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US20010015339A1 - Method of improving the quality of diesel fuel - Google Patents

Method of improving the quality of diesel fuel Download PDF

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Publication number
US20010015339A1
US20010015339A1 US09/735,565 US73556500A US2001015339A1 US 20010015339 A1 US20010015339 A1 US 20010015339A1 US 73556500 A US73556500 A US 73556500A US 2001015339 A1 US2001015339 A1 US 2001015339A1
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diesel fuel
oxidizing gas
sub
tube
bubbles
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US09/735,565
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Jeffrey Sherman
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Reaction 35 LLC
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Priority claimed from US09/325,503 external-priority patent/US6103130A/en
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Priority to US09/735,565 priority Critical patent/US20010015339A1/en
Assigned to GRT, INC. reassignment GRT, INC. ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: SHERMAN, JEFFREY H.
Publication of US20010015339A1 publication Critical patent/US20010015339A1/en
Priority to US10/082,853 priority patent/US6596177B2/en
Assigned to REACTION 35, LLC reassignment REACTION 35, LLC ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: GRT, INC.
Assigned to REACTION 35, LLC reassignment REACTION 35, LLC RELEASE BY SECURED PARTY (SEE DOCUMENT FOR DETAILS). Assignors: HOOK, THOMAS W.
Abandoned legal-status Critical Current

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    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/72—Treatment of water, waste water, or sewage by oxidation
    • C02F1/78—Treatment of water, waste water, or sewage by oxidation with ozone
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
    • B01F23/20—Mixing gases with liquids
    • B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
    • B01F23/231—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids by bubbling
    • B01F23/23105—Arrangement or manipulation of the gas bubbling devices
    • B01F23/2312—Diffusers
    • B01F23/23123—Diffusers consisting of rigid porous or perforated material
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
    • B01F23/20—Mixing gases with liquids
    • B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
    • B01F23/231—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids by bubbling
    • B01F23/23105—Arrangement or manipulation of the gas bubbling devices
    • B01F23/2312—Diffusers
    • B01F23/23126—Diffusers characterised by the shape of the diffuser element
    • B01F23/231265—Diffusers characterised by the shape of the diffuser element being tubes, tubular elements, cylindrical elements or set of tubes
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
    • B01F23/20—Mixing gases with liquids
    • B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
    • B01F23/233—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids using driven stirrers with completely immersed stirring elements
    • B01F23/2331—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids using driven stirrers with completely immersed stirring elements characterised by the introduction of the gas along the axis of the stirrer or along the stirrer elements
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
    • B01F23/20—Mixing gases with liquids
    • B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
    • B01F23/237—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids characterised by the physical or chemical properties of gases or vapours introduced in the liquid media
    • B01F23/2373—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids characterised by the physical or chemical properties of gases or vapours introduced in the liquid media for obtaining fine bubbles, i.e. bubbles with a size below 100 µm
    • B01F23/2375—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids characterised by the physical or chemical properties of gases or vapours introduced in the liquid media for obtaining fine bubbles, i.e. bubbles with a size below 100 µm for obtaining bubbles with a size below 1 µm
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
    • B01F23/20—Mixing gases with liquids
    • B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
    • B01F23/237—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids characterised by the physical or chemical properties of gases or vapours introduced in the liquid media
    • B01F23/2376—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids characterised by the physical or chemical properties of gases or vapours introduced in the liquid media characterised by the gas being introduced
    • B01F23/23761—Aerating, i.e. introducing oxygen containing gas in liquids
    • B01F23/237612—Oxygen
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F25/00—Flow mixers; Mixers for falling materials, e.g. solid particles
    • B01F25/30—Injector mixers
    • B01F25/31—Injector mixers in conduits or tubes through which the main component flows
    • B01F25/313—Injector mixers in conduits or tubes through which the main component flows wherein additional components are introduced in the centre of the conduit
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/72—Treatment of water, waste water, or sewage by oxidation
    • C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/72—Treatment of water, waste water, or sewage by oxidation
    • C02F1/76—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
    • C02F1/763—Devices for the addition of such compounds in gaseous form
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
    • B01F23/20—Mixing gases with liquids
    • B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
    • B01F23/231—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids by bubbling
    • B01F23/23105—Arrangement or manipulation of the gas bubbling devices
    • B01F23/2312—Diffusers
    • B01F23/23126—Diffusers characterised by the shape of the diffuser element
    • B01F23/231262—Diffusers characterised by the shape of the diffuser element having disc shape
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
    • B01F23/20—Mixing gases with liquids
    • B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
    • B01F23/233—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids using driven stirrers with completely immersed stirring elements
    • B01F23/2336—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids using driven stirrers with completely immersed stirring elements characterised by the location of the place of introduction of the gas relative to the stirrer
    • B01F23/23364—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids using driven stirrers with completely immersed stirring elements characterised by the location of the place of introduction of the gas relative to the stirrer the gas being introduced between the stirrer elements
    • B01F23/233641—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids using driven stirrers with completely immersed stirring elements characterised by the location of the place of introduction of the gas relative to the stirrer the gas being introduced between the stirrer elements at the stirrer axis
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/72—Treatment of water, waste water, or sewage by oxidation
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/72—Treatment of water, waste water, or sewage by oxidation
    • C02F1/722—Oxidation by peroxides
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/72—Treatment of water, waste water, or sewage by oxidation
    • C02F1/74—Treatment of water, waste water, or sewage by oxidation with air
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/72—Treatment of water, waste water, or sewage by oxidation
    • C02F1/76—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00—Apparatus for treatment of water, waste water or sewage
    • C02F2201/78—Details relating to ozone treatment devices
    • C02F2201/782—Ozone generators
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00—Technologies for wastewater treatment
    • Y02W10/30—Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
    • Y10S—TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10S210/00—Liquid purification or separation
    • Y10S210/902—Materials removed
    • Y10S210/908—Organic

