であることから、この分野での研究は盛んになりつつある。このように単純なチオフェンあるいはアルキルチオフェンに関してはAu表面への吸着現象とその応用が検討されているが、SAMとして単分子膜を利用する目的からAuの単結晶が専ら用いられており、吸着量が少ないために、吸着脱硫剤として用いられることは無く、液体燃料からの脱硫の対象として重要なジベンゾチオフェン類の吸着については報告された例は無い。
特開平11-169601号公報 (財)石油産業活性化センター 技術企画部 著,ペトロテック,11(2005), 835-840 千代田修著,触媒,47 (2005) 568 M. Xueら著, J. Colloid Interf. Sci., 298 (2006) 535-542 M. Sugiokaら著, J. Jpn. Petrol. Inst., 45 (2002) 342-354 Z. Gaoら著, Synthetic Metals 75 (1995) 5-10
Among the sulfur compounds, alkanethiols (RSH), in particular, are known to regularly adsorb on the gold surface to form a self-assembled monolayer (SAM). As for thiophene, since the SAM formation of polyalkylthiophene by Gao et al. In 1995 (see Non-Patent Document 5 below), SAM formation has also been experimentally confirmed by several researchers. Since it can be applied to an electronic device as a conductive polymer, research in this field is becoming active. For such simple thiophene or alkylthiophene, the adsorption phenomenon on the Au surface and its application have been studied, but the single crystal of Au is exclusively used for the purpose of using a monomolecular film as SAM, and the adsorption amount Therefore, it is not used as an adsorptive desulfurization agent, and there has been no report on the adsorption of dibenzothiophenes that are important as an object of desulfurization from liquid fuel.
Japanese Patent Laid-Open No. 11-169601 Petroleum Industry Revitalization Center, Technical Planning Department, Petrotech, 11 (2005), 835-840 Chiyoda Osamu, Catalysis, 47 (2005) 568 M. Xue et al., J. Colloid Interf. Sci., 298 (2006) 535-542 M. Sugioka et al., J. Jpn. Petrol. Inst., 45 (2002) 342-354 Z. Gao et al., Synthetic Metals 75 (1995) 5-10
 本発明は、上記した従来技術の問題点に鑑みてなされたものであり、その主な目的は、液体燃料中に含まれる硫黄化合物に対して有効な液相吸着による脱硫剤、特に、従来の方法では十分に除去することが困難であったチオフェン系硫黄化合物についても10ppmを下回る硫黄濃度となるまで除去することができ、しかも、脱硫処理後に簡単な処理方法で再利用が可能な新規な脱硫剤を提供することである。 The present invention has been made in view of the above-mentioned problems of the prior art, and its main purpose is to provide a desulfurization agent by liquid phase adsorption effective for sulfur compounds contained in liquid fuel, in particular, It is possible to remove thiophene-based sulfur compounds that were difficult to remove sufficiently by this method until a sulfur concentration of less than 10 ppm is reached, and a new desulfurization that can be reused with a simple treatment method after desulfurization. Is to provide an agent.
 本発明者は、上記した目的を達成すべく鋭意研究を重ねてきた。その結果、各種の化学反応用触媒として知られている金のナノ粒子を担持した金属酸化物が、液体燃料中の硫黄含有有機化合物に対して選択性の良い吸着剤として作用し、特に、従来の方法では十分な低濃度まで除去が困難であったチオフェン系硫黄化合物についても、十分な低濃度まで吸着除去できることを見出した。しかも、吸着処理後には、簡単な加熱処理によって、吸着された硫黄化合物を効率良く除去でき、吸着剤として再利用が可能となることを見出し、ここに本発明を完成するに至った。 The present inventor has intensively studied to achieve the above-mentioned purpose. As a result, metal oxides supporting gold nanoparticles known as various chemical reaction catalysts act as adsorbents with good selectivity for sulfur-containing organic compounds in liquid fuels. It was found that the thiophene sulfur compound, which was difficult to remove to a sufficiently low concentration by this method, could be adsorbed and removed to a sufficiently low concentration. Moreover, after the adsorption treatment, it has been found that the adsorbed sulfur compound can be efficiently removed by a simple heat treatment and can be reused as an adsorbent, and the present invention has been completed here.
 即ち、本発明は、下記の液相用吸着脱硫剤、及び該脱硫剤を用いる脱硫方法を提供するものである。
1. 平均粒径50nm以下の金ナノ粒子を金属酸化物に担持してなる液相用吸着脱硫剤。
2. 比表面積が1m2/g以上である上記項1に記載の脱硫剤。
3. 上記項1に記載の金ナノ粒子担持金属酸化物を支持体上に固定化した液相用吸着脱硫剤。
4. 処理対象が、硫黄含有有機化合物を含む液体燃料である上記項1に記載の脱硫剤。
5. 上記項1に記載の脱硫剤を、硫黄含有有機化合物を含む液体と接触させることを特徴とする脱硫方法。
6. 処理対象が硫黄含有有機化合物を含む液体燃料である請求項5に記載の脱硫方法。
7. 処理対象の液体燃料が、チオフェン環を有する有機化合物を含むものである上記項6に記載の脱硫方法。
8. チオフェン環を有する有機化合物が、ジベンゾチオフェン及びアルキルジベンゾチオフェン類からなる群から選ばれた少なくとも一種の化合物である上記項7に記載の脱硫方法。
9. 上記項5の方法によって脱硫処理を行った後、脱硫剤を加熱処理して該脱硫剤に吸着された硫黄含有有機化合物を除去することを特徴とする脱硫剤の再生方法。
10.上記項9の方法によって再生処理を行った脱硫剤を、請求項5の方法によって硫黄含有有機化合物を含む液体と接触させることを特徴とする脱硫方法。
That is, the present invention provides the following liquid phase adsorption desulfurization agent and a desulfurization method using the desulfurization agent.
1. A liquid phase adsorptive desulfurization agent obtained by supporting gold nanoparticles having an average particle size of 50 nm or less on a metal oxide.
2. Item 2. The desulfurizing agent according to Item 1, wherein the specific surface area is 1 m 2 / g or more.
3. A liquid phase adsorptive desulfurization agent, wherein the gold nanoparticle-supported metal oxide according to Item 1 is immobilized on a support.
4). Item 2. The desulfurization agent according to Item 1, wherein the treatment target is a liquid fuel containing a sulfur-containing organic compound.
5). A desulfurization method comprising contacting the desulfurizing agent according to item 1 with a liquid containing a sulfur-containing organic compound.
6). The desulfurization method according to claim 5, wherein the treatment target is a liquid fuel containing a sulfur-containing organic compound.
7). Item 7. The desulfurization method according to Item 6, wherein the liquid fuel to be treated contains an organic compound having a thiophene ring.
8). Item 8. The desulfurization method according to Item 7, wherein the organic compound having a thiophene ring is at least one compound selected from the group consisting of dibenzothiophene and alkyldibenzothiophenes.
9. A method for regenerating a desulfurization agent, comprising performing a desulfurization treatment by the method of Item 5 above, and then heat-treating the desulfurization agent to remove the sulfur-containing organic compound adsorbed on the desulfurization agent.
10. A desulfurization method, wherein the desulfurization agent regenerated by the method of item 9 is contacted with a liquid containing a sulfur-containing organic compound by the method of claim 5.
 以下、本発明の脱硫剤、その製造方法及び使用方法について具体的に説明する。 Hereinafter, the desulfurization agent of the present invention, its production method and use method will be specifically described.
 脱硫剤
 本発明の脱硫剤は、平均粒子径が50nm以下の金ナノ粒子を金属酸化物に担持させた構造を有するものである。
Desulfurizing agent The desulfurizing agent of the present invention has a structure in which gold nanoparticles having an average particle size of 50 nm or less are supported on a metal oxide.
 この様な金ナノ粒子を担持した金属酸化物は、一酸化炭素やホルムアルデヒドの酸化除去、排ガス中のNOxの炭化水素による還元、一酸化炭素や二酸化炭素の水素化によるメタノール合成反応、一酸化炭素と水から二酸化炭素と水素を生成する水性ガスシフト反応、プロピレンの選択酸化によるプロピレンオキサイド合成反応など各種の化学反応に対する触媒として、高い活性を示すことが知られている。しかしながら、これまで、液相において硫黄化合物に対して選択的な吸着作用を有することは全く知られていない。 Metal oxides carrying such gold nanoparticles are the oxidation removal of carbon monoxide and formaldehyde, the reduction of NOx in exhaust gas by hydrocarbons, the methanol synthesis reaction by hydrogenation of carbon monoxide and carbon dioxide, carbon monoxide It is known to exhibit high activity as a catalyst for various chemical reactions such as water gas shift reaction for producing carbon dioxide and hydrogen from water and water, and propylene oxide synthesis reaction by selective oxidation of propylene. However, until now, it has not been known at all to have a selective adsorption action for sulfur compounds in the liquid phase.
 本発明によれば、上記したナノサイズの金微粒子を金属酸化物に担持させた構造を持つ物質が、液相において、硫黄を含有する各種の有機化合物に対して選択的吸着作用を有し、脱硫剤として有効であることが新たに見出された。 According to the present invention, the substance having a structure in which the above-described nanosized gold fine particles are supported on a metal oxide has a selective adsorption action on various organic compounds containing sulfur in the liquid phase, It was newly found to be effective as a desulfurization agent.
 本発明の脱硫剤は、ナノサイズの金粒子が金属酸化物担体の表面に均一に担持された構造を有することが好ましい。金属酸化物に担持された金微粒子は、ナノサイズという非常に微細な状態であるために、吸着に必要な金の表面積が非常に大きく、優れた吸着性能を発揮できる。また脱硫後の吸着剤再生のために必要な燃焼活性点は、金と金属酸化物の接合界面に形成されると考えられるので、この接合部分を多くするためにもできるだけ粒径が小さいことが好ましい。具体的には、金粒子の平均粒子径は、金原子のサイズ以上であって50nm程度以下であればよく、好ましくは1~10nm程度である。尚、本願明細書において、金粒子の平均粒子径は、透過型電子顕微鏡法による測定値の平均値、または粉末X線回折測定データからSherrerの式により計算された金の結晶子径の値であり、金ナノ粒子触媒の場合には両値はほぼ一致することを確認している。 The desulfurizing agent of the present invention preferably has a structure in which nano-sized gold particles are uniformly supported on the surface of the metal oxide support. Since the gold fine particles supported on the metal oxide are in a very fine state of nano-size, the gold surface area necessary for adsorption is very large and can exhibit excellent adsorption performance. In addition, it is considered that the combustion active point necessary for regeneration of the adsorbent after desulfurization is formed at the bonding interface between gold and metal oxide, so that the particle size should be as small as possible in order to increase this bonding portion. preferable. Specifically, the average particle diameter of the gold particles may be not less than the size of the gold atom and not more than about 50 nm, preferably about 1 to 10 nm. In the present specification, the average particle diameter of the gold particles is the average value of the values measured by transmission electron microscopy, or the value of the crystallite diameter of gold calculated from the powder X-ray diffraction measurement data by the Sherrer equation. In the case of gold nanoparticle catalyst, it is confirmed that both values are almost the same.
