WO2009135319A1 - Methods for treating odors - Google Patents
Methods for treating odors Download PDFInfo
- Publication number
- WO2009135319A1 WO2009135319A1 PCT/CA2009/000641 CA2009000641W WO2009135319A1 WO 2009135319 A1 WO2009135319 A1 WO 2009135319A1 CA 2009000641 W CA2009000641 W CA 2009000641W WO 2009135319 A1 WO2009135319 A1 WO 2009135319A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- oxidizing composition
- aqueous oxidizing
- fluid
- acidic aqueous
- basic aqueous
- Prior art date
Links
- 238000000034 method Methods 0.000 title claims abstract description 130
- 235000019645 odor Nutrition 0.000 title description 37
- 239000000203 mixture Substances 0.000 claims abstract description 205
- 230000001590 oxidative effect Effects 0.000 claims abstract description 153
- 239000012530 fluid Substances 0.000 claims abstract description 120
- 230000002378 acidificating effect Effects 0.000 claims abstract description 88
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims abstract description 46
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 30
- 230000005855 radiation Effects 0.000 claims abstract description 16
- 150000001875 compounds Chemical class 0.000 claims description 32
- 238000011282 treatment Methods 0.000 claims description 32
- 150000001768 cations Chemical class 0.000 claims description 21
- 229910052751 metal Inorganic materials 0.000 claims description 21
- 239000002184 metal Substances 0.000 claims description 21
- 239000003352 sequestering agent Substances 0.000 claims description 21
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 18
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 claims description 15
- 229910052742 iron Inorganic materials 0.000 claims description 12
- 229910052684 Cerium Inorganic materials 0.000 claims description 11
- 229910052802 copper Inorganic materials 0.000 claims description 11
- 229910052748 manganese Inorganic materials 0.000 claims description 11
- 229910052750 molybdenum Inorganic materials 0.000 claims description 11
- 229910052759 nickel Inorganic materials 0.000 claims description 11
- 229910052763 palladium Inorganic materials 0.000 claims description 11
- 229910052719 titanium Inorganic materials 0.000 claims description 11
- 229910052725 zinc Inorganic materials 0.000 claims description 11
- 229910052804 chromium Inorganic materials 0.000 claims description 10
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 claims description 8
- QPCDCPDFJACHGM-UHFFFAOYSA-N N,N-bis{2-[bis(carboxymethyl)amino]ethyl}glycine Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(=O)O)CCN(CC(O)=O)CC(O)=O QPCDCPDFJACHGM-UHFFFAOYSA-N 0.000 claims description 6
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 claims description 6
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 claims description 6
- 229960003330 pentetic acid Drugs 0.000 claims description 6
- 239000002253 acid Substances 0.000 claims description 5
- 150000001412 amines Chemical class 0.000 claims description 5
- 150000002019 disulfides Chemical class 0.000 claims description 5
- 235000006408 oxalic acid Nutrition 0.000 claims description 5
- 150000003568 thioethers Chemical class 0.000 claims description 5
- DHMQDGOQFOQNFH-UHFFFAOYSA-N Glycine Chemical compound NCC(O)=O DHMQDGOQFOQNFH-UHFFFAOYSA-N 0.000 claims description 4
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 4
- UIIMBOGNXHQVGW-UHFFFAOYSA-M Sodium bicarbonate Chemical compound [Na+].OC([O-])=O UIIMBOGNXHQVGW-UHFFFAOYSA-M 0.000 claims description 4
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 4
- 150000001298 alcohols Chemical class 0.000 claims description 4
- 150000001299 aldehydes Chemical class 0.000 claims description 4
- 150000001408 amides Chemical class 0.000 claims description 4
- 150000001735 carboxylic acids Chemical class 0.000 claims description 4
- 239000007788 liquid Substances 0.000 claims description 4
- 150000002894 organic compounds Chemical class 0.000 claims description 4
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 claims description 4
- YGSDEFSMJLZEOE-UHFFFAOYSA-N salicylic acid Chemical compound OC(=O)C1=CC=CC=C1O YGSDEFSMJLZEOE-UHFFFAOYSA-N 0.000 claims description 4
- 150000003573 thiols Chemical class 0.000 claims description 4
- 238000012546 transfer Methods 0.000 claims description 4
- -1 NTA Chemical compound 0.000 claims description 3
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 3
- 229910017604 nitric acid Inorganic materials 0.000 claims description 3
- WXHLLJAMBQLULT-UHFFFAOYSA-N 2-[[6-[4-(2-hydroxyethyl)piperazin-1-yl]-2-methylpyrimidin-4-yl]amino]-n-(2-methyl-6-sulfanylphenyl)-1,3-thiazole-5-carboxamide;hydrate Chemical compound O.C=1C(N2CCN(CCO)CC2)=NC(C)=NC=1NC(S1)=NC=C1C(=O)NC1=C(C)C=CC=C1S WXHLLJAMBQLULT-UHFFFAOYSA-N 0.000 claims description 2
- XMIIGOLPHOKFCH-UHFFFAOYSA-N 3-phenylpropionic acid Chemical compound OC(=O)CCC1=CC=CC=C1 XMIIGOLPHOKFCH-UHFFFAOYSA-N 0.000 claims description 2
- 239000004471 Glycine Substances 0.000 claims description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 2
- 239000000920 calcium hydroxide Substances 0.000 claims description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 2
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 claims description 2
- 239000000347 magnesium hydroxide Substances 0.000 claims description 2
- 229910001862 magnesium hydroxide Inorganic materials 0.000 claims description 2
- FJKROLUGYXJWQN-UHFFFAOYSA-N papa-hydroxy-benzoic acid Natural products OC(=O)C1=CC=C(O)C=C1 FJKROLUGYXJWQN-UHFFFAOYSA-N 0.000 claims description 2
- 239000011736 potassium bicarbonate Substances 0.000 claims description 2
- 229910000028 potassium bicarbonate Inorganic materials 0.000 claims description 2
- 229910000027 potassium carbonate Inorganic materials 0.000 claims description 2
- TYJJADVDDVDEDZ-UHFFFAOYSA-M potassium hydrogencarbonate Chemical compound [K+].OC([O-])=O TYJJADVDDVDEDZ-UHFFFAOYSA-M 0.000 claims description 2
- 229960004889 salicylic acid Drugs 0.000 claims description 2
- 229910000030 sodium bicarbonate Inorganic materials 0.000 claims description 2
- 229910000029 sodium carbonate Inorganic materials 0.000 claims description 2
- 239000001509 sodium citrate Substances 0.000 claims description 2
- NLJMYIDDQXHKNR-UHFFFAOYSA-K sodium citrate Chemical compound O.O.[Na+].[Na+].[Na+].[O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O NLJMYIDDQXHKNR-UHFFFAOYSA-K 0.000 claims description 2
- GCLGEJMYGQKIIW-UHFFFAOYSA-H sodium hexametaphosphate Chemical compound [Na]OP1(=O)OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])O1 GCLGEJMYGQKIIW-UHFFFAOYSA-H 0.000 claims description 2
- 235000019982 sodium hexametaphosphate Nutrition 0.000 claims description 2
- 239000001577 tetrasodium phosphonato phosphate Substances 0.000 claims description 2
- 239000007789 gas Substances 0.000 description 24
- 230000003647 oxidation Effects 0.000 description 7
- 238000007254 oxidation reaction Methods 0.000 description 7
- 238000010586 diagram Methods 0.000 description 6
- 238000012360 testing method Methods 0.000 description 6
- 238000005516 engineering process Methods 0.000 description 5
- 238000010521 absorption reaction Methods 0.000 description 4
- 239000002738 chelating agent Substances 0.000 description 3
- 238000005259 measurement Methods 0.000 description 3
- FERIUCNNQQJTOY-UHFFFAOYSA-N Butyric acid Chemical compound CCCC(O)=O FERIUCNNQQJTOY-UHFFFAOYSA-N 0.000 description 2
- 239000003570 air Substances 0.000 description 2
- 238000010790 dilution Methods 0.000 description 2
- 239000012895 dilution Substances 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- NQPDZGIKBAWPEJ-UHFFFAOYSA-N valeric acid Chemical compound CCCCC(O)=O NQPDZGIKBAWPEJ-UHFFFAOYSA-N 0.000 description 2
- NWUYHJFMYQTDRP-UHFFFAOYSA-N 1,2-bis(ethenyl)benzene;1-ethenyl-2-ethylbenzene;styrene Chemical compound C=CC1=CC=CC=C1.CCC1=CC=CC=C1C=C.C=CC1=CC=CC=C1C=C NWUYHJFMYQTDRP-UHFFFAOYSA-N 0.000 description 1
- 239000012080 ambient air Substances 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 239000003456 ion exchange resin Substances 0.000 description 1
- 229920003303 ion-exchange polymer Polymers 0.000 description 1
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 description 1
- 229910000359 iron(II) sulfate Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 235000011149 sulphuric acid Nutrition 0.000 description 1
- 229940005605 valeric acid Drugs 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Classifications
-
- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
- A61L9/00—Disinfection, sterilisation or deodorisation of air
- A61L9/16—Disinfection, sterilisation or deodorisation of air using physical phenomena
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/77—Liquid phase processes
- B01D53/78—Liquid phase processes with gas-liquid contact
-
- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
- A61L9/00—Disinfection, sterilisation or deodorisation of air
-
- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
- A61L9/00—Disinfection, sterilisation or deodorisation of air
- A61L9/14—Disinfection, sterilisation or deodorisation of air using sprayed or atomised substances including air-liquid contact processes
- A61L9/145—Disinfection, sterilisation or deodorisation of air using sprayed or atomised substances including air-liquid contact processes air-liquid contact processes, e.g. scrubbing
-
- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
- A61L9/00—Disinfection, sterilisation or deodorisation of air
- A61L9/16—Disinfection, sterilisation or deodorisation of air using physical phenomena
- A61L9/18—Radiation
- A61L9/20—Ultraviolet radiation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
- B01D53/04—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/38—Removing components of undefined structure
- B01D53/44—Organic components
-
- 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
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/10—Oxidants
- B01D2251/106—Peroxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/30—Alkali metal compounds
- B01D2251/304—Alkali metal compounds of sodium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/60—Inorganic bases or salts
- B01D2251/604—Hydroxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/70—Organic acids
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/90—Chelants
- B01D2251/902—EDTA
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
- B01D2253/102—Carbon
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/90—Odorous compounds not provided for in groups B01D2257/00 - B01D2257/708
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/06—Polluted 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- 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
- C02F1/68—Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water
- C02F1/683—Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water by addition of complex-forming compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/02—Odour removal or prevention of malodour
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/18—Removal of treatment agents after treatment
Definitions
- the present document relates to the field of odor treatment. More particularly it relates to methods for treating odors. For example, odors present in a fluid can be treated by using such methods.