Definitions

  • This invention relates generally to the treatment of contaminated liquids with oxidizing gases, and more particularly to a method of improving the quality of diesel fuel by removing sulfur compounds therefrom and raising the cetane number thereof.
  • Diesel fuel quality is rated by cetane number, a parameter similar to the octane rating number for gasoline.
  • cetane number a parameter similar to the octane rating number for gasoline.
  • One class of compounds that contributes to a low cetane number are aromatics, including biphenyl derivatives. Thus, when hydrotreating is used to remove sulfur from diesel fuel, thiophenes are converted to biphenyl derivatives and the cetane number of the fuel is reduced.
  • sulfur in diesel fuel is oxidized to a sulfoxide or a sulfone.
  • the sulfur-containing molecule is easily removed from the diesel fuel by distillation or extraction.
  • oxidative desulfurization and the subsequent removal of the molecules containing the oxidized sulfur results in a decrease in aromatic content.
  • the decrease in aromatic content leads directly to an increase in cetane number.
  • oxidizing gas is utilized at its source and is formed into sub-micron size bubbles which are immediately dispersed into flowing diesel fuel. Due to the sub-micron size of the bubbles, the surface area of the oxidizing gas is greatly increased, thereby greatly increasing the efficiency of the oxidation reaction.
  • the oxidizing gas is formed into sub-micron size bubbles by directing it through a sintered glass, sintered ceramic, or porous ceramic tube. Diesel fuel is caused to flow past the exterior of the sintered/porous tube. The flowing diesel fuel cleaves sub-micron size bubbles of the oxidizing gas from the surface of the tube. The sub-micron size bubbles of oxidizing gas are dispersed into the diesel fuel, whereupon sulfur compounds contained within the diesel fuel are efficiently oxidized into sulfoxides or sulfones, which are in turn removed by distillation or extraction.
  • FIG. 1 is a flow chart illustrating a first embodiment of the invention
  • FIG. 2 is a diagrammatic illustration of a first apparatus useful in the practice of the method of the invention
  • FIG. 3 is a diagrammatic illustration of a second apparatus useful in the practice of the method of the invention.
  • FIG. 4 is a diagrammatic illustration of a third apparatus useful in the practice of the method of the invention.
  • FIG. 5 is a diagrammatic illustration of a second embodiment of the invention.
  • FIG. 6 is a further illustration of the embodiment of FIG. 5.
  • the first step of the method comprises the manufacture of an oxidizing gas utilizing conventional and well known techniques.
  • the oxidizing gas preferably comprises ozone, however, other oxidizing gases may be utilized in the practice of the invention, if desired.
  • the selected oxidizing gas is formed into sub-micron size bubbles.
  • a quantity of diesel fuel having organic contaminants contained therein, such as compounds of sulfur, is caused to flow into engagement with the sub-micron size bubbles of oxidizing gas.
  • the oxidizing gas bubbles are dispersed into the diesel fuel whereupon the sulfur compounds contained within the oil are immediately oxidized, thereby forming sulfoxides and/or sulfones.
  • the sub-micron size of the bubbles of the oxidizing gas greatly increases the surface area of the oxidizing gas/diesel fuel interface thereby substantially increasing the efficiency of the oxidizing reaction.
  • the sulfoxides and /or sulfones are removed from the diesel fuel by distillation or extraction.
  • FIG. 2 there is shown an apparatus 10 which may be utilized in the practice in the method of the invention.
  • the apparatus 10 includes a hollow tube 12 formed from sintered glass, sintered ceramic, or porous ceramic. Those skilled in the art will know and understand that other porous materials not subject to attack by oxidizing agents may be used in the practice of the invention.
  • the sintered/porous tube 12 is positioned within a tank 14 .
  • An oxidizing gas is manufactured within a source 16 utilizing conventional and well known techniques.
  • the oxidizing gas is preferably ozone, however, other oxidizing gases may be utilized in the practice of the invention if desired.
  • the oxidizing gas from the source 16 is directed into the interior of the sintered/porous tube 12 through piping 18 .
  • diesel fuel having sulfur compounds initially contained therein is caused to flow from a source 20 through piping 22 and the tank 14 to an outlet 24 .
  • the source 20 may comprise a conventional reservoir, tank, etc., which receives diesel fuel from one or more sources.
  • the pressure of the oxidizing gas within in the interior of the sintered/porous tube 12 is maintained high enough to prevent diesel fuel contained within the tank 14 from flowing inwardly through the tube 12 into the interior thereof. Rather, oxidizing gas flows outwardly from the interior of the tube 12 and is formed into sub-micron size bubbles which are cleaved from the exterior surface of the sintered glass, sintered ceramic, or porous ceramic tube 12 by, and are dispersed in the flowing diesel fuel.
  • the diesel fuel from the source 20 flows through the tank 14 , it passes over the exterior surface of the sintered/porous tube 12 thereby cleaving the sub-micron size bubbles of oxidizing gas from the exterior surface thereof.