 金粒子を担持する金属酸化物としては、例えば、ベリリウム、マグネシウム、アルミニウム、ケイ素、カルシウム、スカンジウム、チタン、バナジウム、クロム、マンガン、鉄、コバルト、ニッケル、銅、亜鉛、ガリウム、ゲルマニウム、ストロンチウム、イットリウム、ジルコニウム、カドミウム、インジウム、スズ、バリウム、ランタノイド元素等の金属元素を含む酸化物を用いることができる。これらの金属酸化物は、上記金属元素を一種のみ含む単一金属の酸化物であってもよく、2種以上の金属元素を含む複合酸化物であってもよい。これらの金属酸化物の内で、特に、チタン、マンガン、鉄、コバルト、ニッケル、亜鉛、ジルコニウム、ランタン、セリウム等の金属元素を一種又は二種以上含む金属酸化物が好ましい。上記した単一金属の金属酸化物及び複合酸化物は、必要に応じて混合して用いることも可能である。なお、周期律第2族元素のベリリウム、マグネシウム、カルシウム、ストロンチウム、バリウムについては、製造方法によっては、対応する酸化物の他に、水酸化物、塩基性炭酸塩等が含まれる場合がある。本発明では、金をナノ粒子状に担持する「酸化物」には、これらの水酸化物、塩基性炭酸塩等が含まれていても良い。 Examples of metal oxides supporting gold particles include beryllium, magnesium, aluminum, silicon, calcium, scandium, titanium, vanadium, chromium, manganese, iron, cobalt, nickel, copper, zinc, gallium, germanium, strontium, yttrium. An oxide containing a metal element such as zirconium, cadmium, indium, tin, barium, or a lanthanoid element can be used. These metal oxides may be single metal oxides containing only one of the above metal elements, or complex oxides containing two or more metal elements. Among these metal oxides, metal oxides containing one or more metal elements such as titanium, manganese, iron, cobalt, nickel, zinc, zirconium, lanthanum, and cerium are particularly preferable. The above-mentioned single metal metal oxide and composite oxide can be mixed and used as necessary. In addition, beryllium, magnesium, calcium, strontium, and barium of the periodic group 2 elements may include hydroxides, basic carbonates, and the like in addition to the corresponding oxides depending on the manufacturing method. In the present invention, the “oxide” supporting gold in the form of nanoparticles may contain these hydroxides, basic carbonates and the like.
 金ナノ粒子を担持した金属酸化物からなる本発明の脱硫剤において、金の含有量は、金をナノ粒子状態に保持できるよう調製できる限りは特に制限はない。例えば、担体として用いる金属酸化物と調製法を適宜選択することにより、金ナノ粒子と金属酸化物の合計量を基準として、0.1~60重量%程度の金含有量を持つ脱硫剤を調製できる。 In the desulfurization agent of the present invention comprising a metal oxide supporting gold nanoparticles, the gold content is not particularly limited as long as it can be prepared so that gold can be maintained in a nanoparticle state. For example, by appropriately selecting the metal oxide used as the carrier and the preparation method, a desulfurization agent having a gold content of about 0.1 to 60% by weight can be prepared based on the total amount of gold nanoparticles and metal oxide.
 本発明の脱硫剤、即ち、金ナノ粒子を担持した金属酸化物の形態は、その使用目的に応じて適宜選択可能である。例えば、粉末状で用いることもできるし、顆粒状、ペレット状等に成形して用いることもできる。また支持体上に金ナノ粒子を担持した金属酸化物を固定化して、支持体の形状として用いることもできる。支持体については、表面に金ナノ粒子を担持した金属酸化物を固定化することができれば支持体の形状は特に限定されず、平板状、ブロック状、繊維状、網状、ビーズ状、ハニカム状等何でも良い。例えばハニカム状として用いる場合、粉末状で調製した脱硫剤をハニカムの表面に付着させて用いることもできるし、ハニカムの表面に予め酸化物を担持しておき、後述する析出沈殿法等を適用してこの表面に金ナノ粒子を直接担持することもできる。支持体の材質についても特に限定的ではなく、金ナノ粒子を担持させる条件や脱硫条件下において安定なものであればよく、例えば、各種のセラミックスを使用することができる。 The form of the desulfurization agent of the present invention, that is, the metal oxide supporting the gold nanoparticles can be appropriately selected depending on the purpose of use. For example, it can be used in a powder form, or can be used after being formed into a granular form, a pellet form, or the like. Further, a metal oxide supporting gold nanoparticles on a support can be fixed and used as a shape of the support. With respect to the support, the shape of the support is not particularly limited as long as the metal oxide carrying gold nanoparticles on the surface can be fixed, and is flat, block, fiber, net, bead, honeycomb, etc. anything is fine. For example, when used as a honeycomb, a desulfurization agent prepared in a powder form can be used by adhering to the surface of the honeycomb, or an oxide is supported on the surface of the honeycomb in advance, and a precipitation method described later is applied. Gold nanoparticles can be directly supported on the surface of the lever. The material of the support is not particularly limited as long as it is stable under conditions for supporting gold nanoparticles or under desulfurization conditions. For example, various ceramics can be used.
 金ナノ粒子を担持させた状態における金属酸化物の比表面積は、BET法による測定値として、1~2000m2/g程度であることが好ましく、5~1000m2/g程度であることがより好ましい。このような金ナノ粒子担持酸化物を得るためには、例えば、金ナノ粒子を担持させる金属酸化物として上記した範囲の比表面積を有するものを用いればよい。 The specific surface area of the metal oxide in a state where gold nanoparticles are supported is preferably about 1 to 2000 m 2 / g, more preferably about 5 to 1000 m 2 / g as measured by the BET method. . In order to obtain such a gold nanoparticle-supporting oxide, for example, a metal oxide supporting gold nanoparticles having a specific surface area in the above range may be used.
 脱硫剤の製造方法
 金属酸化物上に金をナノサイズの粒子として担持させる方法については、特に限定的ではなく、例えば、以下の公知の調製法を採用することができる。
(a) 共沈法(特開昭60-238148号公報等)
(b) 析出沈殿法(特開平3-97623号公報等)
(c) コロイド混合法(Tsubota S. et al., Catal. Lett., 56 (1998) 131)
(d) 気相グラフティング法(特開平9-122478号公報)
(e) 液相グラフティング法(Okumura M. et al., Chem. Lett., (2000) 396)
Production method of desulfurization agent The method for supporting gold as nano-sized particles on the metal oxide is not particularly limited, and for example, the following known preparation methods can be employed.
(a) Coprecipitation method (JP-A-60-238148, etc.)
(b) Precipitation / precipitation method (JP-A-3-97623, etc.)
(c) Colloid mixing method (Tsubota S. et al., Catal. Lett., 56 (1998) 131)
(d) Gas phase grafting method (JP-A-9-122478)
(e) Liquid phase grafting method (Okumura M. et al., Chem. Lett., (2000) 396)
 これらの方法において、金微粒子を析出させるための金の前駆体としては、採用する方法に応じて、例えば、金の水溶性化合物(例えば、塩化金酸)や、金アセチルアセトナト錯体等の加熱により気化する化合物等を用いることができる。 In these methods, as a gold precursor for precipitating gold fine particles, depending on the method employed, for example, heating of a water-soluble gold compound (for example, chloroauric acid), gold acetylacetonate complex, etc. A compound that vaporizes due to the above can be used.
 金属酸化物の原料についても、採用する担持方法に応じて、例えば、各種金属の硝酸塩、硫酸塩、酢酸塩、塩化物等が用いることができる。具体的には、硝酸セリウム、硝酸ジルコニウム等の硝酸塩、硫酸チタン等の硫酸塩、塩化セリウム、三塩化チタン、四塩化チタン等の塩化物等を用いることができる。 Also for the metal oxide raw material, various metal nitrates, sulfates, acetates, chlorides, and the like can be used depending on the loading method employed. Specifically, nitrates such as cerium nitrate and zirconium nitrate, sulfates such as titanium sulfate, chlorides such as cerium chloride, titanium trichloride, and titanium tetrachloride can be used.
 共沈法(a)では、まず、これらの酸化物の前駆体と金の前駆体をアルカリ条件で同時に沈殿させる。次いで、得られた金水酸化物と酸化物前駆体の水酸化物の混合物の沈殿をろ過、水洗、乾燥の後、後述する熱処理を行うことにより金ナノ粒子を担持した酸化物が得られる。 In the coprecipitation method (a), first, a precursor of these oxides and a gold precursor are simultaneously precipitated under alkaline conditions. Subsequently, the precipitate of the mixture of the obtained gold hydroxide and the oxide precursor hydroxide is filtered, washed with water, and dried, and then heat treatment described later is performed to obtain an oxide carrying gold nanoparticles.
 (b)~(e)の調製方法では、酸化物の前駆体は予め酸化物または水酸化物の形にしておいてから金の担持を行う必要がある。最初から酸化物または水酸化物として市販されているものを利用することも可能である。これらは、特に形態を問わず、粉末状の製品の他、ビーズ、ペレット、ハニカムなどでも良く、単一組成でなくても、例えばセラミックハニカム等の表面に酸化チタンをコーティングしたようなものも利用できる。以上のような酸化物または水酸化物の表面に(b)~(e)の方法により金の前駆体を担持させ、必要によりろ過、水洗、乾燥の後、後述する熱処理を行うことにより金ナノ粒子を担持した酸化物を得ることができる。 In the preparation methods (b) to (e), it is necessary that the oxide precursor is preliminarily formed into an oxide or hydroxide before carrying gold. It is also possible to use what is marketed as an oxide or hydroxide from the beginning. These may be in any form, and may be in the form of powder, beads, pellets, honeycombs, etc. Even if they are not of a single composition, for example, a ceramic honeycomb coated with titanium oxide is also used. it can. A gold precursor is supported on the surface of the oxide or hydroxide as described above by the methods (b) to (e), and if necessary, filtered, washed with water, dried, and then subjected to a heat treatment to be described later. An oxide carrying particles can be obtained.
 上記の調製法のうち共沈法と析出沈殿法の場合には、例えば、特公平5-325及び特公平6-29137に示されているように調製中にクエン酸マグネシウムを加えることが金の粒径を小さくするために有効であり、この方法は、特に金の担持量が多い場合に効果的に用いられる。 Among the above preparation methods, in the case of the coprecipitation method and the precipitation method, for example, as shown in Japanese Patent Publication No. 5-325 and Japanese Patent Publication No. 6-29137, it is possible to add magnesium citrate during the preparation. This method is effective for reducing the particle size, and this method is particularly effective when the amount of gold supported is large.
 上記した公知の調製方法において、金を最終的に金属の状態にするためには、例えば、酸素含有雰囲気中、還元性ガス雰囲気中、不活性ガス雰囲気中等の各種の雰囲気中で熱処理すればよい。酸素含有雰囲気としては、大気雰囲気、あるいは酸素を窒素、ヘリウム、アルゴン等で希釈した混合気体雰囲気などを利用できる。還元性ガスとしては、例えば、窒素ガスで希釈した1~10vol%程度の水素ガス、一酸化炭素ガス等を用いることができる。不活性ガスとしては、例えば、窒素、ヘリウム、アルゴンなどを利用できる。 In the above-described known preparation method, in order to finally bring the gold into a metal state, for example, heat treatment may be performed in various atmospheres such as an oxygen-containing atmosphere, a reducing gas atmosphere, and an inert gas atmosphere. . As the oxygen-containing atmosphere, an air atmosphere or a mixed gas atmosphere in which oxygen is diluted with nitrogen, helium, argon, or the like can be used. As the reducing gas, for example, about 1 to 10 vol% hydrogen gas or carbon monoxide gas diluted with nitrogen gas can be used. For example, nitrogen, helium, argon, or the like can be used as the inert gas.