- Each of the chemical compounds has different characteristics with regard to its solubility in water or another solvent, its olfactory threshold and its partial pressure which ensure that the technologies currently used are limited whether this is as regards the effectiveness of the treatment or else the lifetime of the materials used.
- a method for method for treating a fluid having an undesirable odor comprising : contacting the fluid with a basic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr 1 Ce, Zn, Pd, Mo, and mixtures thereof and H2O 2 ; and contacting the fluid with an acidic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O 2 ,
- the fluid can be contacted with the basic aqueous oxidizing composition, and then the fluid can be contacted with the acidic aqueous oxidizing composition, or the fluid can be contacted with the acidic aqueous oxidizing composition, and then the fluid can be contacted with the basic aqueous oxidizing composition.
- the method can optionally further comprise contacting the fluid with activated carbon.
- a method for treating a fluid having an undesirable odor comprising:
- a basic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H 2 O 2 ; and/or contacting the fluid with an acidic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H 2 O2; and contacting the fluid with activated carbon.
- the fluid can be contacted with the basic aqueous oxidizing composition, and then the fluid can be contacted with the acidic aqueous oxidizing composition, or the fluid can be contacted with the acidic aqueous oxidizing composition, and then the fluid can be contacted with the basicaqueous oxidizing composition.
- a method for treating a fluid having an undesirable odor comprising : contacting the fluid with an acidic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2
- the fluid can optionally be further contacted with a basic aqueous oxidizing composition and/or with activated carbon.
- the fluid can comprise at least one organic compound chosen from carboxylic acids, thiols, thioethers, disulfides, alcohols, aldehydes, amines, amides and mixtures thereof.
- the carboxylic acids can comprise C1-C2 0 carboxylic acids.
- the thiols can comprise C1-C2 0 thiols.
- the thioethers can comprise C2-C20 thioethers.
- the disulfides can comprise C2-C2 0 disulfides.
- the alcohols can comprise C1-C2 0 alcohols.
- the aldehydes can comprise C1-C20 aldehydes.
- the amines can comprise C1-C20 amines.
- the amides can comprise C1-C20 amides.
- the fluid can be passed through a bed of activated carbon.
- a treatment can be carried out before or after a treatment with a basic or acidic oxidizing composition.
- the fluid can be treated with the basic aqueous oxidizing composition and then with the acidic aqueous oxidizing composition.
- the fluid can be treated with the acidic aqueous oxidizing composition and then with the basic aqueous oxidizing composition.
- the fluid can be treated with the basic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor and then the fluid can be treated with the acidic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor, thereby at least partially reducing intensity of the undesirable odor.
- the fluid can be treated with the acidic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor and then the fluid is treated with the basic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor, thereby at least partially reducing intensity of the undesirable odor.
- the methods can further comprise submitting the fluid and the acidic aqueous oxidizing composition to UV radiation, when the fluid and the acidic aqueous oxidizing composition are contacting each other.
- the method can also further comprise submitting the fluid and the basic aqueous oxidizing composition to UV radiation, when the fluid and the basic aqueous oxidizing composition are contacting each other.
- the fluid can be contacted with the acidic aqueous oxidizing composition so as to at least partially dissolve at least one compound responsible for the undesirable odor and contained in the fluid into the acidic aqueous oxidizing composition and wherein the method can further comprise submitting, the at least one compound that is at least partially dissolved into the acidic aqueous oxidizing composition, to UV radiation.
- the fluid can be contacted with the basic aqueous oxidizing composition so as to at least partially dissolve at least one compound responsible for the undesirable odor and contained in the fluid into the basic aqueous oxidizing composition and wherein the method can further comprise submitting, the at least one compound that is at least partially dissolved into the basic aqueous oxidizing composition, to UV radiation.
- the fluid can be contacted with the acidic aqueous oxidizing composition so as to at least partially dissolve at least one compound responsible for the undesirable odor and contained in the fluid into the acidic aqueous oxidizing composition and the at least one compound that is at least partially dissolved into the acidic aqueous oxidizing composition can be submitted to UV radiation so as to at least partially oxidize the at least one compound and at least partially reduce intensity of the undesirable odor.
- the fluid can be treated with the basic aqueous oxidizing composition and/or with the acidic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor and then the fluid can be passed through a bed of activated carbon, thereby at least partially reducing intensity of the undesirable odor.
- the basic and/or acidic composition can comprise a cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof.
- the metal can be Fe, or Cu.
- the composition can comprise a cation of Fe.
- the cations can be chosen from Fe 2+ , Cu 2+ , Ni 2+ , Mn 2+ , Ti 4+ , Cr 3+ , Ce 3+ , Zn 2+ , Pd 2+ , Mo 6+ , and mixtures thereof.
- the cation can be Fe 2+ , or Cu 2+ .
- the cation can be Fe 2+ .
- the sequestering agent when oxidation occurs in a basic aqueous composition, can be chosen from diethylenetriaminepentaacetic acid (DTPA), nitrolotriacetic acid (NTA), ethylenediaminetetraacetic acid (EDTA), sodium hexametaphosphate, sodium citrate, and mixtures thereof.
- DTPA diethylenetriaminepentaacetic acid
- NTA nitrolotriacetic acid
- EDTA ethylenediaminetetraacetic acid
- sodium hexametaphosphate sodium citrate
- the sequestering agent can be DTPA or NTA.
- the sequestering agent can be an ion exchange resin such as zeolites.
- the sequestering agent can be NTA and the cation can be Fe 2+ .
- the sequestering agent when oxidation occurs in an acidic aqueous composition, can be chosen from ethylenediaminetetraacetic acid (EDTA), oxalic acid, citric acid, glycine, NTA, salicylic acid, sulfosalicylic acid, trithylenetetramine, and mixtures thereof.
- EDTA ethylenediaminetetraacetic acid
- oxalic acid citric acid
- glycine NTA
- salicylic acid sulfosalicylic acid
- trithylenetetramine trithylenetetramine
- the sequestering agent can be present at a concentration of at least 30 mg/L, about 30 mg/L to about 480 mg/L or about 60 mg/L to about 240 mg/L
- contacting can include mixing the fluid with the basic oxidizing composition so as to at least partially dissolve at least one compound contained in the fluid into the basic oxidizing composition.
- the fluid and the basic oxidizing composition can be mixed together in a packed column.
- the fluid can be introduced at a bottom portion of the column and the basic aqueous composition can be introduced at a top portion of the column.
- the fluid and the basic aqueous composition can be mixed together into the column over a predetermined amount of transfer units.
- the fluid, before contacting the basic aqueous oxidizing composition can be at a temperature of about 1O 0 C to about 85 0 C, about 25°C to about 55°C, or about 15°C to about 40°C.
- the metal cation can be present in the basic composition at a concentration of at least 1 mg/mL, at least 5 mg/mL, or at least 20 mg/mL. about 1 mg/L to about 20 mg/L or about 2 mg/L to about 10 mg/L.
- the concentration of H 2 O 2 in the basic composition can be at least 20 mg/L, about 20 mg/L to about 2000 mg/L, or about 50 mg/L to about 700 mg/L.
- the basic aqueous oxidizing composition can comprise a base chosen from NaOH, KOH, Mg(OH) 2 , Ca(OH) 2 , NaHCO 3 , Na 2 CO 3 , K 2 CO 3 , KHCO 3 , and mixtures thereof.
- the basic composition can have a pH of at least 9.0.
- the pH can be of about 9.3 to about 11.5, about 9.5 to about 10.5, about 9.7 to about 10.0, or about 9.8.
- contacting can include mixing the fluid with the acidic oxidizing composition so as to at least partially dissolve at least one compound contained in the fluid into the acidic oxidizing composition.