  • the sub-micron sized bubbles of oxidizing gas are immediately dispersed throughout the flowing fuel, whereupon organic contaminants contained within the diesel fuel are immediately oxidized into sulfoxides and/or sulfones. It will be appreciated that because of the sub-micron size of the bubbles comprising the oxidizing gas the surface area of the interface between the oxidizing gas and the diesel fuel is greatly increased, thereby greatly increasing the efficiency of the oxidizing reaction.
  • oxidizing gas will be consumed by the oxidizing reaction. If not, excess oxidizing gas may be recovered from the diesel fuel through an outlet 26 and properly disposed of. The diesel fuel is then directed to an apparatus 28 wherein the sulfoxides and/or sulfones which were formed during the oxidation reaction are removed from the diesel fuel either by distillation or by extraction.
  • FIG. 3 An alternative apparatus 30 which may be utilized in the practice of the method of the invention is illustrated in FIG. 3.
  • the apparatus 30 includes a sintered glass, sintered ceramic, or porous ceramic tube 32 having a hollow interior which is supported within a tank 34 for rotation about its longitudinal axis.
  • a motor 36 is positioned at one end of the tank 34 and is operatively connected to the tube 32 to effect rotation thereof relative to the tank 34 .
  • An annulus 38 is located at one end of the tank 34 and is separated from the tank 34 and from the motor 36 by seals 40 .
  • a collar 42 connects the annulus 38 to the interior of the sintered/porous tube 32 through a plurality of passageways 44 .
  • an oxidizing gas is manufactured within a source 46 utilizing conventional and well known techniques.
  • the oxidizing gas is preferably ozone and, however, other oxidizing gases may be utilized in the practice of the invention.
  • the oxidizing gases directed into the annalus 38 through piping 48 . From the annalus 38 the oxidizing gas flows into the interior of the sintered glass, sintered ceramic, or porous ceramic tube through the passageways 44 of the collar 42 .
  • the source 50 may comprise a conventional reservoir or tank which receives the diesel fuel from one or more sources.
  • Diesel fuel continuously flows from the source 50 through piping 52 and through the tank 34 to an outlet 54 .
  • the pressure of the oxidizing gas within the hollow interior of the tube 32 is maintained sufficiently high that diesel fuel flowing through the tank 34 does not flow inwardly through the tube 32 into the interior thereof. Rather, oxidizing gas from the source 46 flows outwardly from the interior of the sintered or porous tube 32 to the outer surface thereof.
  • the outwardly flowing oxidizing gas accumulates on the exterior surface of the sintered tube 32 in the form of sub-micron size bubbles.
  • the sub-micron size bubbles of oxidizing gas are immediately cleaved from the exterior surface of the sintered tube by the flow of the diesel fuel over the exterior surface of the sintered/porous tube 32 .
  • the sub-micron sized bubbles are dispersed throughout the flowing diesel fuel whereby the sulfur compounds initially contained within the flowing diesel fuel are immediately oxidized into sulfoxides and/or sulfones.
  • the sub-micron size of the bubbles of the oxidizing gas greatly increases the size of the interface between the oxidizing gas and the initially contaminated liquid, thereby greatly increasing the efficiency of the oxidation reaction.
  • Treated diesel fuel is recovered through the outlet 54 . It is contemplated that all of the oxidizing gas will be consumed by the oxidizing reaction. If not, excess oxidizing gas may be recovered from the treated liquid through an outlet 56 and thereafter properly disposed of.
  • the diesel fuel flows into an apparatus 58 wherein the sulfoxides and/or sulfones formed by the oxidation reaction are removed by distillation or extraction.
  • the treated diesel fuel is recovered at outlet 59 .
  • the exterior surface of the tube 32 is rotated relative to the diesel fuel flowing through the tank 34 under the action of the motor 36 .
  • the relative movement between the exterior surface of the tube 32 and the diesel fuel flowing through the tank 34 is greatly increased. This in turn increases the number of sub-micron sized bubbles of oxidizing gas which is dispersed into the flowing liquid, thereby increasing the efficiency of the oxidation reaction.
  • FIG. 4 An alternative apparatus 60 which may be utilized in the practice of the method of the invention is illustrated in FIG. 4.
  • the apparatus 60 includes a sintered glass, sintered ceramic, or porous ceramic tube 62 having a hollow interior which is supported within a tank 64 for rotation about its longitudinal axis.
  • One or more turbines 66 are mounted on the sintered/porous tube 62 to effect rotation thereof relative to the tank 64 .
  • an oxidizing gas is manufactured within a source 76 utilizing conventional and well known techniques.
  • the oxidizing gas is preferably ozone, however, other oxidizing gases may be utilized in the practice of the invention.
  • the oxidizing gas is directed into the interior of the sintered or porous tube 62 .
  • Diesel fuel as received from a source 80 may comprise a conventional reservoir or tank which receives the diesel fuel from one or more sources.
  • Diesel fuel continuously flows from the source 80 through piping 82 and through the tank 64 to an outlet 84 .
  • the pressure of the oxidizing gas within the hollow interior of the tube 62 is maintained sufficiently high that diesel fuel flowing through the tank 64 does not flow inwardly through the tube 62 into the interior thereof. Rather, oxidizing gas from the source 76 flows outwardly from the interior of the tube 62 to the outer surface thereof.