 熱処理温度は、公知の金属金生成条件の範囲から適宜選択すればよく、通常室温~600℃程度が好ましい。安定かつ微細な金粒子を得るためには、200~400℃程度がより好ましい。熱処理時間は、例えば、1~12時間程度とすればよい。 The heat treatment temperature may be appropriately selected from the range of known metal gold production conditions, and is usually preferably about room temperature to 600 ° C. In order to obtain stable and fine gold particles, about 200 to 400 ° C. is more preferable. The heat treatment time may be about 1 to 12 hours, for example.
 脱硫処理の対象物
 本発明の脱硫剤は、硫黄を含む各種の有機化合物を液相において吸着除去する方法に適用できる。この様な硫黄含有有機化合物としては、例えば、チオール(R-SH)、スルフィド(R-S-R)、ジスルフィド(R-S-S-R)、テトラヒドロチオフェン、チオフェン類化合物等を挙げることができる。ここで、チオフェン類化合物とは、チオフェン環を有する化合物群を意味するものであり、例えば、チオフェン、アルキルチオフェン、ベンゾチオフェン、アルキルベンゾチオフェン、ジベンゾチオフェン、アルキルジベンゾチオフェン、ジアルキルジベンゾチオフェン等を例示できる。
Object of Desulfurization Treatment The desulfurization agent of the present invention can be applied to a method of adsorbing and removing various organic compounds containing sulfur in the liquid phase. Examples of such sulfur-containing organic compounds include thiol (R-SH), sulfide (RSR), disulfide (RSSR), tetrahydrothiophene, and thiophene compounds. Here, the thiophene compound means a compound group having a thiophene ring, and examples thereof include thiophene, alkylthiophene, benzothiophene, alkylbenzothiophene, dibenzothiophene, alkyldibenzothiophene, and dialkyldibenzothiophene. .
 本発明の脱硫剤は、液体燃料中に残存する硫黄含有有機化合物、特に、チオフェン類化合物の吸着脱硫に有効に用いられる。本発明の脱硫剤を用いることによって、従来の方法では、10ppmを下回る硫黄濃度まで減少させることが困難であった4,6-ジメチルベンゾチオフェンなどのチオフェン類化合物を10ppmを下回る硫黄濃度となるまで吸着除去することが可能となる。 The desulfurizing agent of the present invention is effectively used for adsorptive desulfurization of sulfur-containing organic compounds remaining in liquid fuel, particularly thiophene compounds. By using the desulfurizing agent of the present invention, it has been difficult to reduce the sulfur concentration below 10 ppm by a conventional method until a sulfur concentration below 10 ppm is reached for a thiophene compound such as 4,6-dimethylbenzothiophene. It can be removed by adsorption.
 処理対象となる液体燃料の種類については特に限定は無く、ガソリン、ケロシン、灯油、軽油、重油などのいずれでもよい。処理前の液体燃料に含まれる硫黄濃度についても特に限定はないが、硫黄濃度の高い燃料油を直接処理すると必要とする脱硫剤の量が多くなることを考慮して、水素化脱硫等の方法で予め硫黄濃度を50ppm以下としておくことが好ましく、10ppm以下としておくことがより好ましい。 The type of liquid fuel to be treated is not particularly limited, and any of gasoline, kerosene, kerosene, light oil, heavy oil, etc. may be used. The sulfur concentration contained in the liquid fuel before treatment is not particularly limited, but hydrodesulfurization and other methods are taken into consideration that the amount of desulfurization agent required is increased when directly treating high-sulfur fuel oil. The sulfur concentration is preferably 50 ppm or less in advance, and more preferably 10 ppm or less.
 脱硫方法
 本発明の脱硫剤を用いる脱硫方法では、脱硫対象とする液体、例えば、液体燃料を脱硫剤と接触させることにより液体中の硫黄含有有機化合物を吸着して脱硫することができる。一般的な方法として、バッチ法とフロー法の2つの方法が挙げられる。
Desulfurization method In the desulfurization method using the desulfurization agent of the present invention, a sulfur-containing organic compound in the liquid can be adsorbed and desulfurized by bringing the liquid to be desulfurized, for example, liquid fuel into contact with the desulfurization agent. As a general method, there are two methods, a batch method and a flow method.
 バッチ法では、例えば、液体燃料を収容した容器中に脱硫剤を投入し攪拌する方法を採用できる。脱硫剤の適切な使用量は実際に用いる脱硫剤の種類により異なるが、例えば、液体燃料1リットルに対し脱硫剤1~500gの範囲で用いることが好ましく、液体燃料1リットルに対し脱硫剤10~100gの範囲で用いることがより好ましい。処理温度については、処理対象の燃料が液体の状態を保持できる温度であれば特に限定されず、例えば室温において行えば良い。圧力についても特に限定的ではなく、加圧状態であっても良いが、通常は、大気圧下で処理を行えばよい。 In the batch method, for example, a method of introducing a desulfurizing agent into a container containing liquid fuel and stirring can be employed. The appropriate amount of the desulfurizing agent varies depending on the type of desulfurizing agent actually used. For example, it is preferably used in the range of 1 to 500 g of desulfurizing agent for 1 liter of liquid fuel, and 10 to 10 desulfurizing agent for 1 liter of liquid fuel. More preferably, it is used in the range of 100 g. The processing temperature is not particularly limited as long as the fuel to be processed can maintain a liquid state, and may be performed at room temperature, for example. The pressure is not particularly limited, and it may be in a pressurized state. Usually, the treatment may be performed under atmospheric pressure.
 脱硫剤を投入して一定時間経過後、液体と脱硫剤を分離することによって、含硫黄有機化合物量の減少した液体と脱硫剤とを得ることができる。処理時間については、硫黄化合物の濃度及び脱硫剤の使用量により異なるので、一概に規定できないが、例えば、1時間~数日間程度の範囲内において、目的とする脱硫効果が得られるまで処理を行えばよい。 A desulfurizing agent is added, and a liquid and a desulfurizing agent with a reduced amount of sulfur-containing organic compound can be obtained by separating the liquid and the desulfurizing agent after a predetermined time has elapsed. The treatment time varies depending on the concentration of the sulfur compound and the amount of the desulfurization agent used, so it cannot be specified unconditionally. For example, the treatment is performed within the range of 1 hour to several days until the desired desulfurization effect is obtained. Just do it.
 分離された脱硫剤については、例えば、後述した方法によって、乾燥した後、空気中で加熱する方法などによって、再生し、再使用することができる。 The separated desulfurizing agent can be regenerated and reused by, for example, a method described later, which is dried and then heated in air.
 フロー法の場合には、脱硫剤を管型容器に層状に充填し、処理対象の液体を一定の流量で流通させればよい。この場合の液空間速度(LHSV)は、例えば、0.01~100 h―1程度、好ましくは0.01~1 h-1程度の範囲内で設定することができる。脱硫の際の温度条件、圧力条件などについては、バッチ法の場合と同様に燃料が液体である範囲であれば特に限定されない。外部からの加熱源がない場合は常温にて行えば良い。液体燃料が予め加熱された状態で供給される場合には、そのままの温度で吸着脱硫を行うことも可能である。 In the case of the flow method, a desulfurizing agent is filled in a layered manner in a tubular container, and the liquid to be treated is circulated at a constant flow rate. In this case, the liquid hourly space velocity (LHSV) can be set, for example, within a range of about 0.01 to 100 h −1 , preferably about 0.01 to 1 h −1 . The temperature conditions, pressure conditions, and the like at the time of desulfurization are not particularly limited as long as the fuel is in a liquid range as in the case of the batch method. If there is no external heating source, it may be performed at room temperature. When the liquid fuel is supplied in a preheated state, adsorptive desulfurization can be performed at the same temperature.
 再生方法
 上記した方法によって液体中の硫黄含有有機化合物を吸着脱硫した後、脱硫剤を加熱処理することによって、脱硫剤に吸着された硫黄含有有機化合物を除去して、脱硫剤を再生使用することができる。尚、脱硫剤の加熱処理に際しては、必要に応じて、脱硫剤を溶剤等で洗浄し、乾燥した後に加熱することが望ましい。
Regeneration method After the sulfur-containing organic compound in the liquid is adsorbed and desulfurized by the method described above, the sulfur-containing organic compound adsorbed on the desulfurizing agent is removed by heating the desulfurizing agent, and the desulfurizing agent is regenerated and reused. Can do. In the heat treatment of the desulfurizing agent, it is desirable to heat the desulfurizing agent after washing with a solvent or the like, if necessary.
 加熱処理は、不活性ガス中、希釈酸素中、空気中、水蒸気中、希釈水素中等の各種雰囲気中で行うことができる。 The heat treatment can be performed in various atmospheres such as inert gas, diluted oxygen, air, water vapor, diluted hydrogen and the like.
 本発明の脱硫剤を構成する金ナノ粒子を担持した金属酸化物は、メタン、プロパン等の炭化水素とO2の反応(燃焼反応)、CO等の炭素化合物とH2Oの反応(シフト反応等)、CO, CO2, アルデヒド等の炭素化合物とH2の反応(水素化反応)の何れに対しても触媒活性を有することが知られている。このため、O2, H2O, H2の何れかを含む雰囲気中で加熱処理を行うことによって、これらの分子と脱硫剤表面に吸着した硫黄含有有機化合物との触媒反応や硫黄含有有機化合物の燃焼反応を利用して、吸着した硫黄含有有機化合物を効率的に除去することができる。 The metal oxide supporting the gold nanoparticles constituting the desulfurizing agent of the present invention is a reaction of hydrocarbons such as methane and propane with O 2 (combustion reaction), a reaction of carbon compounds such as CO and H 2 O (shift reaction). It is known that it has catalytic activity for any of the reaction (hydrogenation reaction) of carbon compounds such as CO, CO 2 and aldehyde with H 2 (hydrogenation reaction). For this reason, by performing a heat treatment in an atmosphere containing any of O 2 , H 2 O, and H 2 , a catalytic reaction between these molecules and the sulfur-containing organic compound adsorbed on the surface of the desulfurizing agent or a sulfur-containing organic compound Thus, the adsorbed sulfur-containing organic compound can be efficiently removed.
 雰囲気中のO2, H2O, H2等の濃度範囲については特に制限は無いが、特にH2を含む場合には爆発組成を避けて設定することが必要となる。圧力条件に関しては、燃焼反応の場合は常圧で良いが、水素化反応等を行う場合には10MPa程度以下で加圧することにより、反応促進が期待できる場合がある。加熱温度については50~500℃程度、好ましくは100~400℃程度、より好ましくは150~400℃程度の範囲で選択できる。加熱温度が高くなりすぎると、金ナノ粒子の凝集が起こりやすくなるため再生後の吸着性能が低下するので好ましくない。 The concentration range of O 2 , H 2 O, H 2, etc. in the atmosphere is not particularly limited, but especially when H 2 is included, it is necessary to avoid the explosion composition. Regarding the pressure condition, normal pressure may be used in the case of a combustion reaction, but in the case of performing a hydrogenation reaction or the like, the reaction may be accelerated by pressurizing at about 10 MPa or less. The heating temperature can be selected in the range of about 50 to 500 ° C, preferably about 100 to 400 ° C, more preferably about 150 to 400 ° C. An excessively high heating temperature is not preferable because gold nanoparticles tend to aggregate and the adsorption performance after regeneration deteriorates.