- the fluid and the acidic oxidizing composition can be mixed together in a packed column.
- the fluid can be introduced at a bottom portion of the column and the acidic aqueous composition can be introduced at a top portion of the column.
- the fluid and the acidic aqueous composition can be mixed together into the column over a predetermined amount of transfer units.
- the acidic aqueous oxidizing composition can comprise an acid chosen from H2SO4, HCI, HNO 3 , H 3 PO4, and mixtures thereof.
- the acidic aqueous oxidizing composition can have a pH of at least 1.5, about 1.5 to about 4.0, about 2.0 to about 3.0, or about 2.2 to about 2.6.
- the metal cation can be present in the acidic aqueous oxidizing composition at a concentration of at least 5 mg/L, at least 10 mg/L, or at least 20 mg/L.
- the concentration can also be about 10 mg/L to about 200 mg/L, about 20 mg/L to about 100 mg/L, about 50 to 150 mg/L, or about 30 mg/L to about 50 mg/L.
- a cation can be Fe 2+ , Cu 2+ or a mixture thereof.
- the concentration of H 2 O 2 in the acidic composition can be at least 100 mg/L, about 100 mg/L to about 3500 mg/L, or about 1000 mg/L to about 2500 mg/L.
- H 2 O 2 can be present in the acidic aqueous oxidizing composition at a molar ratio H 2 O 2 : metal of at least 5:1 , at least 10:1 , or at least 20:1.
- H 2 O 2 can be present in the acidic aqueous oxidizing composition at a molar ratio H 2 O 2 : metal of about 10:1 to about 100:1 , or 12:1 to 40:1.
- the fluid, before contacting the acidic aqueous oxidizing composition can be at a temperature of about 10 0 C to about 85 0 C or about 15°C to about 4O 0 C.
- the treatment can permit to reduce by at least 50 %, by at least 60 %, by at least 70 %, by at least 75 %, by at least 80 %, by at least 85 %, by at least 90 %, by at least 95 %, by at least 97 %, by at least 98 %, of about 50 % to about 99 %, of about 60 % to about 99 %, of about 70 % to about 97 %, or of about 70 % to about 99 % the intensity of the at least one indesirable odor.
- sequestering agent includes chemical moieties that bind to, or complex with, any cation or anion.
- sequestering agents or chelators are well known in the art.
- the sequestering agent can bind to a metal cation.
- packed column refers to an absorption tower, in which the packing is used so as to increase contact between a gas and a liquid.
- a packed column can be used for removing a contaminant from a gas stream by absorbing it or dissolving it into a liquid (such as an oxidizing composition).
- fluid refers to a gas, a liquid or a mixture thereof.
- FIG. 1 shows a bloc diagram of an example of a method for treating a fluid
- FIG. 2 shows a bloc diagram of another example of a method for treating a fluid
- FIG. 3 shows a bloc diagram of a further example of a method for treating a fluid.
- the olfactometer is composed of six beakers in which three test specimens are found. Each beaker corresponds to a different dilution level of the odorous gas. In each of these beakers, a single test specimen diffuses odorous air. Each of the individuals that make up the panel must identify, in each beaker, which of the test specimens diffuses the odorous gas. If the individual does not detect any odors, the person passes to the next beaker. The data from the panel are compiled and the results are calculated with the aid of a table by using the air dilution and odorous gas flow rates of each of the test specimens.
- Example 1 treatment by oxidation and absorption in consecutive basic and acidic media
- the gas to be treated contains several organic compounds which, depending on their nature, are more soluble in a basic medium or in an acidic medium.
- compounds such as butyric acid, valeric acid, sulfides and disulfides were found to be compounds that are more soluble in a basic media and certain amines were found to be more soluble in an acidic media.
- Fig. 1 is a bloc diagram concerning the method carried out in Example 1.
- the gas was treated by passing it through a packed column in which a basic aqueous oxidizing composition (comprising H 2 O 2 and NaOH and having a pH of about 10.0) was flowing.
- the oxidizing composition contained about 510 mg/L of hydrogen peroxide, about 4 mg/L of Fe and NTA at a concentration of four times higher than the concentration of Fe on a molar basis.
- the temperature of the medium was about 22 0 C.
- the gas flow rate was about 3000 m 3 /h.
- Fe can be provided in various form such as FeSO 4 , FeCI 2 or any suitable source of Fe 2+ .
- a reactor was disposed at the bottom of the column, and the oxidizing composition was recirculated from the reactor to a top portion of the column by means of a pump. The fluid was introduced at a bottom portion of the column in a counter-current manner.
- the gas is treated in a second packed column that also comprises an oxidizing composition comprising hydrogen peroxide.
- the composition flowing in the second column was an acidic aqueous oxidizing composition (H 2 SO 4 ) having a pH of about 2.2.
- the oxidizing composition contained about 2360 mg/L of hydrogen peroxide, and about 50 mg/L of Fe.
- the temperature of the medium was about 23°C.
- the gas flow rate was about 3.6 m 3 /h.
- Example 2 treatment by oxidation and absorption in a basic medium and adsorption onto activated carbon.
- a gas similar to the one treated in example 1 was treated by using a similar set-up.
- Fig. 2 is a bloc diagram concerning the method carried out in Example 2.
- the gas was treated by passing it through a packed column in which a basic aqueous oxidizing composition (comprising H 2 O 2 and NaOH and having a pH of about 9.8) was flowing.
- the oxidizing composition contained about 75 mg/L of hydrogen peroxide, about 2 mg/L of Fe and NTA at a concentration of four times higher than the concentration of Fe on a molar basis.
- the temperature of the medium was about 21 0 C.
- the gas flow rate was about 2040 m 3 /h.
- the gas was treated by passing it through a bed of activated carbon.
- the temperature of the gas was about 24°C at a gas flow rate of about 3 m 3 /h.
- the height of the activated carbon was about 180 mm.
- Example 3 Treatment by oxidation and absorption in a basic media and then, in an acidic media in which oxidation is enhanced by UV radiation.
- a gas similar to the one in example 1 was treated by using a similar set-up.
- Fig. 3 is a bloc diagram concerning the method carried out in example 3.
- the gas was treated by passing it through a packed column in which a basic aqueous oxidizing composition (comprising H2O 2 and NaOH and having a pH of about 9.8) was flowing.
- the oxidizing composition contained about 300 mg/L of hydrogen peroxide, about 2 mg/L of Fe and NTA at a concentration of four times higher than the concentration of Fe on a molar basis.
- the temperature of the medium was about 22 0 C.
- the gas was at a temperature of about 50 0 C and a flow of 80 L/min.
- the gas was treated in a second packed column that also contained an oxidizing composition comprising hydrogen peroxide.
- the composition flowing in the second column was an acidic aqueous oxidizing composition (HNO 3 ) having a pH of about 2.4.
- the oxidizing composition contained about 350 mg/L of hydrogen peroxide, about 30 mg/L of Fe and oxalic acid at was concentration of four times higher than the concentration of Fe on a molar basis.
- the temperature of the medium was about 22 0 C.
- the gas flow was about 80 L/min.
- Example 3 the mixture of the fluid and the composition in the reactor were submitted to UV radiation in order to enhance the oxidation rate of the organic compounds that cause the unpleasant and/or undesirable odor.
- the UV radiation was produced by a 254 nm lamp at a power of 9 Watts. After a predetermined residence time in the reactor, the mixture is recirculated to the top of the packed column to complete the loop.
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Abstract
There are provided methods for treating a fluid having an undesirable odor. The methods comprise contacting the fluid with a H2O2 basic aqueous oxidizing composition and/or with a H2O2 acidic aqueous oxidizing composition. Optionally, the fluid can be further treated by contacting it with activated carbon and/or by submitting the fluid and the composition to UV radiation when they are contacting together.
Description
METHODS FOR TREATING ODORS
TECHNICAL FIELD
[0001] The present document relates to the field of odor treatment. More particularly it relates to methods for treating odors. For example, odors present in a fluid can be treated by using such methods.
BACKGROUND OF THE DISLCOSURE
[0002] Industrial activity has always generated odors in the ambient air which were and are still able to worry the neighborhood. Despite the implementation of tighter environmental regulations, this problem remains present even more so since, in certain locations, new commercial and residential sectors are developed in proximity to these sources.
[0003] The use of biofilters for reducing the odors has demonstrated its effectiveness. However, their installation requires large surface areas that are not always found on the industrial sites. The odorous gas emitters must then make do with technologies that are more compact and which have limitations due to the nature of the chemical compounds.
[0004] Each of the chemical compounds has different characteristics with regard to its solubility in water or another solvent, its olfactory threshold and its partial pressure which ensure that the technologies currently used are limited whether this is as regards the effectiveness of the treatment or else the lifetime of the materials used.
[0005] For such situations where a problem of space and of the use of compact technologies reaches limits, it would be highly desirable to be provided with an alternative technology.
SUMMARY OF THE DISCLOSURE
[0006] According to one aspect, there is provided a method for method for treating a fluid having an undesirable odor, the method comprising :
contacting the fluid with a basic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr1 Ce, Zn, Pd, Mo, and mixtures thereof and H2O2; and contacting the fluid with an acidic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2,
[0007] The fluid can be contacted with the basic aqueous oxidizing composition, and then the fluid can be contacted with the acidic aqueous oxidizing composition, or the fluid can be contacted with the acidic aqueous oxidizing composition, and then the fluid can be contacted with the basic aqueous oxidizing composition. The method can optionally further comprise contacting the fluid with activated carbon.