  • the outwardly flowing oxidizing gas accumulates on the exterior surface of the sintered/porous tube 62 in the form of sub-micron size bubbles.
  • the sub-micron size bubbles of oxidizing gas are immediately cleaved from the exterior surface of the sintered tube by the flow of the diesel fuel over the exterior surface of the tube 62 .
  • the sub-micron sized bubbles are dispersed throughout the flowing diesel fuel whereby the sulfur compounds initially contained within the flowing diesel fuel are immediately oxidized into sulfoxides and/or sulfones.
  • the sub-micron size of the bubbles of the oxidizing gas greatly increases the size of the interface between the oxidizing gas and the initially contaminated liquid, thereby greatly increasing the efficiency of the oxidation reaction.
  • Treated diesel fuel is recovered through the outlet 84 . It is contemplated that all of the oxidizing gas will be consumed by the oxidizing reaction. If not, excess oxidizing gas may be recovered from the treated liquid through an outlet 86 and thereafter properly disposed of.
  • the diesel fuel flows into an apparatus 88 wherein the sulfoxides and/or sulfones formed by the oxidation reaction are removed by distillation or extraction.
  • the treated diesel fuel is recovered at outlet 90 .
  • the use of the apparatus 30 shown in FIG. 3 or the apparatus 60 shown in FIG. 4 provides certain advantages with respect to the use of the apparatus shown in FIG. 2 in the practice of method of the invention.
  • the relative movement between the exterior surface of the sintered/porous tube 32 and the diesel fuel flowing through the tank 34 depends upon the operation of the motor 36 rather than the flow rate of the liquid. This allows a greater number of sub-micron size bubbles of oxidizing gas to be dispersed into the diesel fuel than would be possible if the cleaving of sub-microns sized bubbles of oxidizing gas from the exterior surface of the tube 32 depended upon the flow of fuel alone. In this manner the efficiency of the oxidation reaction can be further increased.
  • the relative movement between the exterior surface of the sintered/porous tube 62 and the diesel fuel flowing through the tank 34 is greatly increased by the operation of the turbines 66 .
  • This allows a greater number of sub-micron size bubbles of oxidizing gas to be dispersed into the diesel fuel than would be possible if the cleaving of sub-microns sized bubbles of oxidizing gas from the exterior surface of the tube 62 depended upon the flow of fuel alone. In this manner the efficiency of the oxidation reaction can be further increased.
  • FIGS. 5 and 6 there is shown a method of and apparatus for improving the quality of diesel fuel 100 comprising a second embodiment of the invention.
  • a tank 102 having a quantity of diesel fuel 104 contained therein.
  • the diesel fuel is supplied to the tank 102 from a source 106 through piping 107 .
  • a hollow disk 108 is mounted in the lower portion of the tank 102 .
  • the disk 108 includes a gas permeable partition 110 supported on a tube 112 for rotation within the tank 102 under the operation under the motor 114 .
  • the partition 110 may comprise sintered glass, sintered ceramic, or porous ceramic materials depending upon the requirements of particular applications of the invention.
  • Oxidizing gas received from a supply 116 is directed through piping 118 and a suitable commutator 120 into the tube 112 and through the tube 112 into the interior of the hollow disk 108 .
  • the tube 112 has a hollow interior 121 and the disk 108 has a hollow interior 122 connected in fluid communication therewith.
  • the disk 108 is supplied with oxidizing gas at a pressure just high enough to overcome the head pressure of the water or other liquid 104 .
  • the disk 108 is rotated by the motor 114 at an appropriate speed in contact with the diesel fuel 104 such that a shearing phenomen occurs at the surface of the gas permeable partition 110 thus producing bubbles of extremely small, i.e., sub-micron, size.
  • the extreme small size of the bubbles thus produced results in a surface area to volume ratio of small bubbles which significantly improves the efficiency of the oxidation reaction, in particular because the required vertical height of the tank 102 and therefore the pressure of the gas is substantially reduced due to the slower movement of the small bubbles in the liquid.
  • the oxidizing gas reacts with sulfur compounds in the diesel fuel to form sulfoxides and/or sulfones.
  • Diesel fuel is recovered from the tank 102 through outlet 123 and any residual gas is recovered from the tank 102 through outlet 124 .
  • the diesel fuel is directed to an apparatus 126 wherein the sulfoxides and/or sulfones formed duration the oxidation reaction are removed either by distillation or by extraction.
  • the treated diesel fuel is recovered at outlet 128 .
  • the method of improving the quality of diesel fuel comprised in the present invention may be used either as the sole process for treating diesel fuel or in combination with existing hydrotreating techniques.
  • the method of the present invention totally removes sulfur compounds from diesel fuel, thereby improving the cetane rating of the diesel fuel.
  • the aromatic compounds which remain after the hydrotreating process are removed thereby increasing the cetane rating of the diesel fuel.