 本発明の脱硫剤は、液相において、硫黄含有有機化合物に対して選択的な吸着作用を有するものである。特に、液体燃料中の硫黄化合物濃度を従来技術では難しいレベルにまで下げることができる。 The desulfurizing agent of the present invention has a selective adsorption action for sulfur-containing organic compounds in the liquid phase. In particular, the sulfur compound concentration in the liquid fuel can be lowered to a level that is difficult with the prior art.
 本発明の脱硫剤は、この様な硫黄含有有機化合物に対する優れた吸着除去性能を利用して、各種の用途に用いることができる。例えば、従来の水素化脱硫プロセスによって硫黄含有有機化合物の濃度を低下させた後、本発明の脱硫剤を充填した吸着塔を用いて硫黄含有有機化合物を吸着除去することによって、液体燃料中の硫黄濃度を10ppm以下とすることが可能であり、特に、燃料電池用の燃料について望まれている硫黄濃度を0.1ppm以下まで低下させることも可能となる。 The desulfurizing agent of the present invention can be used for various applications by utilizing such excellent adsorption removal performance for sulfur-containing organic compounds. For example, after reducing the concentration of the sulfur-containing organic compound by a conventional hydrodesulfurization process, the sulfur-containing organic compound is adsorbed and removed using an adsorption tower filled with the desulfurizing agent of the present invention, thereby allowing sulfur in the liquid fuel. The concentration can be made 10 ppm or less, and in particular, the sulfur concentration desired for fuel for fuel cells can be lowered to 0.1 ppm or less.
 また、上記の非特許文献1に記されているように、ガソリンスタンドのタンクと給油機の間に本発明の脱硫剤を充填したカラムを設置し、自動車への給油の際に脱硫するような用い方もできる。 In addition, as described in Non-Patent Document 1 above, a column filled with the desulfurization agent of the present invention is installed between a tank of a gas station and a fueling machine, and desulfurization is performed when fueling an automobile. It can also be used.
試験例1における溶液中ジベンゾチオフェン濃度の時間変化を示すグラフである。3 is a graph showing a change over time in a dibenzothiophene concentration in a solution in Test Example 1. FIG. 試験例2において脱硫剤使用量を変化させた際の吸着平衡後に溶液中に残存する硫黄濃度(ジベンゾチオフェン濃度分析値から換算)と脱硫剤に吸着されたジベンゾチオフェン量を示すグラフである。4 is a graph showing the sulfur concentration remaining in the solution after conversion to equilibrium (converted from the analysis value of dibenzothiophene concentration) and the amount of dibenzothiophene adsorbed on the desulfurizing agent when the amount of desulfurizing agent used is changed in Test Example 2. 試験例3における各試料の1回目(再生前)及び2回目(再生後)の吸着操作でのジベンゾチオフェン(DBT)、4,6-ジメチルジベンゾチオフェン(DMDBT)、ナフタレン(NA)の飽和吸着量を示すグラフである。Saturated adsorption amounts of dibenzothiophene (DBT), 4,6-dimethyldibenzothiophene (DMDBT), and naphthalene (NA) in the first (before regeneration) and second (after regeneration) adsorption operations of each sample in Test Example 3 It is a graph which shows. 試験例4において、吸着-再生を繰り返した際の各回吸着操作におけるジベンゾチオフェン(DBT)の飽和吸着量を示すグラフである。6 is a graph showing the amount of saturated adsorption of dibenzothiophene (DBT) in each adsorption operation when adsorption-regeneration is repeated in Test Example 4. 試験例5における再生処理の加熱温度と、再生後の試料のジベンゾチオフェン(DBT)の飽和吸着量との関係を示すグラフである。6 is a graph showing the relationship between the heating temperature of regeneration treatment in Test Example 5 and the saturated adsorption amount of dibenzothiophene (DBT) of a sample after regeneration. 試験例5において350℃での加熱再生処理を行った際に、昇温中に発生したCO2量を温度に対してプロットしたグラフである。6 is a graph in which the amount of CO 2 generated during temperature rise is plotted against temperature when heat regeneration treatment at 350 ° C. is performed in Test Example 5. 試験例6において、各試料について求めた試験溶液Eにおける4,6-ジメチルジベンゾチオフェン(DMDBT)の飽和吸着量を、試験溶液A及びCにおけるDBT, DMDBT, NAの吸着量と比較して示すグラフである。In Test Example 6, a graph showing the saturated adsorption amount of 4,6-dimethyldibenzothiophene (DMDBT) in test solution E obtained for each sample in comparison with the adsorption amounts of DBT, DMDBT, and NA in test solutions A and C It is.
 以下、実施例を挙げて本発明を更に詳細に説明する。 Hereinafter, the present invention will be described in more detail with reference to examples.
 実施例1
 (1)脱硫剤の調製
 脱硫剤1:金/酸化セリウム(Au/CeO 2 )
 塩化金酸[HAuCl4・4H2O] (5mmol/L)の水溶液1000mLを70℃に加温し、KOHを滴下してpHを7に調節した。酸化セリウム粉末の7.7gを加え、ついでクエン酸マグネシウムの10mmol/L溶液を370mL加えた。一時間攪拌の後、ろ過、水洗、乾燥し、得られた粉末を空気中400℃で4時間焼成することにより、平均粒径5.5nmの金ナノ粒子が酸化セリウム表面に担持された構造の脱硫剤1(Au/CeO2)(Au担持量11.3wt%)を調製した。尚、実施例における金ナノ粒子の平均粒径は、粉末X線回折測定データからSherrerの式により計算された金の結晶子径の値である。
Example 1
(1) Preparation of desulfurization agent Desulfurization agent 1: gold / cerium oxide (Au / CeO 2 )
1000 mL of an aqueous solution of chloroauric acid [HAuCl 4 · 4H 2 O] (5 mmol / L) was heated to 70 ° C., and KOH was added dropwise to adjust the pH to 7. 7.7 g of cerium oxide powder was added, and then 370 mL of a 10 mmol / L solution of magnesium citrate was added. After stirring for 1 hour, filtration, washing and drying, the resulting powder is calcined in air at 400 ° C. for 4 hours to desulfurize the structure in which gold nanoparticles with an average particle size of 5.5 nm are supported on the surface of cerium oxide Agent 1 (Au / CeO 2 ) (Au supported amount 11.3 wt%) was prepared. In addition, the average particle diameter of the gold nanoparticles in the examples is the value of the crystallite diameter of gold calculated from the powder X-ray diffraction measurement data according to the Sherrer equation.
 脱硫剤2:金/酸化セリウム(Au/CeO 2 )
 使用する塩化金酸の量を減少させ、更に、クエン酸マグネシウムを無添加とすること以外は脱硫剤1の調製方法と同様にして、平均粒径4.9nmの金ナノ粒子が酸化セリウム表面に担持された構造の脱硫剤2(Au/CeO2)(Au担持量1.0wt%)を調製した。
Desulfurization agent 2: Gold / cerium oxide (Au / CeO 2 )
The gold nanoparticles with an average particle size of 4.9 nm are supported on the cerium oxide surface in the same manner as the preparation of the desulfurizing agent 1 except that the amount of chloroauric acid used is reduced and magnesium citrate is not added. A desulfurizing agent 2 (Au / CeO 2 ) having a structure as described above (Au loading 1.0 wt%) was prepared.
 脱硫剤3:金/酸化亜鉛(Au/ZnO)
 200mLの水に対し、炭酸ナトリウムNa2CO3 8gを溶解した水溶液を70℃に加温した。ここに、硝酸亜鉛14.2gと塩化金酸1.1gを200mLの水に溶解した水溶液を70℃で加え、沈殿を生成させた。一時間攪拌の後、ろ過、水洗、乾燥し、得られた粉末を空気中400℃で4時間焼成することにより、平均粒径5.8nmの金ナノ粒子が酸化亜鉛表面に担持された構造の脱硫剤3(Au/ZnO)(Au担持量10.0wt%)を調製した。
Desulfurization agent 3: Gold / Zinc oxide (Au / ZnO)
An aqueous solution in which 8 g of sodium carbonate Na 2 CO 3 was dissolved in 200 mL of water was heated to 70 ° C. An aqueous solution prepared by dissolving 14.2 g of zinc nitrate and 1.1 g of chloroauric acid in 200 mL of water was added thereto at 70 ° C. to form a precipitate. After stirring for 1 hour, filtration, washing and drying, the resulting powder is calcined in air at 400 ° C. for 4 hours to desulfurize the structure in which gold nanoparticles with an average particle size of 5.8 nm are supported on the surface of zinc oxide Agent 3 (Au / ZnO) (Au supported amount 10.0 wt%) was prepared.
 脱硫剤4:金/酸化チタン(Au/TiO 2 )
 塩化金酸(5mmol/L)の水溶液1000mLを70℃に加温し、KOHを滴下してpHを7に調節した。酸化チタン粉末の3.6gを加え、ついでクエン酸マグネシウムの10mmol/L溶液を400mL加えた。一時間攪拌の後、ろ過、水洗、乾燥し、得られた粉末を空気中400℃で4時間焼成することにより、平均粒径4.0nmの金ナノ粒子が酸化チタン表面に担持された構造の脱硫剤4(Au/TiO2)(Au金担持量21.5wt%)を調製した。
Desulfurization agent 4: Gold / titanium oxide (Au / TiO 2 )
1000 mL of an aqueous solution of chloroauric acid (5 mmol / L) was heated to 70 ° C., and KOH was added dropwise to adjust the pH to 7. 3.6 g of titanium oxide powder was added, and then 400 mL of a 10 mmol / L solution of magnesium citrate was added. After stirring for 1 hour, filtration, washing with water and drying, the resulting powder is baked in air at 400 ° C. for 4 hours to desulfurize the structure in which gold nanoparticles with an average particle size of 4.0 nm are supported on the surface of titanium oxide. Agent 4 (Au / TiO 2 ) (Au gold supported amount 21.5 wt%) was prepared.
 比較脱硫剤1:酸化セリウム(CeO 2 )
 脱硫剤1及び2の調製に用いた酸化セリウム粉末をそのまま用いた。
Comparative desulfurization agent 1: Cerium oxide (CeO 2 )
The cerium oxide powder used for the preparation of the desulfurizing agents 1 and 2 was used as it was.