[0008] According to another aspect, there is provided a method for treating a fluid having an undesirable odor, the method comprising :
contacting the fluid with a basic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2; and/or contacting the fluid with an acidic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2; and contacting the fluid with activated carbon.
[0009] The fluid can be contacted with the basic aqueous oxidizing composition, and then the fluid can be contacted with the acidic aqueous oxidizing composition, or the fluid can be contacted with the acidic aqueous oxidizing composition, and then the fluid can be contacted with the basicaqueous oxidizing composition.
[0010] According to another aspect, there is provided a method for treating a fluid having an undesirable odor, the method comprising :
contacting the fluid with an acidic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2
submitting the fluid and the composition to an UV radiation.
[0011] The fluid can optionally be further contacted with a basic aqueous oxidizing composition and/or with activated carbon.
[0012] It was found that such methods are very effective for treating undesirable and/or unpleasant odors. Such technologies can be operated at low costs and represent a simple manner to treat fluids.
[0013] In the methods previously described, the fluid can comprise at least one organic compound chosen from carboxylic acids, thiols, thioethers, disulfides, alcohols, aldehydes, amines, amides and mixtures thereof. The carboxylic acids can comprise C1-C20 carboxylic acids. The thiols can comprise C1-C20 thiols. The thioethers can comprise C2-C20 thioethers. The disulfides can comprise C2-C20 disulfides. The alcohols can comprise C1-C20 alcohols. The aldehydes can comprise C1-C20 aldehydes. The amines can comprise C1-C20 amines. The amides can comprise C1-C20 amides.
[0014] In the methods previously described, the fluid can be passed through a bed of activated carbon. Such a treatment can be carried out before or after a treatment with a basic or acidic oxidizing composition.
[0015] The fluid can be treated with the basic aqueous oxidizing composition and then with the acidic aqueous oxidizing composition. Alternatively, the fluid can be treated with the acidic aqueous oxidizing composition and then with the basic aqueous oxidizing composition.
[0016] The fluid can be treated with the basic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor and then the fluid can be treated with the acidic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor, thereby at least partially reducing intensity of the undesirable odor.
[0017] The fluid can be treated with the acidic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor and then the fluid is treated with the basic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor, thereby at least partially reducing intensity of the undesirable odor.
[0018] The methods can further comprise submitting the fluid and the acidic aqueous oxidizing composition to UV radiation, when the fluid and the acidic aqueous oxidizing composition are contacting each other. The method can also further comprise submitting the fluid and the basic aqueous oxidizing composition to UV radiation, when the fluid and the basic aqueous oxidizing composition are contacting each other.
[0019] For example, the fluid can be contacted with the acidic aqueous oxidizing composition so as to at least partially dissolve at least one compound responsible for the undesirable odor and contained in the fluid into the acidic aqueous oxidizing composition and wherein the method can further comprise submitting, the at least one compound that is at least partially dissolved into the acidic aqueous oxidizing composition, to UV radiation.
[0020] For example, the fluid can be contacted with the basic aqueous oxidizing composition so as to at least partially dissolve at least one compound responsible for the undesirable odor and contained in the fluid into the basic aqueous oxidizing composition and wherein the method can further comprise submitting, the at least one compound that is at least partially dissolved into the basic aqueous oxidizing composition, to UV radiation.
[0021] The fluid can be contacted with the acidic aqueous oxidizing composition so as to at least partially dissolve at least one compound responsible for the undesirable odor and contained in the fluid into the acidic aqueous oxidizing composition and the at least one compound that is at least partially dissolved into the acidic aqueous oxidizing composition can be submitted to UV radiation so as to at least partially oxidize the at least one compound and at least partially reduce intensity of the undesirable odor.
[0022] The fluid can be treated with the basic aqueous oxidizing composition and/or with the acidic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for the undesirable odor and then the fluid can be passed through a bed of activated carbon, thereby at least partially reducing intensity of the undesirable odor.
[0023] In the methods previously described, the basic and/or acidic composition can comprise a cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof. For example, the metal can be Fe, or Cu. In another example, the composition can comprise a cation of Fe.
[0024] For example, the cations can be chosen from Fe2+, Cu2+ , Ni2+ , Mn2+ , Ti4+ , Cr3+ , Ce3+, Zn2+ , Pd2+ , Mo6+, and mixtures thereof. According to another example, the cation can be Fe2+, or Cu2+. According to another example, the cation can be Fe2+.
[0025] The sequestering agent (or chelator), when oxidation occurs in a basic aqueous composition, can be chosen from diethylenetriaminepentaacetic acid (DTPA), nitrolotriacetic acid (NTA), ethylenediaminetetraacetic acid (EDTA), sodium hexametaphosphate, sodium citrate, and mixtures thereof. For example, the sequestering agent can be DTPA or NTA. Alternatively, the sequestering agent can be an ion exchange resin such as zeolites. For example, the sequestering agent can be NTA and the cation can be Fe2+. The sequestering agent (or chelator), when oxidation occurs in an acidic aqueous composition, can be chosen from ethylenediaminetetraacetic acid (EDTA), oxalic acid, citric acid, glycine, NTA, salicylic acid, sulfosalicylic acid, trithylenetetramine, and mixtures thereof. For example, the sequestering agent can be oxalic acid.
[0026] For example, the sequestering agent can be present at a concentration of at least 30 mg/L, about 30 mg/L to about 480 mg/L or about 60 mg/L to about 240 mg/L
[0027] In the previously described methods, contacting can include mixing the fluid with the basic oxidizing composition so as to at least partially dissolve at least one compound contained in the fluid into the basic oxidizing
composition. The fluid and the basic oxidizing composition can be mixed together in a packed column. For example, the fluid can be introduced at a bottom portion of the column and the basic aqueous composition can be introduced at a top portion of the column. The fluid and the basic aqueous composition can be mixed together into the column over a predetermined amount of transfer units.
[0028] For example, the fluid, before contacting the basic aqueous oxidizing composition, can be at a temperature of about 1O0C to about 850C, about 25°C to about 55°C, or about 15°C to about 40°C.
[0029] For example, the metal cation can be present in the basic composition at a concentration of at least 1 mg/mL, at least 5 mg/mL, or at least 20 mg/mL. about 1 mg/L to about 20 mg/L or about 2 mg/L to about 10 mg/L.
[0030] For example, the concentration of H2O2 in the basic composition can be at least 20 mg/L, about 20 mg/L to about 2000 mg/L, or about 50 mg/L to about 700 mg/L.
[0031] The basic aqueous oxidizing composition can comprise a base chosen from NaOH, KOH, Mg(OH)2, Ca(OH)2, NaHCO3, Na2CO3, K2CO3, KHCO3, and mixtures thereof. The basic composition can have a pH of at least 9.0. For example, the pH can be of about 9.3 to about 11.5, about 9.5 to about 10.5, about 9.7 to about 10.0, or about 9.8.
[0032] In the previously described methods, contacting can include mixing the fluid with the acidic oxidizing composition so as to at least partially dissolve at least one compound contained in the fluid into the acidic oxidizing composition. The fluid and the acidic oxidizing composition can be mixed together in a packed column. For example, the fluid can be introduced at a bottom portion of the column and the acidic aqueous composition can be introduced at a top portion of the column. The fluid and the acidic aqueous composition can be mixed together into the column over a predetermined amount of transfer units.
[0033] The acidic aqueous oxidizing composition can comprise an acid chosen from H2SO4, HCI, HNO3, H3PO4, and mixtures thereof.
[0034] The acidic aqueous oxidizing composition can have a pH of at least 1.5, about 1.5 to about 4.0, about 2.0 to about 3.0, or about 2.2 to about 2.6.
[0035] The metal cation can be present in the acidic aqueous oxidizing composition at a concentration of at least 5 mg/L, at least 10 mg/L, or at least 20 mg/L. The concentration can also be about 10 mg/L to about 200 mg/L, about 20 mg/L to about 100 mg/L, about 50 to 150 mg/L, or about 30 mg/L to about 50 mg/L. For example such a cation can be Fe2+, Cu2+ or a mixture thereof.For example, the concentration of H2O2 in the acidic composition can be at least 100 mg/L, about 100 mg/L to about 3500 mg/L, or about 1000 mg/L to about 2500 mg/L.
[0036] For example, H2O2 can be present in the acidic aqueous oxidizing composition at a molar ratio H2O2 : metal of at least 5:1 , at least 10:1 , or at least 20:1.
[0037] For example, H2O2 can be present in the acidic aqueous oxidizing composition at a molar ratio H2O2 : metal of about 10:1 to about 100:1 , or 12:1 to 40:1.
[0038] For example, the fluid, before contacting the acidic aqueous oxidizing composition, can be at a temperature of about 100C to about 850C or about 15°C to about 4O0C.