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Organic Chemistry (AREA)
  • Nanotechnology (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Physical Water Treatments (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
  • Liquid Carbonaceous Fuels (AREA)

Abstract

In a method of improving the quality of diesel fuel, an oxidizing gas is formed into sub-micron size bubbles which are dispersed into diesel fuel, after which the treated fuel is recovered. The oxidizing gas is preferably ozone and is utilized immediately upon its manufacture. By means of the method, sulfur is removed from the diesel fuel and the cetane rating thereof is increased.

Description

    CROSS REFERENCE TO RELATED APPLICATION
  • This application is a continuation-in-part of application Ser. No. 09/418,445 filed Oct. 15, 1999, currently pending, which is a continuation-in-part of application Ser. No. 09/325,503 filed Jun. 3, 1999, now U.S. Pat. No. 6,103,130. [0001]
    • TECHNICAL FIELD
  • This invention relates generally to the treatment of contaminated liquids with oxidizing gases, and more particularly to a method of improving the quality of diesel fuel by removing sulfur compounds therefrom and raising the cetane number thereof. [0002]
    • BACKGROUND AND SUMMARY OF THE INVENTION
  • Domestic diesel fuel contains, at most, 0.05% sulfur by weight. Refineries produce diesel fuel as a distillate of crude oil which is then hydrotreated to reduce the sulfur content to 0.05% or less. In hydrotreating, a reducing process, the diesel fuel is contacted with high pressure hydrogen gas in the presence of a solid catalyst. The catalyst serves to remove the sulfur in the form of sulfide, while the hydrogen serves to saturate the molecules from which the sulfur is removed. [0003]
  • While hydrotreating is effective at reducing the sulfur content of diesel fuels substantially, certain forms or sulfur are easier to remove then others. For example, sulfur in the form of sulfide is easier to remove than sulfur in the thiophene form. As a result, the sulfur that remains in diesel fuel after hydrotreating is mostly in the thiophene form. As thiophenes increase in complexity, the sulfur becomes more difficult to remove, requiring hydrotreating at more severe conditions. The higher the severity of the hydrotreating process, the shorter catalyst life time. Additionally, severe hydrotreating conditions lead to cracking of the diesel fuel molecules and thus higher yield losses. The sulfur remaining in diesel fuel after hydrotreating is primarily or exclusively in the thiophene form. Thiophenes reduced during the hydrotreating process are converted to biphenyl derivatives. [0004]
  • Recently, the United States Environmental Protection Agency (EPA) promulgated regulations sharply reducing the allowed sulfur content of diesel fuels. No later than year 2006, diesel fuel must contain less than 15 ppm sulfur (0.0015% by weight). This standard will require hydrotreating under conditions of increased severity. [0005]
  • Diesel fuel quality is rated by cetane number, a parameter similar to the octane rating number for gasoline. The higher the cetane number, the higher the quality of the diesel fuel. One class of compounds that contributes to a low cetane number are aromatics, including biphenyl derivatives. Thus, when hydrotreating is used to remove sulfur from diesel fuel, thiophenes are converted to biphenyl derivatives and the cetane number of the fuel is reduced. [0006]
  • In accordance with the present invention, sulfur in diesel fuel is oxidized to a sulfoxide or a sulfone. Once in the sulfoxide or sulfone form, the sulfur-containing molecule is easily removed from the diesel fuel by distillation or extraction. In contrast to hydrotreating, oxidative desulfurization and the subsequent removal of the molecules containing the oxidized sulfur results in a decrease in aromatic content. The decrease in aromatic content leads directly to an increase in cetane number. [0007]
  • In accordance with the one aspect of the invention, oxidizing gas is utilized at its source and is formed into sub-micron size bubbles which are immediately dispersed into flowing diesel fuel. Due to the sub-micron size of the bubbles, the surface area of the oxidizing gas is greatly increased, thereby greatly increasing the efficiency of the oxidation reaction. [0008]
  • In accordance with another aspect of the invention, the oxidizing gas is formed into sub-micron size bubbles by directing it through a sintered glass, sintered ceramic, or porous ceramic tube. Diesel fuel is caused to flow past the exterior of the sintered/porous tube. The flowing diesel fuel cleaves sub-micron size bubbles of the oxidizing gas from the surface of the tube. The sub-micron size bubbles of oxidizing gas are dispersed into the diesel fuel, whereupon sulfur compounds contained within the diesel fuel are efficiently oxidized into sulfoxides or sulfones, which are in turn removed by distillation or extraction. [0009]
    • BRIEF DESCRIPTION OF THE DRAWINGS
  • A more complete understanding of the invention may be had by reference to the following Detailed Description when taken in conjunction with the accompanying Drawings, wherein: [0010]
  • FIG. 1 is a flow chart illustrating a first embodiment of the invention; [0011]
  • FIG. 2 is a diagrammatic illustration of a first apparatus useful in the practice of the method of the invention; [0012]
  • FIG. 3 is a diagrammatic illustration of a second apparatus useful in the practice of the method of the invention; [0013]
  • FIG. 4 is a diagrammatic illustration of a third apparatus useful in the practice of the method of the invention; [0014]
  • FIG. 5 is a diagrammatic illustration of a second embodiment of the invention; and [0015]
  • FIG. 6 is a further illustration of the embodiment of FIG. 5. [0016]
    • DETAILED DESCRIPTION
  • Referring now to the Drawings, and particularly to FIG. 1 thereof, there is shown a method of improving the quality of diesel fuel comprising the preferred embodiment of the invention. The first step of the method comprises the manufacture of an oxidizing gas utilizing conventional and well known techniques. The oxidizing gas preferably comprises ozone, however, other oxidizing gases may be utilized in the practice of the invention, if desired. Immediately upon its manufacture, the selected oxidizing gas is formed into sub-micron size bubbles. [0017]
  • A quantity of diesel fuel having organic contaminants contained therein, such as compounds of sulfur, is caused to flow into engagement with the sub-micron size bubbles of oxidizing gas. The oxidizing gas bubbles are dispersed into the diesel fuel whereupon the sulfur compounds contained within the oil are immediately oxidized, thereby forming sulfoxides and/or sulfones. The sub-micron size of the bubbles of the oxidizing gas greatly increases the surface area of the oxidizing gas/diesel fuel interface thereby substantially increasing the efficiency of the oxidizing reaction. Upon completion of the oxidation reaction, the sulfoxides and /or sulfones are removed from the diesel fuel by distillation or extraction. [0018]