 比較脱硫剤2:白金/酸化セリウム(Pt/CeO 2 )
塩化白金酸[H2PtC6・6H2O](2mmol/L)の水溶液500mLを加熱し、KOHを滴下してpHを7に調節した。酸化セリウム粉末の6.5gを加えた。一時間攪拌の後、ろ過、水洗、乾燥し、得られた粉末を空気中400℃で4時間焼成し、更にH2(3%)+He(balance)混合ガスの流通下で350℃まで昇温してPtを還元して、平均粒径2.0nm以下の白金が酸化セリウム表面に担持された比較脱硫剤2(Pt/CeO2)(Pt担持量3.0wt%)を調製した。
Comparative desulfurization agent 2: Platinum / Cerium oxide (Pt / CeO 2 )
500 mL of an aqueous solution of chloroplatinic acid [H 2 PtC 6 · 6H 2 O] (2 mmol / L) was heated, and KOH was added dropwise to adjust the pH to 7. 6.5 g of cerium oxide powder was added. After stirring for 1 hour, filtration, washing with water and drying, the powder obtained was calcined in air at 400 ° C for 4 hours, and further raised to 350 ° C under the flow of H 2 (3%) + He (balance) mixed gas. Pt was reduced by heating to prepare a comparative desulfurization agent 2 (Pt / CeO 2 ) (Pt loading 3.0 wt%) in which platinum having an average particle size of 2.0 nm or less was supported on the surface of cerium oxide.
 比較脱硫剤3:セリウムイオン交換Y型ゼオライト(Ce-Y)
硝酸セリウム[Ce(NO3)3・6H2O](0.2mol/L)の水溶液30mLにY型ゼオライト粉末0.75gを加え、3日間振とう攪拌した。ろ過、洗浄、乾燥し、得られた粉末を空気中400℃で2時間焼成することにより、セリウムイオン交換Y型ゼオライト(Ce-Y)からなる比較脱硫剤3を調製した。
Comparative desulfurization agent 3: Cerium ion exchange Y-type zeolite (Ce-Y)
0.75 g of Y-type zeolite powder was added to 30 mL of an aqueous solution of cerium nitrate [Ce (NO 3 ) 3 · 6H 2 O] (0.2 mol / L), and the mixture was shaken and stirred for 3 days. The comparative desulfurization agent 3 made of cerium ion-exchanged Y-type zeolite (Ce-Y) was prepared by filtering, washing and drying, and calcining the obtained powder at 400 ° C. in air for 2 hours.
 比較脱硫剤4:銅/酸化亜鉛(Cu/ZnO)
200mLの水に対し、炭酸ナトリウムNa2CO3の7.6gを溶解した水溶液を70℃に加温した。ここに、硝酸亜鉛12.5gと硝酸銅4.3gを 300mLの水に溶解した水溶液を70℃で加え、沈殿を生成させた。一時間攪拌の後、ろ過、水洗、乾燥した。得られた粉末を空気中400℃で4時間焼成し、更にH2(3%)+He(balance)混合ガスの流通下で400℃まで昇温してCuを還元して、平均粒径3.3nmの銅が酸化亜鉛表面に担持された比較脱硫剤4(Cu/ZnO)(Cu担持量25.1wt%)を調製した。
Comparative desulfurization agent 4: Copper / Zinc oxide (Cu / ZnO)
An aqueous solution in which 7.6 g of sodium carbonate Na 2 CO 3 was dissolved in 200 mL of water was heated to 70 ° C. An aqueous solution in which 12.5 g of zinc nitrate and 4.3 g of copper nitrate were dissolved in 300 mL of water was added thereto at 70 ° C. to form a precipitate. After stirring for 1 hour, it was filtered, washed with water and dried. The obtained powder was calcined in air at 400 ° C. for 4 hours, and further heated to 400 ° C. under the flow of a mixed gas of H 2 (3%) + He (balance) to reduce Cu to obtain an average particle size of 3.3 Comparative desulfurizing agent 4 (Cu / ZnO) (Cu supported amount 25.1 wt%) in which copper of nm was supported on the surface of zinc oxide was prepared.
 (2)脱硫試験
 以下の試験溶液A, B, C, D, Eを調製した。
(2) Desulfurization test The following test solutions A, B, C, D and E were prepared.
 試験溶液A
n-デカン(キシダ化学製、特級)を溶媒とし、有機硫黄化合物としてジベンゾチオフェン(関東化学製、特級)を39.9mg/L、溶液分析のための内部標準としてn-テトラデカン(キシダ化学製、特級)を39.5mg/L含む溶液を作製した。この溶液の硫黄濃度は9.5ppmに相当する。
Test solution A
n-decane (manufactured by Kishida Chemical, special grade) as a solvent, dibenzothiophene (manufactured by Kanto Chemical Co., special grade) as an organic sulfur compound, 39.9 mg / L, n-tetradecane (manufactured by Kishida Chemical, special grade) as an internal standard for solution analysis ) Was prepared to contain 39.5 mg / L. The sulfur concentration of this solution corresponds to 9.5 ppm.
 試験溶液B
試験溶液Aと同様にn-デカンを溶媒とし、有機硫黄化合物としてジベンゾチオフェンを51.2mg/L含む溶液を作製した。この溶液の硫黄濃度は12.2ppmに相当する。
Test solution B
Similarly to test solution A, a solution containing 51.2 mg / L of dibenzothiophene as an organic sulfur compound was prepared using n-decane as a solvent. The sulfur concentration of this solution corresponds to 12.2 ppm.
 試験溶液C
n-デカン(キシダ化学製、特級)を溶媒とし、有機硫黄化合物としてジベンゾチオフェン(関東化学製、特級)を22.7mg/L、4,6-ジメチルジベンゾチオフェン(和光純薬製、特級)を23.1mg/L、硫黄を含まない芳香族有機化合物としてナフタレン(和光純薬製、特級)を22.1mg/L、溶液分析のための内部標準としてn-テトラデカン(キシダ化学製、特級)を26.5mg/L含む溶液を作製した。この溶液の硫黄濃度はジベンゾチオフェンとして5.4ppm、4,6-ジメチルジベンゾチオフェンとして4.8ppm、合計10.2ppmである。
Test solution C
n-decane (manufactured by Kishida Chemical, special grade) as a solvent, dibenzothiophene (manufactured by Kanto Chemical Co., special grade) as an organic sulfur compound, 22.7 mg / L, 4,6-dimethyldibenzothiophene (manufactured by Wako Pure Chemical, special grade), 23.1 mg / L, 22.1 mg / L of naphthalene (made by Wako Pure Chemicals, special grade) as an aromatic organic compound not containing sulfur, and 26.5 mg / L of n-tetradecane (made by Kishida Chemical, special grade) as an internal standard for solution analysis A solution containing L was prepared. The sulfur concentration of this solution is 5.4 ppm as dibenzothiophene and 4.8 ppm as 4,6-dimethyldibenzothiophene, for a total of 10.2 ppm.
 試験溶液D
試験溶液Aと同様にn-デカンを溶媒とし、有機硫黄化合物としてジベンゾチオフェンを43.2mg/L、溶液分析のための内部標準としてn-テトラデカンを69.3mg/L含む溶液を作製した。この溶液の硫黄濃度は10.3ppmに相当する。
Test solution D
Similarly to the test solution A, a solution containing n-decane as a solvent, 43.2 mg / L of dibenzothiophene as an organic sulfur compound, and 69.3 mg / L of n-tetradecane as an internal standard for solution analysis was prepared. The sulfur concentration of this solution corresponds to 10.3 ppm.
 試験溶液E
n-デカン(キシダ化学製、特級)を溶媒とし、4,6-ジメチルジベンゾチオフェン(和光純薬製、特級)を46.7mg/L、溶液分析のための内部標準としてn-テトラデカン(キシダ化学製、特級)を45.3mg/L含む溶液を作製した。この溶液の硫黄濃度は9.7ppmに相当する。
Test solution E
n-decane (manufactured by Kishida Chemical, special grade) is used as a solvent, 4,6-dimethyldibenzothiophene (manufactured by Wako Pure Chemical Industries, special grade) is 46.7 mg / L, and n-tetradecane (manufactured by Kishida Chemical Co., Ltd.) is used as an internal standard for solution analysis. , Special grade) 45.3 mg / L. The sulfur concentration of this solution corresponds to 9.7 ppm.
 吸着および再生試験法
 試験例1
 上記した方法で調製した脱硫剤1、2及び比較脱硫剤1の各試料粉末を空気中300℃で30分加熱して、吸着水を除去した後、シリカゲルを入れたデシケータ中で室温まで冷やした。スクリュー管瓶にこの試料100mgを秤量し、試験溶液Aを5mL加えて蓋をし、この時刻を吸着開始時刻とした。室温下、振とう機を用い、溶液を攪拌した。途中、脱硫剤1では8.5時間から24時間の間、脱硫剤2と比較脱硫剤1では27時間から47時間の間に溶液温度を60℃に上げているが、本試験例の実験条件においては吸着に対してほぼ影響のないことを別途の実験で確認している。吸着開始後、数時間毎に、スポイトで溶液約0.1mLを抜き取ってFID-GCで溶液組成の分析をした。溶液中のジベンゾチオフェン濃度の時間変化を図1に示す。
Adsorption and regeneration test method test example 1
Each sample powder of desulfurizing agents 1 and 2 and comparative desulfurizing agent 1 prepared by the above method was heated in air at 300 ° C. for 30 minutes to remove adsorbed water, and then cooled to room temperature in a desiccator containing silica gel. . 100 mg of this sample was weighed into a screw tube bottle, 5 mL of test solution A was added, the cap was capped, and this time was taken as the adsorption start time. The solution was stirred using a shaker at room temperature. On the way, the temperature of the desulfurizing agent 1 is raised to 60 ° C for 8.5 to 24 hours, and the desulfurizing agent 2 and the comparative desulfurizing agent 1 are raised to 60 ° C for 27 to 47 hours. It has been confirmed in a separate experiment that there is almost no effect on adsorption. Every few hours after the start of adsorption, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC. The time change of the dibenzothiophene concentration in the solution is shown in FIG.
 図1から、酸化セリウムに金ナノ粒子を担持させた脱硫剤1及び2については、酸化セリウムのみからなる比較脱硫剤1と比較してジベンゾチオフェンの吸着量が多く、特に、金の担持量が多い(11.3wt%)脱硫剤1では、ジベンゾチオフェンの吸着量が非常に多いことが判る。また、脱硫剤1及び2については、24時間以上経過すると吸着量は安定するのに対して、酸化セリウムのみからなる比較脱硫剤1では、5時間経過後に吸着量が減少する現象が確認できた。 From FIG. 1, the desulfurization agents 1 and 2 in which gold nanoparticles are supported on cerium oxide have a larger adsorption amount of dibenzothiophene than the comparative desulfurization agent 1 made only of cerium oxide. It can be seen that with a large amount (11.3 wt%) of the desulfurizing agent 1, the amount of adsorption of dibenzothiophene is very large. In addition, as for desulfurizing agents 1 and 2, the adsorption amount was stabilized after 24 hours or more, whereas in comparative desulfurizing agent 1 consisting only of cerium oxide, it was confirmed that the adsorption amount decreased after 5 hours. .
 以上の結果より、酸化セリウムに金ナノ粒子を担持させた脱硫剤1及び2を用いることによって、デカン溶液中の硫黄濃度10ppmレベルのジベンゾチオフェンを効果的に吸着脱硫できることが明らかである。 From the above results, it is clear that dibenzothiophene having a sulfur concentration of 10 ppm in the decane solution can be effectively adsorbed and desulfurized by using desulfurization agents 1 and 2 in which gold nanoparticles are supported on cerium oxide.