[0039] In the methods previously defined, the treatment can permit to reduce by at least 50 %, by at least 60 %, by at least 70 %, by at least 75 %, by at least 80 %, by at least 85 %, by at least 90 %, by at least 95 %, by at least 97 %, by at least 98 %, of about 50 % to about 99 %, of about 60 % to about 99 %, of about 70 % to about 97 %, or of about 70 % to about 99 % the intensity of the at least one indesirable odor.
[0040] The expression "sequestering agent" as used herein includes chemical moieties that bind to, or complex with, any cation or anion.
Examples of sequestering agents or chelators are well known in the art. For example, the sequestering agent can bind to a metal cation.
[0041] The expression "packed column" as used herein refers to an absorption tower, in which the packing is used so as to increase contact between a gas and a liquid. For example, such a packed column can be used for removing a contaminant from a gas stream by absorbing it or dissolving it into a liquid (such as an oxidizing composition).
[0042] The term "fluid" as used herein refers to a gas, a liquid or a mixture thereof.
BRIEF DESCRIPTION OF DRAWINGS
[0043] The following drawings represent in a non-limitative manner, various examples:
[0044] Fig. 1 shows a bloc diagram of an example of a method for treating a fluid;
[0045] Fig. 2 shows a bloc diagram of another example of a method for treating a fluid; and
[0046] Fig. 3 shows a bloc diagram of a further example of a method for treating a fluid.
DETAILLED DESCRIPTION
[0047] Further features and advantages will become more readily apparent from the following non-limitative examples:
[0048] The following examples are non-limiting examples.
Examples
[0049] In order to determine the effectiveness of each of the treatments that are part of the examples, dynamic olfactometry measurements have been carried out. The olfactometer is composed of six beakers in which three test specimens are found. Each beaker corresponds to a different dilution level of the odorous gas. In each of these beakers, a single test specimen diffuses
odorous air. Each of the individuals that make up the panel must identify, in each beaker, which of the test specimens diffuses the odorous gas. If the individual does not detect any odors, the person passes to the next beaker. The data from the panel are compiled and the results are calculated with the aid of a table by using the air dilution and odorous gas flow rates of each of the test specimens.
Example 1 : treatment by oxidation and absorption in consecutive basic and acidic media
[0050] The gas to be treated contains several organic compounds which, depending on their nature, are more soluble in a basic medium or in an acidic medium. In the present examples, compounds such as butyric acid, valeric acid, sulfides and disulfides were found to be compounds that are more soluble in a basic media and certain amines were found to be more soluble in an acidic media. Fig. 1 is a bloc diagram concerning the method carried out in Example 1.
[0051] The gas was treated by passing it through a packed column in which a basic aqueous oxidizing composition (comprising H2O2 and NaOH and having a pH of about 10.0) was flowing. The oxidizing composition contained about 510 mg/L of hydrogen peroxide, about 4 mg/L of Fe and NTA at a concentration of four times higher than the concentration of Fe on a molar basis. The temperature of the medium was about 220C. The gas flow rate was about 3000 m3/h. Fe can be provided in various form such as FeSO4, FeCI2 or any suitable source of Fe2+. A reactor was disposed at the bottom of the column, and the oxidizing composition was recirculated from the reactor to a top portion of the column by means of a pump. The fluid was introduced at a bottom portion of the column in a counter-current manner.
[0052] Then, the gas is treated in a second packed column that also comprises an oxidizing composition comprising hydrogen peroxide. The
composition flowing in the second column was an acidic aqueous oxidizing composition (H2SO4) having a pH of about 2.2. The oxidizing composition contained about 2360 mg/L of hydrogen peroxide, and about 50 mg/L of Fe. The temperature of the medium was about 23°C. The gas flow rate was about 3.6 m3/h.
[0053] These conditions were maintained for 19 days and five dynamic olfactometry analyses were carried out. The results were the following (average values):
odor level at the inlet: 131 ;
odor level after 1st treatment: 69;
effectiveness after 1 st treatment: 47%;
odor level after 2nd treatment: 36; and
effectiveness after 2nd treatment: 73%.
Example 2: treatment by oxidation and absorption in a basic medium and adsorption onto activated carbon.
[0054] In the present example, a gas similar to the one treated in example 1 was treated by using a similar set-up. Fig. 2 is a bloc diagram concerning the method carried out in Example 2.
[0055] The gas was treated by passing it through a packed column in which a basic aqueous oxidizing composition (comprising H2O2 and NaOH and having a pH of about 9.8) was flowing. The oxidizing composition contained about 75 mg/L of hydrogen peroxide, about 2 mg/L of Fe and NTA at a concentration of four times higher than the concentration of Fe on a molar basis. The temperature of the medium was about 210C. The gas flow rate was about 2040 m3/h.
[0056] Subsequently, the gas was treated by passing it through a bed of activated carbon. The temperature of the gas was about 24°C at a gas flow rate of about 3 m3/h. The height of the activated carbon was about 180 mm.
[0057] These operating conditions were maintained for 5 days and 8 olfactometry measurements were taken. The results are the following:
odor level at the inlet: 155;
odor level after 1st treatment: 70;
effectiveness after 1st treatment: 55%;
odor level after 2nd treatment: 5; and
effectiveness after 2nd treatment: 97%.
Example 3 : Treatment by oxidation and absorption in a basic media and then, in an acidic media in which oxidation is enhanced by UV radiation.
[0058] In the present example, a gas similar to the one in example 1 was treated by using a similar set-up. Fig. 3 is a bloc diagram concerning the method carried out in example 3.
[0059] The gas was treated by passing it through a packed column in which a basic aqueous oxidizing composition (comprising H2O2 and NaOH and having a pH of about 9.8) was flowing. The oxidizing composition contained about 300 mg/L of hydrogen peroxide, about 2 mg/L of Fe and NTA at a concentration of four times higher than the concentration of Fe on a molar basis. The temperature of the medium was about 22 0C. The gas was at a temperature of about 50 0C and a flow of 80 L/min.
[0060] Then, the gas was treated in a second packed column that also contained an oxidizing composition comprising hydrogen peroxide. The composition flowing in the second column was an acidic aqueous oxidizing composition (HNO3) having a pH of about 2.4. The oxidizing composition
contained about 350 mg/L of hydrogen peroxide, about 30 mg/L of Fe and oxalic acid at was concentration of four times higher than the concentration of Fe on a molar basis. The temperature of the medium was about 22 0C. The gas flow was about 80 L/min.
[0061] As explained in example 1, the mixture of the gas and the composition was flowing down from the packed column to a reactor. In Example 3, the mixture of the fluid and the composition in the reactor were submitted to UV radiation in order to enhance the oxidation rate of the organic compounds that cause the unpleasant and/or undesirable odor. The UV radiation was produced by a 254 nm lamp at a power of 9 Watts. After a predetermined residence time in the reactor, the mixture is recirculated to the top of the packed column to complete the loop.
[0062] These operating conditions were reapeated over more than 30 tests. Each test was carried out over a period of time of about 8 to about 12 hours. The same amount of olfactometry measurements were taken. The results were the following:
• odor level at the inlet : 386
• odor level after 1st treatment : 127
• effectiveness after 1 st treatment : 66 %
• odor level after 2nd treatment : 50
• effectiveness after 2nd treatment : 86 %
[0063] It can thus be seen that the results presented in examples 1 to 3 clearly show that these three different methods permit to considerably reduce the intensity (or odor level) of the undesirable odor. It can thus be the that such methods permit to efficiently at least partially reduce the intensity or an undesirable or unpleasant odor.
[0064] The methods have been described with regard to specific examples. The description as much as the drawings were intended to help the understanding of the document, rather than to limit its scope. It will be apparent to one skilled in the art that various modifications may be made to the methods previously defined without departing from the scope of the document as described herein, and such modifications are intended to be covered by the present document.
Claims
1. A method for treating a fluid having an undesirable odor, said method comprising :
contacting said fluid with a basic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2; and
contacting said fluid with an acidic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2,
said fluid being contacted with said basic aqueous oxidizing composition, and then said fluid being contacted with said acidic aqueous oxidizing composition; or
said fluid being contacted with said acidic aqueous oxidizing composition, and then said fluid being contacted with said basic aqueous oxidizing composition.
2. The method of claim 1 wherein, said fluid is treated with said basic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for said undesirable odor and then said fluid is treated with said acidic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for said undesirable odor, thereby at least partially reducing intensity of said undesirable odor.
3. The method of claim 1 wherein, said fluid is treated with said acidic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for said undesirable odor and then said fluid is treated with said basic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for said undesirable odor, thereby at least partially reducing intensity of said undesirable odor.
4. The method of any one of claims 1 to 3, wherein said basic aqueous oxidizing composition comprises a base chosen from NaOH, KOH, Mg(OH)2, Ca(OH)2, NaHCO3, Na2CO3, K2CO3, KHCO3, and mixtures thereof.
5. The method of claim 4, wherein said base is NaOH.
6. The method of any one of claims 1 to 5, wherein basic aqueous oxidizing composition has a pH of at least 9.0.
7. The method of any one of claims 1 to 5, wherein said basic aqueous oxidizing composition has a pH of about 9.3 to about 11.5.
8. The method of any one of claims 1 to 5, wherein said basic aqueous oxidizing composition has a pH of about 9.5 to about 10.5.
9. The method of any one of claims 1 to 5, wherein said basic aqueous oxidizing composition has a pH of about 9.7 to about 10.0.