  • Referring to FIG. 2 there is shown an [0019] apparatus 10 which may be utilized in the practice in the method of the invention. The apparatus 10 includes a hollow tube 12 formed from sintered glass, sintered ceramic, or porous ceramic. Those skilled in the art will know and understand that other porous materials not subject to attack by oxidizing agents may be used in the practice of the invention. The sintered/porous tube 12 is positioned within a tank 14.
  • An oxidizing gas is manufactured within a [0020] source 16 utilizing conventional and well known techniques. The oxidizing gas is preferably ozone, however, other oxidizing gases may be utilized in the practice of the invention if desired. Immediately upon its manufacture the oxidizing gas from the source 16 is directed into the interior of the sintered/porous tube 12 through piping 18.
  • Meanwhile diesel fuel having sulfur compounds initially contained therein is caused to flow from a [0021] source 20 through piping 22 and the tank 14 to an outlet 24. The source 20 may comprise a conventional reservoir, tank, etc., which receives diesel fuel from one or more sources.
  • The pressure of the oxidizing gas within in the interior of the sintered/[0022] porous tube 12 is maintained high enough to prevent diesel fuel contained within the tank 14 from flowing inwardly through the tube 12 into the interior thereof. Rather, oxidizing gas flows outwardly from the interior of the tube 12 and is formed into sub-micron size bubbles which are cleaved from the exterior surface of the sintered glass, sintered ceramic, or porous ceramic tube 12 by, and are dispersed in the flowing diesel fuel.
  • As the diesel fuel from the [0023] source 20 flows through the tank 14, it passes over the exterior surface of the sintered/porous tube 12 thereby cleaving the sub-micron size bubbles of oxidizing gas from the exterior surface thereof. The sub-micron sized bubbles of oxidizing gas are immediately dispersed throughout the flowing fuel, whereupon organic contaminants contained within the diesel fuel are immediately oxidized into sulfoxides and/or sulfones. It will be appreciated that because of the sub-micron size of the bubbles comprising the oxidizing gas the surface area of the interface between the oxidizing gas and the diesel fuel is greatly increased, thereby greatly increasing the efficiency of the oxidizing reaction.
  • It is contemplated that all of the oxidizing gas will be consumed by the oxidizing reaction. If not, excess oxidizing gas may be recovered from the diesel fuel through an [0024] outlet 26 and properly disposed of. The diesel fuel is then directed to an apparatus 28 wherein the sulfoxides and/or sulfones which were formed during the oxidation reaction are removed from the diesel fuel either by distillation or by extraction.
  • An [0025] alternative apparatus 30 which may be utilized in the practice of the method of the invention is illustrated in FIG. 3. The apparatus 30 includes a sintered glass, sintered ceramic, or porous ceramic tube 32 having a hollow interior which is supported within a tank 34 for rotation about its longitudinal axis. A motor 36 is positioned at one end of the tank 34 and is operatively connected to the tube 32 to effect rotation thereof relative to the tank 34. An annulus 38 is located at one end of the tank 34 and is separated from the tank 34 and from the motor 36 by seals 40. A collar 42 connects the annulus 38 to the interior of the sintered/porous tube 32 through a plurality of passageways 44.
  • In the operation of the [0026] apparatus 30 an oxidizing gas is manufactured within a source 46 utilizing conventional and well known techniques. The oxidizing gas is preferably ozone and, however, other oxidizing gases may be utilized in the practice of the invention. Immediately upon its manufacture the oxidizing gases directed into the annalus 38 through piping 48. From the annalus 38 the oxidizing gas flows into the interior of the sintered glass, sintered ceramic, or porous ceramic tube through the passageways 44 of the collar 42.
  • Diesel fuel received from a [0027] source 50. The source 50 may comprise a conventional reservoir or tank which receives the diesel fuel from one or more sources.
  • Diesel fuel continuously flows from the [0028] source 50 through piping 52 and through the tank 34 to an outlet 54. The pressure of the oxidizing gas within the hollow interior of the tube 32 is maintained sufficiently high that diesel fuel flowing through the tank 34 does not flow inwardly through the tube 32 into the interior thereof. Rather, oxidizing gas from the source 46 flows outwardly from the interior of the sintered or porous tube 32 to the outer surface thereof.
  • The outwardly flowing oxidizing gas accumulates on the exterior surface of the [0029] sintered tube 32 in the form of sub-micron size bubbles. The sub-micron size bubbles of oxidizing gas are immediately cleaved from the exterior surface of the sintered tube by the flow of the diesel fuel over the exterior surface of the sintered/porous tube 32. The sub-micron sized bubbles are dispersed throughout the flowing diesel fuel whereby the sulfur compounds initially contained within the flowing diesel fuel are immediately oxidized into sulfoxides and/or sulfones. The sub-micron size of the bubbles of the oxidizing gas greatly increases the size of the interface between the oxidizing gas and the initially contaminated liquid, thereby greatly increasing the efficiency of the oxidation reaction.
  • Treated diesel fuel is recovered through the [0030] outlet 54. It is contemplated that all of the oxidizing gas will be consumed by the oxidizing reaction. If not, excess oxidizing gas may be recovered from the treated liquid through an outlet 56 and thereafter properly disposed of. The diesel fuel flows into an apparatus 58 wherein the sulfoxides and/or sulfones formed by the oxidation reaction are removed by distillation or extraction. The treated diesel fuel is recovered at outlet 59.
  • In the operation of the [0031] apparatus 30 shown in FIG. 4, the exterior surface of the tube 32 is rotated relative to the diesel fuel flowing through the tank 34 under the action of the motor 36. By this means the relative movement between the exterior surface of the tube 32 and the diesel fuel flowing through the tank 34 is greatly increased. This in turn increases the number of sub-micron sized bubbles of oxidizing gas which is dispersed into the flowing liquid, thereby increasing the efficiency of the oxidation reaction.
  • An [0032] alternative apparatus 60 which may be utilized in the practice of the method of the invention is illustrated in FIG. 4. The apparatus 60 includes a sintered glass, sintered ceramic, or porous ceramic tube 62 having a hollow interior which is supported within a tank 64 for rotation about its longitudinal axis. One or more turbines 66 are mounted on the sintered/porous tube 62 to effect rotation thereof relative to the tank 64.
  • In the operation of the [0033] apparatus 60 an oxidizing gas is manufactured within a source 76 utilizing conventional and well known techniques. The oxidizing gas is preferably ozone, however, other oxidizing gases may be utilized in the practice of the invention. Immediately upon its manufacture the oxidizing gas is directed into the interior of the sintered or porous tube 62.