 試験例2
 上記した方法で調製した脱硫剤1試料粉末を空気中300℃で30分加熱して、吸着水を除去した後、シリカゲルを入れたデシケータ中で室温まで冷やした。5本のスクリュー管瓶にこの試料を各々26, 51, 101, 200, 300mg秤量したものを入れ、試験溶液Bを各スクリュー管瓶に5mL加えて蓋をし、この時刻を吸着開始時刻とした。室温下、振とう機を用い、溶液を攪拌した。吸着開始後74時間後(吸着平衡に達していることを確認している)にスポイトで溶液を抜き取り分析した。各々の分析溶液には内部標準物質として既知量の2,8-ジメチルジベンゾチオフェン(東京化成製)を添加してFPD-GCで組成分析を行った。
Test example 2
One sample powder of the desulfurizing agent prepared by the above method was heated in air at 300 ° C. for 30 minutes to remove adsorbed water, and then cooled to room temperature in a desiccator containing silica gel. Weighed 26, 51, 101, 200, and 300 mg of this sample in 5 screw tube bottles, added 5 mL of test solution B to each screw tube bottle, capped, and this time was taken as the adsorption start time. . The solution was stirred using a shaker at room temperature. The solution was extracted and analyzed with a dropper 74 hours after the start of adsorption (confirming that the adsorption equilibrium was reached). A known amount of 2,8-dimethyldibenzothiophene (manufactured by Tokyo Chemical Industry Co., Ltd.) was added to each analysis solution as an internal standard substance, and composition analysis was performed by FPD-GC.
 図2は、使用した脱硫剤重量と、吸着後に試験例溶液中に残存する硫黄濃度及び脱硫剤によって吸着されたジベンゾチオフェン(DBT)量との関係を示すグラフである。尚、図2における試験溶液中の硫黄濃度は、DBT濃度を硫黄濃度に換算したものである。 FIG. 2 is a graph showing the relationship between the weight of the desulfurizing agent used, the sulfur concentration remaining in the test example solution after adsorption, and the amount of dibenzothiophene (DBT) adsorbed by the desulfurizing agent. The sulfur concentration in the test solution in FIG. 2 is obtained by converting the DBT concentration into the sulfur concentration.
 図2から、脱硫剤の使用量を増加するに従って吸着されるジベンゾチオフェン(DBT)の総量が増加し、溶液に残存するDBTの量が減少することが明らかである。特に、脱硫剤300mgを用いた場合には、5mLの試験溶液の初期DBT量(1.38μmol)に近い1.37μmolのDBTが吸着して、吸着前には12.2ppmであった硫黄濃度を0.1ppmまで減少させることができた。 FIG. 2 clearly shows that the total amount of adsorbed dibenzothiophene (DBT) increases and the amount of DBT remaining in the solution decreases as the amount of the desulfurizing agent increases. In particular, when 300 mg of desulfurizing agent was used, 1.37 μmol DBT close to the initial DBT amount (1.38 μmol) of the 5 mL test solution was adsorbed, and the sulfur concentration, which was 12.2 ppm before adsorption, was reduced to 0.1 ppm. It was possible to decrease.
 試験例3
 上記方法で調製した脱硫剤1、3、4及び比較脱硫剤2~4を用いて、下記(1)~(3)の手順で吸着及び再生実験を行った。
Test example 3
Using the desulfurizing agents 1, 3, and 4 and comparative desulfurizing agents 2 to 4 prepared by the above method, adsorption and regeneration experiments were performed by the following procedures (1) to (3).
 (1)1回目の吸着
 各脱硫剤を空気中300℃で30分加熱して、吸着水を除去した後、シリカゲルを入れたデシケータ中で室温まで冷やした。スクリュー管瓶に各脱硫剤100mgを秤量し、試験溶液Cを5mL加えて蓋をし、この時刻を吸着開始時刻とした。室温下、振とう機を用い、溶液を攪拌した。24時間以上経過し吸着平衡に達した時点で、スポイトで溶液約0.1mLを抜き取ってFID-GCで溶液組成の分析をした。
(1) First adsorption Each desulfurization agent was heated in air at 300 ° C for 30 minutes to remove adsorbed water, and then cooled to room temperature in a desiccator containing silica gel. 100 mg of each desulfurizing agent was weighed into a screw tube bottle, 5 mL of test solution C was added and the solution was capped, and this time was taken as the adsorption start time. The solution was stirred using a shaker at room temperature. When the adsorption equilibrium was reached after 24 hours or more had passed, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC.
 (2)再生
 上記方法で吸着実験を行った後、脱硫剤をろ別し、ヘキサンで洗浄し、室温で乾燥した。乾燥後の脱硫剤粉末を石英ガラス反応管に充填し、前後に石英ウールを詰めて固定した。反応管にHe(80%)+O2(20%)のガスを100mL/minで流通しながら、350℃まで10℃/minで昇温し、その後350℃で10min保持した。この操作により、脱硫剤の表面に吸着していた成分は、熱脱離または触媒燃焼により除去され、脱硫剤が再生された。反応管の出口ガスを質量分析計によりモニターすることで、この過程の進行状況を把握した。
(2) Regeneration After performing the adsorption experiment by the above method, the desulfurizing agent was filtered off, washed with hexane, and dried at room temperature. The desulfurizing agent powder after drying was filled in a quartz glass reaction tube, and quartz wool was packed in front and back and fixed. While flowing a gas of He (80%) + O 2 (20%) through the reaction tube at 100 mL / min, the temperature was raised to 350 ° C. at 10 ° C./min, and then maintained at 350 ° C. for 10 min. By this operation, the component adsorbed on the surface of the desulfurizing agent was removed by thermal desorption or catalytic combustion, and the desulfurizing agent was regenerated. The progress of this process was grasped by monitoring the outlet gas of the reaction tube with a mass spectrometer.
 (3) 2回目の吸着
 上記した方法で各脱硫剤を再生させた後、室温に戻した脱硫剤粉末を秤量し、スクリュー管瓶に入れた。この際、再生処理後に回収された脱硫剤量が減少したので、脱硫剤に対する試験溶液の割合が上記(1)の吸着試験と同一となるように、脱硫剤粉末100mgに対して5mLとなる割合で試験溶液Cを加えて蓋をした。24時間以上経過し吸着平衡に達した時点で、スポイトで溶液約0.1mLを抜き取ってFID-GCで溶液組成の分析をした。
(3) Second adsorption Each desulfurization agent was regenerated by the above-described method, and then the desulfurization agent powder returned to room temperature was weighed and placed in a screw tube bottle. At this time, since the amount of the desulfurizing agent recovered after the regeneration treatment decreased, the ratio of 5 mL with respect to 100 mg of the desulfurizing agent powder so that the ratio of the test solution to the desulfurizing agent is the same as the adsorption test of (1) above. Test solution C was added and the lid was closed. When the adsorption equilibrium was reached after 24 hours or more had passed, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC.
 溶液組成の分析結果から、脱硫剤粉末1gあたりのジベンゾチオフェン(DBT)、4,6-ジメチルジベンゾチオフェン(DMDBT)、及びナフタレン(NA)の吸着量を計算した。結果を図3に示す。 From the analysis results of the solution composition, the adsorption amounts of dibenzothiophene (DBT), 4,6-dimethyldibenzothiophene (DMDBT), and naphthalene (NA) per 1 g of the desulfurizing agent powder were calculated. The results are shown in FIG.
 図3から、金属酸化物に金ナノ粒子を担持させた脱硫剤1、3及び4を用いた場合には、ジベンゾチオフェン類(DBT+DMDBT)を選択的に吸着でき、特にDBTの選択性が高いことが判る。また、セリウムイオンY型交換ゼオライト (Ce-Y) からなる比較脱硫剤2は、1回目の全体の吸着量は脱硫剤1、3及び4よりも多いが、DBT, DMDBT, NAをほぼ等モルで吸着しており、硫黄含有有機化合物に対する選択的吸着性は認められなかった。 From FIG. 3, when desulfurizing agents 1, 3 and 4 in which gold nanoparticles are supported on a metal oxide are used, dibenzothiophenes (DBT + DMDBT) can be selectively adsorbed. It turns out to be expensive. Moreover, the comparative desulfurizing agent 2 made of cerium ion Y-type exchanged zeolite (Ce-Y) has a larger total adsorption amount than the desulfurizing agents 1, 3, and 4, but DBT, DMDBT, NA are almost equimolar The selective adsorption to sulfur-containing organic compounds was not observed.
 また、脱硫剤1,3及び4については、2回目の吸着試験においても、1回目の70%以上のジベンゾチオフェン類(DBT+DMDBT)を吸着でき、再生後の吸着率は、比較脱硫剤2及び3と比べて格段に高いことが明らかである。 In addition, desulfurizing agents 1, 3 and 4 can adsorb 70% or more of dibenzothiophenes (DBT + DMDBT) in the first adsorption test, and the adsorption rate after regeneration is comparative desulfurizing agent 2 It is clear that it is much higher than 3 and 3.
 硫化水素の吸着剤として有効なCu/ZnO(比較脱硫剤4)については、Auと同じIB族元素であるCuが多量に担持されているにもかかわらず、ジベンゾチオフェン類の吸着量は少なく、硫黄含有有機化合物に対する吸着剤としての性能が劣ることが判る。 Cu / ZnO (Comparative desulfurization agent 4), which is effective as an adsorbent for hydrogen sulfide, has a small amount of dibenzothiophenes adsorbed despite the fact that Cu, which is the same group IB element as Au, is supported in large quantities. It can be seen that the performance as an adsorbent for sulfur-containing organic compounds is poor.
 試験例4
 下記(1)~(3)の方法で、ジベンゾチオフェン(DBT)の吸着及び脱硫剤の再生の繰り返し試験を行った。尚、この試験は、再生後の脱硫剤の回収量の減少を防止するために、再生時の処理方法を工夫して行ったものである。
Test example 4
Repeated tests of adsorption of dibenzothiophene (DBT) and regeneration of desulfurization agent were performed by the following methods (1) to (3). This test was conducted by devising a treatment method during regeneration in order to prevent a decrease in the recovered amount of the desulfurizing agent after regeneration.
  (1)1回目の吸着
 脱硫剤1を100mg秤量し、容量20mLの梨型フラスコ(耐熱ガラス製)に入れ、フラスコごと電気炉に入れ空気中350℃で30分加熱して、吸着水を除去した後、シリカゲルを入れたデシケータ中で室温まで冷やした。デシケータからフラスコを取り出して直ちにテフロン(登録商標)栓をし、秤量して加熱脱水後の脱硫剤重量を求めた。試験溶液Dを5mL加えてテフロン(登録商標)栓をし、この時刻を吸着開始時刻とした。室温下、振とう機を用い、溶液を攪拌した。24時間以上経過し吸着平衡に達した時点で、振とうを止めてフラスコを静置し脱硫剤粉末を沈降させた。スポイトで上澄み液を抜き取ってFID-GCで溶液組成の分析をした。
(1) First adsorption 100 mg of desulfurizing agent 1 is weighed and placed in a pear-shaped flask (made of heat-resistant glass) with a capacity of 20 mL. The whole flask is placed in an electric furnace and heated in air at 350 ° C. for 30 minutes to remove adsorbed water. Then, it was cooled to room temperature in a desiccator containing silica gel. The flask was taken out from the desiccator, immediately sealed with a Teflon (registered trademark) stopper, and weighed to determine the weight of the desulfurization agent after heat dehydration. 5 mL of test solution D was added and a Teflon (registered trademark) stopper was added, and this time was taken as the adsorption start time. The solution was stirred using a shaker at room temperature. When the adsorption equilibrium was reached after 24 hours or more, the shaking was stopped and the flask was allowed to stand to allow the desulfurizing agent powder to settle. The supernatant was extracted with a dropper and the solution composition was analyzed with FID-GC.