10. The method of any one of claims 1 to 5, wherein said basic aqueous oxidizing composition has a pH of about 9.8.
11. The method of any one of claims 1 to 10, wherein said basic aqueous oxidizing composition further comprises a sequestering agent.
12. The method of claim 11 , wherein said sequestering agent is chosen from diethylenetriaminepentaacetic acid (DTPA), nitrolotriacetic acid (NTA), ethylenediaminetetraacetic acid (EDTA), sodium hexametaphosphate, sodium citrate, and mixtures thereof.
13. The method of claim 12, wherein said sequestering agent is NTA.
14. The method of claim 12, wherein said sequestering agent is DTPA.
15. The method of claim 12, wherein said sequestering agent is NTA and said basic aqueous oxidizing composition comprises Fe2+.
16. The method of any one of claims 11 to 15, wherein said sequestering agent is present in said basic aqueous oxidizing composition at a concentration of at least 30 mg/L.
17. The method of any one of claims 11 to 15, wherein said sequestering agent is present in said basic aqueous oxidizing composition at a concentration of about 30 mg/L to about 480 mg/L.
18. The method of any one of claims 11 to 15, wherein said sequestering agent is present in said basic aqueous oxidizing composition at a concentration of about 60 mg/L to about 240 mg/L.
19. The method of any one of claims 1 to 12, wherein said basic aqueous oxidizing composition comprises Fe2+, Cu2+, or mixtures thereof.
20. The method of any one of claims 1 to 12, wherein said basic aqueous oxidizing composition comprises Fe2+.
21. The method of any one of claims 1 to 12, wherein said basic aqueous oxidizing composition comprises Fe2+ at a concentration of at least 1 mg/L.
22. The method of any one of claims 1 to 12, wherein said basic aqueous oxidizing composition comprises Fe2+ at a concentration of about 1 mg/L to about 20 mg/L.
23. The method of any one of claims 1 to 12, wherein said basic aqueous oxidizing composition comprises Fe2+ at a concentration of about 2 mg/L to about 10 mg/L.
24. The method of any one of claims 1 to 23, wherein H2O2 is present in said basic aqueous oxidizing composition at a concentration of at least 20 mg/L.
25. The method of any one of claims 1 to 23, wherein H2O2 is present in said basic aqueous oxidizing composition at a concentration of about 20 mg/L to about 2000 mg/L.
26. The method of any one of claims 1 to 23, wherein H2O2 is present in said basic aqueous oxidizing composition at a concentration of about 50 mg/L to about 700 mg/L.
27. The method of any one of claims 1 to 26, wherein said contacting includes mixing said fluid with said basic aqueous oxidizing composition so as to at least partially dissolve at least one compound contained in said fluid into said basic aqueous oxidizing composition.
28. The method of any one of claims 1 to 27, wherein said fluid and said basic aqueous oxidizing composition are mixed together in a packed column.
29. The method of claim 28, wherein said fluid is introduced at a bottom portion of said column and said basic aqueous oxidizing composition is introduced at a top portion of said column, said fluid and the basic aqueous oxidizing composition being mixed together into said column over a predetermined amount of transfer units.
30. The method of any one of claims 1 to 29, wherein said fluid, before contacting the basic aqueous oxidizing composition, is at a temperature of about 1O0C to about 85°C.
31. The method of any one of claims 1 to 29, wherein said fluid, before contacting the basic aqueous oxidizing composition, is at a temperature of about 15°C to about 40°C.
32. The method of any one of claims 1 to 31 , wherein said acidic aqueous oxidizing composition comprises an acid chosen from H2SO4, HCI, HNO3, H3PO4, and mixtures thereof.
33. The method of claim 32, wherein said acid is H2SO4.
34. The method of any one of claims 1 to 33, wherein said acidic aqueous oxidizing composition has a pH of at least 1.5.
35. The method of any one of claims 1 to 33, wherein said acidic aqueous oxidizing composition has a pH of about 1.5 to about 4.0.
36. The method of any one of claims 1 to 33, wherein said acidic aqueous oxidizing composition has a pH of about 2.0 to about 3.0.
37. The method of any one of claims 1 to 33, wherein said acidic aqueous oxidizing composition has a pH of about 2.2 to about 2.6.
38. The method of any one of claims 1 to 37, wherein said acidic aqueous oxidizing composition further comprises a sequestering agent.
39. The method of claim 38, wherein said sequestering agent is chosen from ethylenediaminetetraacetic acid (EDTA), oxalic acid, citric acid, glycine, NTA, salicylic acid, sulfosalicylic acid, trithylenetetramine, and mixtures thereof.
40. The method of claim 38, wherein said sequestering agent is oxalic acid.
41. The method of any one of claims 1 to 40, wherein said acidic aqueous oxidizing composition comprises Fe2+, Cu2+, or mixtures thereof.
42. The method of any one of claims 1 to 40, wherein said acidic aqueous oxidizing composition comprises Fe2+.
43. The method of any one of claims 1 to 40, wherein said acidic aqueous oxidizing composition comprises Fe2+ at a concentration of at least 5 mg/L.
44. The method of any one of claims 1 to 40, wherein said acidic aqueous oxidizing composition comprises Fe2+ at a concentration of at least 10 mg/L.
45. The method of any one of claims 1 to 40, wherein said acidic aqueous oxidizing composition comprises Fe2+ at a concentration of at least 20 mg/L.
46. The method of any one of claims 1 to 40, wherein said acidic aqueous oxidizing composition comprises Fe2+ at a concentration of about 10 mg/L to about 200 mg/L.
47. The method of any one of claims 1 to 40, wherein said acidic aqueous oxidizing composition comprises Fe2+ at a concentration of about 20 mg/L to about 100 mg/L.
48. The method of any one of claims 1 to 40, wherein said acidic aqueous oxidizing composition comprises Fe2+ at a concentration of about 30 mg/L to about 50 mg/L.
49. The method of any one of claims 1 to 48, wherein H2O2 is present in said acidic aqueous oxidizing composition at a molar ratio H2O2 : metal is at least 5:1 .
50. The method of any one of claims 1 to 48, wherein H2O2 is present in said acidic aqueous oxidizing composition at a molar ratio H2O2 : metal is at least 10:1 .
51. The method of any one of claims 1 to 48, wherein H2O2 is present in said acidic aqueous oxidizing composition at a molar ratio H2O2 : metal of about 10: 1 to about 100: 1.
52. The method of any one of claims 1 to 48, wherein H2O2 is present in said acidic aqueous oxidizing composition at a molar ratio H2O2 : metal of about 12:1 to 40:1.
53. The method of any one of claims 1 to 52, wherein said acidic aqueous oxidizing composition comprises Fe2+, Cu2+, or mixtures thereof.
54. The method of any one of claims 1 to 50, wherein said acidic aqueous oxidizing composition comprises Fe2+.
55. The method of any one of claims 1 to 54, wherein said fluid, before contacting said acidic aqueous oxidizing composition, is at a temperature of about 100C to about 85°C.
56. The method of any one of claims 1 to 54, wherein said fluid, before contacting said acidic aqueous oxidizing composition, is at a temperature of about 15°C to about 400C.
57. The method of any one of claims 1 to 54, wherein said fluid, before contacting said acidic aqueous oxidizing composition, is at a temperature of about 25°C to about 550C.
58. The method of any one of claims 1 to 57, wherein said contacting includes mixing said fluid with said acidic oxidizing composition so as to at least partially dissolve at least one compound contained in said fluid into said acidic oxidizing composition.
59. The method of any one of claims 1 to 58, wherein said fluid and said acidic oxidizing composition are mixed together in a packed column.
60. The method of claim 59, wherein said fluid is introduced at a bottom portion of said column and said acidic aqueous composition is introduced at a top portion of said column, said fluid and said acidic aqueous composition being mixed together into said column over a predetermined amount of transfer units.
61. The method of any one of claims 1 to 60, wherein said fluid comprises at least one organic compound chosen from carboxylic acids, thiols, thioethers, disulfides, alcohols, aldehydes, amines, amides and mixtures thereof.
62. The method of claim 61 , wherein said carboxylic acids comprises C1-C20 carboxylic acids, said thiols comprise C1-C20 thiols, said thioethers comprise C2-C20 thioethers, said disulfides comprise C2-C20 disulfides, said alcohols comprise C1-C20 alcohols, said aldehydes comprise C1-C20 aldehydes, said amines comprise C1-C20 amines, and said amides comprise C1-C20 amides.
63. The method of any one of claims 1 to 62, further comprising contacting said fluid with activated carbon.
64. The method of claim 63, wherein said fluid is passed through a bed of activated carbon.
65. The method of any one of claims 1 to 64, further comprising submitting said fluid and said acidic aqueous oxidizing composition to UV radiation, when said fluid and said acidic aqueous oxidizing composition are contacting each other.
66. The method of any one of claims 1 to 64, further comprising submitting said fluid and said basic aqueous oxidizing composition to UV radiation, when said fluid and said basic aqueous oxidizing composition are contacting each other.