  • Diesel fuel as received from a [0034] source 80. The source 80 may comprise a conventional reservoir or tank which receives the diesel fuel from one or more sources.
  • Diesel fuel continuously flows from the [0035] source 80 through piping 82 and through the tank 64 to an outlet 84. The pressure of the oxidizing gas within the hollow interior of the tube 62 is maintained sufficiently high that diesel fuel flowing through the tank 64 does not flow inwardly through the tube 62 into the interior thereof. Rather, oxidizing gas from the source 76 flows outwardly from the interior of the tube 62 to the outer surface thereof.
  • The outwardly flowing oxidizing gas accumulates on the exterior surface of the sintered/[0036] porous tube 62 in the form of sub-micron size bubbles. The sub-micron size bubbles of oxidizing gas are immediately cleaved from the exterior surface of the sintered tube by the flow of the diesel fuel over the exterior surface of the tube 62. The sub-micron sized bubbles are dispersed throughout the flowing diesel fuel whereby the sulfur compounds initially contained within the flowing diesel fuel are immediately oxidized into sulfoxides and/or sulfones. The sub-micron size of the bubbles of the oxidizing gas greatly increases the size of the interface between the oxidizing gas and the initially contaminated liquid, thereby greatly increasing the efficiency of the oxidation reaction.
  • Treated diesel fuel is recovered through the [0037] outlet 84. It is contemplated that all of the oxidizing gas will be consumed by the oxidizing reaction. If not, excess oxidizing gas may be recovered from the treated liquid through an outlet 86 and thereafter properly disposed of. The diesel fuel flows into an apparatus 88 wherein the sulfoxides and/or sulfones formed by the oxidation reaction are removed by distillation or extraction. The treated diesel fuel is recovered at outlet 90.
  • In the operation of the [0038] apparatus 60 shown in FIG. 5 the exterior surface of the sintered/porous tube 62 is rotated relative to the fuel flowing through the tank 64 under the action of the turbines 66. By this means the relative movement between the exterior surface of the sintered tube 62 and the diesel fuel flowing through the tank 64 is greatly increased. This in turn increases the number of sub-micron sized bubbles of oxidizing gas which are dispersed into the flowing diesel fuel, thereby increasing the efficiency of the oxidation reaction.
  • Those skilled in the art will appreciate the fact that the use of the [0039] apparatus 30 shown in FIG. 3 or the apparatus 60 shown in FIG. 4 provides certain advantages with respect to the use of the apparatus shown in FIG. 2 in the practice of method of the invention. When the apparatus 30 of FIG. 3 is utilized, the relative movement between the exterior surface of the sintered/porous tube 32 and the diesel fuel flowing through the tank 34 depends upon the operation of the motor 36 rather than the flow rate of the liquid. This allows a greater number of sub-micron size bubbles of oxidizing gas to be dispersed into the diesel fuel than would be possible if the cleaving of sub-microns sized bubbles of oxidizing gas from the exterior surface of the tube 32 depended upon the flow of fuel alone. In this manner the efficiency of the oxidation reaction can be further increased.
  • When the [0040] apparatus 60 of FIG. 4 is utilized, the relative movement between the exterior surface of the sintered/porous tube 62 and the diesel fuel flowing through the tank 34 is greatly increased by the operation of the turbines 66. This allows a greater number of sub-micron size bubbles of oxidizing gas to be dispersed into the diesel fuel than would be possible if the cleaving of sub-microns sized bubbles of oxidizing gas from the exterior surface of the tube 62 depended upon the flow of fuel alone. In this manner the efficiency of the oxidation reaction can be further increased.
  • Referring now to FIGS. 5 and 6, there is shown a method of and apparatus for improving the quality of [0041] diesel fuel 100 comprising a second embodiment of the invention. In accordance with a second embodiment of the invention, there is provided a tank 102 having a quantity of diesel fuel 104 contained therein. The diesel fuel is supplied to the tank 102 from a source 106 through piping 107.
  • A [0042] hollow disk 108 is mounted in the lower portion of the tank 102. As is best shown in FIG. 6, the disk 108 includes a gas permeable partition 110 supported on a tube 112 for rotation within the tank 102 under the operation under the motor 114. The partition 110 may comprise sintered glass, sintered ceramic, or porous ceramic materials depending upon the requirements of particular applications of the invention. Oxidizing gas received from a supply 116 is directed through piping 118 and a suitable commutator 120 into the tube 112 and through the tube 112 into the interior of the hollow disk 108. The tube 112 has a hollow interior 121 and the disk 108 has a hollow interior 122 connected in fluid communication therewith.
  • The [0043] disk 108 is supplied with oxidizing gas at a pressure just high enough to overcome the head pressure of the water or other liquid 104. The disk 108 is rotated by the motor 114 at an appropriate speed in contact with the diesel fuel 104 such that a shearing phenomen occurs at the surface of the gas permeable partition 110 thus producing bubbles of extremely small, i.e., sub-micron, size. The extreme small size of the bubbles thus produced results in a surface area to volume ratio of small bubbles which significantly improves the efficiency of the oxidation reaction, in particular because the required vertical height of the tank 102 and therefore the pressure of the gas is substantially reduced due to the slower movement of the small bubbles in the liquid. The oxidizing gas reacts with sulfur compounds in the diesel fuel to form sulfoxides and/or sulfones. Diesel fuel is recovered from the tank 102 through outlet 123 and any residual gas is recovered from the tank 102 through outlet 124. The diesel fuel is directed to an apparatus 126 wherein the sulfoxides and/or sulfones formed duration the oxidation reaction are removed either by distillation or by extraction. The treated diesel fuel is recovered at outlet 128.
  • The method of improving the quality of diesel fuel comprised in the present invention may be used either as the sole process for treating diesel fuel or in combination with existing hydrotreating techniques. The method of the present invention totally removes sulfur compounds from diesel fuel, thereby improving the cetane rating of the diesel fuel. In particular, when the method of the present invention is used subsequently to hydrotreating, the aromatic compounds which remain after the hydrotreating process are removed thereby increasing the cetane rating of the diesel fuel. [0044]
  • Although preferred embodiments of the invention have been illustrated in the accompanying Drawings and described in the foregoing Detailed Description, it will be understood that the invention is not limited to the embodiments disclosed, but is capable of numerous rearrangements, modifications, and substitutions of parts and elements without departing from the spirit of the invention. [0045]