 (2)再生
 上記方法で吸着実験を行った後、フラスコを静置し脱硫剤粉末を沈降させた。静かにフラスコを傾けて脱硫剤粉末が流失しない程度に残りの上澄みの溶液を捨て、ヘキサンを約5mL加えた。ヘキサンを加えて上澄みの溶液を捨てる操作を合計3回繰り返した後、フラスコ内に窒素ガスを吹き込んでヘキサンを揮発させた。フラスコごと電気炉に入れ空気中350℃で30分加熱して、脱硫剤を加熱再生した。加熱後シリカゲルを入れたデシケータ中で室温まで冷やし、デシケータからフラスコを取り出して直ちにテフロン(登録商標)栓をし、秤量して再生後の脱硫剤重量を求めた。このようにフラスコから吸着剤粉末を取り出すことなく再生を行うことで、再生を4回行っても最初に用いた吸着剤の99%以上の重量を保つことができた。
(2) Regeneration After performing the adsorption experiment by the above method, the flask was allowed to stand and the desulfurizing agent powder was allowed to settle. The flask was gently tilted, and the remaining supernatant solution was discarded to such an extent that the desulfurizing agent powder was not washed away, and about 5 mL of hexane was added. The operation of adding hexane and discarding the supernatant solution was repeated a total of 3 times, and then nitrogen gas was blown into the flask to volatilize the hexane. The flask was placed in an electric furnace and heated in air at 350 ° C. for 30 minutes to regenerate the desulfurizing agent by heating. After heating, the mixture was cooled to room temperature in a desiccator containing silica gel, the flask was taken out of the desiccator, immediately plugged with Teflon (registered trademark), and weighed to determine the weight of the desulfurizing agent after regeneration. Thus, by performing regeneration without taking out the adsorbent powder from the flask, it was possible to maintain a weight of 99% or more of the adsorbent used initially even after performing regeneration four times.
 (3)2回目以降の吸着と再生
 上記した方法で脱硫剤を再生させた後、フラスコ中の脱硫剤粉末100mgに対して5mLの割合で試験溶液Dを加えてテフロン(登録商標)栓をした(2回目の吸着開始)。室温下、振とう機を用い、溶液を攪拌した。24時間以上経過し吸着平衡に達した時点で、振とうを止めてフラスコを静置し脱硫剤粉末を沈降させた。スポイトで上澄み液を抜き取ってGCで溶液組成の分析をした。以下、同様に再生と吸着の操作を繰り返した。再生を繰り返すうちに、吸着剤粉末がフラスコ上部の器壁にも貼りついて溶液との接触が悪くなったために、4回目以降の吸着においては吸着開始時に吸着溶液を入れてテフロン(登録商標)栓をした後で、フラスコを超音波洗浄器の水に浸して10秒~数分運転することで吸着剤粉末の分散を良くし、溶液との接触を回復することができた。
(3) Adsorption and regeneration after the second time After regenerating the desulfurizing agent by the method described above, the test solution D was added at a rate of 5 mL to 100 mg of the desulfurizing agent powder in the flask, and the Teflon (registered trademark) stopper was attached. (Second adsorption start). The solution was stirred using a shaker at room temperature. When the adsorption equilibrium was reached after 24 hours or more, the shaking was stopped and the flask was allowed to stand to allow the desulfurizing agent powder to settle. The supernatant was extracted with a dropper and the solution composition was analyzed with GC. Thereafter, the regeneration and adsorption operations were repeated in the same manner. During repeated regeneration, the adsorbent powder stuck to the vessel wall at the top of the flask and contact with the solution worsened. Therefore, in the fourth and subsequent adsorptions, the adsorbent solution was added at the start of adsorption, and the Teflon (registered trademark) plug was inserted. Then, the flask was immersed in the water of an ultrasonic cleaner and operated for 10 seconds to several minutes to improve the dispersion of the adsorbent powder and to recover the contact with the solution.
 各回の吸着終了時の溶液組成の分析結果から、脱硫剤粉末1gあたりのジベンゾチオフェン(DBT)の吸着量を計算した。結果を図4に示す。 The amount of dibenzothiophene (DBT) adsorbed per gram of desulfurizing agent powder was calculated from the analysis result of the solution composition at the end of each adsorption. The results are shown in FIG.
 図4から、吸着-再生を繰り返し行っても吸着量に大きな低下の無いことが明らかである。2回目と3回目においては吸着量が若干少なくなっているが、1~3回目の吸着では吸着開始時に超音波洗浄器を用い吸着剤の分散性を良くする操作を加えていないために、溶液との接触状態が若干悪くなっているためと考えられ、4、5回目の吸着では吸着量も安定し、1回目吸着時の95%以上の吸着量を保つことができた。 FIG. 4 clearly shows that there is no significant decrease in the amount of adsorption even if adsorption-regeneration is repeated. The adsorption amount is slightly reduced in the second and third times, but in the first to third adsorptions, the operation of improving the dispersibility of the adsorbent is not performed at the start of adsorption using an ultrasonic cleaner. This is probably due to the fact that the state of contact with the sample was slightly worse. The adsorption amount was stable in the fourth and fifth adsorption, and the adsorption amount of 95% or more during the first adsorption could be maintained.
 以上の結果から、金属酸化物に金ナノ粒子を担持させた本発明の脱硫剤は、硫黄含有有機化合物、特に、ジベンゾチオフェン類に対する選択的吸着性能に優れたものであり、また、加熱による再生処理を行った後、十分な吸着性能を発揮でき、脱硫剤として再利用が可能であることが明らかである。 From the above results, the desulfurization agent of the present invention in which gold nanoparticles are supported on a metal oxide is excellent in selective adsorption performance for sulfur-containing organic compounds, particularly dibenzothiophenes, and is also regenerated by heating. After the treatment, it is clear that sufficient adsorption performance can be exhibited and reused as a desulfurization agent.
 試験例5
 上記方法で調製した脱硫剤1を用いて、下記(1)~(3)の手順で吸着及び再生を行い、再生時の加熱温度の影響を調べた。
Test Example 5
The desulfurization agent 1 prepared by the above method was used for adsorption and regeneration in the following procedures (1) to (3), and the influence of the heating temperature during regeneration was examined.
 (1)1回目の吸着
 7本のスクリュー管瓶に脱硫剤1を各100mgづつ秤量した。空気中350℃で30分加熱して、吸着水を除去した後、シリカゲルを入れたデシケータ中で室温まで冷やし、塩化カリウム飽和溶液により相対湿度を85%に調節したデシケータの中に1晩放置して吸湿させた。尚、試験例5は、再生時の加熱温度のジベンゾチオフェン(DBT)吸着量への影響を調べることを目的とすることから、残存水分量の違いによるDBT吸着への影響を排除するために、DBT吸着のスタート前に一定条件で試料を吸湿させるよう条件を統一している。
(1) First adsorption 100 mg of desulfurizing agent 1 was weighed in 7 screw tube bottles. Heat at 350 ° C in air for 30 minutes to remove adsorbed water, cool to room temperature in a desiccator containing silica gel, and leave overnight in a desiccator with relative humidity adjusted to 85% with saturated potassium chloride solution. To absorb moisture. In addition, since Test Example 5 aims to investigate the influence of the heating temperature during regeneration on the amount of adsorption of dibenzothiophene (DBT), in order to eliminate the influence on the adsorption of DBT due to the difference in the amount of residual water, The conditions are unified so that the sample absorbs moisture under certain conditions before the start of DBT adsorption.
 各々のスクリュー管瓶に試験溶液Aを5mL加えて蓋をし、この時刻を吸着開始時刻とした。室温下、振とう機を用い、溶液を攪拌した。24時間以上経過し吸着平衡に達した時点で、スポイトで溶液約0.1mLを抜き取ってFID-GCで溶液組成の分析をした。 5 mL of the test solution A was added to each screw tube bottle and the lid was covered, and this time was taken as the adsorption start time. The solution was stirred using a shaker at room temperature. When the adsorption equilibrium was reached after 24 hours or more had passed, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC.
 (2)再生
 上記方法で吸着実験を行った後、試験例4と同様の操作でスクリュー管瓶の中の残存溶液を捨て、ヘキサンで洗浄後、乾燥させた。スクリュー管瓶1本は室温下(25℃)、シリカゲルを入れたデシケータ中で1晩放置した。スクリュー管瓶5本については、1本づつ電気炉に入れ、設定温度を100, 150, 200, 250又は300℃として、空気中で30分加熱した。残りのスクリュー管瓶1本については、中身の脱硫剤粉末を取り出して石英ガラス反応管に充填し、前後に石英ウールを詰めて固定し、反応管にHe(80%)+O2(20%)のガスを100mL/minで流通しながら、350℃まで10℃/minで昇温し、その後350℃で30min保持した。昇温途中に発生したCO2については、質量分析計及び光音響マルチガスモニタ(INNOVA社製)により濃度を測定した。
(2) Regeneration After performing the adsorption experiment by the above method, the remaining solution in the screw tube bottle was discarded by the same operation as in Test Example 4, washed with hexane and dried. One screw tube bottle was left overnight in a desiccator containing silica gel at room temperature (25 ° C.). About five screw tube bottles, it put into the electric furnace one by one, set temperature was 100, 150, 200, 250, or 300 degreeC, and heated in the air for 30 minutes. For the remaining one screw tube bottle, take out the desulfurizing agent powder and fill it into a quartz glass reaction tube, and fill it with quartz wool before and after fixing it. He (80%) + O 2 (20% ) Was circulated at 100 mL / min, the temperature was raised to 350 ° C. at 10 ° C./min, and then maintained at 350 ° C. for 30 min. The concentration of CO2 generated during the temperature increase was measured with a mass spectrometer and a photoacoustic multigas monitor (manufactured by INNOVA).
 このように脱硫剤を25, 100, 150, 200, 250, 300又は 350℃で熱処理後、シリカゲルを入れたデシケータ中で室温まで冷やし、塩化カリウム飽和溶液により相対湿度を85%に調節したデシケータの中に1晩放置して吸湿させた。 After the heat treatment of the desulfurization agent at 25, 100, 150, 200, 250, 300 or 350 ° C in this way, it was cooled to room temperature in a desiccator containing silica gel and the relative humidity was adjusted to 85% with a saturated potassium chloride solution. It was left overnight to absorb moisture.
 (3) 2回目の吸着
 上記した方法により各温度で加熱再生処理後に吸湿させた脱硫剤について、脱硫剤粉末100mgに対して5mLとなる割合で試験溶液Aを加えて蓋をした。24時間以上経過し吸着平衡に達した時点で、スポイトで溶液約0.1mLを抜き取ってFID-GCで溶液組成の分析をした。
(3) Second adsorption With respect to the desulfurization agent absorbed after the heat regeneration treatment at each temperature by the method described above, the test solution A was added at a ratio of 5 mL with respect to 100 mg of the desulfurization agent powder, and the cap was capped. When the adsorption equilibrium was reached after 24 hours or more had passed, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC.