67. The method of any one of claims 1 to 64, wherein said fluid is contacted with said acidic aqueous oxidizing composition so as to at least partially dissolve at least one compound responsible for said undesirable odor and contained in said fluid into said acidic aqueous oxidizing composition and wherein said method further comprises submitting, said at least one compound that is at least partially dissolved into said acidic aqueous oxidizing composition, to UV radiation.
68. The method of any one of claims 1 to 64, wherein said fluid is contacted with said basic aqueous oxidizing composition so as to at least partially dissolve at least one compound responsible for said undesirable odor and contained in said fluid into said basic aqueous oxidizing composition and wherein said method further comprise submitting, said at least one compound that is at least partially dissolved into said basic aqueous oxidizing composition, to UV radiation.
69. A method for treating a fluid having an undesirable odor, said method comprising :
contacting said fluid with an acidic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2; and submitting said fluid and said composition to UV radiation when said fluid and said composition are contacting each other.
70. The method of claim 69, wherein said fluid is contacted with said acidic aqueous oxidizing composition so as to at least partially dissolve at least one compound responsible for said odor and contained in said fluid into said acidic aqueous oxidizing composition and said at least one compound that is at least partially dissolved into said acidic aqueous oxidizing composition is submitted to UV radiation so as to at least partially oxidize said at least one compound and at least partially reduce intensity of said odor.
71. A method for treating a fluid having an undesirable odor, said method comprising :
contacting said fluid with a basic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2; and/or contacting said fluid with an acidic aqueous oxidizing composition comprising at least one cation of a metal chosen from Fe, Cu, Ni, Mn, Ti, Cr, Ce, Zn, Pd, Mo, and mixtures thereof and H2O2; and
contacting said fluid with activated carbon.
72. The method of claim 71 wherein, said fluid is treated with said basic aqueous oxidizing composition and/or with said acidic aqueous oxidizing composition so as to at least partially oxidize at least one compound responsible for said undesirable odor and then said fluid is passed through a bed of activated carbon, thereby at least partially reducing intensity of said undesirable odor.
73. The method of claim 71 or 72 wherein, said fluid is treated with said basic aqueous oxidizing composition and then with said acidic aqueous oxidizing composition.
74. The method of claim 71 or 72 wherein, said fluid is treated with said acidic aqueous oxidizing composition and then with said basic aqueous oxidizing composition.
75. The method of claim 71 or 72 wherein, said method essentially consists in treating said fluid with said basic aqueous oxidizing composition and then treating said fluid with activated carbon.
76. The method of claim 71, wherein said fluid is passed through a bed of activated carbon.
77. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by at least 50 % intensity of said undesirable odor.
78. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by at least 60 % intensity of said undesirable odor.
79. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by at least 70 % intensity of said undesirable odor.
80. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by at least 80 % intensity of said undesirable odor.
81. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by at least 85 % intensity of said undesirable odor.
82. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by at least 90 % intensity of said undesirable odor.
83. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by at least 95 % intensity of said undesirable odor.
84. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by about 50 % to about 99 % intensity of said undesirable odor.
85. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by about 60 % to about 99 % intensity of said undesirable odor.
86. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by about 70 % to about 97 % intensity of said undesirable odor.
87. The method of any one of claims 1 to 76, wherein said treatment permits to reduce by about 70 % to about 99 % intensity of said undesirable odor.
88. The method of any one of claims 1 to 76, wherein said fluid is a gas.
89. The method of any one of claims 1 to 76, wherein said fluid is a liquid.
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP2419196A1 (en) * | 2009-04-14 | 2012-02-22 | Uniboard Canada Inc | Process for reducing the content of water soluble volatile organic compounds in a gas |
CN115520952A (en) * | 2021-06-24 | 2022-12-27 | 中国石油化工股份有限公司 | Fenton oxidation treatment method for organic wastewater |
Families Citing this family (19)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20110189049A1 (en) | 2008-05-09 | 2011-08-04 | Martin Beaulieu | Method for treating odors |
WO2014004582A1 (en) * | 2012-06-28 | 2014-01-03 | Steen Research, Llc | Methods and equipment for treatment of odorous gas streams from industrial plants |
CA2898872C (en) | 2013-01-22 | 2019-04-09 | Steen Research, Llc | Methods and equipment for treatment of odorous gas streams |
CN105268425B (en) * | 2014-07-17 | 2018-08-24 | 中国科学院大连化学物理研究所 | A kind of modified active carbon catalyst and its preparation and application |
WO2018035165A1 (en) | 2016-08-15 | 2018-02-22 | Steen Research, Llc | Processes for removing a nitrogen-based compound from a gas or liquid stream to produce a nitrogen-based product |
US10239016B2 (en) | 2016-12-07 | 2019-03-26 | Nuorganics LLC | Systems and methods for nitrogen recovery from a gas stream |
MX2020011624A (en) | 2017-01-16 | 2020-12-07 | Nuorganics LLC | System and method for recovering nitrogenous compounds from a gas stream. |
CN108251844B (en) * | 2018-03-29 | 2020-03-10 | 山西银光华盛镁业股份有限公司 | Bright treatment liquid for magnesium alloy die castings |
CN109012094A (en) * | 2018-08-01 | 2018-12-18 | 福建皓尔宝新材料科技有限公司 | A kind of composition for administering gaseous acetaldehyde |
CN110115905A (en) * | 2019-03-04 | 2019-08-13 | 福建皓尔宝新材料科技有限公司 | A kind of ionic associate solution and sweep-out method for the online Indoor Air Benzene of removing in real time |
MX2022002382A (en) | 2019-08-28 | 2022-03-17 | Steen Res Llc | Methods for absorbing a targeted compound from a gas stream for subsequent processing or use. |
US11881093B2 (en) | 2020-08-20 | 2024-01-23 | Denso International America, Inc. | Systems and methods for identifying smoking in vehicles |
US12017506B2 (en) | 2020-08-20 | 2024-06-25 | Denso International America, Inc. | Passenger cabin air control systems and methods |
US11636870B2 (en) | 2020-08-20 | 2023-04-25 | Denso International America, Inc. | Smoking cessation systems and methods |
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US11828210B2 (en) | 2020-08-20 | 2023-11-28 | Denso International America, Inc. | Diagnostic systems and methods of vehicles using olfaction |
US11813926B2 (en) | 2020-08-20 | 2023-11-14 | Denso International America, Inc. | Binding agent and olfaction sensor |
US11760170B2 (en) | 2020-08-20 | 2023-09-19 | Denso International America, Inc. | Olfaction sensor preservation systems and methods |
US11932080B2 (en) | 2020-08-20 | 2024-03-19 | Denso International America, Inc. | Diagnostic and recirculation control systems and methods |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5348665A (en) * | 1991-11-22 | 1994-09-20 | Degussa Aktiengesellschaft | Method for the degradation of harmful substances in water by means of hydrogen peroxide under UV irradiation |
US6365099B1 (en) * | 1998-11-12 | 2002-04-02 | Fmc Corporation | In situ gas scrubbing method and system for odor and corrosion control in wastewater collection systems |
US20070059229A1 (en) * | 2000-03-03 | 2007-03-15 | Temple Stephen R | Method and apparatus for use of reacted hydrogen peroxide compounds in industrial process waters |
Family Cites Families (51)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4002711A (en) * | 1971-03-19 | 1977-01-11 | Peters Timothy V | Method for drawing polyurethane filaments |
JPS5144898B2 (en) * | 1974-03-16 | 1976-12-01 | ||
US4104162A (en) * | 1974-04-22 | 1978-08-01 | Deutsche Gold- Und Silber-Scheideanstalt Vormals Koessler | Process for detoxification of formaldehyde containing waste waters |
US4012321A (en) * | 1975-03-25 | 1977-03-15 | The United States Of America As Represented By The Secretary Of The Navy | Oxidation of refractory organics in aqueous waste streams by hydrogen peroxide and ultraviolet light |