Claims (5)

I claim:
1. A method of removing sulfur compounds from diesel fuel comprising the steps of:
providing an oxidizing gas;
forming the oxidizing gas into sub-micron size bubbles;
providing a flow of diesel fuel;
dispersing the sub-micron size bubbles of oxidizing gas into the flowing diesel fuel thereby oxidizing the sulfur compounds initially contained within the diesel fuel into sulfoxides and/or sulfones;
removing the sulfoxides and sulfones from the diesel fuel; and
recovering the treated diesel fuel.
2. The method of
claim 1
 wherein the oxidizing gas is ozone.
3. The method of
claim 2
 wherein at least part of the oxidizing gas is formed into sub-micron size bubbles and dispersed into the flowing diesel fuel immediately upon its manufacture.
4. The method according to
claim 1
 wherein:
the oxidizing gas is directed through sintered material to an exterior surface; and
the flowing diesel fuel is directed across the exterior surface thereby cleaving sub-micron sized bubbles of oxidizing gas from the exterior surface.
5. The method according to
claim 4
 including the additional step of moving the exterior surface relative to the flowing diesel fuel.
US09/735,565 1999-06-03 2000-12-12 Method of improving the quality of diesel fuel Abandoned US20010015339A1 (en)

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US09/735,565 US20010015339A1 (en) 1999-06-03 2000-12-12 Method of improving the quality of diesel fuel
US10/082,853 US6596177B2 (en) 1999-06-03 2002-02-25 Method of improving the quality of diesel fuel

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US09/325,503 US6103130A (en) 1999-06-03 1999-06-03 Treatment of contaminated liquids with oxidizing gases
US09/418,445 US6251289B1 (en) 1999-06-03 1999-10-15 Treatment of contaminated liquids with oxidizing gases and liquids
US09/735,565 US20010015339A1 (en) 1999-06-03 2000-12-12 Method of improving the quality of diesel fuel

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US10/082,853 Continuation US6596177B2 (en) 1999-06-03 2002-02-25 Method of improving the quality of diesel fuel

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US09/619,009 Expired - Fee Related US6444131B1 (en) 1999-06-03 2000-07-19 Treatment of contaminated liquids with oxidizing gases and liquids
US09/735,565 Abandoned US20010015339A1 (en) 1999-06-03 2000-12-12 Method of improving the quality of diesel fuel
US09/767,287 Expired - Fee Related US6383399B2 (en) 1999-06-03 2001-01-22 Treatment of contaminated liquids with oxidizing gases and liquids
US10/082,853 Expired - Fee Related US6596177B2 (en) 1999-06-03 2002-02-25 Method of improving the quality of diesel fuel

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US6251289B1 (en) 2001-06-26
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US6383399B2 (en) 2002-05-07
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