 溶液組成の分析結果から、脱硫剤粉末1gあたりのジベンゾチオフェン(DBT)の吸着量を計算した。1回目の吸着については、同一条件で吸着した7本のスクリュー管瓶についていずれも3.3±0.1μmol/g-触媒のDBT吸着量であった。各温度で熱処理再生後の2回目のDBT吸着量について、熱処理温度とDBT吸着量との関係を図5に示す。図5から、脱硫剤1(Au/CeO2)については、100℃以下の熱処理温度では、2回目の吸着量は1回目に比べて大きく減少しており、熱処理が十分でないことが判る。また、200℃以上の熱処理温度では、2回目の吸着量は1回目とほぼ同じになり、完全に再生されていることが確認できる。 The amount of dibenzothiophene (DBT) adsorbed per gram of desulfurizing agent powder was calculated from the analysis results of the solution composition. As for the first adsorption, the DBT adsorption amount of 3.3 ± 0.1 μmol / g-catalyst for each of the seven screw tube bottles adsorbed under the same conditions. FIG. 5 shows the relationship between the heat treatment temperature and the DBT adsorption amount for the second DBT adsorption amount after the heat treatment regeneration at each temperature. From FIG. 5, it can be seen that for the desulfurization agent 1 (Au / CeO 2 ), at the heat treatment temperature of 100 ° C. or less, the second adsorption amount is greatly reduced compared to the first treatment, and the heat treatment is not sufficient. Further, at a heat treatment temperature of 200 ° C. or higher, the amount of adsorption at the second time becomes almost the same as that at the first time, and it can be confirmed that the regeneration is completely completed.
 図6は、350℃までの加熱した際に、加熱中に発生したCO2量を温度に対してプロットしたグラフである。CO2のピークは115℃と225℃の2つの温度で観測された。このうち低温側のピークはDBTを吸着していないAu/CeO2試料についても観測され、空気中のCO2を吸着したものと考えられる。高温側のピークはDBT吸着後のみに観測され、吸着したDBTが触媒表面で燃焼してCO2となったものと考えられる。図6の網掛けで示した部分に対応するCO2量は37.2μmol /g-触媒であり、1回目の吸着で吸着していたDBT(3.3μmol/g-触媒)が全て燃焼してCO2になったと仮定した場合のCO2量(39.6μmol/g-触媒)と良く一致している。 FIG. 6 is a graph in which the amount of CO 2 generated during heating is plotted against temperature when heated to 350 ° C. CO 2 peaks were observed at two temperatures, 115 ° C and 225 ° C. Of these, the peak on the low temperature side was also observed in the Au / CeO 2 sample that did not adsorb DBT, which is thought to have adsorbed CO 2 in the air. The peak on the high temperature side was observed only after DBT adsorption, and it is considered that the adsorbed DBT burned on the catalyst surface and became CO 2 . The amount of CO 2 corresponding to the shaded portion in FIG. 6 is 37.2 μmol / g-catalyst, and all of the DBT (3.3 μmol / g-catalyst) adsorbed by the first adsorption burns to CO 2. This agrees well with the amount of CO 2 (39.6 μmol / g-catalyst).
 試験例6
 上記方法で調製した脱硫剤1、3及び4について、試験溶液E(ジベンゾチオフェン類として、4,6-ジメチルジベンゾチオフェンのみを含む溶液)を用いて下記の手順で吸着実験を行った。
Test Example 6
The desulfurization agents 1, 3 and 4 prepared by the above method were subjected to adsorption experiments according to the following procedure using the test solution E (a solution containing only 4,6-dimethyldibenzothiophene as dibenzothiophenes).
 各脱硫剤を空気中350℃で30分加熱して、吸着水を除去した後、シリカゲルを入れたデシケータ中で室温まで冷やした。スクリュー管瓶に各脱硫剤100mgを秤量し、試験溶液Eを5mL加えて蓋をし、この時刻を吸着開始時刻とした。室温下、振とう機を用い、溶液を攪拌した。24時間以上経過し吸着平衡に達した時点で、スポイトで溶液約0.1mLを抜き取ってFID-GCで溶液組成の分析をした。 Each desulfurization agent was heated in air at 350 ° C. for 30 minutes to remove adsorbed water, and then cooled to room temperature in a desiccator containing silica gel. 100 mg of each desulfurizing agent was weighed into a screw tube bottle, 5 mL of the test solution E was added and the lid was covered, and this time was taken as the adsorption start time. The solution was stirred using a shaker at room temperature. When the adsorption equilibrium was reached after 24 hours or more had passed, about 0.1 mL of the solution was extracted with a dropper and the solution composition was analyzed with FID-GC.
 溶液組成の分析結果から、脱硫剤粉末1gあたりの4,6-ジメチルジベンゾチオフェン(DMDBT)の吸着量を計算した。結果を図7に示す。図7には、更に、試験例1及び試験例3の結果から算出した試験溶液A(DBTのみを含む溶液)及び試験溶液C(DBT、DMDBT及びNAの混合溶液)を用いた吸着試験の結果も併せて示す。尚、試験溶液A、C及びEの組成は、下記表1に示す通りである。 From the analysis result of the solution composition, the adsorption amount of 4,6-dimethyldibenzothiophene (DMDBT) per 1 g of the desulfurizing agent powder was calculated. The results are shown in FIG. FIG. 7 further shows the results of an adsorption test using test solution A (a solution containing only DBT) and test solution C (a mixed solution of DBT, DMDBT, and NA) calculated from the results of Test Example 1 and Test Example 3. Also shown. The compositions of the test solutions A, C, and E are as shown in Table 1 below.
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000001
 図7に示す結果では、DBT、DMDBT及びNAを含む試験溶液Cを用いた吸着試験の結果、脱硫剤1,3及び4のいずれについても、DMDBTの吸着量と比較して、DBTの吸着量が多くなった。これは、DBTとDMDBTが同じ吸着サイトに対し競争吸着し、メチル基がなく立体障害の少ないDBTの方が選択性良く吸着されていることによると思われる。 In the results shown in FIG. 7, as a result of the adsorption test using the test solution C containing DBT, DMDBT, and NA, the amount of DBT adsorbed in all of the desulfurization agents 1, 3 and 4 was compared with the amount adsorbed in DMDBT. Increased. This seems to be because DBT and DMDBT are adsorbed competitively at the same adsorption site, and DBT with no methyl group and less steric hindrance is adsorbed with better selectivity.
 一方、DMDBT単独の溶液である試験溶液Eを用いた吸着試験では、DMDBT吸着量は、混合溶液である試験用液CからのDMDBT吸着量よりも格段に大きな値となった。脱硫剤1(Au/CeO2)について、DMDBT単独の溶液(試験溶液E)からのDMDBTの吸着量を、DBT単独溶液(試験溶液A)からのDBT吸着量と比較すると、ほぼ97%に相当する値であり、本発明の吸着剤が、DMDBTに対する吸着性能に優れていることが確認できる。 On the other hand, in the adsorption test using test solution E, which is a solution of DMDBT alone, the DMDBT adsorption amount was much larger than the DMDBT adsorption amount from test solution C, which is a mixed solution. For desulfurization agent 1 (Au / CeO 2 ), the amount of DMDBT adsorbed from a solution of DMDBT alone (test solution E) compared to the amount of DBT adsorbed from a solution of DBT alone (test solution A) is approximately 97%. It can be confirmed that the adsorbent of the present invention has excellent adsorption performance for DMDBT.
 現在供給されているサルファーフリー燃料では、残存するジベンゾチオフェン類の中で、現状技術で最も難除去性の4,6-ジメチルジベンゾチオフェンが相対的に大きな部分を占めている。図7に示された結果は、本発明の脱硫剤が、微量に残存した4,6-ジメチルジベンゾチオフェンの除去に好適な特性を有することを示している。 In the currently available sulfur-free fuels, among the remaining dibenzothiophenes, 4,6-dimethyldibenzothiophene, which is the most difficult to remove with the current technology, occupies a relatively large part. The results shown in FIG. 7 indicate that the desulfurization agent of the present invention has characteristics suitable for removing a trace amount of 4,6-dimethyldibenzothiophene.

Claims (10)

  1. 平均粒径50nm以下の金ナノ粒子を金属酸化物に担持してなる液相用吸着脱硫剤。 A liquid phase adsorptive desulfurization agent obtained by supporting gold nanoparticles having an average particle size of 50 nm or less on a metal oxide.
  2. 比表面積が1m2/g以上である請求項1に記載の脱硫剤。 The desulfurizing agent according to claim 1, wherein the specific surface area is 1 m 2 / g or more.
  3. 請求項1に記載の金ナノ粒子担持金属酸化物を支持体上に固定化した液相用吸着脱硫剤。 A liquid phase adsorptive desulfurization agent, wherein the gold nanoparticle-supported metal oxide according to claim 1 is immobilized on a support.
  4. 処理対象が、硫黄含有有機化合物を含む液体燃料である請求項1に記載の脱硫剤。 The desulfurizing agent according to claim 1, wherein the treatment target is a liquid fuel containing a sulfur-containing organic compound.
  5. 請求項1に記載の脱硫剤を、硫黄含有有機化合物を含む液体と接触させることを特徴とする脱硫方法。 A desulfurization method comprising contacting the desulfurizing agent according to claim 1 with a liquid containing a sulfur-containing organic compound.
  6. 処理対象が硫黄含有有機化合物を含む液体燃料である請求項5に記載の脱硫方法。 The desulfurization method according to claim 5, wherein the treatment target is a liquid fuel containing a sulfur-containing organic compound.
  7. 処理対象の液体燃料が、チオフェン環を有する有機化合物を含むものである請求項6に記載の脱硫方法。 The desulfurization method according to claim 6, wherein the liquid fuel to be treated contains an organic compound having a thiophene ring.
  8. チオフェン環を有する有機化合物が、ジベンゾチオフェン及びアルキルジベンゾチオフェン類からなる群から選ばれた少なくとも一種の化合物である請求項7に記載の脱硫方法。 The desulfurization method according to claim 7, wherein the organic compound having a thiophene ring is at least one compound selected from the group consisting of dibenzothiophene and alkyldibenzothiophenes.
  9. 請求項5の方法によって脱硫処理を行った後、脱硫剤を加熱処理して該脱硫剤に吸着された硫黄含有有機化合物を除去することを特徴とする脱硫剤の再生方法。 6. A method for regenerating a desulfurizing agent, comprising performing a desulfurization treatment by the method of claim 5 and then heat-treating the desulfurizing agent to remove a sulfur-containing organic compound adsorbed on the desulfurizing agent.
  10. 請求項9の方法によって再生処理を行った脱硫剤を、請求項5の方法によって硫黄含有有機化合物を含む液体と接触させることを特徴とする脱硫方法。
      
    A desulfurization method wherein the desulfurization agent regenerated by the method of claim 9 is brought into contact with a liquid containing a sulfur-containing organic compound by the method of claim 5.
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