DE2931692A1 (en) * | 1979-08-04 | 1981-02-26 | Basf Ag | METHOD FOR REMOVING FORMALDEHYDE FROM AQUEOUS SOLUTIONS OF 2-BUTINDIOL-1,4 |
FR2503130B1 (en) * | 1981-03-31 | 1985-10-31 | Interox | TREATMENT OF WATER AND EMISSION GAS CONTAINING SULPHIDIC ORGANIC COMPOUNDS |
US4446029A (en) * | 1982-09-22 | 1984-05-01 | Fmc Corporation | Destruction of iron cyanide complexes |
US4780287A (en) * | 1984-07-03 | 1988-10-25 | Ultrox International | Decomposition of volatile organic halogenated compounds contained in gases |
US5207877A (en) * | 1987-12-28 | 1993-05-04 | Electrocinerator Technologies, Inc. | Methods for purification of air |
US4880609A (en) * | 1988-11-23 | 1989-11-14 | Champion Chemicals, Inc. | Chelate catalyst system for H2 S removal from a gas stream |
US5043080A (en) * | 1990-02-26 | 1991-08-27 | Solarchem Enterprises Inc. | Treating contaminated effluents and groundwaters |
US5480524A (en) | 1991-12-21 | 1996-01-02 | Robert Aalbers | Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and brines |
KR940004118B1 (en) * | 1992-06-27 | 1994-05-13 | 아니코산업 주식회사 | Gas washing apparatus with multi-ejector |
US5266214A (en) | 1992-12-22 | 1993-11-30 | Cryptonics Corporation | Photocatalytic method for treatment of contaminated water |
US5762808A (en) | 1995-05-09 | 1998-06-09 | Research Corporation Technologies, Inc. | Destruction of electron affinic contaminants during water treatment using free radical processes |
CA2178258A1 (en) | 1995-06-06 | 1996-12-07 | Phillip A. Lincoln | Method and apparatus for removing volatile organic compounds by cold oxidation |
DE69620171T2 (en) * | 1995-06-06 | 2002-11-07 | Bp Corp. North America Inc. (N.D.Ges.D. Staates Indiana), Chicago | CATALYTIC EXHAUST GAS TREATMENT SYSTEM FOR CONTROLLING VOLATILE CHEMICAL EMISSIONS |
US6503471B1 (en) * | 1995-08-29 | 2003-01-07 | Korea Institute Of Science & Technology | Process for malodorous gas treatment |
FR2747924B1 (en) * | 1996-04-26 | 1998-07-24 | Deotech | FILTRATION DEVICE AND METHOD FOR NEUTRALIZING BAD ODORS |
CA2178377A1 (en) | 1996-06-06 | 1997-12-07 | Janis Avotins | Process and apparatus for the removal of aromatic amines from soil and water |
US5907066A (en) * | 1996-11-27 | 1999-05-25 | Lehigh University | Treating methanol-containing waste gas streams |
US6410793B1 (en) * | 1997-05-27 | 2002-06-25 | Lehigh University | Production of formaldehyde from carbon oxides and H2S |
US5914305A (en) | 1997-10-29 | 1999-06-22 | Lever Brothers Company, Division Of Conopco, Inc. | Peroxynitrite based bleaching systems |
GB9723258D0 (en) * | 1997-11-05 | 1998-01-07 | British Nuclear Fuels Plc | Treatment of organic materials |
US6541038B1 (en) * | 1997-11-26 | 2003-04-01 | Sds Biotech K.K. | Method for treating wood with a metal-containing treating agent and wood treated thereby |
AR014299A1 (en) * | 1998-01-14 | 2001-02-07 | Ecolab Inc | A PROCEDURE FOR REMOVING A ODOR FROM AN ATMOSPHERIC EFFLUENT, A PRIOR TREATMENT OR A AFTER TREATMENT TO REMOVE A ODOR FROM AN ATMOSPHERIC EFFLUENT AND ATMOSPHERIC EFFLUENT OBTAINED WITH SUCH PROCEDURE. |
WO1999036160A1 (en) | 1998-01-14 | 1999-07-22 | Ecolab Inc. | Peroxyacid compound use in odor reduction |
DE19823155A1 (en) * | 1998-05-23 | 1999-11-25 | Henkel Kgaa | Process to reduce the free formaldehyde content of aqueous acidic melamine-formaldehyde solutions |
CA2344339A1 (en) | 1998-09-16 | 2000-03-23 | James K. Jeanblanc | Desulfurization process |
US6497795B1 (en) * | 1998-12-16 | 2002-12-24 | Canon Kabushiki Kaisha | Method and apparatus for decomposing gaseous aliphatic hydrocarbon halide compound |
JP4095737B2 (en) * | 1999-03-29 | 2008-06-04 | 日本エア・リキード株式会社 | Cleaning dust collector and exhaust gas treatment facility |
AU6476000A (en) | 1999-08-13 | 2001-03-13 | Kirin Beer Kabushiki Kaisha | Mouse having human cytochrome p450 transferred therein |
AU2001245416A1 (en) | 2000-03-03 | 2001-09-17 | Steen Research, Llc | Method and apparatus for use of reacted hydrogen peroxide compounds in industrial process waters |
US6774277B2 (en) * | 2000-03-07 | 2004-08-10 | Waste Management, Inc. | Methods of destruction of cyanide in cyanide-containing waste |
US6315963B1 (en) | 2000-03-22 | 2001-11-13 | Samuel E. Speer | Method and apparatus for the enhanced treatment of fluids via photolytic and photocatalytic reactions |
US6518477B2 (en) * | 2000-06-09 | 2003-02-11 | Hanford Nuclear Services, Inc. | Simplified integrated immobilization process for the remediation of radioactive waste |
US7022297B2 (en) | 2000-07-24 | 2006-04-04 | Shawn Alan Stewart | Method and system for purifying or cleansing a gas stream or gaseous body |
US6402940B1 (en) * | 2000-09-01 | 2002-06-11 | Unipure Corporation | Process for removing low amounts of organic sulfur from hydrocarbon fuels |
WO2002022541A2 (en) * | 2000-09-14 | 2002-03-21 | Georgia Pacific Corporation | Vanadia-titania/metal-molybdate dual catalyst bed system and process using the same for methanol oxidation to formaldehyde |
US6770174B1 (en) * | 2002-03-14 | 2004-08-03 | Air Control Techniques, P.C. | Photochemical system and method for removal for formaldehyde from industrial process emissions |
US6531634B1 (en) * | 2001-06-29 | 2003-03-11 | Peter Zhu | Non-hazardous oxidative neutralization of aldehydes |
US20040062697A1 (en) | 2002-10-01 | 2004-04-01 | Airborne Pollution Control Inc. | Flue gas purification method |
US20050178733A1 (en) | 2003-12-30 | 2005-08-18 | Conger Harry C. | Sub-critical oxidative processes |
US6977049B2 (en) * | 2003-12-31 | 2005-12-20 | The Boc Group, Inc. | Treatment process for industrial waste stream |
US7135449B2 (en) * | 2004-02-20 | 2006-11-14 | Milliken & Company | Composition for removal of odors and contaminants from textiles and method |
EP1609886B1 (en) | 2004-06-11 | 2007-05-02 | Matgas 2000, AIE | Process for the production of hydrogen |
US7304187B2 (en) * | 2005-10-07 | 2007-12-04 | Groupe Conseil Procd Inc. | Process for reducing the formaldehyde content of a gas |
PL1931450T3 (en) | 2005-10-07 | 2014-09-30 | Exp Services Inc | Process for reducing the formaldehyde content of a gas |
US20070179072A1 (en) * | 2006-01-30 | 2007-08-02 | Rao Madhukar B | Cleaning formulations |
US20110189049A1 (en) | 2008-05-09 | 2011-08-04 | Martin Beaulieu | Method for treating odors |
PL2419196T3 (en) * | 2009-04-14 | 2018-01-31 | Uniboard Canada Inc | Process for reducing the content of water soluble volatile organic compounds in a gas |
-
2008
- 2008-05-09 US US12/989,155 patent/US20110189049A1/en not_active Abandoned
-
2009
- 2009-05-08 EP EP09741637A patent/EP2282826A4/en not_active Ceased
- 2009-05-08 CA CA2721684A patent/CA2721684C/en active Active
- 2009-05-08 CA CA2767544A patent/CA2767544C/en active Active
- 2009-05-08 WO PCT/CA2009/000641 patent/WO2009135319A1/en active Application Filing
-
2015
- 2015-08-26 US US14/836,757 patent/US9522206B2/en active Active
-
2016
- 2016-11-09 US US15/347,332 patent/US20170056821A1/en not_active Abandoned
-
2019
- 2019-02-01 US US16/264,778 patent/US20190160425A1/en not_active Abandoned
-
2022
- 2022-05-13 US US17/743,611 patent/US11964234B2/en active Active
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5348665A (en) * | 1991-11-22 | 1994-09-20 | Degussa Aktiengesellschaft | Method for the degradation of harmful substances in water by means of hydrogen peroxide under UV irradiation |
US6365099B1 (en) * | 1998-11-12 | 2002-04-02 | Fmc Corporation | In situ gas scrubbing method and system for odor and corrosion control in wastewater collection systems |
US20070059229A1 (en) * | 2000-03-03 | 2007-03-15 | Temple Stephen R | Method and apparatus for use of reacted hydrogen peroxide compounds in industrial process waters |
Non-Patent Citations (1)
Title |
---|
See also references of EP2282826A4 * |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP2419196A1 (en) * | 2009-04-14 | 2012-02-22 | Uniboard Canada Inc | Process for reducing the content of water soluble volatile organic compounds in a gas |
EP2419196A4 (en) * | 2009-04-14 | 2013-01-09 | Uniboard Canada Inc | Process for reducing the content of water soluble volatile organic compounds in a gas |
CN115520952A (en) * | 2021-06-24 | 2022-12-27 | 中国石油化工股份有限公司 | Fenton oxidation treatment method for organic wastewater |
Also Published As
Publication number | Publication date |
---|---|
EP2282826A4 (en) | 2012-12-05 |
EP2282826A1 (en) | 2011-02-16 |
US20150359917A1 (en) | 2015-12-17 |
US20170056821A1 (en) | 2017-03-02 |
US20220323903A1 (en) | 2022-10-13 |
CA2721684C (en) | 2012-04-24 |
US11964234B2 (en) | 2024-04-23 |
US20110189049A1 (en) | 2011-08-04 |
CA2767544C (en) | 2013-10-29 |
US9522206B2 (en) | 2016-12-20 |
US20190160425A1 (en) | 2019-05-30 |
CA2721684A1 (en) | 2009-11-12 |
CA2767544A1 (en) | 2009-11-12 |
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